Water Quality Criteria Data Book: Volume 5 - Effects of Chemicals on Aquatic Life (Compilation From the Literature Dated 1968-1972)

'tf \ o WATER POLLUTION CONTROL RESEARCH SERIES 18O50HLA O9/73 WATER QUALITY CRITERIA DATA BOOK VOLUME 5 EFFECTS OF CHEMICALS ON AQUATIC LIFE U.S. ENVIRONMENTAL PROTECTION AGENCY ------- WATER QUALITY CRITERIA DATA BOOK - VOL. 5 EFFECTS OF CHEMICALS ON AQUATIC LIFE (Compilation From the Literature Dated 1968-1972) Homer T. Kemp Robert L. Little Verna L. Holoman and Ralph L. Darby Grant Number R-8009^2 Project Number 18050 HLA Project Officer Robert Andrew U.S. Environmental Protection Agency National Water Quality Laboratory Duluth, Minnesota 55&OU for the OFFICE OF RESEARCH AND DEVELOPMENT U.S. Environmental Protection Agency Washington, D.C. 20U60 September 1973 For ttte by the Superintendent of Document. U.S. Government Printing Office, Washington, D.C. 20402 ------- EPA REVIEW NOTICE This report has been reviewed by the Office of Research and Development, EPA, and approved for publication. Approval does not signify that the contents necessarily reflect the views and policies of the Environmental Protection Agency, nor does mention of trade names or commercial products constitute endorsement or recommendation for use. ii ------- ABSTRACT This report is an extensive compilation of data on the effects of chemicals on aquatic life which were extracted from literature published during the period 1968-1972. It is an update of an earlier report entitled "Water Quality Criteria Data Book, Volume III, Effects of Chemicals on Aquatic Life" (Kemp, et al., 1971). The data are arranged alphabetically by chemical and are concisely presented in a columnar format which includes organism names, type of study, chemical effect, controlled parameters, significant comments on the test, and source of the data. The data were compiled using a program prepared as part of the work. iii ------- CONTENTS Section Page I Recommendations 1 II Introduction 3 III Procedure 5 IV Acknowledgements 9 V References 11 VI Appendices A, Chemical Names A-l B. Species Index B-l C. Chemical Index C-l iv ------- SECTION I RECOMMENDATIONS In a prior report (Water Quality Criteria Data Book, Volume III. Effects of Chemicals on Aquatic Life, Kemp, H. T., Abrams, J. P., Overbeck, R. C., EPA Contract No. 68-01-0007, Project No. 18050 GWV, 1971, 528 pp), several recommendations were presented. These are restated as follows with any appropriate comments. (l) Establishment of a Chemical Pollution Effect Information Analysis Center.The Analytical Methodology Information Center (AMIC) sponsored by EPA at Battelle's Columbus Laboratories fills this need. (2) Preparation of Listings of Chemical Constituents in Effluents by Cooperative Input From Industry". To the authors' knowledge this has not been done nor is there a current attempt to do so. (3) Development of a Standard Pattern of Laboratory Evaluations for Estimating More Accurately the Effect of Chemicals on Aquatic Life.To the authors' knowledge no standard pattern of laboratory evaluations is widely accepted. Considerable progress has been made recently, however, in particular at the National Water Quality Laboratory (Duluth, Minnesota) and Virginia Polytechnic Institute. Significant efforts to compile bioassay information are in progress by Drs. Seba, Stephans, Tarzwell, and Weber, respectively, located at EPA establishments at Denver (Colo.), Duluth (Minn.), West Kingston (R.I.), and Cincinnati (Ohio). The classic report by McKee and Wolf (1963) is reportedly now being updated. (U) Development of In Situ Field Bipassay Procedures for More Realistic Results Than Those Obtained in Laboratory Bioassays.Although increased publication of these types of data are apparent, there appears to be no large-scale trend in the published literature toward this approach. (5) Improved Reporting Would Greatly Enhance the Utility of Chemical Effects Data and Allow More Precise Development of Multiyariate" Analysis and Mathematical Modeling.There is a large volume of literature on mathematical modeling, a significant amount of which is concerned with environmental pollution problems. For the most part, these models are not refined enough for practical utility in water pollution problems. Improved, more detailed data would assist greatly in verifying these models and enhancing their practical utility. The next few years will be crucial in this development. ------- SECTION II INTRODUCTION This report was prepared to update the document, "Water Quality Criteria Book, Volume 3", published in May, 1971 (Kemp, et al., 1971). This updated version primarily contains extracted information from original published data, but does not critically review bioassay procedures, factors affecting chemical toxicity, and other subject areas important in the study of water pollution by chemicals. ------- SECTION III PROCEDURE The literature search technique primarily involved acquisition of docu- ments cited in selected sections of annual reviews published in the Journal of the Water Pollution Control Federation, for the years 1968-1972. These listings were quite comprehensive, but were supplemented by addi- tional documents identified in routine screening activities of the Analytical Methodology Information Center (AMIC), Battelle's Columbus Laboratories. The data were prepared on punched paper tape so that the compilation could be prepared by computer. In addition, the format of the data is such that they can be loaded in the Analytical Methodology Information Center data base. Since index terms were added to each line of data, they can be remotely searched on an on-line real-time computer system located at Battelle's Columbus Laboratories. Persons interested in having access to this system should contact the AMIC Project Officer: Mr. Luther E. Garrett Data & Information Research Division Office of Research & Development Environmental Protection Agency UoU M Street, S.W. Washington, D.C. 2002^ As in the earlier document, extracted data are alphabetically arranged by chemical name (Appendix A). In all cases, chemical names and names (common or scientific) of organisms designated by the authors were used in this report. Nomenclature was not changed or corrected in any manner, that is, when the common name of a fish or a chemical was cited by an author, this and this alone was used. Therefore, in using these data compilations, care should be exercised by the reader to search chemical and biological synonomy. For example, in Appendix B, Species Index, data searches on bluegills (Page B-2) should include the scienti- fic name, Lepomis macrochirus (page B-6) for completeness. Likewise trade names such as Sevin and Carbaryl should be searched for all data on this insecticide. In the authors' Judgment, the most significant toxicity levels in the aquatic studies are those for fish specifically designated 96-hr TLjQ. These were usually selected but other values were included when these were not available. 96-hr TLm is designated as TU to abbreviate this notation. T2 was used for U8-hr TLm, and so on. When £050, LC5Q, and LD50 were Judged to be essentially equivalent to TLjn or TL5Q» then the designation T was used to improve the consistency of data presentation. The authors acknowledge that this is not standard practice and that there may be important differences in these designations. ------- Experimental conditions noted by authors in column six are denoted in lower case letters (see page A-l) with asterisks to indicate when condi- tions vere controlled. In some cases, authors briefly referred to previ- ous publications as a simple means of describing experimental conditions. No asterisks were included in these instances although some conditions were probably controlled. The letters in footnote k were augmented so that additional conditions could be indicated. These were light (q) (r) and (s). Comments in general are brief, and it is recommended that interested readers consult the original document for more complete information. The chemical nature of most industrial effluents is very complex and difficult to characterize. Although increased numbers of publications on this type of pollution problem are being published, there is no highly satisfactory technique to include these data in the tabular format used here. For these reasons, this document must be described as primarily containing data on the effect of single chemicals or simple mixtures of chemicals on aquatic life. There was no attempt to extract data from the various reviews available since these rarely contained descriptive information concerning experi- mental conditions. Furthermore, only selective data are usually discussed. In the earlier report, more than 83 review papers were cited. To these can be added: Becker, C. D., Thatcher, T. 0., "Toxicity of Power Plant Chemicals to Aquatic Life", Battelle Memorial Institute, Pacific Northwest Laboratories. Richland, Washington, Report Nos. WASH-1214-9, UC-11, June 1973, 2k& pp. AMIC-9135. Boccardy, J. A., Spaulding, W. M., Jr., "Effects of Surface Mining on Fish and Wildlife in Appalachia", Bureau of Sport Fisheries and Wildlife, Publication No. 65, 1968. AMIC-6389. Hunt, E. G., Keith, J. 0., "Pesticide Analysis in Fish and Wildlife", Analytical Methods for Pesticides, Plant Growth Regulators, and Food Additives, Vol. 5. 1907, p 147.AMIC-5758. Johnson, D. W., "Pesticides and Fishes - a Review of Selected Literature", Transactions of the American Fisheries Society, Vol. 97 1968, pp 39852T;AMIC-5^63. Jones, A. N., Howells, W. R., "Recovery of the River Rheidol", Effluent Water Treatment Journal, Vol. 9, 1969, pp 605-610. AMIC-5752. Seagran, H. L., "Mercury in Great Lakes Fish", Limnos, Vol. 3 No. 2, Summer 1970, pp 3-10. AMIC-153. Sprague, J. B., "Measurement of Pollutant Toxicity to Fish. I. Bioassay Methods for Acute Toxicity", Water Research, Vol. 3, 1969, PP 793-821. AMIC-137. ------- Sprague, J. B., "Measurement of Pollutant Toxicity to Fish. II. Utilizing and Applying Bioassay Results", Water Research, Vol. k, 1970, pp 3-32. AMIC-358. Swabey, Y. H., "The Autopsy of Fish Collected in Fish Kills", The Ontario Water Resources Commission, Canada, Publication No. 11. 1966, 19 PP. Not reviewed in this report are bioassay procedures, field assessment techniques, and related topics. A number of recent documents would be useful for this purpose, including: Bell, M. C., "Fisheries Handbook of Engineering Requirements and Biological Criteria", Fisheries-Engineering Research Program, Corps of Engineers, North Pacific Div., Portland, Oregon, Contract No. DACW57-68-C-0086, 1973, 508 pp. Cairns, J., Dickson, K. L., "Biological Methods for the Assessment of Water Quality", ASTM Special Technical Publication No. 528, 1973, 262 pp. Dills, G. G., Rogers, D. T., "Aquatic Community Structure as an Indicator of Pollution", Geological Survey of Alabama, Circular 80, 1972, 25 pp. Smith, L. S., Saddler, J. B., Cardwell, R. C., et al., "Responses of Teleost Fish to Environmental Stress", University of Washington, Fisheries Research Institute, Seattle, Washington, EPA Grant No. 18050EBK, 1971, 11^ pp. One report by McPhee and Ruelle (1969) was received too late to include in this compilation. In it are summarized toxicity data for 1888 chemicals against five fish species in a piscicide screening program. It was previously suggested that ecological investigators be encouraged to include in their reports: • Positive identity of chemicals under test • Precise description of test organisms • Use of standard test or field methods, where applicable, or of procedures if standard methods are not used • Closer definition and control of test conditions Although papers have generally improved in these regards, not all investigators include all desirable details of their experimentation. A species index is included as Appendix B. Appendix C is a list of commercial chemicals cited in the data section (Appendix A) and includes, when available, the chemical nature of the compound. ------- SECTION IV ACKNOWLEDGEMENTS The authors wish to express their appreciation to the Project Officer, Mr. Robert Andrew, for his assistance and concern for this work. Homer T. Kemp Robert L. Little Verna L. Holoman Ralph L. Darby ------- REFERENCES Abedi, Z. H., McKinley, W. P. "ZEBRA FISH EGGS AND LARVAE AS AFLATOXIN BIOASSAY TEST ORGANISMS", Journal of the Association of Official Analytical Chemists, Vol. 51, No. U, 1968, pp 902-905. AMIC-3712. Abedi, Z. H., Turton, D. E. "NOTE ON THE RESPONSE OF ZEBRA FISH LARVAE TO FOLPET AND DIFOLATAN", Journal of the Association of Official Analytical Chemists, Vol. 51, No. 5, 1968, pp 1105-1109. AMIC-3717. Adelman, I. R., Smith, L. L., Jr. "EFFECT OF HYDROGEN SULFIDE ON NORTHERN PIKE EGGS AND SAC FRY", Transactions of the American Fisheries Society, Vol. 99, No. 3, 1970, pp 501-509.AMIC-5516. Alabaster, J. S. "SURVIVAL OF FISH IN l6U HERBICIDES, INSECTICIDES, FUNGICIDES, WETTING AGENTS AND MISCELLANEOUS SUBSTANCES", International Pest Control, torch/ April 1969, PP 29-35. AMIC-5U25. Anderson, J. M. "EFFECT OF SUBLETHAL DDT ON THE LATERAL LINE OF BROOK TROUT, SALVELINUS FONTINALIS", Journal of the Fisheries Research Board of Canada, Vol. 25, No. 12, 1968, pp 2677-2652. AMIC-37651. Anderson, J. M., Peterson, M. R. "DDT: SUBLETHAL EFFECTS ON BROOK TROUT NERVOUS SYSTEM", Science, Vol. 16U, April 25, 1969, PP UUo-UUl. AMIC-3838. Anderson, J. M., Prins, H. B. "EFFECTS OF SUBLETHAL DDT ON A SIMPLE REFLEX IN BROOK TROUT", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 2, 1970, pp 331-331. AMIC-3782.""""" Arthur, J. W., Leonard, E. N. "EFFECTS OF COPPER ON GAMMARUS PSEUDOLIMNAEUS, PHYSA INTEGRA, AND CAMPELOMA DECISUM IN SOFT WATER", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 7, July 1970, pp 1277-12«3.AMIC-B67. Ashley, L. M. "ACTION OF IRON SALTS IN SOLUTION ON GOLDFISH", The Progressive Fish- Culturist, Vol. 32, April 1970, p 109. AMIC-5^3^ Aubin, A. E., Johansen, P. H. "THE EFFECTS OF AN ACUTE DDT EXPOSURE ON THE SPONTANEOUS ELECTRICAL ACTIVITY OF GOLDFISH CEREBELLUM", Canadian Journal of Zoology. Vol. kj, No. 2, March 1969, PP 163-166. AMIC-3B35. 11 ------- Bache, C. A., Gutenmann, W. H., Lisk, D. J. "RESIDUES OF TOTAL MERCURY AND METHYLMERCURIC SALTS IN LAKE TROUT AS A FUNCTION OF AGE", Science, Vol. 172, May 28, 1971, PP 951-952. AMIC-3818. Bahr, T. G., Ball, R. C. "ACTION OF DDT ON EVOKED AND SPONTANEOUS ACTIVITY FROM THE RAINBOW TROUT LATERAL LINE NERVE", Comp, Biochem. Physiol., Vol. 3&A, 1971, PP 279-284, AMIC-3&08. Baker, J. T. P. "HISTOLOGICAL AND ELECTRON MICROSCOPICAL OBSERVATIONS ON COPPER POISONING IN THE WINTER FLOUNDER ( PSEUDOPLEURONECTES AMERICANUS) ", Journal of the Fisheries Research Board of Canada, Vol. 26, No. 11, 1969, pp 2785-2793. AMIC-3763. Baldridge, H. D., Jr. "KINETICS OF ONSET OF RESPONSES BY SHARKS TO WATERBORNE DRUGS", Bulletin of Marine Science, Vol. 19, No. U, 1969, PP 88U-892. AMIC-3832. Ballard, J. A., Oliff, W. D. "A RAPID METHOD FOR MEASURING THE ACUTE TOXIC ITY OF DISSOLVED MATERIALS TO MARINE FISHES", Water Research, Vol. 3, 1969, pp 313-333. AMIC-300. Batterton, J. C., Boush, G. M. , Matsuraura, F. "GROWTH RESPONSE OF BLUE -GREEN ALGAE TO ALDRIN, DIELDRIN, ENDRIN AND THEIR METABOLITES", Bulletin of Environmental Contamination and Toxicology, Vol. 6, No. 6, November/December 1971, PP 589-594. AMIC-lU?l. Bell, H. L., Nebeker, A. V. "PRELIMINARY STUDIES ON THE TOLERANCE AQUATIC INSECTS TO LOW pH", Journal of the Kansas Entomological Society, Vol. 42, No. 2, April 1969, pp 230- Bender, M. E. "THE TOXICITY OF THE HYDROLYSIS AND BREAKDOWN PRODUCTS OF MALATHION TO THE FATHEAD MINNOW (PIMEPHALES PROMELAS, RAFINESQUE ) ", Water Research, Vol. 3, 1969, PP 571-582. AMIC-3787. Bender, M. E. "UPTAKE AND RETENTION OF MALATHION BY THE CARP", The Progressive Fish. Culturist. Vol. 31, July 1969, PP 155-159. AMIC-5731. Bender, M. E., Eisele, P. "LONG TERM EFFECTS OF PESTICIDES ON STREAM INVERTEBRATES", University of Michigan, Department of Environmental and Industrial Health, Ann Arbor, Michigan, Project Completion Report, December 1971, 28 pp, PB-206 692. AMIC-3279. Bennett, H. J., Day, J. W., Jr. "ABSORPTION OF ENDRIN BY THE BLUEGILL SUNFISH, LEPOMIS MACROCHIRUS ", Pesticides Monitoring Journal, Vol. 3, No. U, March 1970, pp 201-203. AMIC-195. 12 ------- Berger, B. L., Lennon, R. E., Hogan, J. W. "LABORATORY STUDIES ON ANTIMYCIN A AS A FISH TOXICANT", U. S. Bureau of Sport Fisheries and Wildlife, Fish Control Laboratory, La Crosse, Wisconsin, Investigations in Fish Control No. 26, February 1969, 21 pp. AMIC-5^95. Bhatia, H. L. "TOXICITY OF SOME PESTICIDES TO PUNTIUS TICTO (HAMILTON)", Science and Culture, Vol. 37, No. 3, March 1971, pp 160-161. AMIC-5^23. Birdsong, C. L., Avault, J. W., Jr. "TOXICITY OF CERTAIN CHEMICALS TO JUVENILE POMPANO", The Progressive Fish- Culturist, Vol. 33, No. 2, April 1971, PP 76-80. AMIC-5570. Boer, H. H., Lever, J. "THE EFFECT OF AMPHENONE B ON THE EGG PRODUCTION OF LYMNAEA STAGNALIS", Malacologia, Vol. 5, No. 3, 1967, PP U31-UUU. AMIC-5^5. Brown, V. M., Dalton, R. A. "THE ACUTE LETHAL TOXICITY TO RAINBOW TROUT OF MIXTURES OF COPPER, PHENOL, ZINC, AND NICKEL", Journal of Fish Biology, Vol. 2, 1970, pp 211-216. AMIC-5991. Brown, V. M., Jordan, D. H. M., Tiller, B. A. "THE ACUTE TOXICITY TO RAINBOW TROUT OF FLUCTUATING CONCENTRATIONS AND MIXTURES OF AMMONIA, PHENOL, AND ZINC", Journal of Fish Biology, Vol. 1, 1969, pp 1-9. AMIC-5993. Brungs, W. A. "CHRONIC TOXICITY OF ZINC TO THE FATHEAD MINNOW, PIMEPHALES PROMELAS RAFINESQUE", Transactions of the American Fisheries Society, Vol. 98, 1969, pp 272-2791AMIC-5458. Buhler, D. R., Shanks, W. E. "INFLUENCE OF BODY WEIGHT ON CHRONIC ORAL DDT TOXICITY IN COHO SALMON", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 2, 1970, PP 3^7-358. AMIC-3701. Burton, D. T. "LACTIC AND FYRUVIC ACID CHANGES IN BLUEGILL SUNFISH (LEPOMIS MACROCHIRUS RAFINESQUE) DURING GRADUAL HYPOXIA AT TWO ACCLIMATION TEMPERATURES. (5 AND 20 C)", The ASB Bulletin, Vol. 17, No. 2, April 1970, p 35. AMIC-6385. Butler, G. W., Ferguson, D. E., Sadler, C. R. "EFFECTS OF SUBLETHAL PARATHION EXPOSURE ON THE BLOOD OF GOLDEN SHINERS, NOTEMIGONUS CRYSOLEUCAS", Journal of the Mississippi Academy of Science, Vol. 15, 1969, PP 33-36. AMIC-5977. Cairns, J., Jr., Sparks, R. E. "THE USE OF BLUEGILL BREATHING TO DETECT ZINC", Virginia Polytechnic Institute and State University, Center for Environmental Studies, Blacksburg, Virginia, Water Pollution Control Research Series 18050 EDQ 12/71, December 1971, fc5 PP. AMIC-3232. 13 ------- Cairns, J., Jr., Waller, W. T. "THE USE OF FISH MOVEMENT PATTERNS TO MONITOR ZINC", Virginia Polytechnic Institute and State University, Center for Environmental Studies, Blacksburg, Virginia, Water Pollution Control Research Series 18050 EDP 12/71, December 1971, 55 pp. AMIC-323L Cairns, J., Loos, J. J. "CHANGED FEEDING RATE OF BRACHYDANIO RERIO (HAMILTON-BUCHANAN) RESULTING FROM EXPOSURE TO SUBLETHAL CONCENTRATIONS OF ZINC, POTASSIUM BICHROMATE, AND ALKYL BENZENE SULFONATE", Pennsylvania Academy of Science, 1967, pp U7-52. AMIC-5707. Chen, C. W., Selleck, R. E. "A KINETIC MODEL OF FISH TOXICITY THRESHOLD", Journal Water Pollution Control Federation. Vol. Ul, 1969, PP R29^-R30^. AMIC-3831. Coler, R. A., Gunner, H. B., Zuckerman, B. M. "TUBIFICID SENSITIVITY TO STREPTOMYCIN", Transactions of the American Fisheries Society. Vol. 97, 1968, pp 502-503. AMIC-5^60. Cooke, A. S. "SELECTIVE PREDATION BY NEWTS ON FROG TADPOLES TREATED WITH DDT", Nature, Vol. 229, January 22, 1971, pp 275-276. AMIC-381^. Cordone, A. J., Nicola, S. J. "INFLUENCE OF MOLYBDENUM ON THE TROUT AND TROUT FISHING OF CASTLE LAKE", California Fish and Game, Vol. 56, No. 2, 1970, pp 96-108. AMIC-5750. Cowmeadow, M. M., Steege, P. T., Pang, P. K. T., Grant, F. B. "A STUDY OF THE PHYSIOLOGICAL EFFECTS OF SULFISOXAZOLE ON THE KILLIFISH", The Progressive Fish-Culturist, Vol. 31, October 1969, PP 226-228. AMIC-5736. Davis, H. C., Hindu, H. "EFFECTS OF PESTICIDES ON EMBRYONIC DEVELOPMENT OF CLAMS AND OYSTERS AND ON SURVIVAL AND GROWTH OF THE LARVAE", U.S. Fish and Wildlife Service Fishery Bulletin, Vol. 67, No. 2, 1969, pp 393-^04. AMIC-5990. Dimond, J. B., Getchell, A. S., Blease, J. A. "ACCUMULATION AND PERSISTENCE OF DDT IN A LOTIC ECOSYSTEM", Journal of the Fisheries Research Board of Canada, Vol. 28, No. 12, December 197!, pp 1877-1882. AMIC-3291. Duke, T. W., Lowe, J. I., Wilson, A. J., Jr. "A POLYCHLORINATED BIPHENYL (AROCLOR 125 0 IN THE WATER, SEDIMENT, AND BIOTA OF ESCAMBIA BAY, FLORIDA", Bulletin of Environmental Contamination and Toxicology, Vol. 5, No. 2, March/April 1970, pp 171-180. AMIC-720. Earnest, R. D. "THE EFFECT OF PARAQUAT ON FISH IN A COLORADO FARM POND", The Progressive Fish-Culturist, Vol. 33, No. 1, January 1971, PP 27-31. ------- Eaton, J. G. "CHRONIC MALATHION TOXICITY TO THE BLUEGILL (LEPOMIS MACROCHIRUS RAFINESQUE)", Water Research, Vol. k, October 1970, pp 673-6$f. AMIC-1312. Ebel, W. J. "SUPERSATURATION OF NITROGEN IN THE COLUMBIA RIVER AND ITS EFFECT ON SALMON AND STEELHEAD TROUT", Fishery Bulletin, Vol. 68, No. 1, 1969, pp 1-9. AMIC-6198. Eisler, R. "CADMIUM POISONING IN FUNDULUS HETEROCLITUS (PISCES: CYPRINODONTIDAE) AND OTHER MARINE ORGANISMS", Journal of the Fisheries Research Board of Canada, Vol. 28, No. 9, September 1971, pp 1225-123^.AMIC-1621. Eller, L. L. "PATHOLOGY IN REDEAR SUNFISH EXPOSED TO HYDROTHOL 191", Transactions of the American Fisheries Society, Vol. 98, 1969, PP 52-59. AMIC-5^59. Epifanio, C. E. "EFFECTS OF DIELDRIN IN SEAWATER ON THE DEVELOPMENT OF TWO SPECIES OF CRAB LARVAE, LEPTODIUS FLORIDANUS AND PANOPEUS HERBSTII", Marine Biology, Vol. 11, No. k, December 1971, PP 356-362. AMIC-2653. Erickson, S. J., Lackie, N., Maloney, T. E. "A SCREENING TECHNIQUE FOR ESTIMATING COPPER TOXICITY TO ESTUARINE PHYTOPLANKTON", Journal Water Pollution Control Federation, Vol. U2, No. 8, Part 2, August 1970, pp R270-R278. AMIC-W?. Ferguson, D. E., Ludke, J. L., Finley, M. T., Murphy, G. G. "INSECTICIDE^RESISTANT FISHES: A POTENTIAL HAZARD TO CONSUMERS", Mississippi Academy of Science Journal, Vol. 13, 1967, PP 138-1^0. AMIC-5970. Fletcher, G. L., Hoyle, R. J., Home, D. A. "YELLOW PHOSPHORUS POLLUTION: ITS TOXICITY TO SEAWATER-MAINTAINED BROOK TROUT (SALVELINUS FONTINALIS) AND SMELT (OSMERUS MORDAX)", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 8, August 1970, pp 1379-13W. AMIC-839. Fredeen, F. J. H., Duffy, J. R. "INSECTICIDE RESIDUES IN SOME COMPONENTS OF THE ST. LAWRENCE RIVER ECOSYSTEM", Pesticides Monitoring Journal, Vol. 3, No. U, March 1970, pp 219-226. AMIC-53^. Gardner, G. R., Yevich, P. P. "HISTOLOGICAL AND HEMATOLCGICAL RESPONSES OF AN ESTUARINE TELCOST TO CADMIUM", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 12, 1970, pp 210-5-2193. AMIC-3«27. Garrison, R. L. "THE TOXICITY OF PRO-NOXFISH TO SALMONID EGGS AND FRY", The Progressive Fish-Culturist, Vol. 30, January 1968, pp 35-38. AMIC-573TK 15 ------- Gibson, J. R., Ludke, J. L., Ferguson, D. E. "SOUBCES OF ERROR IN THE USE OF FISH-BRAIN ACEIYLCHOLINESTERASE ACTIVITY AS A MONITOR FOR POLLUTION", Bulletin of Environmental Contamination and Toxicology, Vol. U, No. 1, 1969, pp 17-23. AMIC-3783. Gibson, J. R., Ludke, J. L. "EFFECT OF SESAMEX ON BRAIN ACETTLCHOLINESTERASE INHIBITION BY PARATHION IN FISHES", Bulletin of Environmental Contamination and Toxicology. Vol. 6, No. 2, 1971, PP 97-99. AMIC-3799. Grant, B. F., Mehrle, P. M. "CHRONIC ENDRIN POISONING IN GOLDFISH, CARASSIUS AURATUS", Journal of the Fisheries Research Board of Canada. Vol. 27, No. 12, 1970, pp 2225-223^. AMIC-3t42b. Grosch, D. S. "POISONING WITH DDT: SECOND- AND THIRD-YEAR REPRODUCTIVE PERFORMANCE OF ARTEMIA", Pollution - Foundations for Today. Vol. 2, 1971, pp 8U-85. AKLC-2090. ' Guthrie, J. E., Acres, 0. E. "TOXICITY TO FISH OF TWO ORGANIC REACTOR COOLANTS", BvT»0tin of Environmental CpntaMnatipn and Toxicology. Vol. 5, No. 2, March/ April 1970, pp W-5-151.AMIC-721. Hones, D., Krueger, H., Pilcher, K. S. "PENTACHLOROPHENOL AND CULTURES OF EMBRYONIC CELLS FROM ONCORHYNCHUS KISUTCH", Proceedings of the Western Pharmacological Society, Vol. 13 1970* PP 62-68. AMIC-5753. Hansen, D.J., Parrish, P.R., Lowe, J.I., Wilson, A.J., Jr., Wilson, P.D. "CHRONIC TOXICITY, UPTAKE, AND RETENTION OF AROCLOR 125^ IN TWO ESTUARINE FISHES", Bulletin of Environmental Contamination and Toxicology, Vol. 6, No. 2, March/April 1971, pp 113-119. AMIC-1811. Hatfield, C, T. "EFFECTS OF DDT LARVICIDING ON AQUATIC FAUNA OF BOBBY'S BROOK, LABRADOR", Canadian Fish Culturist. Vol. Uo, 1969, pp 61-72. AMIC-5770. Haven, D. S. "LEVELS OF THE HERBICIDE DIQUAT IN TWO ESTUARINE MOLLUSCS AND IN THE WATER AND MUD", Journal of Science. Vol. 20, 1969, pp 51-53. AMIC-5978. Hazel, C. R., Meith, S. J. "BIOASSAY OF KING SALMON EGGS AND SAC FRY IN COPPER SOLUTIONS", California Fish and Game. Vol. 56, No. 2, 1970, pp 121-12U. AMIC-5572. Henderson, C., Inglis, A., Johnson, W. L. "RESIDUES IN FISH, WILDLIFE, AND ESTUARIES. ORGANOCHLORINE INSECTICIDE RESIDUES IN FISH - FALL 1969 NATIONAL PESTICIDE MONITORING PROGRAM", Pesticides Monitoring Journal. Vol. 5, No. 1, June 1971, PP 1-11. AMIC-1W7. 16 ------- Hiltilaran, R. C. "A PROPOSED BIOCHEMICAL MECHANISM OF THE TOXIC ACTION OF DDT", Trans- actions of the Illinois Academy of Science, Vol. 6k t No. 1, 197!, PP U6-5^. AMIC-5975. Hogan, R. L. , Roeloes, E. W. "CONCENTRATIONS OF DIELDRIN IN THE BLOOD AND BRAIN OF THE GREEN SUNFISH, LEPOMIS CYANELLUS, AT DEATH", Journal of the Fisheries Research Board of Canada. Vol. 28, No. k, 1971, pp 610-612. Holland, H. T., Coppage, D. L. "SENSITIVITY TO PESTICIDES IN THREE GENERATIONS OF SHEEPSHEAD MINNOWS", Bulletin of Environmental Contamination and Toxicology, Vol. 5, No. U, July /August 1970, pp 3o2-367. AMIC-726. Houston, A. H., Madden, J. A., Woods, R. J., Miles, H. M. 'VARIATIONS IN THE BLOOD AND TISSUE CHEMISTRY OF BROOK TROUT, SALVELINUS FONTINALIS, SUBSEQUENT TO HANDLING, ANESTHESIA, AND SURGERY", Journal of the Fisheries Research Board of Canada, Vol. 28, No. 5, 1971, PP 035-642. AMIC-3B22. Houston, A. H., Madden, J. A., Woods, R. J., Miles, H. M. "SOME PHYSIOLOGICAL EFFECTS OF HANDLING AND TRICAINE METHANE -SULPHONATE ANESTHETIZATION UPON THE BROOK TROUT, SALVELINUS FONTINALIS", Journal of the Fisheries Research Board of Canada, Vol. 28, No. 5, May 1971, PP 025.533. AMIC-3B23. Rowland, R. M. "INTERACTION OF ANTIMYCIN A AND ROTENONE IN FISH BIOASSAYS", The Progressive Flsh-Culturist. Vol. 31, January 1969, pp 33-31. "AMIC-5725. Hubschman, J. H. "EFFECTS OF COPPER ON THE CRAYFISH ORCONECTES RUSTICUS (GIRARD) I. ACUTE TOXICITY", Crustaceana, Vol. 12, 1967, PP 33-^2. AMIC-5985. Huner, J. V., Dovden, B. F., Bennett, H. J. "THE EFFECTS OF ENDRIN ON THE OXYGEN CONSUMPTION OF THE BLUEGILL SUNFISH LEPOMIS MACROCHIRUS", Louisiana Academy of Sciences. Vol. 30, 19^7, PP 80-86. AMIC-5981. Jackson, D. A., Anderson, J. M., Gardner, D. R. "FURTHER INVESTIGATIONS OF THE EFFECT OF DDT ON LEARNING IN FISH", Canadian Journal of Zoology, Vol. ^8, 1970, pp 577-580. AMIC-3837. Johnson, B. T., Saunders, C. R., Sanders, H. 0. "BIOLOGICAL MAGNIFICATION AND DEGRADATION OF DDT AND ALDRIN BY FRESHWATER INVERTEBRATES", Journal of the Fisheries Research Board of Canada, Vol. 28, No. 5, 1971, pp 705-709. AMIC-3«20. Kawatski, J. A., Schmulbach, J. C. "ACCUMULATION OF INSECTICIDE IN FRESHWATER OSTRACODS EXPOSED CONTINUOUSLY TO SUBLETHAL CONCENTRATIONS OF ALDRIN OR DIELDRIN", Trans- actions of the American Fisheries Society, Vol. 100, No. 3, 1971, PP ^5-567. AMIC-5506. 17 ------- Kihlstrom, J. E., Lundberg, C., Hulth, L. "NUMBER OF EGGS AND YOUNG PRODUCED BY ZEBRAFISHES (BRACHYDANIO RERIO, HAM. .BUCK. ) SPAWNING IN WATER CONTAINING SMALL AMOUNTS OF PHENYLMERCURIC ACETATE", Environmental Research, Vol. k, No. U, October 1971, PP 355-359. AMIC-2707. Konar, S. K. "TOXIC ITY OF HEPTACHLOR TO AQUATIC LIFE", Journal Water Pollution Control Federation. Vol. te, No. 8, Part 2, August 1970, pp R299-B303. Konar, S. K. "EFFECTS OF HEPTACHLOR AND NICOTINE ON THE BARBELS OF A CATFISH (HETEROPNEUSTES FOSSILIS)", The Progressive Fish-Culturist. Vol. 31, 1969, pp 62-63. AMIC-5726. Konar, S. K. "NICOTINE AS A FISH POISON", The Progressive Fish-Culturist. Vol. 32, April 1970, pp 103-10U. AMIC-5^35. Konar, S. K. "LABORATORY STUDIES ON TWO ORGANOPHOSPHORUS INSECTICIDES, DDVP AND PHOSPHAMIDON, AS SELECTIVE TOXICANTS", Transactions of the American Fisheries Society. Vol. 98, No. 3, 1969, PP ^30-^37. AMIC-5^53. Konar, S. K. "LETHAL EFFECTS OF THE INSECTICIDE DDVP ON THE EGGS AND HATCHLINGS OF THE SNAKE -HEAD, CHANNA PUNCTATUS (Bl) (OPHICCEPHALIFORMES: OPHIOCEPHA1IDAE)", Japanese Journal of Ichthyology, Vol. 15, No. 3, February 15, 1969, PP 130-133. AMic-6388. Lane, C. E., Scura, E. D. 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"SURVIVAL OF BURIED BULLHEADS SUBJECTED TO U'-IODO-3JfITROSALICYLANILIDE", New York Fish and Game Journal, Vol. 13, No. 2, July 1966, pp 196-205. AMIC-6199. Lucas, H. F., Jr., Edgington, D. N. "CONCENTRATIONS OF TRACE ELEMENTS IN GREAT LAKES FISHES", Journal of the Fisheries Research Board of Canada, Vol. 27, No. k, 1970, pp 677-6W. AMIC-3778. Lyraan, L. D., Tompkins, W. A., McCann, J. A. "RESIDUES IN FISH, WILDLIFE, AND ESTUARIES", Pesticides Monitoring Journal, Vol. 2, No. 3, December 1968, pp 109-122. AMIC-3b39. Macek, K. J. "REPRODUCTION IN BROOK TROUT (SALVELINUS FONTINALIS) FED SUBLETHAL CONCENTRATIONS OF DDT", Journal of the Fisheries Research Board of Canada, Vol. 25, No. 9, 1968, pp 1707-1796.AMIC-3716. Macek, K. J., Korn, S. "SIGNIFICANCE OF THE FOOD CHAIN IN DDT ACCUMULATION BY FISH", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 8, August 1970, pp 1496-1198.AMIC-tm. Macek, K. J., McAllister, W. A. "INSECTICIDE SUSCEPTIBILITY OF SOME COMMON FISH FAMILY REPRESENTATIVES", Transactions of the American Fisheries Society, No. 1, 1970, pp 20-27. AMIC-5510."~ MacPhee, C., Ruelle, R. "A CHEMICAL SELECTIVELY LETHAL TO SQUAWFISH (PTYCHOCHEILUS OREGONENSIS AND P. UMPQUAE)", Transactions of the American Fisheries Society, Vol. 98, 1969, pp 676-68^. AMIC-5^50. Manion, P. J. "EVALUATION OF LAMPREY IARVICIDES IN THE BIG GARLIC RIVER AND SAUX HEAD LAKE", Journal of the Fisheries Research Board of Canada, Vol. 26, No. 11, 1969, PP 3077-3002. AMIC-3761. Mann, H. "BIOLOGICAL EFFECTS OF FATTY ALCOHOLS ON FRESHWATER ANIMALS", Internationale Revue der Gesamten Hydrobiologie, Vol. 56, No. U, 1971, PP 599-607, AMIC-3079. 19 ------- Marking, L. L. "TOXICm OF METHYLPENTYNOL TO SELECTED FISHES", U. S. Bureau of Sport Fisheries and Wildlife, Fish Control Laboratory, La Crosse, Wisconsin, Investigations in Fish Control No. 30, February 1969, 7 pp. AMIC-5^77. Marking, L. L. "JUGLONE (5-HYDROXY-l,U-NAPHTHOQUINONE) AS A FISH TOXICANT", Transactions of the American Fisheries Society, Vol. 99, No. 3, 1970, pp 510-514. AMIC-5517. Marking, L. L. "TOXICITY OF RHODAMINE B AND FLUORESCEIN SODIUM TO FISH AND THEIR COMPATIBILITY WITH ANTIMTCIN A", The Progressive Fish-Culturist, Vol. 31, July 1969, pp 139-lte. AMIC-5729. Mathur, D. S. "TOXICITY OF ALDRIN TO CERTAIN FISH", Science and Culture, Vol. 35, No. 8, August 1969, pp 418-^19. AMIC-5^22. Mawdesley-Thomas, L. E. "TOXIC CHEMICALS - THE RISK TO FISH", New Scientist, Vol. k?t No. 73^, January Ik, 1971, pp 7^-75. AMIC-10561 Mclngvale, C. R., Ludke, L., Ferguson, D. E. "OXYGEN CONSUMPTION OF ENDRIN-SUSCEPTIBLE AND ENDRIN-RESISTANT GAMBUSIA DURING SUBLETHAL AND ACUTE ENDRIN EXPOSURE", Journal of the Mississippi Academy of Science, Vol. lU, 1968, pp 116-1211AMIC-5V75. McKim, J. M., Christensen, G. M., Hunt, E. P. 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"MORTALITY OF MARINE INVERTEBRATE LARVAE IN MERCURY, COPPER, AND ZINC SOLUTIONS", Australian Journal of Marine and Freshwater Research, Vol. 18, 1967, pp 63-72. AMIC-570B. Woodhead, P. M. J. "AN EFFECT OF THYROXDJE UPON THE SWIMMING OF COD", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 12, 1970, pp 2337-2338. AMIC-3825. 25 ------- Worthley, E. 0., Schott, C. D. "THE COMPARATIVE EFFECTS OF CS AND VARIOUS POLLUTANTS ON FRESH WATER PHYTOPLANKTON COLONIES OF WOLFFIA PAPULIFERA THOMPSON", U.S. Department of the Army, Biomedical Laboratory, Edgewood Arsenal, Maryland, Technical Report EATR 1595, December 1971, P 12. AMIC-3233. Young, R. G., St. John, L., Lisk, D. J. "DEGRADATION OF DDT BY GOLDFISH", Bulletin of Environmental Contamination and Toxicology, Vol. 6, No. U, 1971, PP 351-35^. AMIC-3796. Zillich, J., Wuerthele, M. "THE TOXIC EFFECTS OF THE LANSING WASTEWATER TREATMENT PLANT EFFLUENT TO THE FATHEAD MINNOW, PIMEPHALES PROMELAS", Michigan Department of Natural Resources, Water Resources Commission, Lansing, Michigan, paper, January 19-20, 1970, k pp. AMIC-2899. Zillich, J., Wuerthele, M. "THE TOXIC EFFECTS OF THE GRANDVILLE WASTEWATER TREATMENT PLANT EFFLUENT TO THE FATHEAD MINNOW, PIMEPHALES PROMELAS", Michigan Department of Natural Resources, Water Resources Commission, Lansing, Michigan, Report, November 17-21, 1969, 10 pp. AMIC-2898. Zillich, J. "THE TOXICITY OF THE WYOMING WASTEWATER TREATMENT PLANT EFFLUENT TO THE FATHEAD MINNOW AND THE WHITE SUCKER - JULY 28 - AUGUST 1, 1969", Michigan Department of Natural Resources, Water Resources Commission, Lansing, Michigan, Paper, 1969, 7 pp. AMIC-2906. Zillich, J. "A BIOLOGICAL EVALUATION OF SIX CHEMICALS USED TO DISPERSE OIL SPILLS", Michigan Department of Natural Resources, Water Resources Commission, Lansing, Michigan, Paper, April 1969, 12 pp. AMIC-2909. Zitko, V., Aiken, D. E., Tibbo, S. N., Besch, K. W. T., Anderson, J. M. "TOXICITY OF YELLOW PHOSPHORUS TO HERRING (CLUPEA HARENGUS), ATLANTIC SALMON (SALMO SALAR), LOBSTER (HOMARUS AMERICANUS), AND BEACH FLEA (GAMMARUS OCEANICUS)", Journal of the Fisheries Research Board of Canada, Vol. 27, No. 1, 1970, pp 21-29.AMIC-3817. Zitko, V. "POLYCHLORINATED BIPHENYLS (PCB) SOLUBILIZED IN WATER BY NONIONIC SURFACTANTS FOR STUDIES OF TOXICITY TO AQUATIC ANIMALS", Bulletin of Environmental Contamination and Toxicology, Vol. 5, No. 3, 1970, pp 279-205. AMIC-23. Zitko, V. "POLYCHLORINATED BIPHENYLS AND ORGANOCHLORINE PESTICIDES IN SOME FRESHWATER AND MARINE FISHES", Bulletin of Environmental Contamination and Toxicology, Vol. 6, No. 5, 1971, PP 464-470. AMIC-3715. 26 ------- SECTION VI APPENDICES ------- Abbreviations for Appendix A Note; Names of chemicals and organisms are as given by the various authors. Readers should search for alternate, common, and/or scientific names of both chemical and aquatic species. (1) Letters represent: B • bioassay, used in combination with S = static, CF m continuous flow, A = acute, and CH = chronic. L " laboratory bioassay. BOD « biochemical oxygen demand. F • field study, used in combination with R - river, stream, creek, etc., L = pond, M - marine, E = estuarine, and 0 • other (port facility, flooded area, etc.). (2) Field location is indicated by abbreviation of the state or county. (3) The number indicates ppm (mg/1), unless otherwise indicated by appropriate designations. The letters within parentheses following indicate T - TI^, K = kill, SB » sublethal effects, NTE - no toxic effect. The number following these indicates the time in days (unless otherwise noted) at which observations were made. ECjg, LCjQ, and similar designations for 50 percent lethality were all considered as TLn and designated as such. The numbers within parentheses following these designations indicate the time in days when the effect was observed. (4) The following indicate (when followed by an asterisk the variable was controlled): a • water temperature b - ambient air temperature c - pH d - alkalinity (total, phenolphthalein or caustic) e • dissolved oxygen f - hardness (total, carbonate, Mg, or CaO) g - turbidity h m oxidation-reduction potential i « chloride as Cl j - BOD, 5 day; (J) - BOD, short-term k - COD 1 - nitrogen (as N02 or N03) m - ammonia nitrogen as NH3 n • phosphate (total, ortho-, or poly) o - solids (total, fixed, volatile, or suspended) p • C02 q - light r - flow rate s « sound (5) Other miscellaneous abbreviations are: SM - sterilized media SSM - synthetic seawater medium NSW • natural seawater MSC • maximum safe concentration The AMlC-xxxx number following each reference is the accession number which was assigned by the Analytical Methodology Information Center to facilitate location of original documents. A-l ------- Cowound •BS »BS BS •as •cataldehyde cet aldehyde •cataldehyde Toxicltyt Experimental Active Variables, Field Field Ingredient, Controlled Or9anls» Study Location Pp» or Noted Comments Br achy dan lo BSt — rerlo Lepoals BSt. ~ •acrochlrus L Nltzsehlaj as. — linear! L Phvsa BS, — heferostrooha L Leoomls BSA, — •eerochlrus L Nltzsehla BSk. ~ II near is L Crangon BS — crangon 32 (SB) a,e, and synthetic tt 1 1 ii # 1 nn o 1 1 u • i on Hater 17. (Tfc) a»,e, and synthetic dilution •ater 10 (T5I a«,e, and synthetic dilution water 31.. 2 IT) a,e, and synthetic dilution Mater 53 IT) a»,e, and synthetic d 1 1 ut 1 on Mater 236.6 ITS) ,..., ,„„ synthetic dilution Mater greater than A«(contin- 100 IT2) uoua, aor- Feedlnq behavior «as affected by zinc, chromluir, and Aq<; in that more tl«e amounts of food. Feeding resoonse Mas alto affrctft'l by aeration, feeding schedule, light Intensity, and outside disturbances. The authors note that «uch •ore MorK is needed to establish the reliability of this procedure. This study Mas conducted to determine the relative toxieities of ?0 common constituents of Industrial wastes to a fish, an atqi, and n invertebrate. The experiments Mere conducted over a ID-year period for varied purposes. The authors recoaoend hloassays Mith at least three conoonents of the food Neb. same as above sae as above This study Mas conducted to determine the relative toxlcltles of 20 coiinon constituents of industrial Hastes to a fish, an alga, an-) an invertebrate. The experiments Mere conducted over a 10-year period for varied purposes. The authors recommend bloassays Mith at least three components of the food web. same as above same as above ation, soa- Reference Cairns, et al (19.67> , MIC— 5707 Patrick, et al (I960). NIC-«7?0 Patrick, et al M, »MIC-57?8 Patrick, et al 111691. »IIC-5720 Patrick, et al (196M. «NIC-5720 Patrick, «t at (196S). • MIC-57Z!) Porteann, at 81(1971), 4MIC-7701 ------- water, and daily solution renewal) Acetic acid Leooals aaerechlrus BSA, I 75 (T> > U> Acetic ecld Acetic acid Nltrschla Uncarts Carclnus eaenas BSA, L BSA 7 (T5» 180 (TZl Aeatle acid Crangon cranqon BS* — greater than 100 (TZl a»,e, and synthetic dilution water a, a, and synthetic dilution water «»(contin- uous aer- ation, sea. water, and daily solution renewal) This study was conducted to determine the relatlve' toxlclties of ?fl contort constituents of Industrial wastes to a fish, an alqa, and an Invertebrate. The experiments Here conducted over a 10-year period for varied purposes. The authors reconnend bloftssays with at least three components of the food xeb. sane as above Patrick, at at (1968), a«( contin- uous aer- ation, sea- water, and daily solution renewal) One hundred-forty surface active aq»nts, solvent enulslflers, pesticides, ,polychlorlnate ------- Compound Ice tone > I •cetene acetone Toxlclty, Experimental Active Variables. Field Field Ingredient, Controlled Organise Study Location Ppm or Noted Comments Lepomls BSA, — macrochlrus L Nltzschla BSA, — linear Is L Hercenarla L •ercenarla (eggs) 8,3011 found to be essential. This study was conducted to determine the relative toxlcltles of ?0 common constituents of industrial wastes to a fish, an alga, and an invertebrate. The experiments were conducted over a 10-vear period for varied purposes. The authors recommend bioassays with at least three components of the food web. same as above The effect of 5? pesticides on embryonic development of clais and oysters was reported. Synerqlstlc Reference Patrick, al (1968) AMIC-5770 Patrick, al (196$) ANIC-S7?0 et et • Davis, et al (19691. AHIC-^990 I •eaten* •cetene Acetone Hercenarl a •ercenarla (larvae! Crassostrea virqlnlca Phormidium ••blauuB L — L qreater than 100.0 (T13) qreater than 100.0 (TZ) 0.5-10.0 (NTE) — effects with solvents Here also reported. Host of the compounds affected develoc«ent more than survival. Some. however, drastically reduced larval growth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that Mould not have serious effect on shellfish. same as above same as above Of 7i> chemicals evaluated as algieides. only 9 were more toxic than CuSOnts Has more toxic tnan CuS04 alone. Davis, eta! (19591 , »MIC-5990 Oavls, et at (19691, AMIC-S990 otto AHIC-892 ------- »erlflavin* (neutral) Moron* saxatllis (finger!ings) BS» 16.* > vn tcrlftavine TraeMnotus carollnu» (Juvenile) BSk llV-llt (Ti>) AeroI•In Rasbora 8CFA heteromorphe and BSA Acrrlonltril* Crangon crangon BS* ~ Coooer ehiorairlne Mas also found to be more toxic thar CuSO2$ wHe range of toxlclty spanning 12 orders of magnitude. Knowing the toxlcity and percentage of all co«oonents of a formulation did not result In easy predictability of the toxlclty of a mixture oT materials. Somot lines pesticides were most toxic In hard water and sometimes the opposite was true. Testing the actual material as soM was found to be essential. 10-3J (Til a«(contln- One hundred-forty surface active Portmann, et uoua aer- agents, solvent emulslfiers, pesticides, al (1971), aticn, sea- potychlorlnated blohenyls, pure AHIC-7701 water, and Inorganic, and organic chemicals Hera dally evaluated against as many as ten marine 0.06 IT2) a,c,e,f,1, and sulfate, sodium, calcium, potassium, magnesium, carbonate, bicarbon- ate, ••Unity a»,c,o,f, hard IBWJ or soft (SW) syn- thetic dilution water, or seawater for some species ------- Compound Orqanlsn Field Field Study Location Toxic! ty, Active Ingredient, Ppm Experimental Variables, Control led or Noted Comments Reference solution renewal) Ac tuo I Steelh»ad trout (IIngerlIngs) BSA Actusol Actusal • Matoxln ai •gridID Coho salmon BSA (fInqerllnqs) In lltu Hood Canal, Hoodsportt Nash. Pacific oyster (larvae) Br achydanto rerlo (eggs) Rasbora heteromorpha BS» — BCF ~ and BSA ".0.0 IK) ?«. 0-1.0.0 CS) 1.0 (X) 1.9 synthetic dilution Mater, or seawatfir for some species Aldrln IC-1« labelled) Oaphnia aaqna BCF (adult) (residue) orqanlsms. The authors noted that most published data of this type deal with toxlclty of ehenlcals to freshwater organisms. Evaluation of 11 oil dlspersants resulted In a ranklnq for each and a recommendation for use according to the ranking. Ranking was based on toxlclty and oil dispersal effectiveness. Corexlt TT&H acoeared to have the least toxlclty with fair to good oil dispersion caoablllty. same as above sane as above This fungal toxin was acutely toxic to Rrachydanlo rerlo embryos and larvae, especially the latter. The authors suggest this response as an easily performed assay for aflatoxln. same as above Tracy, «* al I Magnification of DOT and Aldrln taqo«rt with R-tu occurred rapidly. Bloloqlcal magnification factors of 2900 to llfc.100 denendlnq on the species were found for DDT, and Z?,AOQ to Ul.OOO for Aldrln. Harked deqradatlon of DOT as determined by analysis for DOT metabolites occurred. The authors conclude that aquatic Invertebrates Influence Duality and quantity of Insecticide residue passed via the fish Tracev* ' al (1969>« Tracy, r a I (19691* Abedl,«t (1968), Alabaster (1969) 5«5 Johnson,et at 11971' • AMlC-38?» ------- Aldrln IC-1* I•belled) Aldrln (C-l* labelled) Hexaqctnla blllneata (nyaoh) Chi ranonus so. (larval BCF — BCF 0.7 (residue) a* 0.5 (residue) a* food chain. sane as above same as above Johnsoni et al (l"»7il, AHIC-38ZO Johnson,et al (197D, AHIC-3878 Aldrln (C-l* labelled! Oaohnla naqna BCF (adult) 0.0001 (SB3) a* same as above Johnson,et al (1971), A1IC-3S79 • Idrln (C-l* labelled) Aldrln CC-1* labelled) Hexagenla blllneata (nyoph) Ch Iron-onus so. (larva) BCF 8CF — 0.0001 (SB3) a* 0.0001(383) a* sane as above same as above Johnson., et al (1971), Johnson, et al (19711, AMIC-3«?0 • Idrln • Idrln Aldrln Fish (not specifled) Tctalurus punetatus Woima papullfera FRLO Tana greater Than 0.001-0.91 0.91 (accumulation, SB) Ha«deslev- Thomas H<71) , AMIC- 1000 (X) ~ Approximate toxlcltles of nuovrous ce«tlcin>s commonly us»d In nrltaln rre summarized. An excellent brief, grnvral discussion of toxlcity testinq is also present. — Edible flesh of fish collected Horrls, et fro* rivers, lakes, ponds, and reservoirs al(1971), was analyzed. Fish taKen In areas AMIC-H5? receiving agricultural runoff shOHed highest accumulation, especial Iv In bottoa feeding fish. Hunter1* All compounds wore harmful to Worthier, at medium duckweed to some degree. Decreased al (1971), diluted populations wore noted at non-1 a thai AMIC-3233 1:5 concentrations and sone comrounO.3 (Hnlathlan and 2,!\|-D) caused teratocenlc effects at concentrations as low as 1 ?p». • Idrln •Idrln Aldrln •Idrln Anacvstls nldulans Aqaenellua quadrup- lloatun Channa punctata Channa punctata BSA BSA NTE NTE a»,c,r SM a»»e»,r SH 0.000166 (K Z a,C hr) 0.000333 (K 30 a,c • in) Hetabollc products of Aldrln, Batterton, Oleldrln, and Endrin can be as toxic as et al (1971), the parent compounds, as sho»n by 00 AMZC-1471 measurement. s»«e as above Ratterton, et al (197l),AHIC- 171 Aldrin Has shown to be more toxic Katbur (1969), than DOT, BHC, dieIdrln, and llndane. AM1C-5U22 Behavioral responses prior'to death Her? recorded In some detail. same as above Hathur (19691.»MIC- ------- Compound Ifdrln Afdrln Organism Puntlus sophore Puntlus soohore arcuate Field Field Study Location BSA BSA BSCH -• and A Toxiclty, Active Ingredient, Ppn O.OOD166 (K 1.5 hr) 0.000133 (K 30 •tin) 1130-1700 ppbresldue 6i» HK) Experimental Variables. Control led or Noted a»,c a»,c 0.01 neeKs each Comments same as above same as above and 0.1 cpb of the toxicants Tor ?5 after Hhich time the amounts added Reference 51.3? Hathur (1969), AHIC- 51.22 Mathur (1969>,AHIC- 51.22 al (1971), AMIC-5506 the Initial amounts. Ulothrlx occurred spontaneously In the test tanks. The results shoH that chronic accumulations In Chlamydotheca exceeded levels which Here toxic In acute tests. Residues In Chlaroydotheca ranqed fro1" 12.000 to 260,300 times Greater than the theoretical Concentrations In the water! those In Ulothrlx Here 235-3,000 tines exposure levels. Aldrln Aldrin Chlamydotheca BSCH arcuata and A Ulothrlx SD. BSCH — 0.0015 (Tl) 0.00001-0.001 <120-1700 opb residue 33-<>8 same as above same as above Kaxatskl, et al (197H ,A1IC- 5506 et al (1971), AMIC-5506 Aldrln Tubltex tub If ex FL and BSA Belzonli Miss. 3.0 (NTE) The response of pesticide-resistant aauatlc organisms to various pesticides Has coloured to the response of non-resistant species. Pesticide-resistant soecles Here collected at Belzonl and non-resistant soeeles at State Colleqe. Cooeoods. clans, snails,, and sludqe norms from Belzonl were considerably more tolerant to pesticides than the non-resistant organisms. The authors note that the effect of Increased tolerance In the organisms is an Increase In the amount of pesticide residues available to animals of higher trophic levels. Naqvi, et al (1969),AHIC- 5979 ------- Hercan aria awcenarla (ego.0 1ha> 11.0 (T2) • Idrln •lelstat •Iqlstat • lolstat Alglstat Alglatat Algletat • Ikyl dlaethyl benzy I aeaienl ua chloride Mercenarla aercenarla I larvae) Cyprlnus car pie Splroqyra L — t — OscillatorI* L — Anabaena Hierocratla Buglena Phoraldiua L •abiautn O.»l IT 1Z) ~ 8.66 (Kl — •.8 flO 0.66 (Kl 0.66 (K> 0.66 (K) 1.0 (1TB) 0.5-10.0 I33p«rcnt qrewth inhibited Ul Tt>» atliiet ol 5? pesticides on Davli. at al ••bryonlc d«vloo«nt of cfavs and (19691 < oysters was reported. Synerqlstle HIC-5998 eftaets with solvents were also reported. Host of the compounds affected dcveloraent a ore than survival. Soaat however t drastically reduced larval aronth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an orqanisa and note the possibility of selecting chealcals for pest control that would not have serious effect on shellfish. saae as above The results are described as preliminary and the authors state that further testing should be conducted before Aigistat Is used In hatcheries and rearing ponds. saae as above Davis* at a I I 19691. HIC- 599« Pal, et al (1968)f Pat, et al (196S). saaa as above saae as above sama as aaM ai above Pal, et al (1968),»KIC- 575 Pal, et al (196«>, NIC-57S Pal. et al (1963). AMXC-57A Pal, et al U9&8). Of 7it chemicals evaluated as alqlcldesi only 9 were more toxic than CuSOd. None Inhibited growth of mat-forming alqae for more than 2 weeks. CuSOi> formulated with certain wetting aqents was more toxic than CuSCH alone. Cooper chlorarlne was also found to be more toxic than CuSOU. No Netting agents were found to be Inhibitory at the concentrations investigated (0.09 and 0.005 ppal. Also reported are factors affecting growth of algae In canals to Otto (19701, AHIC-S9Z ------- Compound Organism Field Field Study Location Toxlclty, Active Ingredient, Ppa Experimental Variables i Control led or Noted Comments Reference Allldene dlacetate Phormldlum amblguum • Myl alcohol Hertenart a •ercenarla 0.5-10.0 (NTEJ — 1.03 ITZ) •llrl alcohol Ally I alcohol Mercenarla •ercenarla (larvaa) Asterlas rubens BSA less than fl.?5 — (T1Z) 10-33 CTZ) Ally I alcohol Cardlua edule USA greater than 100 ITZ» a(contin- uous aer- ation, aea. water, and daily solution renewal) a (contin- uous aer- ation, sea- water, and duUy solution ranawel) determine whether there were leads to controlling algae by environmental •anaqevent. No practical environmental means Mere found. same as above Ottoll970), Davis, «t al The effect of ?2 pesticides on embryonic devetooment of clams and oysters was reported. Synerqlstlc (1969),AMIC- effects Nith solvents were also reoorted. 5990 Host of the eonoounds affected development more than survival. Some, however, drastically reduced larval qrpwth. The authors colnt out the necessity of evatuatinq the effects of Pesticides on all life stages of an orqinlsm and note the possibility of selecting chemicals for nest control that would not have serious effect on shell fish. same as above One hundred-forty surface active agents, solvent emulslfiers, pesticides, polychlorinated blohenyls, pure Inorganic, and organic chemicals were evaluated against as many as ten marine organisms* The authors noted that most published data of this type deal with toxlclty of chemicals to freshwater organisms. same as above Davis,et al ei96<>>, AHIC-5990 Portmann, et al (I97l>, Portmann, et al (19711. ANIC-7701 Ally! alcohol Crangon BSA — qraater than »»(contin- sane as above Portaann, et ------- dlehlorobenzal- doxine HOI crangon Rasbora heteroBorpha BCFA and BSA 100 (T?) 190 (T2) aloha-aBlno-2,6 Rasbora dleniorobenzaldoxlne Ftttaroaoroha BCF* — and BSA (T?) Alualnua Paratabrax clathratus FN Scattergood 25 (dorsal Steaa Plantf nusclc Los reaid.ua) Angeles,Cal. Aluainua Paralabrax clathratus FH Catallna a (dorsal Islandi Cat. muscle residue) uous aer- ation, sea- water, and dally solution renewal) «o,c,e,r, bard I Hit; or soft ISO syn- thetic dilution water, or seawater for aor.e species One hundred sixty-four DestlcldeSt netting aqentSt and miscellaneous Hater pollutants showed a xlde rungr of toxlclty soainlnq 12 orders of magnitude. Knowing the toxlclty and percentage of 81 I components of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides were most toxic In hard water and sometimes the oooosite was true. Testing the actual material as sold was found to be essential. sae as above hard (HHt or soft ISM) synthetic dilution Hater, or seaMater for son species al (14711, AHIC-7701 Alabaster (19691, ANIC-51.35 Alabaster (19691. AHTC-S4.2S Fish collected from an effluent ploe of a steam olant and from offshore waters of Catalina Island were analyzed for trace element content. Trace element content of the effluent water was at least 5 times greater than that of normal se? water for cadmium, coooer, nickel, zinc, and chromium. Livers of fish from the effluent were nearly twice the size of those from the ocean. Greatest differences In concentration occurred with aluirinum, cadmium, and nickel. Silver, barium, lithium, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on marine organisms. sane as above Staoleton (19681.AHIC- 5980 Staoleton (1968). ------- Compound Alualnua '-Im- Alualnua Alualnua Alualnua Alualnua Alualnua Alualnua Alualnu Alualrtww Organls* Paral abrax cl athratus Paralabrax el athratus Paralabrax el athratus Paral »br ax cl athratus Paralabrax clathretus (gravid leaales) Paralabrax el athratus Paral abrax cl athratus Paral abrax el athratus Paral abrax cl athratus Paralabrax el athratus Toxlclty, Experlaental Active Variables. Field Field Ingredient, Controlled Study Location Poa or Noted Coeaents FH Scatterqood 2? (ventral — saae as above Steaa Plant, nuscle Los raaidue) Angeles, Cal. FH Catallna 8 (ventral — saae as above Island, Cal. auscl* residue) FH Scatterqood 28 (gonads — sane as above Steaa Plant, residue) Los Angeles, Cal. FH Catal Ina 38 — saae as above Island, Cal. (gonads residua) FH Catallna 22 (gonads — saae as above Island, Cal. residue) FH Scattergood 28 (liver — saae as above Steaa Plant, residue) Los Angeles, Cat . FH Catal Ina ?« — saae as above Island, Cal. (liver raaidua) FH Scattergood 69 (Intequaent — saae as above Steaa Plant, residue) Los Angeles, Cal. FH Catal Ina 23 — saae as above Island, Cal. (Intequaent residue) FH Seattergood 1* (heart — saae as above Steaa Plant, residua) Los Reference AHIC-S980 Stapl eton (I960), 4HIC-5980 Staoleton (L1IC-5980 Staoleton (1968), Staoleton (1968). AMIC-S980 Staol eton (1968) . AMIC-S980 Staol eton AHIC-5980 Staol eton (1968), AHTC-S980 Staoleton (1968), Staoleton (1968), AHIC-5980 Staoleton (19681, AHIC-S988 ------- Angeles,Cal. Aluminum Aluminum Alualnum Aalnotrlazole ••\|trol-T Parafabrax FH clathratus Paralahrax FH clathratus Paralabrax FN clathratus Fish (not specif l««ll Crassostrea L vlrglnlca (eggs) Cat* Una k Island. Cal. (heart r«idu«) Scattergood 33 (eyeball Steam Plant, residua) Los Angeles,Cat. CatalIna 3 Island, cat. (eyeball raaidue) — greater than 1000 (Kl greater than 10 IT2) •altrol-T Aaltrol-T Crussostrea vlrginlea (larvae) Catiaarus fasciatus a ^^ as* — greater than 10IT1I.) greater than 100.0 CT2) saae as above sane as above same as above Aporoxlmate toxlcltles of nuoerous o«stlcldes cownonly used In Britain Here summarized. An excellent brief, qen«ral discussion of toxlclty testing is also present. The effect of ^2 oesflcldes on enbryonlc dvelocent of clans and oysters was r»oorfrt. Syn»rqltlc effects nith solvents Here also reoorted. Host of the coioounds affecfed develocnent more than survival. Some, however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stages of an organlsr and note the possibility of selecting chemicals for pest control that would not have serious effect on shall fish. same as above Staoleton (19681, AMIC-^BO Staoleton (19681, ANIC-5980 Staoleton (1943). »MIC-?98D Nandesley- Iho'aas (19/1),»NIC- 1056 Davis, et • 1(1969), »MIC-S990 Aaltrol-T Paleoaontes kadiaKens Is BS» ~ greater than 100.0 ------- t Compound Amltrol-T Amltrol-T Amltrol-T Amltrol-T Amltrol-T Amltrol Amltrol Field Field Organism Study Location Asell us BSA — brevlcaudus Orconectes BSA — nals Daphnla maqna BSA — Cyprtdoosls BSA — vldua Leoouls BSA macrochlrus Crassostrea L -- vlrqlnlea (eqqs) Crassostrea L vlrglnlca (larvae) Toxlclty, Active Inqredlentt Ppm greater than 100.0 (T?) greater than 100.0 (T2) 30.0 (TZ) 3Z.O (TZ) qr eater than 100.0 (T2) 733.7 (T2> 255. fc (Til.) Experimental Variables, Controlled or Noted Comments a* sane as above a* sane as above a* sane as above a* sane as above a* sane as above ~ The effect of 5Z pesticides on eobryonlc development of clans and oysters was reoortel. Svnerglstle effects with solvents were also reported. Host of the compounds at fected * * growth. The authors oolnt out the necessity of evnluatlnq the effects of pesticides on all life stages of an organism and note the possibility of selecting chenlcals for pest control that would not have serious effect on shell fish. — sane as above Reference Sanders (1970I.AHIC- Sanders 453 Sanders (1970), A1IC-W53 Sanders (1970). AMIC-1.53 Sanders (1970). «MIC- Oavls, et al (1969) .1IO- 5990 Oavls. et al •1969), AMIC- 5990 Aanonla (plus ohenol Sal no BSA and zinc) galrdnerl 0.5-2.5". «T?I a.c,d,e. Rainbow trout Mere exposed to Brown, et al f,n concentrations of fluctuating levels of (1969), aniionla, phenol, and zinc and to constant AHIC-5993 •Ixtures of the three. Tests with fluctuating levels of toxicants showed that LC50 values were slillar to those for constant concentrations as tonq as the periodicity of the fluctuation did not exceed the resistance tine for the poison. Except when zinc predominated In the mixtures, the fractional toxlclties could be summed to qlve the toxtclty of the mixture. ------- Amaonla •••enla Salao qalrdnerl Salno galrdnerl BSA BSA Anoonlun carbonate Phorraidium plus Copper sulfato arabiguum Aaaonlm chloride Pbormldium plus Copper aulfate ambiguum (1.-2J 22.5-67.5 a,c,d,e, (fluctuating f,m Cone, T 370- greaterthan 700 mln) V5.0 IT greater a,c,d,e. than 700 Bin) f,m 0.5-10.0 (100 percent growth Inhibited Id) 0.5-10.0 (100 percent growth Inhibited ll\|) same as above sane as above Bronn. et at (1969)i Of 7i> chemicals evaluated as alglcldes, only 9 were more toxic than CuSO ------- Field Field Comoound Organism Study Location heteronorpha and USA Ammonium sultanate Rasbora BCFA — • heferomorpha and BSA Ammonium sulfamate Rasbora BCF ~ heteromorpha and BSA Ammonium Irs NH3I leoomls BSA, — macroettlrus L Ammonium (as NM3) Nitzschla BSA, — 11 near Is L Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppot or Noted Conaents 5.7) hard (HM) or soft (SM) synthetic dilution water, or seaxater lor sone soecles 610 (Tl, DH a'.c.p.f. 7.1> hard (HM) or soft 1SW) synthetic <11 1 u t i on Mater, or seaHater •or some soecies 55 (Tl.pH S.OI a,c.e,f. hard (HM) or soft (SH) synthetic dilution water, or aeawater for aorao species >.<> (T4I a«,e, and synthetic dilution water 1.20 (SB5) a»,e, and synthetic dilution water saae as above sane as above This study Has conducted to determine the relative toxlclties of 20 common constituents of Industrial Hastes to a fish, an alga, and an Invertebrate. The experiments Here conducted over a 10-year period for varied purposes. The authors recoanend bloassays with at least three components of the food web. same as above Reference (1969), ANIC-5ii25 Alabaster (1969). AhIC-5«S Alabaster (1969). AMIC-S«?S Patrick, et al (1968), AMIC-5720 Patrick, et al (1968), ANIC-5730 ------- la Amphenon* B Antimony > Antimony Antimony •ntlneny Antimony AntIaony Antimony Antlmyeln A Physm BSA, heterostroona L Lymnaea staqnalIs (adults) 90.0 mi 10.0 ISB71 «»,e,. and synthetic dilution water a»»o same as above Patrick, et at (1961. AMIC-5720 Coregonus FL Moose Lake, 0.002 cluoeaformis Can. (residue) Coregonus FL clupeaformls Esox luclus FL Esox tuclus FL Esox luclus FL Osier us aordax Peree flavescens FL FL Lake Ontario. Can. Moose Luke. Can. Lake St. Pierre Can. Lake Erie, Can. Lake Erie, Can. Lake Erie, Can. Leplsosteus BS», piatostoaus FO 0.003 (residue) 0.003 (residue) 0.001. (residue) O.OOd (residue) 0.00". (residue) 0.003 (residue) 0.000, AMIC-J819 Uthe, et al (19711,AHIC- 3B19 Uthe, et al (1971),ANIC- 3819 Uthe, et ALU971). AMIC-3819 B«rg«r, et al (1969). same as above same as above same as above same as above same as above Liquid and sand formulations of antlmycin A Here tested as a fish toxicant In lab Maters of various temperature, hardness, PH. and turbidity aqalnst 31 species of freshMater fish of various sizes and life stages. Each formulation of toxicant MBS lethal under all Mater conditions to fish eggs, fry, finger IInqs, and adult fish. Trout Mere the most sensitive and cat fishes the least sensitive. Of the 31 species. ?<• ------- Coaoound Antlaycln A Antl.ycln A Antlnyeln A Antlaycln A Antlaycin A Antlaycln A Antlaycln A Organise Aala ealva Sal no galrdnerl Salao trutta Sal vel Inus fontlnal Is Sal vel Inus naaaycush Esox luclus Carasslus auratus Field Field Study Location BSA, -- FO BSA, — FO BSA, — FO BSA, — FO BS», — FO BSA, — FO BSA, — FO Toxlclty, Active Ingredient, Pp* 0.015 (60 percent K> 0.00003-0. DODOS 0.009 (K3> 0.00003-0.00006 0.00007 (TU) 0.00011-0.00059 0.00070-0.001 Experimental Variables, Control led or Noted Comments deionized water a,c,e,f,e, deionized water a.c.e.f »q, deionized Hater a»c,e,f,s, deionized water deionized nater deionized Hater a,c,e,f,g, deionized water succunbed to 0.009 opm or less of the toxicant! only certain catflshes survived 0.025 CPU. saae as above sane as above saae as above saae as above saae as above saae as above saae as above Reference Berger, et al (1969), AHIC-5I.9S Berqer, et al (1969). ANIC-5U95 Berqer, et al (1969). Berqer, et al (1969). • MIC-51.95 Berq»r, et al (1969), Berqer, et al (19691, Berger, et al (1969), ANIC-9«»95 Antlaycln A Cnrosoaus eos BSA, — 0.00009-0.00052 a,C,e,f,q, saae as above Berger, et ------- LeDOBlS glbbosus BS», FO O.OOOOS-O.OOOZ a,c,e,f,E, IT) deionized water sane as above BergPt t a I (1969), 4HIC-5I.9S AntlBycln BS« •acrochlrus FO 0.00006-0.ODDS mt deionlzed water sane as above Berger, «t a I (19691 • • WIC-Si.9 ••ttleycln •ntlaycln » Anttaycln Lvoouls ••galotit BS«, FO Lepouls BS«, •IcreloDhus FO Hlcrooterus BS», deloaleul FO D.OOD08 (TV) 0.00009 d«lonlz«d •atr delonlzed Hat«r O.OOOOV-O.OOOOt a.e.e.f.g, IT) dilution ua tor save as above ••• as above saae as above 6erqerf »t al (1969) i »MIC-5V95 Berqer, et al (1969). •HIC-5V9S B«ro»r, et al (1969). tnttvycln ••(•oldes FO 0.00009-O.OOflllf »,c,e,f,s, deionlzed water cane as above Brq«r, t a I (1969)t •HIC-SV9S •ntlarcln « > BS», nigro- FO •aoulatua 0.001 (V3 percent K) a,c,e,f,s, daionized water sane as above Berqer, t al (1969). tntlaycln A Perce BS», flavescens FO 0.00003-0.00012 «,e,e,f,E, IT) deionized water s«e as above al (196<>», •ntl«rcln * Stlzostedlon BS», vltreu* FO 0.00002-0.OOOOd »,c,e,f,g, dilution water sa«e as above fterqer, et al (1969). •ntlavcln * •plodlnotus BS». orunnlens FO 0.00002-0.0001* a,e,e,f,c. ITI deionizad water sane as above Rerger, et al (1969). HIC-S95 Cyorlnus carolo BSA, FO 0.00012-0.0003 a,c,e,f,g, (T) deionlzed water saae as above Berqcr, et al (1969). ------- Compound Antlaycln A Antlaycln A Antlmycln A Antlaycln A Antlmycln A Antlaycln A Antlaycln A Antlmycln A Antlmycln A Antlmycln A Antlmycln A Orqsnlsm •iaephales promelas Car pio 0. 021-0. 08S 0.0052-0.0105 m> 0.2 CK> 0.0000 ------- FO IT) delonieed Ma tar • I (196911 AntUycIn A •ntlaycln • Antlaycln Saleo galrdnerl Leooals L — aacrochlru* 0.00003 m> 0.00016 ITU a* Salao elarkl Ft Copper Lake. 0.005 (K) Idaho a.c.d.e Antlaycin * Sal BO BS* galrdnerl 0.00009 (TV) Antlaycln A AntlayeIn A Aphltex Ictalurus 8SA punctatus lepoels BS* eacrochlrus Rasbora BCFA heteroaorpha and BSA 0.017 o.oooi m> 27 (TZ) bard (HW) or soft (3W) syn- thetic water, or •eavater tor aona •paelas The plsclcldes Antlaycln A and HoKland Rotenone Here found to be compatible nhen (t969 •Ixed >nd furthereore appeared to have an 5725 additive effect In cnbination. That Is both compounds Here "ore toxic In the presence of the other than alone. sane as above Rapid fish kill occurred In a otlQotrophic situation and toxlctty persisted for at least 10 days following application. Plankton Has also reduced. Later the lake Has successfully stocked •Ith cutthroat trout. The rapidity of kill and persistence Indicated that the Antlaycln concentration Has hlqher than necessary. The authors recoooendrd further research. The dyes Rhodanlne B and Fluoresceln sodlun Here found to be relatively non-toxic In ppe concentrations Hhlle antlnycln Has toxic at oob levels. The author states that neither dye at field use concentrations should significantly Influence the activity of Antlycln A aqalnst fish. saae as above sane as above HOHI and (1969). ANIC-5T2S Rabe, et al (1969), AMIC-573Z Harking (1969). AHIC-5720 Harking (1969). ANIC-S7Z9 Harking (1969). ANIC-57Z9 One hundred sixty-four Alabaster pesticides, netting aaents. and (1969). alscellaneous Hater pollutants showed a AHIC-542? Hide range of toxiclty spanning 12 orders of eagnitude. Knowing the toxiclty and percentage of all coaponents of a foraulatlon did not result In easy predictability of the toxlclty of a alxture of Materials. Soeetiees ------- Field Field Compound Organlsa Study Location Toxlclty, Active Ingredient, POU Experimental Variables. Control led or Noted Comments Reference Aauaclene lap Aquaclene 100 •quaclene 100 Aauaclene Plmephales BSA or owe I as Pimephales USA prone I as Biochemical L oxygen deaand Cardlua edule BSA 35.0 (T%» .Z (NSC) 80,00 33-100 «T2» •quaclene Crangon crangon BSA 100-330 (TZ> soeeles pesticides Here most toxic In hard Mater and sometimes the opposite Has true. Testing the actual material as sold Mas found to be essential. c,d,e,f Toxlclty of six oil spill dlspersants Has determined along Kith 800 values. Pond Hater Mas used as diluent and oil Has Included In the experiment. Oil markedly reduced toxlcity of all disoersants. Data are given as "most probable* gft-hr TL sub m. dd,e, f sane as above c,d,e,f same as above a>t(contin- One hundred-forty surface active uoua aer- aoents, solvent emulsifiers, Pesticides, atlon, sea-polychlorlnated blohenyls. Pure water, and Inorganic, and organic cheitlcals Here •Jaiiy evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal Kith toxlcity of chemicals to freshwater organisms. a«(contln- same as above uous aer- ation, sea- water, and daily solution renewal) 71 Mich <19>9),AMIC- 7909 711 IIch (19«i9),AHIC- 2909 ZlIllch (1969I.AH.T.C- 2909 Portmann, at al (1971), •iic-7701 Portmann,et at 1197II, •MIC-7701 •quatheI Horone saxatllli Cflngarllngsl BSA — 710 (Tl>) a,c,d,e,f. All compounds Here Investigated Wellborn p becauso of their probable usage in (1971), hatchery production of Mhite bass. AMIC-5571 Comoounds that can be used at recommended concentrations Mere Aquathol, Casaron, LIndane, and Terraaycln concentrate. Those that should not be used Mere Acrlflavlne, Baylusclde, Malachite green oxalate, and Malathlon. ------- Mere Is vlrens BSA 0.00011-0.OOOVI, 8",c,e, and synthetic seanater Ar he tine DOT Fundulus BSA heteroclItus Rasbora BCFA heteroaorpha and BSA 0.00032-0.00035 a«c,e.and synthetic seanater A laboratory procedure based on Standard Methods lor 9«>-hr loxlclty determinations of cruel* ell and oll-dlsper«nt Mixtures was described. The dlsoersants varied considerably In toxlclty, ranging fro 0.01 to 7.1 inl/l, TLSfl for 9fi hr. These did not differ significantly fro* ? ------- Compound Organise) Field Field Study Location Toxlclty. Active Ingredient, Ppa Experimental Variables, Control led or Noted solution renewal) Comments Reference •rector t9onus BSA — cataphraetus greater than 10 a«(contln- ITZI uoua aer- ation, sea- water, and dally solution renewal) sane as above Portmann. at at (1971), »HIC-7701 tree Ior 12« Cardlua edule BSA — greater than Itt ,a»(contln- IT2) uous aer- ation, sea- wetar, and dully solution renewal) sane as above et al C1971I. »HIC-770l •roc Ior 1?8 Crangon crangon BSA — O.OS-1.0 (T2)' a«(contin- uous aer- ation, aaa- wator, and dally solution renewal) sae as above Portmann, et al (1971), AHIC-7701 •rector 175 (plus Gorexlt 7661 Salno sal IparrI ar t (K 90 hr) •rocIor 125* <»lth eorexlt 76«, colloidal solution! Caemarus ocean Icus BSA ~ 0.001-0.01 (threshold concentration) a,e Aroclors t?^<> and 1721 Mere (nixed tap evaluated lor toxic effect with Corexlt or 766* (Height ratio 1:19) a« an seanater) enulslfylnq aqent. Since only tito fish were used for each exposure, me author notes that the results are only preliminary. However, RGB's appeared to be less toxic to Atlantic salnon parr than chlorinated hydrocarbon pesticides. Zltko (1970>,AMIC- ?3 a«( weekly- solution chan^o, aeawater) Aroetor 1?;* solutions or suspensions with Corexlt 766* at varied concentrations In seaxater resulted in varying toxlclty of the Aroclor. Corexlt •as not lethal at 1900 po« but caused WHdlsh (1970),AMIC- 69 ------- •roc I or 125* (tilth Gammarus corexlt 766 ------- Compound Organism (Juvenile) Field Field Study Location Toxlctty, Active Ingredient, Ppm Experimental Variables. Controlled or Noted Comments Reference Aroclor 1251. Aqonus eataphractus heoatopancreas Has narked (up to 510 AHIC-261.5 PPM). The biological half-life for this chemical Has found to be 17 days with tissue distribution In the shrimp being similar to that of DOT. Delayed mortality Kith no prior poisoning symptoms Has also observed. Considerable additional data are oresented. greater than 10 a«(contin- One hundred-forty surface active Portmann, et (T2I UOU3 aer- agents, solvent emulsl tiers. oestlcidesf al (1971), at! on, sea-pol ychlorlnated blphenyls, pure AHIC-7701 water, and Inorganic, and organic chemicals Here evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal with toxiclty of chemicals to freshwater organisms. BS» — solution renewal) Aroclor 1251. Card!urn edule BSA qreater than 10 »(contln_ uous aer- ation, sea- water, and daily solution renewal) same as above Portmann, et al (1971), »HIC-770t Aroclor IZSt Crangon crangon BSA — 3-10 (T2) a«( contin- uous aer- ation, sea- water, and solution rene-..-al ) saae as above Portmann, et al (1971),AMIC- 7701 Aroclor 1251. Parallchthys FH sp. Cscambla Bay, Fia. t. 5-181, Iros1 due) Residue analysis of dead and dying animals led to the source ol the PCS Mhich Has an accidental leakage from an Industrial clant. The concentrations of the PCR in Hater and sediment nere less than 0.03-1.86 and less than 0.001 ppm, respectively. Bioassavs shOH<d juvenile shrimp to be the most suseDtlbl» species* but inhibition of shell qroHth of oysters Mas the most sensitive parameter studied. Continued surveillance and long-term testing at sublettal concentrations Her* pointed out as urgently needed. Duke, et al (1970), AMIC-720 ------- tractor 125* •roclor 125* •roc I or 125* •roclor 125* •roclor 125* troclor 125* •roctor 129% •roc I or •roclor 125* •reel or 125* •roclor 125* •roclor 125* Laqodon rhonboides ()uvenll«) Penaeus duoraru* (Juvenile) Crassostrea vlrglnica P»naeus duorarui* (Juvenile) Penaeus duoraru* (Juvenile) CalIinectes saoidus (Juvenile) CalIinectes saoldus (Juvenile) Mlcroooqon undulatus Brewoortla oatronus Laqodon rhomholdes Cynosclon nebulosus Penaeus setlferus BS« BS» — 8S« BCHCF — BCMCF — BCHCF BCHCF — FM FM FH FM Eseambla Bay, Fla. Esc*bla Bay, Fla. F«canbla Ray, Fla. fscant la Bay, Fla. Fscaabla Bay, Fla. 17 (residue) 3.9 (residue) 0.1 (SB) 0.1105 172 oercent K?0) 0 (residue) 0.005 (Soercent K20) 23 (residue) 1? (residue) 5.7-11(residue) — 10 (residue) 7.5-20(residue) — 1.5-2.5 (residue) sane as above sane as above sa»e as above sane as above same as above sane as above sane as above sane as above same as above same as above sane as above sane as above et 70), •NIC-730 Duke, et •L(1970), AMIC-720 DuKe, et al (1970),»MIC- 720 Duke, et al (1970) , Oukr, et • LU970), •MIC-7JO Duke, et al (1970), AMIC-720 Duke, et •1(19701. AMIC-720 Duke, et al (1970) , ANIC-720 Duke, et a I (1970), AHIC-720 Duk, et al (1970), •MIC-72D Ouke, et al (1970), AHIC-720 Duke, et al (1970), ------- > I Compound •roc I or 135 •rector 125* •roc lor 125* •roc lor 1260 •roc lor 1260 •rector 1260 Aroelor 1262 Field Field Organise Study Location Calllne-ctes FH Escaabla sapldus Bay, Ft a. Laqodon BSA — rhomboldes (Juvenile) Penaeus BSA — duorarua (Juvenile) Agonus BSA cataphractu* Card tun edule BSA — Crangon BSA -— erangon Agonus BSA — cataphractui ToxlcJty, Active Ingredient, Po« 1.0-7.0 (residue) 0.1 (NTE) 0.01 (KZ> less than 10 «T2) less than 10 (T2) less than 10 (T2) less than 10 (T2) Experimental Variables, Controlled or Noted Coaeents — sane as above •— same as above sex* as above a»(contlii- One hundred-forty surface active uous aer- agents, solvent enulslf lers, pesticides. at ion, aea-DOlychlorinated Mohenyts, pure water, and Inorganic, ana organic cheirlcats x»re daily evaluated against as nany as ten narine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organises. a«lcontln_ saee as above uous aer- ation, aea- wator, and daily solution renewal ) a* (con tin- see* as above •uous aer- ation, sea- water, and daily solution renewal) aUcontin- »«• » »bove uous aer- ation, sea- water, and Reference AMIC-720 DuKe, et I (1970J, AMIC-720 DuKe« et AL(1970), AMIC-72,0 OuKe, et AK1970), AMIC-720 Portnann, at (1<)71) AHIC-7701 Portaann, al (19711 AHIC-7701 Portwann, al (1971) AMIC-7701 Portaann, at (1971) ANIC-7701 ll et t • t t • t t • t • ------- •roc Ior 1262 Cardlum edule BS» — less than 10 IT2) daily solution renewal) a«(contin- uous aer- ation, sea. water, and dally solution renewal) same as abovo Portmann, «t at (1971). •MIC-7701 •rector 1Z6Z Crangon erangon BS» — less Than 10 a«(contin- uous aer- ation, aea- wator, and dally solution renewal) same as above Portmann. at at (1971), »MIC-77fll Arsenic • losa pseudo- harengui FL Arsenic •rsonic •r sonic Arsenic Coregonus FL artedll Coregonus FL eluoeaformls Coroqonus FL ttoyl Prosoplum FL cyllndraeeum Croat LaKos - Superior, Michigan, and Erie O.OZ3(resldue> — Grcit LaHes - Superior, Michigan, and Erie Great LaKos - Superior, Michigan, and Erlo Groat Lakes - Superior, Michigan, and Erlo Great Lakes - Superior, 0.069lroslduel — O.Olt(resldue) — 0.063(rosldu> 0.0056(resldue) — Trace element content of fish from Lakes Superior, Michigan, and Erie Has determined by activation analysis. Whole body and liver residues Here determined. Concentrations varied with species and lake. Other elements found Here antlnony - 5 to 100 ppb, barium - 0«2 opm, cesium - 3 ppb, lanthanum - 1 to 20 OPb, mercury - 10 opb, rhenium - 0.5 to 5 ppb, rubidium - 0.06 to 6 ppm, scandlu* - 7 ppb, selenium - 0.1 to 2 ppb, silver - 0.001 ppb. same as above Lucas, et (1970). 4MIC-3778 at same as abovo same as abovo sane as above Lucas, et at (1970), AMIC-3778 Lucas, et at (1970), •MIC-3778 Lucas, at al (1970), AMIC-3778 Lucas, et al (1970), ------- s Compound Arsenic Arsenic Ar sen i c Arsenic Arsenic Arsenic Arsenic Arsenic Arsenic Organism Salvellnus namaycush Osmerus mordax Carasslus auratus No tr op Is hudsonlus Percopsls pmlseomayeus Roccus chrysops Perca f lavescens Stizostedlon vl treum vltreum Coregonus clupeaformls Field Study FL FL FL FL FL FL FL FL FL Field Location Hlchiqan, and Erie Great Lakes - Superior, Mlchiqan, and Erie Great Lakes - Superior, Hlchiqan, and Erie Great Lakes - Superior, Hlchiqan, and Erie Great Lakes - Superior, Hlchiqan, and Erie Great Lakes - Superior, Michigan, and Erie Great Lakes - Superior, Michigan, and E.-le Great Lakes - Superior, Hlchiqan, and Erie Great Lakes - Superior, Michigan, and Erie Hoose Lake, Can. Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments 0.0l>9(resldue) ~ same as above 0.020 (residue) ~ same as above 0.006(resldue> — same as above 0.0035(resldue) -- same as above O.OZ9(resIdue) — same as above 0.098(resldue) — same as above 0.007(resldue) — same as above 0.098(resldue) ~ same as above 0.09 (residue) -- Concentrations of 13 toxic elements in dressed fish fro* heavily Industrialized and non-industrial ized Reference AMIC-3778 Lucas, et al (1970), AHIC-3778 Lucas, et al (1970), AMIC-3778 Lucas, et al (1970), AMIC-3778 Lucas, et al (1970), SMIC-377S Lucas, et al (1970), AMIC-3778 Lucas, et al (1970), AMIC-3778 Lucas, et al (1970), AMIC-3778 Lucas, et al (1970), AMIC-3778 Uthe.et al (1971), AMIC-3819 ------- •runic Arsenic Arsenic Arsenic Arsenic Arsenic AsuliM (K s»ltl Coregonus FL clupeaformls Esox luclus FL F.SOX luelus FL F.SOX luclus FL Lake Ontario* Can. Hoose Lake, Can. Lake St. Pierre, Can. 0.7 (residue) 0.05 (residue) — 0.09 (residue) — Osmerus •ordax Perca flavescens FL FL L»ke Erie. Can. Lake Erie, Can. Lake Erie. Can. 0.0? (residue) — 0.19 (residue) — 0.05 (residue) — Rasbora 8CFA heteromorpha and BS» 5.260 (Tl, hardxater) a,c,e,f . hard (HW) or soft (SH) synthetic a II u 1 1 on nnt<>r, or Asuluej IK salt) ffasbora BCF» heteromorpha and BS i,roo (Ti, soltnater) for some soecles a,c.«,f. hard (HW) or soft ISM) synthetic dilution Hater, or seanater areas Mere deternlned. Only aercury exceeded regulatory limits, and concentrations of most elements Here essentially the sane in fIsn fro both areas. sa«e as above sane as above sa«e as above same as above sane as above sane as above One hundred sixty—four Hwttinq agents, and miscellaneous Hater pollutants shoned a Hide range of toxielty spanning 12 orders of magnitude. Knoxlnq the toxielty And percentage of all components of a formulation did not result In easy predictability of the toxielty of a mixture of materials. Sometimes pesticides Here most toxic In hard Hater and sometimes the opposite Has true. Testing the actual material as sold was found to be essential. same as above Uthe, etat (197H, •MIC-3B19 Uthe, et at (19^1) ,»MIO 3819 Uthe, e.t AMIC-S819 Uthe, et al (1971), MIC 3814 Uthe, et al (1971 3819 Uthe, et AL(1971), (NIC-3819 Alabaster ( 69), 4HIC-5I.2S Alabaster(19 69), AMIC-5«i2S ------- Field Field Compound Organise Study Location Asuntol (sheep dip) Rasbora BCFA — hater oner oha and BSA Atlas 1401 Cardlua «dul« BSA — Atlas 1901 Crangon BSA — crangon Atlas 1901 Pandalus BSA •ontagul Toxlclty, Experimental Active Variables, Ingredient, Controlled PPM or Noted Comments for some species 0.0<>6 (TZ> a,c,e,t, sae as above hard (HHlor soft (SHI synthetic dilution Hater, or seawater for some spec les 33-100 (T2) a»(contln- One hundred-forty surface active UOU3 aer- aoents, solvent eiiulsl f iers, pesticides. ation, sea- po' ychlorlnated blohenyls« pure water and morqanlc, ana orqanic cheitlcals were diily evaluated against as many as ten narlne solution organisms. The authors noted that nost renewal) published data of this type deal with toxlclty of chemicals to freshwater organlsns. 100-330 (TZ) ac(contin- sane as above uoua aer- ation, sea- water, and daily solution renewal) 33-100 «T8) a(contin- sane as above uoua aer- ation, see- water, and dally solution renewal) Reference Alabaster, (1969) ,AHIC- 51.25 Porfnann, et al (1971J,AMIC- 7701 Port«ann, at al (1971), AHIC-7701 Portaann, et al (1971). AHIC-7701 Atlavar Rasbora BCFA h«teroorpha and BSA 1,300 (T2) ft,c,e,f, One hundred sixty-four Alabaster bard (HWJ pesticides, netting aqents, and (1969), or sort ulscel laneous water pollutants snowed a AH.IC-5<>25 syn- Hide range of toxlclty spanning 12 orders ------- Atrezlne Carelnu* •aenas SSA — 100 ITZ) than Atraxine Cardlua adula 8SA — greater than 108 u> tbetlc of magnitude. Knowing the toxlclty and dilution percentage of all components of a water, or formulation did not result In easy seawater predictability of the toxlclty of a Tor sosie Mixture of materials. Sometimes species pesticides Here most toxic In hard water and sometimes tn* opposite Has true. Testing the actual material as sold was found to be essential. a,»(coatln- ' One hundred-forty surface active uoua aer- agents, solvent enulslflerst pestlcldest ation, sea- polychlorlnated blphenylst pure water, and Inorganic, and organic chenlcals were dally evaluated against as many as ten marine solution orqanlsas. The authors noted that aost renewal) published data of this type deal Hlth toxlclty of cheelcal* to freshwater organises. a«Icontin- uous aer- ation, sea. utter, and dally solution renewal) same as above Portxann, et al (1971), •NIC-7701 PorTmann, et a I (1971), •MIC-7701 Atrazine Crangon crangon BS« — 10-33 (T2t a* (contin- uous aer- ation, aea. water, and Oally solution renewal) saae as above Porfmann, at al (19711, •MIC-7701 Avatfex 8H •asbora BCFA heterenorpha and BSA 6 (T2) a«,c,e,f. bard (KW) or soft (SV) syn- thetic dilution miter, or sea water for some species One hundred sixty-four Alabaster pesticides, HCftlno aqents, and (1969), miscellaneous water oollutants showed a AHIC-S4K Hide range of toxlclty scanning 12 orders of magnitude. Knowing Tne toxlclty and percentaoe of all components of a formulation did not result In easy predictability of the toxlclty of a elxture of Materials. Sometimes pesticides Here most toxic In hard Hater end sometimes the opposite was true. Testing the actual Material as sold Has found to be essential. ------- Toxlclty, Active Field Field Ingredient, Compound Organism Study Location Ppm Avadex Rasbora BCFA ~ B.Z (TZ) heteromorpha and aSA Az Inphosme thy) Fish (not — — greater than specified) 0.01-0.1 (K) Experimental Variables, Control led or Noted Comments a»,c,e,f , hard (HHI or soft (SH)synthe tic dilution Hater, or soanater for soe species — same as above Approximate toxlcltlvs of numerous pesticides commonly used In Orl-talr Here summarized. An excellent brief, general discussion of toxlclty testing Is also pri-s»nt. Reference Alabaster (1969), AMIC-5I.Z5 Mawdeslev- Thomas(1971l AMIC-1056 Az Inphosme thy I I UJ Carclnu •aenas USA 0.033-0.1 (TZ) at(contin- One hundred-forty surface active uous aer- agents, solvent emulslflers, pesticides, atlon, see-polychlorlnatod blohenyls, pure water, and. Inorganic, and organic chemicals Here dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. tzlnohosaethy I Cardlun edute BSA — greater (TZ) than 10 a«(contin- uous aer- ation, sea- water, and dally solution renewal) sa«e as above Portmann, et al (1971), ANIC-7701 Portmann, et al (19711. AHIC-7701 »2lnphos«ethyl Crangon crengon BS« — 0.0003-0.001 (TZ) a«( contin- uous aer- ation, sea- water, and dally solution renewal) same as above Portmann, et al (1971), »HIC-7701 AZlnphotMthyl LIvanda BSA 0.01-0.03 (TZ) a»(contin- saac as. above Portmann, et ------- llmanda uous aer- ation, sea- water, and daily solution renewal) al (1971), AMIC-7701 AzlnDnosmethyl Panda 1 us montaqul as* Azlnphos ««thvl Rasbora BCFA heteromorpha and 8SA 0.0003-0.001 CT2) 0.076 (T?) U) Bacterial •ndotexlns Salmo qalrdnerl (1.00-5(10 q> 10 (NTEt Bacterial tndotoxlns Oncorhynchus klsutch C.00-500 q> Balan Gammarus fasclatus BS» ~ 10 (NTE) 1.1 IT%) a«(contln- same as above Portmann, at uoua aer- al (1971), ation, sea- AMIC-7701 water, and daily solution renewal) a,Cte,f, One hundred sixty-four Alabaster hard (HH> pesticides, Netting aqents. and (1969), orsott mlscpl laneous Mater ootlutants showed a AMIC-5«»?S (SW) Hide ranqe of toxlclty soannlnq 12 orders synthetic of maonltude. Knoxlnq the toxlclty and dilution oercentaqe of all conoonents of a xater, or formulation did not result In easy seauater predictability of the toxlclty of a for some mixture of materials. Sometimes species pesticides Here most toxic In hard Hater and soiretlmes the opposite Has true. Testinq the actual material as sold Has found to be essential ™ Salmon and trout were Injected Medemeyer* Hlth endotoxins preoared from Eseherlchla et at coll and Aeromonas salmonicida. No significant cardiovascular response or effect on liver tryptoohan pyrroles* activity in vitro occurred. It Has concluded that metabolic effects of bacterial endotoxins In salaonids are qualitatively different from those of hlqher vertebrates. same as above (1968), AMIC-3771. Wedemeyer,et al (196B), AHIC-377* Of the aquatic Heed herbicides Sanders evaluated, Olclone Has the most toxic, (1970), Oaphnia Has generally the most sensitive AMIC-WSJ organism. All of the Crustacea Here affected by «uch lower concentration levels of herbicides than Indicated by the Tl sub 50.values. All ot the animals ------- Coaoound Field Field Organise Study Location Toxlclty, Active Ingredient, Pom Experimental Variables, Controlled or Noted Consents Reference Banner 0601 Crangon BSA — crangon 10-33 (T?) Banner OG02 Crangon crangon BS* 10 «TZ> > I represent Important food chain links. a«(contin- One hundred-forty surface active uous aer- aqents, solvent emutsiflers, pesticides, ation, raa-polychlorln»ted blohenyts, pure water, and inorganic, and organic chemicals were daily evaluated against as aany as ten Marine solution organisms. The authors noted that aost renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. a«(contln- saae as above uous aer- ation, sea. water, and dally solution renowti) Portaann, et a I (1971). AHIC-7701 Portaann, et al (1971). ANIC-7701 ••mar 0603 Crangon crangon BSA 19-33 IT?> a«(contin- uous aer- ation, sea- water, and daily solution renewal) saae as above Portaann, et al (1971), AMIC-7701 tanner 060* Crangon crangon BSA •— 10-33 ITZ1 a«(contin- uous aer- ation, sea. water, and dally solution renewal) saae as above Portaann, et al (1971). ANIC-7701 •arban Rasbora heteroMorpha BCF* and BSA 0.91 (TZ) a,c,e,f. One hundred sixty-four hard (HH) pesticides, wetting agents, and or miscellaneous water pollutants showed a SOFT(SH) wide range of toxiclty spanning 12 orders synthetic of Magnitude. Knowing the toxlclty and dilution percentage of.all components of a Alabaster (1969). ------- Barium Paralabrax elmthrafus FH > Barium Barium Barlua Barlua Barlua Barium Paralabrax FN clathratus Paratahrax clathratus Paralabrax clathratus Paralabrax elathratus clathratus Paralabrax clathratus (gravid FN FN FN Scattergood ? (dorsal Steam PI not, muscle LosAngeles, residua) Cal. water, or formulation did not result In easy seawater predictability of the toxlelty of a for some mixture of materials. Sometimes species pesticides Here most toxic in hard water and sometimes the ooposlte was true Testlnq the actual material as sold was found to be essential. — Fish collected froin an effluent Staoleton ploe of n stenm olant and from offshore t!968)« waters of Catallna Islana were analyzed HHIC-5980 for trace element content. Trace element content of the effluent water was at least 5 times greater than that of normal sea water for cadmium, coooer, nickel, zinc? and chromium. Livers of fish from the effluent were nearly twice the size of those from the ocean. Greatest differences in concentration occurred with aluminum, cadnlun, and nickel. Silver, barium, lithium, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the •ffect of pollutants on Marina organises. Catatlna 1.7 (dorsal Island, Cal. muscle r«sldu«) Scatterqood !.<> (ventral Steam Plant, muscle LosAnqeles, raaidua) Cal. Catallna 1.3 (ventral Island, Cal. Muscle r»iidu«) Scattergood 7.8 (gonads Steam Plant, residue) lostnqeles, Cal. Catalina Z.6 Island, Cal. (gonads raaldua) Catatlna 2.2 Island, Cal. (qonads residua) same as above same as above same as abova saac as abova same as abova same as abova S taoleton (196M, Staoleton (196!) .AM.IC- Staoleton (1968). A1IC-S9SO Staoleton (1948). ANIC-5980 Stapleton (1968). AHIC-5989 Stapleton (1968). AHXC-S980 ------- > Coaoound •awlua •arlua Barlua ••rlu* •arlua •arlua Barlua •arlua •asol AM Organise Paralabrax el athratus Paratabrax cl athratus Paralabrax elathratus Paralahrax elathratus Paralabrax elathratus Paralabrax elathratus Paralabrax elathratus Paralabrax el athratus Cranqon cranqon Field Study FH FM FM FN FH FM FM FM as* Field Locat Ion Seatterqood Stean Plant, LosAnqeles. Cal. Catal Ina Island, Cal. Seatterqood Steaa Plant, LosAnqeles, Cal. Catal ina Island, Cal. Scattergood Steaa Plant, LosAnqeles, Cat. Catallna Island, Cal. Seatterqood Steam Plant, LosAngeles, Cal. Catal Ina Island, Cal. Toxicity, Active Ingredient, Ppa !.<• (liver residue) 1.8 (liver residua) 2.8 (Intequaent residue) 1.6 (Integuaent raaidua) 1.2 (heart residue) 2 (heart residua) 5.8 (eyeball residue) 9.1 (eyeball residua) 10-33 (T2I Experlaenta Variables, Controlled or Noted — — — ~ — — — — a«( contin- uous aer- ation, sea- water, and solution renewal) 1 Coaaents saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above One hundred-forty surface active agents, solvent eaulslflers, pesticides, polychlorlnated blohenyls, pure Inorqanlc, and orqanic che»lcals nere evaluated aqalnst as nany as ten aarlne organises. The authors noted that aost published data of this tyoe deal with toxlclty of ehealcals to freshwater organ ISMS. Reference Staoleton (1968). ANIC-S980 Staoleton 11968), Staoleton (1968). AMIC-MSO Staoleton 11968) , AMIC-5980 Staoleton 11968), AHIC-5980 Staoleton (1968), AMIC-5980 Staoleton (1968), AMIC-5989 Staoleton (1968). AMIC-S980 Portnann, et at (1971), AHIC- 7781 ------- ••sol 99 Rasbora hateroaerpha BCFA and BS» 1.2 NO Bayer 39(07 Rasbora BCFA heteromorpha and BSA 1* (TZ, hardwater) Bayer 39DD7 Rasbera heteromorpna BCFA and BS* 7.5 (T2, softwater) BayIuseIda Moron* saxatllis If IngerlInqsl BSA — 0.78 (T3) »",cTe,f , hard (HH)or soft (SW) synthetic dilution water, or seaxafer tor some soecies hard (HH)or sott (SH) synthetic dilution •at«r. or scaMater for son« soecles a,c.d,«,T. P same as above Alabaster (1969), same as above Alabaster (1969), AMIC-5«i2S All compounds were Investigated Wellborn because of their probable usage in (1971), hatchery production of white cass. AMIC-5571 Compounds that can be used at recommended concentrations were Aquathol, Casaron, Llndane, and Terramycln concentrate. ------- Compound Baytex Baytex Baytex Baytex Baytex Baytex Baytex Baytex Organism Orconectes nals Procambarus slmulans Channel catfish Roccus saxatllls Dragonf 1 les (larvae! Whirligig beetles BacKsNimmers Ictaturus punctatus Toxlclty, Active Field Field Ingredient, Study Location Ppm FP Pratt, 0.1 (Kit! Kansas FP Pratt, 0.1 (K<.) Kansas FP Pratt, 0.1 (NTEO Kansas FP Pratt, 0.1 CNTEU) Kansas FP Pratt, 0.1 (Kl Kansas FP Pratt. 0.1 (Km Kansas FP Pratt, 0.1 (KO Kansas BSA — 1.66 mi Experimental Variables, Control led or Noted Comments a,b,c,d,e, ,9.P a,b,c,d,e, f ,9,P a,b,c,d,e, f ,q,p a.b,c,d,e. a,b,c,d,e, f ,9,P a,b,c,d,e, f ,9,P a,b,c,d,e. a, synthetic Those that should not be used were Acrlflavlne, Baylusclde, Malachite green oxalate, and Halathlon. Baytex applied at various rates up to ?50 PDb resulted In significant reduction of crayfish. Ponds treated at less than 100 ppb had to be retreated to eradicate crayfish. This chemical appears to have utility in fish culture for controlling crayfish. same as above same as above same as above save as above sane as above same as above Organochlor Ine insecticides Here the most toxic compounds. Reference Ray, et al (1970) , AMIC-51.33 Ray, etal (1970) , Ray, et al (1970), AHIC-S ------- > •p- Baytax Bayt«x Baytex Baytex Baytex Baytex let slur us •el as Carass 1 us auraTus Cyprlnus carplo Plneohales eronelas Lepools •aerochlrus leoonls •Icroloohus BS» — BSA — BSA — 8S» BS» BS« 1.62 (Tl.) 1.16 (Tfc) (Tli) 1.38 (U) 1.8S (Tit) a. synthetic test water a. synthetic test Mater a» synthetic test water a, synthetic test Mater 8, synthetic test Mater a, synthetic test water centrarchlds would likely be safe for cvorlnlds and Ictalurlds. Sate levels for Ictalurlds or cyprlnlds would probably be hazardous for centrarchlds and salBonlds. The use of goldfish In bloassays was discouraged. sane as above sane as above sane as above saae as above sane as above sane as above HaceK, et al(1970). AMIC-5510 HaceK, et • K19TO), AMIC-5510 HaceK, et al(19ro) , • NIC-5511) XaceK, et 81(1970). AHIC-5510 HaceK, et • H1970), HaceK, et al (1970) . ANIC-5510 Bsytex Baytex Baytex Baytex Baytex Mlcrooterus salnoldes Salae galrdnerl BSA ~ BSA — Sal no trutta BSA Oncorhynchus BSA Klsutch Perea flav«se«n< BSA — 0.93 1.33 (Tl.) 1.3Z (T%) 1.6S (Tit) a, synthetic test Mater a. synthetic test water at synthetic test water a. synthetic test water a. synthetic test water saae as above sane as above saae as above saae as above sane as above HaceK, et al (19/0), ANIC-5519 HaceK, et al (1970), AMIC-SSIO HaceK, et al (1970). AMIC-5510 HaceK, etal (1<<70) , AHIO5S10 HaceK, et al (1970). AHIC-5510 Baynood %I Rasbora BCFA B«0 (TZ) a,c,e,f, One hundred sixty-four Alabaster ------- 15 Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled CoBDOundJ Organism Study Location Pom or toted Comments heteroMorpha and hard (HH> BSA or SOFT(SH) synthetic dilution water, or seawater for some species inazolln Rasbora BCFA — 325 ITZ) a«,c,e,f. heteromorpha and hard (HW) BSA or soft (Sif) syn- thetic dilution water, or •eawater for - aoma •paclea >nsullde Cammarus BSA — !.«. (T%) a fasclatus pesticides, wetting agents, and miscellaneous water pollutants showed a wide range of toxlclty soannlng 12 orders of magnitude. Knowing the toxlclty and percentage of all coxoonents of a formulation did not result In easy predictability of the toxlcity of a mixture of materials. Sometimes pesticides were most toxic In hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. One hundred sixty-four pesticides, wetting agents, and miscellaneous water pollutants showed a wide ranoe of toxlclty scanning 1? orders of magnitude. Knowing the toxiclty and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides were most toxic in hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. Of the aquatic weed herbicides evaluated, Dlclone was the most toxic. Reference (1969). AHIC-51.25 Alabaster (1969), AHIC-5V25 Sanders (1970), •HC (Plus llndane) Hhlta sucker FRL Nice, states 0.01-0.2? residua (SB) Oaphnla was generally the most sensitive organism. All of the Crustacea were affected by much lower concentration levels of herbicides than indicated by the TL sub SO values. Alt of the animals represent Important food chain links. The Bureau of Sport Fisheries continued Its fish monitoring program by collecting 1<»7 composite fish samples from 50 nationwide monitoring stations during the fall of 1969. Fish were analyzed for residues of 11 organochlorlne Insecticides, Holds, and PC9-S. Henderson, et al (1971), AHIC-H.07 BMC (olus Itndane) Tel low parch FRL Misc. states 0.01-0.31 same as above Henderson, ------- residue (SB) • t al (1971), §MC fptuc llndenel Chain pickerel FRL Mite. states 0.07 residue (SBt BMC (plus llndanel White catfish FRL Misc. states 0.33 residue CSB) saae as above save as above Henrterson, et al (19711, »MIC-HD7 Henderson, et at Nic-i«»o7 BMC fetus llndanel White perch FRL Hlsc. states 0.18-0.26 residue ISO)' saae as above Henderson, et at (19711 , »MIC-1«.07 BHC (plus llndanel Goldfish FRL Hlsc. states 0.51 residue (SB) saae as above Henderson, • t al BHC lotus llndane) Puapklnseed FRL Hlsc. states 0.09 residue (SB) saee as above Henderson, et al 0HC (plus llndane) largeaouth FRL Hlse. states 0.01-0.47 bass residue (SB) saae as above Henderson, et al (19711 , 4HTC-1U07 BMC (otws llndane) Brown FRL Misc. states 0.01-«.37 bullhead residue (SB) sane as above Henderson, et al •MC (plus llndane) Carp FRL Hlsc. states D.01-0.99 residue (SB) saae as above Henderson,et al (1971), • NIC-11.07 •MC (plus llndanel Channel catfish FRL Hlsc. states 0.01-1.50 residue (SB) saae as above Henderson, et al (1971), BMC (plus llndane) Redhorse FRL Misc. states 0.02-0.10 sucker residue (SB) saae as above Henderson, et al (1971), AHIC-1<»07 ------- Compound Field Field Study Location Toxlclty, Active Ingredient, Pom Experimental Variables, Controlled or Noted Comments Reference BHC lolus llndane) Gizzard shad FRL Hlsc. states 0.06-0.10 residue (SB) BHC (plus llndaneI Spotted sucker BHC talus llndane) Bluegllls BHC (plus llndane) Striped mullet FRL Hlsc. states 0.01-0.03 residue (SB) FRL Hlsc. states 0.01-0.02 resIdue(SB) FRL Hlsc. states 0.?8-1.1<» residue (SB) BHC (Plus llndane) Blue catfish FRL Hlsc. states O.lt residue (SB) BHC (plus llndane) Rock bass FRL Hlsc. states 0.01-0.1<. reslduelSB) BHC (Plus llndane) Freshwater FRL Hlsc. states 0.01 residue drum (SB) BHC (plus llndane) Bloater BHC (plus llndane) Lake •hitefIsh BHC (plus llndane) Lake trout FRl Hlsc. states 0.03-0.08 residue (SB) FRL Hlsc. states 0.05 residue(SB) FRL Hlsc. states 0.01-0.01 residua (SB) same as above same as above same as above same as above same as above same as above same as above same as above same as above same as above Henderson, et al (1971) . HIC-1<»07 Henderson, et al (1971), AHIC-l«i07 Henderson. et al (19711, AHIC-H.07 Henderson, et al (1971), »HIC-1<»07 Henderson, et al (1971), ANIC-11.07 Henderson, et al (1971), AHTC-107 Henderson, et al C19M», AMIC-K.07 Henderson,et al (1971), AHIC-11.07 Henderson,et al (1971), AHIC-H07 Henderson, et al ------- > V/l •HC (plus llndane) Unite crapple FRL Hlse. state 0.07-2.19 residue (SB) SHC telu* llndane) Blojiouth buffalo •HC Cplus Itndanal Saallaouth buffalo FRL MISC. State* 0.03-0.07 residue (SB) FRL Hlse. states 0.08 residue (SB) BHC lotus llndane) Ftathead FRL Misc. states 0.02 residue catfish (SB) BHC lotus llndane) Coldeye BHC lolus llndane) Hal leva BNC lolus llndane) Saucer FRL Misc. states 0.02-0.08 residue (SB) FRL Nlse. states 0.01 residue (SB) FRL Hlse. states 0.01 residue (SB) BMC (plus llndane) Flannelaouth FRL Hlse. states 0.02 residue sucker (SB) BMC (plus llndane) BlaeK bullhead FRL Hlse. states 0.01 residue (SB) BHC (Plus llndane) Hhlte bass FRL Hlse. states O.tl residue (SB) BMC lolus llndane) Black crapple FRL Misc. states 0.01-0.03 residue (SB) saae as above sane as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above sane as above saae as above (1971), AHIC-H.07 Henderson, et al (19711, AMIC-1407 Henderson, et al (1971) , AHIC-H07 Henderson, et al (1971), ANTC-l«t07 Henderson, et al (1971), AHIC-1%07 Henderson, at al (197U, AHIC-U.Q7 Henderson, et al (1971), AHIC-1W07 Henderson, et al (19711, AHIC-1V07 Henderson, et al (1971), AHIC-1%07 Henderson, et al (1971), A MIC- 107 Henderson, et at (1971), AMIC-ld07 Henderson, et al AMIC-H07 ------- Conoound Field Field Organise Study Location Toxlclty, Active Ingredient, Ppn Experimental Variables, Controlled or Noted Comments Reference k BHC (olus llndan) Largescale sucker BHC (plus IIndanel Small mouth bass FRL Hlsc. states 0.01-0.1Z residue (SB) FRL Hlsc. states 0.01 residue (SB) BHC (olus llndan) Northern FRL Hlsc. states 0.01 residue squaw fish (S3) BHC (Dlus IIndane) Chlselnouth FRL Hlsc. states 0.03-0.03 residue (SB) BHC (olus llndan) Rainbow trout FRL Hlsc. states 0.01 residue (S3) BHC (olus IIndane) Brldgello FRL Hlsc. states 0.03 residue sucker (SB) BHC (plus llndan) Arctic grayling BHC (olus IIndane) Round MhlteTish BHC (olus IIndane) Longnos sucker FRL Hlsc. states 0.13 residue (SB) FRL Hlsc. states 0.0* residue (SB) FRL Hlsc. states 0.01-0.03 residue (SB) sane as above sane as above sane as above sane as above sane as above same as above sane as above sane as above sane as above Henderson. et al (19711 , Henderson, et al AMIC-K.07 Henderson, et al (1971), AMIC-11.07 Henderson, et al (1971), Henderson,et al (1971), AMIC-11.07 Henderson, et al (1971), AHIC-1".07 Henderson, et al (1971), Henderson, et al (1971), AMIC-K.07 Henderson, et al (1971), An-IC-K.07 BHC Puntlus tlcto —• 70 (Tit) a,c,d,e< f Of the pesticides Investigated, Bnatla ------- 8HC Carclnus •aenas BS* — the most toxic Has Klofos followed In (1971), decreasing order by Sumlthlon. Halathlon, «HIC-523 Formlthlon, Dlmecron, Sevln, and BHC. The author cites the need for more selective Pesticides nontoxic to fish or antagonistic agents for reducing fish toxlcl ty. greater than a(contin- One hundred-forty surface active 100 (12) uous aer- agents, solvent emulslflers, pesticides, ation, sea-Polychforlnated blphenyls, pure water, and Inorganic, and organic chenicals Here daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chenlcals to freshwater organisms. BHC Cardlum edule BSA greater (TZ) than 10 a»(contin- uous aer- ation, sea- water, and daily solution renewal) same as above Portmann, et al (1171), »HIC-7701 Portmann, «t al (1971), »HIC-7rot BHC Crsngon crangon BS* 0.001-0.003 a(contin- uous aer- ation, sea- water, and dally solution renewal) same as above Portmann, at al (1971). AMIC-7701 Bis hydroxymethyl) Ohosphlnlc acid Plmeohates oromelas BSA Bis (dimethyl thlo Phormldlum carbomoyl) dlsulflde amblguum .29.8 ITI»> a»,d,e,o, Malathlon and Its hydrolysis Bender and Fa products Here evaluated with the finding (1969), that one such product (dlethyl funaratc) AHIC-3787 Has more toxic than lalathlon to fathead minnows. Synerglsm occurred between Halathlon and two products of hydrolysis. Continuous exposure resulted In Increased toxlclty. O.S-10.0 — Of 71. chemicals evaluated as Otto (1970), (f>6percent alqicldes, only 9 were more toxic than AHIC-49Z growth CuSOfc. None Inhibited growth of Inhibited 1<>1 mat-forming algae for more than ? weeks. CuSO"» formulated with certain watting aqents Has more toxic than CuSOfc alone. Cooper chloraalne Has also found to be ------- Organism Field Field Study location Toxlclty, Active Ingredlentt Experimental Variables, Controlled or Noted Concents Reference Bis Itrl-n-butyll tin avlde •eraseeu Phormldlum amtaiguum Sal BO galrdnerl L ~ 8CF» and BSA 1.5-10.0 HOD percent Inhibited 1U) l.tOO CTZI •ore toxic than CuSO. No wetting agents Mere found to b« Inhibitory at the concentrations Investigated CO.05 and 0.005 DP). Also reported are factors affecting growth of algae in canals to determine whether there were leads to controlling algae by environmental management. No practical environmental •eans Mere found same as above Otto 11970). ANIC-89? Bewrben Betta splendens L — 250 ISB 6 hr) a Carclnus BSA — a,c,e,f« One hundred sixty-four Alabaster hard IHH) pesticides, wetting agents, and (1969), or alscellaneous water pollutants showed a AMIC-5%?S SOFT(SM) Hide range of toxlclty spanning 12 orders synthetic of magnitude. Knowing the toxlcity and dilution percentage of all components of a Hater, or formulation did not result in easy seaiiater predictability of the toxlclty of a for some mixture of materials. Sometimes species pesticides were most toxic In hard mater and sometimes the opposite was true. Testing the actual material as sold was found to be essential. The effects of ethanol and Raynes, etal bourbon on the aggressive response of SJanese fighting fish were determined. (1968),ANIC Fthanol Increased gill show 57l£ (aggressiveness) and bourbon and bourbon congeners decreased It. The authors tentatively concluded that the delayed effect of the congener resulted from Involvement of a different physiological mechanism and that this may be related to hangover effects In man. 10-33 a»(contln- One hundred-forty surface active Porteann, et uous aer- agents, solvent emulsltiers, pesticides, at (1971), ation, se«-oolychlorlnated blphenyls, pure AHIC-77tl water, and Inorganic, and organic chemicals were daily evaluated against as many as ten aarine ------- BP 1002 Cardlun edule BSA 33-100 tT2) solution organisms The authors noted that nost renawal) published data of this type deal with toxielty of chemicals to freshwater organises. a(contin- uous aer- ation, sea- wator, and dally solution renewal) sane as above Portnann, et •I (1971), AHIC-7701 BP 1902 Cranqon cranqon BSA 3.3-10 (T21 at-( contin- uous aer- ation, sea- water, and daily solution renewal) sane as above Portnann, et al (1471), AHIC-7701 BP 1002 Llmanda llnanda 8SA 10-33 (T2) a«(contin- uous aer- ation, sea- water, and daily solution renewal) sane as above Porfnann, et at (1971), &MIC-7701 BP 1002 Ostrea edulIs BSA 33-100 (T2) a(contin- uous aer- ation, sea- water, and daily solution renewal) sane as above Portnann, et al (1971), MIC-7701 BP 1002 Panda I us •ontsqul BSA 3.3-10 (T?> a(contin- uous aer- ation, sea- vatcr, and daily solution renewal) sane as above Portnann, et al (1971), ASIC-7701 110OX Agonus catapnractus BSA — greater than 10,000 (TW) a«-( contin- uous aer- sane as above Portnann* et al (1971), ------- Coapound 11MX llltX Ml O BP lltO BP lift lift Field Field Organise Study Location Cardlua edule BSA — Crangon 8S» — crangon Agonus BSA cataohraetus Cardlua «dula BS» Crangon BSA — crangon Toxlclty, Experimental Active Variables. Ingredient. Controlled Pom or Noted Comients ation, sea. water, and daily solution renewal) greater than a«(contin- same as above 10.000 m> uoua aer- ation, sea- water, and daily solution renewal) greater than ae(contin- saae as above 10.000 (T«) uoua aer- ation, sea- viator, and dally solution renewal) 1000-3300 ,AMIC- 7701 Port»ann, et al (1971). AHIC-7701 ------- Fundulus heteroclItu* BSA ~ 0.00001-0.00022 a,c,e,and ------- Vfl ro Compound Broelne Broalne Broalne Brenephos Broaoxynll (K salt! Broaoxynll \|K salt! Field Organise) Study Carasslus FL auratus Roc c us FL chrysops Stlzostedlon FL vltreum vltreua Rasbora BCFA neteroaorpha and BSA Rasbora 6CFA heteronorpha and BSA Rasbora BCFA heteroeorpha and BSA Toxlcity, Active Field Ingredient, Location ppa HIchlqan, and Erie Great Lakes O.Kreslduel - Superior, HIchlqan, and Erie Great LaKes O.SIreslduet - Superior, Mlchl gan,and Erie Great LaKes O.B(resIdue) - Superior, Hlchlgan, and Erie — 0.62 (T2) — 60 (TZ, hardwater) — 5.9 !T2, soft Ha tar) Experlmenta Variables, Controlled or Noted —— __ — _ a»,c,e,f, hard IHW) or soft 13WJ syn- thetic dilution . water, or aeawater for aoao species a,c,e,f ,h ard (HH) or soft (SWI synthetic dilution Mater, or for some species a,e,e,f. hard (HH) or soft 1 Coaaents sane as above sane as above sane as above One hundred sixty-four pesticides, wrttlna aqents, and miscellaneous water pollutants showed a wide range of toxlcity spanning 1Z orders of magnitude. Knowing the toxlcity and percentage of al 1 components of a formulation did not result In easy predictability of the toxiclty of a mixture of materials. Sometimes pesticides were nost toxic in hard water and sometimes the opposite mas true. Testing the actual naterlal as sold Has found to be essential. sane as above sane as above Reference AH1C-3778 Lucas, et al (1970) , AMIC-3778 Lucas, .et al (1970>, AMIC-S778 Lucas, et al (1970», AHIC-37TB Alabaster (19691, AMIC-51.25 Alabaster (1969),»HIC- 525 Alabaster 119691, AHIC-5I»Z5 ------- Ul ftasbora 8CF» heteroaorpha end BSA 8.65 ITZI Bvsan 99 I \n u> Rasbora BCFA heterooorone and BSA 1.8 III, hardwater) »uan Rasbora BCFA hetaroaorpha and BSA t.z ITI, SoftMeter) Cadaiua chloride las Agonus BSA cataphraetus 33 mi (SU) synthetic dilution water, or for SOB soeeles a'.c,«,f , hard (HH)or soft ISM) synth* tie dilution Mater, or seanater for so«e so«cl«s One hundred sixty-four Alabaster pesticides, wettlnq aqents, and (1969),»MIC- •Iscellaneous Hater oollutants showed a 5425 wide range of toxlclty soannlng 12 orders of naqnltude. Knowlnq the toxlctty and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a • Ixtur* of Materials. Sometimes pesticides Mere »ost toxic In hard Mater and sonetlaes the opposite Mas true. Testing the actual •aterlal as sold Has found to be essential. a«,c,e,f, hard (KW) or soft ISW) ayn- thatte dilution water, or aaawater for soee opoclas a,c,e,ft hard IHM)or soft (5M) synthetic dilution Mater, or seaMater for sone species a»(contin- uous aer- ation, sea- water, and dally solution renewal) saae as above Alabaster C1969), »MIC-5«.?5 saae as above Alabaster (19K9 5425 One hundred-forty surface active Port"»nn, «t aoents, solvent enutslflers, pesticides, al I197D, ooIych1 orInated blohenyls? oure lnorqanic« and organic chemicals Mere evaluated against as nany us ten narlne organisms. The authors noted that >ost published data of this type deal nlth toxlclty of chenicats to freshwater organlsBS. AHIC-7701 ------- I vn •P- Toxlclty, Active Field Field Ingredient Coaoound Organise) Study Location Ppm Cadmium chloride (as Cardlun edule BS» — 3.3 (Ti>) cadalum) Cadalua chloride (as Crangon 8S» — 1.0 (T2> cadalumt crangon CadBlua chloride Fundulus L — 50 (SB2) heteroclltus Exoerlnental Variables, Control led or Noted Comments at (con tin- sa«e as above uoua aer- ation, sea- water, and dally solution renewal) a»(contln- sane as above uous aer- ation, sea- water, and daily solution renewal ) *iC Abnormalities observed Included Intestine, Kidney, gill filaments, and resolratory lamellae. The earliest and Reference Portaann, et al (1971), AMIC-7701 Portaann, et al (1971), ANIC-7701 Gardner, et al (190). AMI C- 3827 Cadelua sultate las •croneurla 8SA Cd> Cadailua sulfate (as Epheaerella 8SA Cdl CadBlua sultate las Hydroasyche BSA Cd) 32 ITld) 2 (Tt> 32 (T10) •,c,d,e most severe was the Intestine (and mucus within one hr). Eoslnooh1 11 a occurred after it hr exoosurc, and lymohocytethrombocyte Irregularities occurred after 12 hr exoosure. The authors suggest broader study of blood/natholoqy as a means for developing a Hater pollution classification simitar to those used In mammalian toxicology. f Ephenerella (mayfly) Mas the most Narnlck, et sensitive aquatic Insect of those al(196. •HIC-3767 Marnlck. et al(1969), •HIC-3767 ------- Cadvlua »los» paeudo. harangua FL Cadaltw I VJl Cadalua Cadalua Cadalua Cadalua Coregonus FL artedli Coregonus FL clupeaforals' Coregonus FL hoy I Prosoolua FL cylIndraeeu* Salvellnus FL naaaycush FL FL FL aordax Carass1us auratus Notrepls hudsenlus Great Lakes - Superior. Michigan, •nd 0.00006 Great Lakes - Superior, Nlchlqan, and Frle Great Lakes - Suoerlor. Michigan, •nd Erie Great Lakes - Suo«rlort Michigan, •nd Erie Great Lakes • Suoerjort Mlch_lqant and Erie Great Lakes - Superior, Michigan, and Erie 0.0016(resldue) — O.OOOZtresldue) — O.OOOS(resldue) O.OOOklreslduel — 0.003(residue) — Trace element content of fish Iron Lakes Superior, Michigan, and Erie Mas deternlned by activation analysis. Whole body ana Iiver residues Here deternlned. Concentrations varied Mlth species and lake. . Other etenents found were! antlnony - 5 to 100 Don, bartun - 0.2 Don, cesium - 3 opb, lanthanu* — 1 to 20 pob, nercury - 10 ppb, rhenlua - 0.9 to 5 pob, rubldlu* - 0.06 to 6 DO, scandlua - 2 cob, selenlua - 0.1 to 2 OOb, silver - 0.001 oob. saae as above Lucas, et ml (1970), M1IC-3T78 Great Lakes 0.00007 - Superior, realdu) Michigan, and Erie Great Lakes - Superior, Nlchlqan, and Frle Great Lakes - Superior, Michigan, and Erie O.OOlUresldue) O.OOOllfesldue) — sane as abova saae as above saae as above sa«e as above saae as above saae as above sane as above Lucas, et at I19TOI, MIC-3778 Lucas, et al •MIC-J778 Lucas, et al 4MIC-3778 Lucas, et at (14701, •WIC-3770 Lucas, et al (1970). •NIC-377B Lucas, et al (19701, »HIC-3778 Lucas, et al (1970), AHIC-3778 Lucas, et al (1970). AHIC-3778 ------- Comoound Organism Cadmium Percoosls omlscomaycus Cadmium Roccus chrysoos Cadmium Perca II avescens Cmdmlum Stlrostedlon Jt> wltreum 1 vl treum O\ Cadmlu Coregonus clupeaformis Field Field Study Location FL Great Lakes - ^uoerior. Hichl qan. and Frle FL Great Lakes - Superior, f ich I qan, and Erie FL Great Lakes - Superior, Hlchl qan. and Erie FL Great Lakes - Superior, Michigan, and Erie FL Moose Lake, Can. Toxlclty, Experimental Active Variables, Inqredlenf, Controlled Pom or Noted Comments 0.0001 (residue) — - same as above 0.000? (residue) — same as above 0. 0005 (residue) -- same as above 0.0002(resldue) -- same as above 0.05 (residue) -- Concentrations of 13 toxic elements in dressed fish from heavily Industrialized and non-industrialized Reference Lucas, et i (1"70) , AMIC-3778 Lucas, et (19701, AHIC-3778 Lucas, et (1970), 4MTC-377S Lucas, et (1970) , AMIC-3778 Uthe.et al (1971) , AHIC-3819 al al al at Cad'Iui Cadilui Cadmium Cadmium Coregonus FL cluoeaforvis Esox luclus FL Esox lucius FL Esox lucius FL Lake 0.05 (residue) Ontario, Can. Moose Lake, 0.0? (residue) Can. Lake St. 0.09 (residue) Pierre, Can. Lake Frle, 0.05 (residue) Can. areas were determined. Only mercury exceeded regulatory limits, and concentrations of most elements Here essentially the same In fish from both areas. same as above same as above same as above same as above Uthe.et al (1971), AMIC-3819 Uthe, et al (1971) ,«>1IC- 3819 Uthe, et »HrC-3819 Uthe, et al 11971),I 3819 ------- CadBlua Cadalua Osaerus FL Lake frit, 0.16 (residue) •ordex Can. Perca FL lake Eric. 8.05 (residue) flv«sc«ns Can. Paralabrax FH Scatterqood 3 (dorsal clathratus Steam Plant, muscle Los Angeles» residue) Cat. saae as above same as above Cadalua Paralabrax FH Clathratus Paralabrax FH clathratus Catallna 3 (dorsal Isl»nrtt Cat. ousel residue) Seatterqood k (ventral Sf«»» Plant, Muscle Los Anqelest residue) Fish collected fro« an ettluent ploe of a steao olant and fro» offshore Maters of Catatlna Island Here analyzed for trace element content. Trace element content of the effluent Hater Has at least 5 times qreater than that of noraal sea water for cadmium, corner, nlcHel, zinc, and chromium. Livers of fish fro" the effluent were nearly titlce the size of those from the ocean. Greatest differences In concentration occurred •1th aluminum, cadmium, and nickel. Silver, barium, lithium, and lead Shooed the leest differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on aarlne organises. same as above Uthe, et »L«l«Tl>, AHIC-3819 Uthe. et L(147ll, • HIC-3819 Staoleton (1968). »«IC-5988 saae as above Staoleton •HIC-S980 Stuoteton (1968), »MIC-S980 Cadmlua Cadalua Cadalua CadBlua Paralabrax FH Catallna ? (ventral etathratus Island, Cal. Muscle residue) Paralabrax FH Scattergood 10 (gonads clathratus Straa Plant, residue) Los Anqeles, Cal. Paralabrax FH Catallna 6 (qonads clathratus Island, cat. residue) Paralabrax FH Catallna 3 clathratus Island, Cal. (gonads (gravid residue) feaales) same as above same as above saae as above same as above Staoletoo (19681, •HIC-9989 Staeleton (1968), »MIC-5980 Staoleton (1968), »MIC-S980 Staeteton (1968), •HIC-S988 ------- SJI CD Coaoound Cadalua Cadalua Cadalua Cadvlua Cadalua Cadalua Cadnlua Calclua chloride Organise, Paralabrax elathratus Paralabrax clathratus Paralabrax clathratus Paralabrax el athratus Paralabrax cl athratus Paralabrax cl athratus Paral abrax elathratus Paral abrax elathratus Lepoals •acrochlrus Toxlclty, Active Field Field Ingredient. Study Location Ppa FH Seatterqood 11 (liver Steaa PI ant • residua) Los Anqeles, Cal. FM Catal Ina 2t (1 Iver Tslandt Cal. residua) FH Scattergood 6 (integuaent Steaa Plant, residue) Los Angel es« Cal. FH Catal Ina I (Integument Island, Cal. residue) FH Scattergood . HIC-59»8 — sane as above Staateton (19f.»), »Hic-5g»o sane as above Staoleton (1966), •MIC-5980 — sae as above Staoleton (1968), AMIC-5980 sa»e as above Staoleton (19681, •HIC-598D -- saae as above Staoleton (1968), AMIC-5980 saae as above Staoleton (19681, AHIC-S980 a«,e» and This study xas conducted to Patrick, at aynthetle determine the relative toxlcltles of ?0 al (1968). dilution coamon constituents of Industrial wastes AHIC-5720 water to a fish, an alaa, and an Invertebrate. The experiments were conducted over a 10-year period for varied purposes. The authors recoaaend bloassays with at least three eoaoonents of the food neb. ------- Catclun chloride Nltzschla linear Is Calclu) hypochlorlte Phormldlum (as CD amblguua BS», L L — 3,130 (T5) a,e, and synthetic dilution water sa»e as above 0.5>tO.O (NTE1 — oxide (olu SulfurIc acid) Ictalurus punctatus • •»« ?,200-30,00 IK?. 5-9 PPX 001 a'.c.e' o Calcium oxide (plus Ictalurus L Sulfur 1C acid) punctatus Calclua sulfata Lepovls •acrochlrus BS. L 367-509(67 percent K 2?-2«, 5-9 ppm DOI 2,980 (Tbl ,c,e,f, a«,e, and synthetic dilution Water Patrick, et al (1968). mC-5720 Of 7i> chemicals evaluated as Otto (19701, alqlcldes, only 9 were more toxic than AMTC-892 CuSnfc. None Inhibited growth of nat-fornlng alcae for more than 2 weeks. CuSOU formulated Kith certain Netting aqents was more toxic th^n CuSO<» alone* Coooer ch I or-anlne was also found to be more toxic than CuSOi. No Netting aqents were found to be Inhibitory at the concentrations Investloated 10.05 and 0.005 ppi»» . Also reported are factors affecting growth of alqae In canals to determine whether there were leads to controlling alcae t>v environmental management. No practical environmental means were found. Large and small catfish Here Sparks, et subjected to a neutral synthetic Maste al (1969), aonroxlmatIng that being dumped py the AMIC-5902 Sunflower Army Ammunition Plant into the Kansas River. There were no apparent differences between the resoonses of the large end small fish. Fish In the neutral mixture swam continuously with particles of the mixture clinging to the mucus of the skin. Also, the mucus stripped away In places, and stranos of mucus extended from the gills. The degree of coating of the skin, stripping of the mucus, and mortality depended on the amcunt of solids Kept In suspension by aeration. same as above Sparks, et all 1969), 4NIC-590? This study was conducted to determine the relative toxlcltles of 20 common constituents of Industrial wastes to a fish, an alga, and an Invertebrate. The experiments were conducted over a 10-year period for varied purposes. The authors recommend bloassays with at least three components of the food web. Patrick, et at (1968), AHTC-57ZO ------- Coaoound Calclua sulfate Calciu Organism. Mltzschla line arts Paralabrax Clathratus Fiald Study BS«, L FH Field Location — Scatfergood Staa* Plant, Los Angelas, Toxieity, Active Ingredient, Ppa 3,308 (T5> 7Z8 (dorsal muscle residue) Experimental Variables, Control led or Noted a,, a, and synthetic dilution water oioe of waters Comments seme as above Fish collected from an effluent a steam plant and from offshore of Catalina Island Here analyzed Reference Patrick, at al (1966). •MIC-5720 Staoleton (1968), ANIC-S9.80 Gal. Calclua Calclua Calcium Catclua Cafclua Paralanrax elathratus Paralahrax Clathratus Paralabraic elathratus Paralabrax Clathratus Paralaprax elathratus FH FM FH FN PH Catalina «67 (dorsal Island, Cal. auscle residue! Scattergood 1020 (ventral Steam Plant, museI Loskngetes, residue) Cal. Catalina 53 (ventral Island, Cal. muscle residue) Scattarqood (53 (gonads Steam Plant, residue) los »nqa\%$, Cal. Catalina 565 (gonads Il«nd, C«l. for trace element content. Trace element content of the effluent Mater Has at least 5 times greater than that of normal sea water for cadmium, cooper, nickel< Zinc, and chronluff. Livers of fish from the effluent Mere nearly tulce the size of those from the ocean. Greatest differences In concentration occurred Hlth aluminum, cadoilu. and nlcKel. Silver, barium, lithium, and lead shooed the least differences. The author concluded that trac aleaent analysis of tissues could be usad to determine the effect of pollutants on marina organisms. save as abova same as abova saaa as abova same as abova same as abova Staoleton (1968>, •HIC-5980 Staolefon (196BI , •HtC-5980 Staoleton (196M, Staoleton (19661, AHIC-5980 Staoleton (196»), tmc-sm ------- Calclua Calcium Calcium Calcium Calcium Calctun Calcium Calcium Calcium GanaI bank •••dHlller Paralabrax clathratus (gravid Paralabrax clathratus Paralabrax elathratus Paralabrax clathratus Paralabrax elathratus Paralabrax el athratus Paralabrax elathratus Paralabrax clathratus Paralabrax clathratus rn FM FH FH FM FM FH FM Rasbora BCFA hataroaorpha and BSA Catallna 550 (qonads Island. Cat. residua) Scatterqood 155 (liver Steaa Plant, residual Los Angeles, Cat. Catallna Z65 (liver Island. Cat. residue) Scatterqood 1158 Steam Plant. (Integument Los Angeles, residue) Cal. Catallna Island. Cal. (Integument residue) Scatterqood 380 (heart Steam Plant, residual Los Anqeles. Cal. Catallna tBO (heart Island. Cal. residue) Scattergood 19.000 (eyeball Steaa Plant, residue) Los Anqeles, Cal. Catallna Island. C ?6,200(evebatl — residue) sane as above sane as abova saae as above same as abova same as abova same as above same as above saae as abova same as above 610 (T2) a,c,e,», hard(HH) or soft (SM) synthetic dilution water, or seawater for some species One hundred sixty-four pesticides, nettlno agents, and mlsce I laneous Mater oollutants showed a Hide range of toxiclty soanning 12 orders of magnitude Knowing the toxiclty and percentage ot all comoonents of a femulation did not result In easy predictability of the toxiclty of a mixture of materials. Sometimes pesticides were moS't toxic In hard water and sometimes.the opeoslta was true. Staoleton 11968) . AMIC-5980 Staoleton (1968). Staoleton (1968). AMIC-S980 Staoleton (1968), AMrC-5989 Staoleton (1968), AMIC-5980 Staoleton (196M, AMIC-5980 Staoleton (1968), AMTC-S988 Staoleton (1968), AMIC-5980 Staoleton (1968), AMIC-5980 Alabaster (1969), ------- Compound Organism Field Field Study Location Toxlclty. Active Ingr«di«nt( Ppm Experimental Variables. Control led or Noted Conments Reference Caotan Captan Fish loot specified) Brachydanlo rerle (larvae! * J><> greater than 8.1-1.0 ------- Cartoaryl (1.37 ql Salao Clark I 11.30 9) BCF» — t.2 mi Cartarvt Carbaryl Satno 8CF» qalrdnerl II.ZV 9} Oncorhyncnus SCFA klsuter <.>0 1.1.7 1.3 U) Carbaryl ictalurus punctatus BS» 15.80 (U) Carbaryl Tctalurus •etas BS» — 20.00 (Tl>) e.f.I.o, aulfato, copper, manganese, Iron, and chroralun »»c,, e,r,l,o, aulTate, coppor, manganese, Iron, and chromium saa as above saa* as abov* sa«e as above I1971J.AHIC- 181Z Post, et al (1971),»H1C- 1813 Post, et al (197D, AMIC-1812 Post, et al (1971), AM.IG-181Z oulTato, copper, nanganaae, Iron, and chromium a»,c,d, •,f,l,o, 3ulfat«, coppor, manganese, Iron, and chromium a( orqanochior \|n« insecticides were MaceKtet al synthetic the "lost toxic coDounds, <197C)« test Hater orqanoohosofiates lnte>-nd late, carbanates AMIC-S510 the I ast toxic. Brown trout MSS the soeclrs most su^ceotlble TO orqanochlorlnesi coho salmon the most susceptible to carbamat rs( and goldfish were tb least susceotlble ol all soecles. Safe concentrations established bv bioassavs tilth sal nonld* or centrarcMds wouM likely be safe for cyorlnlds and ictalurlds. >aT» levels for Ictalurlds or cyorinlds xould probably be hazardous for centrarchtds and salnonlds. The use of qoldflsh In blo»ssavs Has discouraged. sae as above synthetic test Mater MaceK, etal (1970). •MIC-5510 ------- Compound Carbaryl Carbaryl Carbaryl Carbaryl Carbaryl Carbaryl Carbaryl Carbaryl Carbaryl Carbaryl Carbon dioxide Field Field Organism Study Location Carasslus BSA — auratus Cyprlnus BSA carpi o Plmrphales BSA prove las Lepomls BSA — macrochlrus Lepomls BSA mlcroloohus Hlcropterus BSA sal noliles Sat no BSA galrdnerl Salmo trutta BSA — Oncorhynchus BSA — Klsuten Perca BSA — f lavescens Salmo BSA — galrdnerl (yearling) Toxlclty, Active Ingredient, Ppm 13.20 (TV) 5.?S (TV) 1V.60 (TV) 6.76 (TV) 11. ZO (TV) 6.VO (TV) V.3V (TV) 1.95 (TV) 0.76 (TV) 0.75 (TV) 35 (SRI) Experimental Variables, Control led or Noted Comments a, synthetic testnater a, synthetic test Mater a, synthetic test Mater a, synthetic test Mater a, synthetic test Mater a, synthetic test Mater a, synthetic test Mater a, synthetic test Mater a, synthetic test Mater a, synthetic test water a, c, bi- carbon- ate, and total aollds saae as above same as above saae as above same as above same as above sane as above same as above same as above same as above same as above Bicarbonate In blood serum of brook trout rose to 5 times greater than that of contra Increase Mas slow, being half complete at 6 hr. Sodium and Inorganic phosphate Mare not affected, but serua chloride Increased. The Reference Macek.et al (1970), AMIC-5510 Macek, et al(1970). AMIC-5510 Macek.et al AMIC-5510 Macek.et at (1970), AMIC-5519 Macek.et al 119701 . AMIC-5510 Macek.et al AMIC-5510 Macek, etal AM.IC-5510 Macek, et at (1970), AMIC-5510 Macek.et al (1970) , AMIC-5510 Macek. etal (1970), AMIC-5510 Lloyd, et al (1967), AMIC-7?1 ------- Carbophenoth 1 on Rasbora BCF» heteromorpha and BS» ITZ» Carbyne Rasbora - BCFA heteromoroha and 8S» 0.9 ITZI vn a,c,e,f, hard (HH) or SOFT(SW) synthetic dilution water, or sawater for soaa species a»,c,e,f, bard (HW) or soft (SW; syn- thetic water, or sea, water for sone species authors note that the data Indicate an environmental stress not related to problems of osmotic adaptation. One hundred sixty-four Alabaster pesticides, wettlnq aqents. and (1969), Miscellaneous water pollutants showed a AHIC—5 Hide range of toxlcltv spanning 12 orders of maanltude. KnoMlnq the toxlelty and percentaae of all components of a femulation did not result In easy predictability of the toxlclty of a mixture of Materials. Soaetlnes pesticides «re nost toxic in hard Hater and soaetlmes the opposite Mas true. Testing the actual aaterlal as sold was found to be essential. sane as above Alabaster (1969). •NIC-S12S Carbyne Rasbor* BCF* heteronorpha and BS* l.k Carbyne Asterlas BSA rubens J.3-10 (K 1 HRI Carbyne Cardluin edule BSA — 100 a,c,e,f, hard (KM) or soft 13W) sjn- thetlo dilution water, or •eawater for some species a«( contin- uous aer- ation, sea- water, and dally solution renewal) c»(contin- uous aor- saae as above Alabaster (1969). One hundred-forty surface active aqents. solvent enulslflers. pesticides. polych1 orInated biphenyls. pure inorqanic. and organic chemicals were evaluated against as many as ten marine organisms. The authors noted that aost published data of this type deal with toxlclty of chemicals to freshwater organisms. same as above Portmann. at al (1971), AHIC-7781 Portmann, et al (1971), ------- Compound Carbyne Casol Casol Casol Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Organise Study Location Ppn or Noted Comments ction, sea- water, and daily solution renewal) Crangon BS ~ 3.3-10 (T2) a(contn- sa»e as above crangon uous aer_ atlon, sea- water, and dally solution renewal) Plmephales BSA — 12.0 (HSC) c,d,«, f same as above cromelas Biochemical L -- 610,000 c,d,e,f same as above oxygen demand Reference AMIC-77B1 Portmann, et al (197.1), AHIC-7701 Zllllch 1 1 QftQl . \ 1 7OT I , AHIC-Z909 711 llch (19b9»,»1IC- 2999 711 llch (1969), Casoron G Rasbora BCFA heteronorpha and BSA 100 (TZ) a»,c,o,f, hard (KW; or soft ISW) syn- the tic dilution water, or seawater for sorre species One hundred sixty-four Alabaster pesticides, Mettlnq aoents, and (1969), nlscel laneous Hater oollutants showed a AMIC-51.75 Hide ranae of toxlclty scanning 12 orders of Magnitude. Knowing the toxlclty and percentage of all components of a formulation did not result In easy predictability 'of the toxlclty of a mixture of materials. Sometimes pesticides Here most toxic In hard Hater and sometimes the ooposlte was true. Testing the actual •aterlal as sold was found to be essential. ------- Casoron 133 Rasbora heteroaorpha BCTA and BSA 13 tTZ) Casoron Horone saxatltls (fInqerlInqs) BSA — 6,208 (Tit) Casoron Cardlua edule BSA — qreater than 100 (T2) Casoron Cranqon crangon BS* — 3.3-10 a,c,e,f, same as above Alabaster hard (HtO (1969), or AHIC-5«?% SOFTfSH) synthetic dilution Mater, or seaNater for some spec las a,c,d,e,f. All compounds were Investigated Ncltborn D because of their probable usaqe In (1971), hatchery production of Mhite bass. AHIC-5571 Compounds that can be used at recommended concentrations Here Bquathol, Casaron, I. Ind^ne, and Terramycln concentrate. Those that should not be used Mere Acrlflavlne, Rayluseldv, Halachlte qreen oxalate, and Malathion. ao-(coritin- One hundred-forty surface active Portaann, et uous aer- aqents, solvent emulslflers, pesticides, al (1971), ation, aea.-nolychlorlnated blphenyls, pure AHIC-7701 water, and Inorqanlc, and organic chenlcals were daily evaluated aqainst as many as ten narlne solution organisms. The authors noted that Host renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. «•( contin- uous aer- ation, sea. water, and sane as above Portmann, «t al C197U. AHIC-7701 solution renewal) Cd CIZ . 2.9 HZO (ax Crangon BSA Cd Z plus! seotemsplnosa 0.3Z(T<>) a«,c,e, SSH Although data cited en at Elsler 70 C and 2.0 percent salinity, varying temperature and salinity Mere also studied. Hlqher temperature (20 C) and IOMer salinity (5.0 oercenf) resulted In greater susceptibility of nuininlchoqs to cadmiuir. TL sub 25, TL sub 50, and TL sub 7> for 2 ------- CD Com oun« Cd CI2 . 2.5 H20 Cd 2 plus) Cd CI2 . 2.5 H20 Cd 2 plus) Cd CI2 . 2.5 H20 Cd 2 plus) Cd CI2 . 2.5 H2t Cd 2 plus) Cd CI2 . 2.5 H20 Cd 2 plus) Cd CI2 . 2.5 H2D Cd 2 plus) Cd CI2 . 2.5 H20 Cd 2 plus) Cd CI2 . 2.5 H20 Cd 2 plus) Cd CI2 . 2.5 H24 Cd 2 plus) Cd CI2 . ?.5 H20 Cd 2 plus) Field Field Orqunlsa Study Location (as Fundulus BSA — h« tercel Itus (as Paqurus BSA — lonqlcarpus (as Palaeaonetes BSA — vu 1 gar 1 s (as Asterlas BSA — forbesl (as My a arenarla BSA — (as Carclnus BSA — aaenus (as Urosalolnx BSA — elnerea (as Fundulus BSA — (as Hytllus BSA edutis (as Cyprlnodon BSA — varlegatus Toxlclty, Active Ingredient, Pom 55. 0 (Tl.) 0.32 (Tl.) 0.1.2 (Tl.) 0.82 (T<>) 2.2 (Tl.) fc.l (Tl.) 6.6 (Tl.) 21.0 (Tit) 25.0 (Tl>> 50.0 (Tl,) Experiaental Variables. Control led or Noted a'.c.e, SSM a»,c,e, SSH a»,c,e, SSH SSM a»,c,e, SSM a,c,e, SSM a,c,e, SSM a»,c,e, SSM a,c,e, SSM a",e,e, SSM Comments saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above sane as above Reference Elsler (1971), AMIC-1621 Elsler (1971), A1IC-1621 ElsJer (11711, AMIC-1621 Elsler AMIC-1621 Elsler 11971) , AMIC-16?! Elsler (1971). AMIC-1621 Elsler (1971), AMIC-1621 Elsler (1971), AMIC-1621 (1971), AMIC-1621 Elsler (1971), AMIC-1621 ------- Cd CI2 . 2.5 H2« (•« Nasser 1us Cd 2 Plus) obsoletus BS — Cd CI2 . 2.* HZO (M Nereis vlrens BSA Cd 2 Plus) Chevron Ml-fl Steel head trout tfIngerlInqs) BS* — ID.5 (Tl>) 11.0(11.) 3.2 mi a'.C.C, SSH a,Cte, SSM Charron KI-O Chloral hydrate Coho aalnon BSA. Hood Canal (flngerllAga) in . Hoodaport, •Itu Wash. Negaprlon. BSA — brevlrostrls 11-3 Kg) 0.001 (K) 300 (SB 1 hr> CM or iaIn Caaaaru« p««udo- BCF 0.22 (T<») a»,c,d,e. f,r»,a CMeraaln* CMoraaln* Plaephalas BCF prone I as Daphnla aaqna BCF ChloraBphenlcol Kercanarla L — 0.15 (T3) 0.09-0.15 (TV) 0.001 (K 3-9) TI..S »T2> a«,o,d,e, (O.o.d.e, f.wt.a saa« as above sa»« as above Elsler (1971), »MIC-162l Evaluation of 11 oil dlsoersants resulted In a ranking for each and a recommendation for use according to the ranking. Banking Has based on toxlclty and oil dispersal effectiveness. Corexit 776U appeared to have the least toxlclty nlth fair to good oil dispersion capablllty. sane aa above Tracy, t at(1969), Data from study of druq effects on young lemon sharks were treated mathematically to demonstrate apollcablllty of classical rate theory to the study of chemical shark deterrents. Tncaoacltat Ion (narcosis) Has the orl»ary parameter timed for effectiveness. This •as usually quite rapid for the more effective druqs Chloranlne toxlclty Mas very carefully studied uslnq Height reduction and reoroductlon over 15 to ?1 Heek exoosure periods. Loss of Height and ability to reproduce were observed at concentrations less than that observed for toxlclty. The loHest chloramlne concentration having no significant effect was less than 3.d pob for Gammarus and 0.017 ppb for the fathead minnon. same as above Tracy, et al (1969), AMIC-383U Baldrldoed? 69). •MIC-3$3> Arthur, et al (1971), attIC-3?90 saae as above The effect of 52 pesticides on Arthur, et al (1971). AMIC-3299 Arthur, et AMTC- 3290 Davis, et al ------- Compound OrqanlSB Field Flaltf Study Location Toxlcity, Active Ingredient, Pen Experimental Variables, Control led or Noted Comments Reference •ercenarla (egqs) Ctilora'ohenlcol C.ttloraaoh«n(col Mercenarla •ercenarla (larva! Phornldlu anblguua SO.O (Tl?) 0.5-10.0 (NTE) — CM or ax Sal BO galrdncrl BCFA •nd BS» 1,800 (T?) a«,c,e,f. hard (KW) or soft (3W) syn- thetic dilution water, or •eawator for some spaeies etrbryonle development of clams and oysters «as reported. Synerolstlc (1969), AHIC- effects Mlth solvents Here also reoorted* 5990 Most of the -compounds affected development more than survival* Sone, however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life staqes of an organism and note the oossiblllty of selecting chemicals for oest control that Mould not have serious effect on shellf ish. same as above Of 7<» chemicals evaluated as alqlcidest only <5 Here more toxic than CuSO"t. None Inhibited growth of mat-tormina alqa? for more than ? weeks. CuSni* formulated nith certain wettlnq aqents was more toxic than CuSO, AMIC-892 Alabaster (19691, ------- Ch Ionian* CM or dan* Nhlt* sucker FRL Misc. stares 0.13-0.1.1, residue (SB) Mhlt* perch FRL HIsc. states 1.7? residue (SB) Testlnq the actual material as sold was found to be essential. The Bureau of Sport Fisheries continued Its fish monitoring orogram by collectlnq li»7 composite fish samples from 50 nationwide monitoring stations during the fall of 1969. Fish were analyzed for residues of 11 organochlorlne Insectlcidest llplds, and PCB-s. same as above Henderson,et al (1971), • NIC-ior Henderson. et al (19M), AMIC-1U07 CMordan Largemouth bass FRL Misc. states 0.95 residua (SB) same as above Henderson, etal (1971), »MIC-l ------- Compound Organism Field Field Study Location Toxlclty, Active Ingredient, Ppa Experiment) Variables, Control led or Noted Comments Reference Chtordan Lepomls evanellus (Resistant) BS» — 3.2B IT2» 107 Green sunflsh from Betzonl, Miss. HIncheM, et were resistant to CMordane, Meptaehtor, al(1970), Llndane, and Strobane. but not to «NIC-571 Parathlon. Golden shiners fro" the sane location were resistant to Llndane and Strobane, tolerant to CMordane and Heptachtor, and susceptible to ParatMon. Lack of resistance to Parathlon Indicated lack ot agricultural usage of orqanochosphates In that area. Resistant fish oere compared to susceptible ones collected at StarKvIlle. Chiordan* Lepomls eyanellus (Susceptible) as* — B.09 (T2) sane as above MlncheM, et al(1970>t 4NIC-5UT1 CMordane Chiordan* Chiordene Notemlaonus crysoleucas (Resistant) Notemlgonus crysoleuces (Susceptible) Palaemonetes Kadlfthensls (resistant! BS* — BSA ~ BS» 2.33 (TZ) (T2I 0.0779-0.33* CMordane Copapeda I Cyclop a blcuspldus Cyclops varicans, Buerelopa FL and BSA State Colleqe.niss 0.30 (KZ) sane as above sane as above et al • HIC-51,71 HlncheM, eta) (1970), ' AHIC-SI.T1 Bloassays Mere conducted Mlth Naavl, et al from three areas of Intensive (1970), pesticide use and fro" an unexoosed area. AMIC-SS19 Previously exposed shrimp Mere from 1 to ?5 times more resistant than unexposed shrimp. Both types of shrimp Mere also exposed In caqes to Maters of the contaminated areas. Susceptible shrimp suffered 6f> percent more mortality Than did resistant shrimp. The toxlclty ot the Insecticides ranked In descending order Mas as follOMs! most toxic, Endrln, DOT, Methyl oaratnlon, Parithloni medium toxlclty, Guthlon, Llndane, Toxaohene, Strobanet lease toxic CMordane, Sevln, and Heptachlor. The response of Nagvl, et at pe^t lcl ------- Cnlordane Cnlordane CMer«« Chlorfenvlnphos Cnforfenvlnphos •gills. Macro cyclops. albldus, Orthocyclops oodeatus) Cooepods ICvcloos blcusoldus* Cyiloes varlcans. Cyclone vernal is, Eucyelops •Sills, Hacrocycloos atbldus, Orthoeycloos •onestus) TubI fax tubIfex FL and BSA Betzonl, Hiss B.30 I96preent Ft and 8lzenli Hiss. Salao BCFA — galrdnerl and BSA 1.50 25 wide range of toxlcity soannlng 1? orders of magnitude* Knowing the toxlcity and percentage of all eonoonents of a formulation did not result In easy predictability of the toxlcity of a •Ixture of materials. Sometimes pesticides were most toxic In hard Hater and sometimes the opooslte Has true. Testing the actual material as sold MBS found to be essential. save as above Alabaster (1969), same as above Alabaster <19691,AHIC- ------- Chlorine . Toxlclty, Active Field Field Ingredient, ind Organise) Study Location Pom t Plmephales BSA Grand River, 0.07-0.15 (Tl>) cromelas (ML) Wyoming, Experimental Vviahtes, Control led or Noted Comments synthetic dilution Mater, or seawater tor SOB* species -- The Indicated toxic levels of chloride occurred In S.8 ------- ChlortMaald Rasbora heteromorpha BCF» and 8SA 30 ITZI Chroaates (as chroalua) Aqonus cataohractus •BSA — 33-100 ------- Comoound Organism Field Field Study Location Toxlclty, Active Ingredient, Experimental Variables. Control led or Noted Comments deference Chromic chloride (as Aeronmurla Cr» Chromic chloride las Ephemerella Crl Chromic chloride las Hydroosyche Crl Chromium trloxlde Phormldlum (»« Crl ambiguum BS» ~ L — SZ (T7) 2 IT»> m> a,c,d,e,f same as above 0.5-10.0 (NTE) — Chromium llosa paoudo- FL Creat Lakes - Superior, Michigan, and Erie 1.1 (residue) •,c,d,e,f Eohemerella (mayfly) Mas the most NarnicK, «t sensitive aauatlc Insect of those studied, and cooper the most broadly toxic metal. The authors suggest that aquatic Insects may not be as sensitive to heavy metals as fish. a>.c,d,e,f same as above Varnlck, et •1(1964), »HIC-3767 Warnlck, et •1(1969), •NIC-3767 Of 7 ppb, rubidium - 0.06 to 6 pom, scandlun - 2 ppb, selenium - 0.1 to 2 OOb, silver -.0.001 pob. ------- Chroalue. Chromium Chroalu* Notropls Fl Great Lakes 5.5 hudsonlus - Superior, Michigan, and Erie PereoDsls FL Great Lakes ?.Mresldue) omlscomaycus - Superior, Mlchioan, and Erie Coregonus FL Moos* Lake, 0.03 (res)<1ue) ctupeatornls Can. Chromium Chromium: Chromium Chromium Chromium Chromium Chroalum Coregonus FL elupeaforals Esox locius FL Esox luclus FL Esox luclus FL Osmerus FL •ordax Perca FL flaveseens Paralabrax FH clathratus Lake 0.03 (residue) Ontarl». Can. tjoose Lake, 0.04 (residue) Can. Lake St. 0.03 (residue1) Pierr, Can. LaKe Erie, 0.03 (residue) Can. Lake Erie, 0.03 (residue) Can. Lake Erie, 0.07 (residue) Can. Scattergood 1.3 (dorsal Steam Plant, Muscle Los Angeles, residue) Cat. saae as above sane as above Concentrations of 13 toxic elements In dressed fish from heavily Industrialized and non-IndustrialIzed areas Mere determined. Only aercury exceeded regulatory Units, and concentrations of aost elements Mere essentially the saae In fish fro both areas. saae as above saae as above saae as above saae as above saae as above sane as above Lucas, et al (1970), •HIC-J77B Lucas, et al (1970J, AHIC-J778 Uthe, et •LdPTl), 1HIC-J819 Uthe, etal (1971), »MIC-3»19 Uthei et al (1S71),A1IC- 3819 Uthe, et »L(197t), A1IC-3»19 Uthe, et al (t ------- Coaoound Chromium Chro«lua Cnro«lua Cnroalue ChroBlua) Chroalue Chroaiua Chroaiua OrqanlsB Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrax cl athratus Paralabrax cl athratus Parat abrax clathratus Paralabrax clathratus Flald Study FN FH FM FN FH FM FN FH Toxlclty, Experimental Active Variables, Field Ingredient, Controlled Location Ppa or Noted Consents Scattergood (ventral — saae as above St«ai» Plant, muscle Los Angeles, residue) Cal. Catallna 1.% (ventral ~ - saae as above Island, Cal. muscle residue) Scatterqood 2 (gonads -- saae as above Steaa Plant, residue) Los Angeles, Reference Stapleton (1S68J, AMIC-S98B Staoleton (1968) , ANIC-5950 Staoleton (1961), ANIC-S9SO Staoleton (196M, AHIC-S980 Staoteton (1968), AMIC-S980 S tao 1 eton (1968), AMIC-5989 Staoleton (1«68), ANIC-S980 Staoleton (1968), AMIC-S988 cat. ------- Chroalua Ctiroaluo Cnroalua Paralabrax FH Catallna ?.3 (gonads clathratus Island, Cal. residue) Paralabrax FH Catallna 7.6 Clathratus Island, Cal. (qonads (gravid residual females) Paralabrax FH Scattergood 1 (liver clathratus Steam Plant, residue) Los Angeles, Cal. > ChroBlua Cnroaiu* Citric ccld Paralabrax FH clathratus Paralabrax FH clathratus Paralabrax FH clathratus Catallra 1.5 (liver Island, Cal. residue) Scattergood 1.9 (Integuaent — Stean Plant, residue) Los Angeles, Cal. Catallna 1.* (Integuaent — Island, Cal. residue) Carclnus •aenas BS» — 160 CTZ) CI Fundulus BS» heteroclitus o.ooom-o.ooi? (TO ct Nereis vlrens BSA — 0.0003-0.0007 saae as above saae as above saae as above sane as above sane as above saae as above Stapleton ANIC-5981) Staoleton (196M, AMIC-59SH Staoleton AMIC-5980 Staoleton (1968), Staoleton (1966), Staoleton (196S), AMIC-S9M a«lcontin- uous eor One hundred-forty surface active Portaann, et aqents, solvent enulsitl«rs, oestlcldes, al ation, sea- oolychlorlnated blohenyls, oure water, and inorqanlc, and organic cheivicats nere daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this tyoe deal »ith toxlclty of chemicals to freshwater organises. a»c»e» A laboratory procedure based on and Standard Methods for 96-hr toxlclty synthetic determinations of crude oil and seanater oll-dispersant mixtures Has described. The dlspersants varied considerably in toxlclty, ranging from 0.01 to 7.1 ml/1, TLSO for 96 hr. These did not differ significantly from ZVO hr values. The dlsoersants H«re designated as CX, no, CI, 00, AO, PC, MM, TN, BP, and NA nlth no further description of their chemical nature or source. Only a fex bloassays Mere conducted Hith shrlmo. HollusKs and echlnoderms Here suggested as suitable test animals. The authors stated that the method could be used to test any product for toxlclty In seawater. (1971),AHIC- 7701 LaRoche, et al (1970), AMIC-'.'.S a,e,e, and synthetic seawater saae as above LaRoche,et al (1970), ANIC-I.1.5 ------- Cleanoxol Cleanosol Clopnen A30 Toxlclty, Experimental Activ* Variables, Field Field InqredlenT, Controlled Organism Study Location Pp« or Noted Comments Cardlua edule BSA — 10-33 (T2) ao(eontln- One hundred-forty surface active uoua aer- agents, solvent emulsi f lers, pesticides. ation, sea-oolychlorlnated blphenyls, pure water, and Inorganic, and organic chenlcats Mere daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal)" published data of this type deal with toxlclty of chemicals to freshwater organisms* Crangon BSA — 33-100 (TZ> a»(eontin- same as above crengon uous aer- ation, sea- water, and dally solution renewal ) Panda (us BSA — 33 a«(contin- same as above montagul uous aer- ation, sea- water, and daily solution renewal } Agonus BSA — greater than 10 a«(contin- One hundred-forty surface active eataohractus (T2t uous acr- agents, solvent enulslfiers, pesticides. ation, sea- polychlorlnated blphenyls, pure Reference Portmann, et al (19711, AMIC-7701 Portmann, et al (1971). ANIC-7701 Portmann, et al (1971), AMIC-7701 Portmann, et al (1971), AHIC-7701 water, and Inorganic, and organic chevlcals Here daily evaluated against as many as ten marine solution organisms* The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. Cleohen A30 Cardlum edule BSA — a«I contin- uous aer- ation, sea- water, end daily solution renewal) same as above Portmann, et al (1971), AMIC-7701 Clophen A30 Crane, on crangon BSA — 0.83-1.0 (T2> a«(contin- uous aer- ation, sea- water, and same as above Portmann, et al (1971), ANIC-7701 ------- "dally solution renewal) Clophen A60 Agonus cataohractus BSA — greater than ID ae(contin- (TZ) uous aer- ation, sea- water, and dally solution renewal) sine as aboye Port»ann,et al (1471). ANIC-7701 Clophen A60 Cardlu* «dul« BSA — greater than 10 a«(contln- ITZ) uous aer- ation, sea. water, and dally solution rene-jal) sane as abov« Portwann, «t at(1971), •HIC-7701 Clephen »60 Crangon eranqon BS» — greater than 10 a«(contin- CT2) uous aer- ation, sea- water, and daily solution renewal) saae as above Portaann, et al (197U, HIC-7701 Clophcn A M Crangon cr»ngon 8SA 1.8-3.3 (TZ) &«•( contin- uous aor- atlon, sea- water, and dally solution renewal) saae as above Portiann, «t at (1971), 4MIC-7701 Clophen A 50 Crangon erangon BSA — 3.3-10 (TZI a«(contin- uous aer- ation, sea- water, and dally solution renewal) saae as above Portnann, et al (1971), AHIC-7701 CN« Co, Nit Cr and Plueo 2n premelas BSACF Grand River IHL) at betMeen 1.25-3.75 a,c,e, eon- A mobile bloassav unit was ductiylty, utilized to conduct this study of municipal Nastexater containing the Indicated toxicants. River Mater was used as diluent. The conclusion H»S reached that svneralstlc or additive toxic effects occurred since toxlclty was greater than that of any of the Ions singly. Zllllch (1969). ------- Compound Organism CM, Cut Nl • O, and Catostoous In commersonl Toxiclry, Active Field Field Ingredient, Study Location Ppn Wyoming, Mich percent (T3) loan BSACF Grand River between (HL) at 1.25-3.75 Wyoming, Mich percent (T3) loan Experimental Variables, Control led or Noted Comments Btt.Cu.Cr, OH, and Zn &>C,e, con- sane as above duotlvlty, Jtt,Cu,Cr, ON, and Zn Reference AMIC-2906 71 Mich (1969), ANIC-2906 Cobaltous sulfate fas Co) CobaItous sulI ate (as Co) Cobaftous sulfate (as Co) Cobalt Acroneurla BSA — 32 ) a,c,d,e,f 32 (T7) a,e,d,e.r sensitive aquatic insect of those studied, and coooer the most broadly toxic metal. The authors sugqest that aquatic Insects nay not be as sensitive to heavy metals as fish. same as above Great lakes 0.029(rsldue) - Superior, Michigan, and Erie Great Lakes - Superior, Michigan, and Erie Great Lakes - Superior, Michigan, 0.020(residue) — 0.023(resldue) — same as above Trace element content of fish from Lakes Superior, Michigan, and Erie Has determined by activation analysis. . Whole body and liver residues Here determined. Concentrations varied with species and lake. Other elements found nerei antlnony - 5 to 100 ppb, bariu - 0.2 opn, cesium - 3 ppb, lanthanum - 1 to ?0 DOb, mercury - 10 ppb, rhenium - 0.5 to 5 ppb, rubidium — 0.06 to 6 ppm, scandium - 2 ppb, selenium - o.l to 2 ppb, silver - 0.001 ppb. same as above al(1969). AMIC-3767 Harnick, et al(1969), AMIC-3767 Warnick, et al(1969), AMIC-3767 Lucas, et al (1970), AMIC-3778 Lucas, et (1970), AMIC-3778 al same as above Lucas, et al (1970), AMIC-3778 ------- and Erie Cobalt Cobalt Cobalt Cobalt Cobalt Cobalt Cobalt Cobalt Cobalt Cobalt Coreqonus FL hoyl ProsODlu" FL eylIndraccua S»lv»lInu* naaaycush Os uterus •ordax Notropls hudsonlus ftoccus cnrysops FL FL FL Pereopsls FL oalscooaycus FL Perea FL flavescens Stlzostedlon FL vlTreum vltreu* Paralabrax FH elathratus Great Lakes 0.036(residue) - Superior, Hichlqan, and Erie Great Lakes 0.0<»7(resldue> - Superior, Mlcnlqn, and Erie Great Lakes - Superior, Michigan, and Erie Great Lakes - Superior, Hlchlqan, and Erie Great Lakes - Superior, Michigan, and Erie Great Lakes - Superior, Michigan, and Erie Great Lakes - Superior, Michigan, and Erie Great Lakes - Superior, Michigan,and Erie Great Lakes 0.0<.5 — 0.013(rasldue) — 0.033(resldue> — O.OZ3(resldue) 0.0<>3(rasldue> — O.lZO(rasldue) — saae as above saae as above saae as above saae as above same as above sane as above sane as above saae as above saae as above Lucas, et al CITO) t •MIC-^778 Lucas, et al (19701, AMIC-3778 Lucas, et at (1970), »«1IC-377 Luc«s, et al AMIC-377* Lucas, et al »«IC-377n Lucas, «t al (1970) , •MTC-3778 Lucas, et al (lc'70), 4HIC-3778 Lucas, et al (1170), AMIC-3779 Lucas, et al (1170), AMIC-3778 Fish collected fron an effluent Staoleton pipe of a steam plant and froa offshore (1968), waters of Catallna Island Mere analyzed AHIC-5980 for trace aleaent content. Trace element ------- Compound Field Field Organise Study Location Toxlclty, Active Ingredient, Ppa Experimental Variables, Control led or Noted Comments Reference > Cobalt Cobalt Cobalt Cobalt CobaIt Cobalt Cobalt Paralabrax FH Catallna 2.3 (dorsal clathratus Island, Cal. muscle residual Paralabrax FH Scatter'qood 1.2ventral elathratus Steam Plant, muscle LosAngeles, residue) Cal. Paralabrax FH ratalIna .3 (ventral clathratus Tslandt Cal. auscle residue) Paralabrax FN Scattergood 3.6 (gonads clathratus Steam Plant, residue) LosAnqeles, Cat. Paralabrax FN Catallna li.lt (qonads clathratus Island. Cal. residue) Paralahrax FN Catallna 3.7(qonads clathratus Island, Cal. residue) (qravld feaales) Paralabrax FH Seattergood l.t (liver clathratus Stean Plant, residue) LosAnqelKS, Cal. content of the effluent water Mas at least 5 times greater than that of noraal sea water for cadmium, coooer, nickel, zinc, and chromium. Livers of t ish from, the affluent Here nearly titlce the size of those from The ocean. Greatest differences in concentration occurred with aluminum, cadmium, and nickel. Silver, barlufft lithium, and lead shoned the least differences. The author conduced that trace element analysis of tissues could be used to determine the effect of pollutants on marine organisms. same as abov sane as above same as above sane as above saae as above same as above saae as above Stapleton U96M , AMIC-5980 Staoleton (19681, AMIC-5980 Staoleton (1061, AMIC-S980 Staoleton (1968), AMIC-S980 Staoleton (19S8), •1IC-S9SO Staoleton (1968), AMIC-59H8 Staoleton (19681, ANIC-S980 ------- CobIt Cobalt Cobalt Cobalt Paralabrax FM clathratus Paralabrax FH clathratus Paralabrax clathratus Paralabrax FM clathratus Catalina 1.9 (liver Island, Cal. residue) Scattergood 1.8 (integument Steam Plant, residue) LosAngeles, Cal. Catallna 1.it (Integument Island* Cal. residue) Scattergaod 1.7 (heart Steam Plant, residue) LosAngeles, Cal. same as above sane as above saae as above same as above Staoleton (1968). AMIC-59RO Stapllt Mill eton (10.681, AMIC-5980 Staol eton (1168), AMIC-5980 Staoleton (1968), AMIC-S980 CD Cobalt Cobalt Cobalt Paralahrax . FH Catalina 1.2 (heart clathratus Island, Cal. residue) Paralabrax FH Scattergood 5.2 (eyeball clathratus Steam Plant, residue) LosAngeles, Cal. Paral abrax clathratus Cocoaalne dlacetate Phormld-lum amblguum FH Coco •onoethanoIam1 d« (plus ethylene oxide, ethoxy Catallna 5.1 (eyeball Island, Cal. residue) L — D.5-10.0 (NTF» — same as above same as above same as above Cardlum edule BS» — greater than 100 (T2) Of 7<» chemicals evaluated as alqlcldes, only 9 Here more toxic than CuSOU. None Inhibited growth of mat-forming algae for more than ? weeks. CuSO>> formulated with certain wetting agents Has more toxic than CuSOt» alone. Coooer ehloraiMne was also found to be more toxic than CuSO<>. No netting agents were found to be Inhibitory at the concentrations investigated (0.05 and 0.005 DPI"). Also resorted are factors affecting growth of algae in canals to determine whether there were leads to controlling algae by environmental management. No practical environmental means were found. ao(contln- One hundred-forty surface active uoua aer- aqents, solvent emulslflers, pesticides, atlon, sea- polychlorlnated bienenyls, pure water, and Inorganic, and organic chemicals were Staol eton (1968), AMIC-5980 Staoleton (1968), AMIC-5980 Staoleton (1968), AHIC-SS80 Otto(1970l, AMIC-892 Portmann, at al (1971), AMIC-7701 ------- Compound •onocthanolamlde) Coco •onoethanolamlde (olus ethylene oxide, ethoxy •one* thanoIami de) Field Field Organism Study Location Toxlclty. Active Ingredient, ppm Experlmental Variables. Controlled or Noted Comments Reference Cr angon cr angon BS» — greater than 100 -( contin- uous aer- ation, sea- water, and daily solution renewal) same as above Portmann, et at C1971), »IC-7701 Coco •onoe thanoIam 1 de •plus ethylene oxide* ethoxy monoethanoIamide) Carelnus maenas BS» — greater than 100 a«(contin- uous aer- ation, sea- vrater, and daily solution renewal) same as above Portmann. et al (1971), •HIC-7701 Coco monoethanoI am1de Coca •one* thane Iam1de Compass Cardlurn edule BS* — Crangon BS» erangon Card1urn edule 6S» — greater than a^lcontin- same as above Portmann, et 100 IT2) uoua aer- al ei<»71), atlon, sea- »MIC-7701 va t«r, nnd daily solution renewal) greater than ac-tcontin- same as above Portmann. et 100 CT2J uoug aor- al (1971), ation, sea- »«IC-7701 water, and daily solution renewal) greater than a<-(conti:i- On* hundred-forty surface active Porfmann, et 100 ITZI uous aor- agents, solvent emulslflers, pesticldest al (1971), ation, 3ea-00'vch1orln»fd blohcnyls, pure »MIC-7701 water, and Inorganic, and organic chemicals Here daily evaluated against as many as ten marine solution organisms. The authors noted that most ------- Compass Crangon erangon BSA — greater than 100 (T2J renewal) pub! Ished data of this type deal tilth toxleltv of chemicals to treshtiater organises acleontln- sane as above uous aer- ation, sea- water, and daily solution renewal) Portmann, et al (1971), AMT.C-7701 Compass Carclnus •aenas BSA — qreater than 100 (TZ) a(contin- uous aer- ation, sea- vater, and daily solution renewal) sane as above Portmann, et al (197.1). ANIC-7701 Cooper's My dlo (new typel Rasbora • BCF» heteromorpha and BSA 3.55 (TZ) Copper chloride (»s Cut Leoomls macrochlrus BSA, L 1.Z5 (Ti.1 Copper chloride (as Cu) Nltzschla linear Is BSA, I 0.81 ITS) a.c,<>, t* hard(HH) or soft (SH) synthetic dilution Hater, or seaxater for soe species a»,e, and synthetic dilution water a.,a, and synthetic dilution water One hundred sixty-lour Alabaster, , netting aqents, and (iqS9),AHIC- «i Isce I laneous water DO! lutants showed a 5"»?5 Hldf^ ranqe of toxlclty scanning 12 orders of magnitude. Knowing the toxlclty and percentage of al I co .chemicals evaluated as Otto (1970), ------- Organise Field Field Study Location Toxlclty, Active Ingredient, f>p« Experimental Variables. Control led or Noted Comments Reference amblguua percent groMth lnhlbltedl<>> Copper salts Copper salt of endothall Fish (not specified! Pnormldlua aablguua t greater than 0.1-1.0 IK) 0.5-10.0 I.MTE1 — alqlcldes, only 9 Here more toxic than AMIC-892 CuSOit. None Inhibited growth of •at-tor«Inq algae Tor more than Z Meeks. CuSO<» formulated with certain wetting agents Has more toxic than CuSOit alone. Copoer chtcrattine Mas also found to be •ore toxic than CuSO<>. Mo wetting agents Mere found to be Inhibitory at the concentrations investigated (0.05 and 0.005 DOW). Also reported are factors affecting growth of algae in canals to determine whether there t»er« leads to controlling algae by environmental Management. No practical environmental means Here found. Approximate toxlcltles of MaNdesley- numerous pesticides commonly used In Thomas(19M> Britain were summarized. An excellent AHIC-1056 brief, general discussion of toxlclty testing is also present. PI 71, chemicals evaluated as Otto (1970), alglcldes> only 9 Here more toxic than AHIC-39? CuSO<». None inhibited growth of mat-forming algae for more than 7 oeeks. CuSOd formulated with certain wettlnq agents MBS more toxic than CuSOfc alone. Cooper chloramlne was also found to be •ore toxic than CuSQ<>. No Hefting agents Mere"found to be inhibitory at the concentrations investigated 10.OS and 0.00? pp»). Also reported are factors affecting growth of algae In canals to determine whether there Mere leads to controlling algae by environmental •anageent. No practical environmental •cans were found. Copper sodiun cltratfl (as Cu) Uateralpor eueullata (larva} 0.63 (T 2 hr) ato,l, and salinity data: Ihls study was conducted to Ine gpoclea of marine Inrvaa suitable for use in test screening antifoulIng cheoieals. A salina (brine ahrlav) appeared to have the best potential for this purpose. A salina larvae sensitivity urns greatest starting at age 2O-80 hr, and tolerated relatively low pH ($.0). Wisely, et al (1967), AMIC-5703 ------- Copper sodlua citrate (aa Cu) Copper sodluB citrate (as Cu) Copper sodlua citrate (as Cu) Copper sodium citrate (aa Cu) Copper sul late plus •Ihylaryl oolyoxethylene alycols Bugula nerltlna (larvae) Splrorbla . lamellosa (larvae) Oaleolaria caeapltoaa (larvae) Kytilua edulla planulatua (larrae) Phormldlum amblguu • ^^ 3.90 IT 2 hr) 0.18 (X 2 hr) 2.90 (» 2 hr) 23 (T 2 hr) 0.5-10.0 (100 percent growth Inhibited !<•> a.c.l, and salinity a,c,l, nnd salinity a,c.l, and salinity a.c.l, and salinity as above aaaa aa above same aa above sane aa above Of 74 chemicals evaluated as alqlclces, only 9 Here more toxic than CuSOU. None Inhibited growth of •at-formlng algae for more than ? weeks. CuSOt formulated Kith certain wetting agents was more toxic than' CuSO<» alone. Copoer chloranlne was also found to be iiore toxic than CuSO ------- I Compound Copper sul fat plus Calclu* salt of polyoxyethylene Copper sul fat* plus Dodecy lethr of polyethylene glycol Copocr sul fate plus Cnulslflable polyethylene Copper sul fate plus Cthoxylated isooctyt phenoxy polyethoxy •thanol Copper sul fat plus Cthoxylated nonyl phenyl ether Copper sul fate plus Potyoxyethfene nonyl phenyl ether Copper sul fat* (as cooper) Field Field Organise Study Location Phor»Idlu« L — anblguu* Phornldlua L ~ amnlguu* Ptiornidlu* L anblquun PnoraldluB L — anblguun Phornldlua L — aablguua Phoraldlua L aabiguua Carclnus 8S» — •aenas Toxlclty, Active Ingredient. Pp« 0.9-10.0 (100 percent tjroxth Inhibited !<•) 0.5-10.0 (50 percent qroxth Inhibited lit) 0.5-10.0(?S percent growth Inhibited l ------- Copper sut fat* (as copper) CardluM edule BSA 1.0 (T2I «(contin- uous aer- ation, sea- water, and daily solution renewal) saaa as above Portnann, et al (1971) i AHIC-7701 Copper cut fat (as capper) Cranqon crangon 8S» — 19 mi •«(contin- uous aer- ation, sea- water, nnd daily solution renewal) saae as above Portnann, «t al (1971), ANIC-7701 Copper sulfate (as cepptr) Ostrea edulls BSA — too ITZ> a»(contin- uous aer- ation, sen- water, and daily solution renewal) sane as above Portaann, et al (1971), AMIC-7701 Copper sul fate las copperl Panda Ius •9«it BSA — (TZ) a»(contin- uous aer- ation, sea- water, and daily solution renewal) sane as above Portnann, et al (19711, AHIC-7701 Copper sul fate las copper) Copper sulfate Cut Plus* (as Platlcthys fIesus Sal HO galrdnerl (eggs and speral BSA — 1.0-3.3 IT2) LCF 1.0 (NTE) a«( contin- uous aer- ation, sea- water, and dally solution ronewal) i.c.f sane as above Portnann, et a» (197l>, AMIC-7701 Data were given In mq/t which xas Shax, et al taken to be the equivalent of DP. (1971), Fertilization rates were statistically XIC-1<»<>« Slnllar in both test (Cu and Nl) and control waters* The rate of hatching Has significantly different for eggs exposed to Cu and the-rate of development Has ------- Comoound Field Field Organ Is* Study Location ToxleMy, Active Ingredient, Ppn Experimental Variables, Control led or Noted Comments Reference VO fU Cooper sulfate (as Acroneurla BSA Cut Copper sulfate (as Ephemeral la BSA Cut Copper sulfate (as Hydroosyche BSA Cut Copper sulfate (as Pnoraldlu* L Cut aabiquue 8.3 0.32 (T2> 32 ITU.) 0.5-10.0 163 percent qrowth inhibited!) Increased. The authors concluded that In hard waters neither Cu nor Nl Is likely to Impair fertilization In rainbow trout. a»,c,d,e,f Ephemerella (mayfly) was the most Harnlek, et sensitive aquatic Insect of those studied, and copper the most broadly toxic metal. The authors suggest that aauatlc insects may not be as sensitive to heavy metals as fish. ,c,d,e,f same as above a,c,d,e,f Copper sul fata Pseudopleuro LCF neetea aaericanus (3 yr) 0.180 (SRI ,c,e same as above at (1969), AHIC-3767 Warnlck, etal AHIC-3767 Marnlck, etal (19<>9>. AHIC-3767 Of 71, chemicals evaluated as Otto (1970), alqlcldes, only 9 were more toxic than AMIC-892 CuSOii. None Inhibited growth of mat-forming algae for more than Z weeks. CuSOU tormulatert with certain wetting agents was more toxic than CuSOC» alone. Cooper chloramlne was also found to be more toxic than Cu30U. No wettlnq agents were found to be Inhibitory at the concentrations Investlaated (0.05 and 0.005 com). Also reported are factors affecting growth of alqae In canals to determine whether there were leads to controlling alqae by environmental management. No oractical environmental means were found. Winter flounder were exposed to Baker varied concentrations ol cooper and (1969), selected tissues examined by light and ANIC-3763 electron microscopy. Medium to high concentrations of copper resulted In fatty liver decoslts, kidney necrosis, hemoooetlc tissue destruction, and gill architectural changes as determined by Iiqht microscopic analysis. Seven additional organs or structures were ------- Copper sul fat* Coppr sulfat Pseudopleuro LCF n«ot«s aaerlcanus 13 vrl Plaephales BS* proaelas 0.560-3.3 0.08. CT4.) Copper sulfate Plaephales BCF» prove I as Copper sulfat Plaephales BCFCH proaelas Copper sulfat* lepoals L aacroeMrus o.ors mi 0.018 (T HO) 1-5 CSBl) Copper sulfat* Trachtnotus BS* caroltnus (\|uvnll«) !.«.-?. 0 ITU apparently unaffected. Low levels of eoooer caused varied anoaalles In oil I taaellae as determined by electron •icroscopy. saae as above •«(old,al CooDer at 1B.<> Dob affected f, acidity survival• growth, and scanning. Loner conduc- concentrations also reduced growth and tlvlty, soawnlrq but apparently not eaq and Cu hatcnabllIty. The naxlnu acceptable < toxicant concentration 9>, •HIC-3763 Mount, et (1969), »«IC-376S al sane as above Mount, et al 11969), »NIC-3T65 Mount, et al (1969), AM1C-376S a«,o.d,e, t, acidity, conduc- tivity, and Cu «,e,d,o, f, acidity, conduc- tivity, and Cu a,c,e,f Coooer caused a respiratory 0"H»ra Increase as concentration levels were (1971), Increased. Oreovrry from Initial stress »MIC-3793 by copper was delayed at higher concentrations. The author su99ests the f lotting Hater fish resplroneter techniaue as » fast Hnd sensitive tool for evaluating pollutants. a,c,e,f,I, In this study of ponpano salinity Birdsonq, et and Mas controlled at 10, ?0, and 30 ppt and al (1971), sulfate, Investloated as a variable, (crlflavln, AMIC-S570 sod 1UK, formalin, and potassium permanganate uere calcluH. slightly nore toxic at the highest POtasslua, salinity, Hhll* copoer sulfate Mas •agneslum, slightly less-toxic. These compounds ar* ------- Compound Toxlclty, Active Field Field Ingredient, Organise Study Location ppn Experimental Variables, Control led or Noted Comments Reference carbonate, used as cronhylactic bacterial blcarbon- treatments. All appeared to be ato, reasonably safe to use exeeote possibly sallalty potassium permanganate. Copper sulfate Copper sul tat* Copper sulfat* Copper sulfat* Copper sulfat* Copper sul fat* Oncorhynehus tshaxytscha (eggs) BCF» 0.08 (NTE) a,e,d»f OneorMynchus BCFA tshaNytscha (fry) Poccus saxatllls (fIngerlInqs) Orconeetes rustlcus BS» BCFA — Orconect» BCFCH — rustlcus Oreonectes BCFCH —- rustleus Copper (as Coooer Canptoaa BCF — sulfat) dec 1 SOB andCH Chinook salmon egqs Mere more Hazel, et al resistant to copper sulfate than were (1970), fry. Growth xas also Inhibited. Adverse AMIC-5572 effects on fry Mere noted at concentrations as low as 0.02 ppn. The authors recommend further laboratory and In situ studies. O.Oi. (93 percent K) 0.62 3.0 (T«») a,c,d,f same as above Hazel, et al (1970), AHIC-557? B.e,c,d,e, Striped bass flngprllnas Mere Met (born r,pt 8Jld anoarently much none sensitive to (1991, iron therapeutic and herbicldal compounds than &MIC-5723 many freshwater fish. a,c,«,f,a Adult crayfish Mere found to be Hubscnnan more resistant to coocer sutfate than the (1967), young. Several life stages were studied, AMIC-5985 and additional exoosure variations were included in the exoerImentation. Mortality of neMly-hatched crayfish occurred at 0.1?? pom, and growth Mas Inhibited at concentrations down to 0.015 ppn over a 70-day period. Sublethal effects of cooper Mere Hell established and the procedure appears to be a good one. 1.0 (TU) 0.015 (SB) 1.7 (TV) a,c,e,f,Q a,c,e,f,q same as above sane as above ,c,d,e,f Survival, qroHth, reproduction, and feeding Mere the responses used to Hubschman (1967) , AMIC-5985 Hubschman (19675 , AMIC-5985 Arthur, et al (1970), ------- vi) vn Copper (as Copper sulfate) Copper (as Copper sulfate) Copper (as Cooper sulfate) Campeloaa dec 1 sun BCFA and CH Physa Integra BCFA and CH Physa Integra BCFA and CH Cooper (as Cooper sulfate) Cooper (as Copper sulfate) Cooper (plus PHENOL > Gammarus paeudo- llan«ua Gammarus paeudo- llnaaaua Sal «o galrdnerl BCFA and CH BCFA and CH BSA Cooper (plus Zinc, nickel) Sat «io galrdnerl BSA 0.008-0.011(8 (NTE6 Hh) 0.019 (T) a,c,d,e,f a,c,d,e,f a,c,d,e,f a,c.d«e«( 0.008-0.01 oom. Safe limits for Gammarus were O.OIH6-0.008 In a continuous flok system and fl.01Z9-0.OZ39 In a static system. same as above same as above same as above same as above same as above Arthur, et at (liroi, AMIC-967 Arthur, et al (1470), AKIC-8S7 Arthur, et al (1970), ANIC-867 Arthur, et al (1970), ANIC-K67 Arthur, et al (1970), AMIC-867 PalnboH trout Here exposed to Brown, et copoer, phenol, zinc, or nlcKel solutions al(1970), to determine i>8-hour LC90 values for AHTC-S994 mixtures of copoer and phenolt copper, zinc, and phenol> and copper, zinc, and nlcKel. It Has concluded that acute lethal toxlcltles of the mixtures could be adequately described by summations of the fractional toxlcltles. same as above BroHn,«t al (1970), AHIC-599% ------- Toxlclty, Experimental Active Variables. Field Field Ingredient, Controlled Comoound Orqanlsm Study Location Ppm or Noted Convents Copper (plus zinc, Slao BSA — 0.6-Z.<>0 (T2) a.c.e phenol) qalrdnerl Cooper A lose FL Great Lakes 0.9Cresldue) pa«udo- - Superior, harongu* Michigan, and Erie same as above Trace element content of fish from Lakes Suoerlor, Michigan, and Erie Mas determined by activation analysis. Whole body and liver residues were determined* Concentrations varied Hlth species and lake. Other elements found Here! antimony - 5 to 100 cob, barium - 0.7 oom, cesium - 3 oob, lanthanum - 1 to 20 pobt mercury - 10 oob, rhenium - 0.5 to •> pob. rubidium - 0.06 to 6 opm. scandium - ? ppb. selenium - 0.1 to 2 ODb, silver - 0.001 oob. Reference RroMn.et al (1970) , AMIC-5S9U Lucas, et al 11970). ANIC-3778 Copper Copper Copper Copper Copper Copper Coreqonus FL artedll Coreqonus FL clupeaformls Coreqonus FL hoy! Prosoplum FL cyl Indraceum Salvellnus FL naaaycush Osmerus FL mordax Great Lakes - Suoerlor, nichlqan, and Frle Great Lakes - Suoerlor, Michigan, and Erie Great Lakes - Suoerlor, Michigan, and Erie Great Lakes - Suoerlor, Michigan, and Erie Great Lakes - Suoerlor, Michigan, and Erie Great Lakes - Suoerlor, Michigan, end Erie 12(resldue) 5.(residueI <».9(resldue) 3.8 ------- Copper Copper Copper Copper Copper Copper Car-ass 1 us FL auratus Notroois Fl hudsonlus Percoosls FL omlscomaycus Roecus chrysops FL Peres FL I lavescens• SHzostedlon FL vltreum vltreum. Great Lakes l ------- Compound Copper Copper Copper Copper Organise Esox tuclus Osmerus •ordax Perca f lavescens Sal vel Inus Toxlclty, Experimental Active Variables. Field Field Ingredient. Controlled Study Location Ppm or Noted FL Lake Erie, 0.7 (residue) -- Can. ' FL Lake Erie. 0.8 (residue) — Can. FL Lake Erie. 1.3 (residue) Can. BDFCH — 0.018 (NTE) a.c,de.f Comments Reference sane as above Uthe, et at 3819 sane as above Uthe et al (1971), MIC- 3819 same as above Uthe* et al 3819 A concentration of 17.5 ppb McKIm, et a fontlnalIs (eqgs) Copper Copper Copper SalvelInus fontInalis (Juveniles) SalvelInus fontlnalls (adults) BDFCH BOFCH — 0.017 (K) 0.1 ITI.I cooper did not adversely affect survival, (1970), qroHth, or scanning of brook trout. ANIC-38Z1 However, this concentration level had drastic effect on Juvenile trout. The coooer also delayed yolk sac absorption and delayed fry development. The maxlaun acceotable toxicant concentration (NATO was calculated to be between 9.5 to 17.fc ppb copper. a*cdef same as above «cKlm,et al (1970), AMIC-3821 a'.c.d.e.f sane as above Paralabrax Fn Scattergood 2 (dorsal clathratus Stean Plant* nuscte LosAngeles. RESIDUE) Cal. Fish collected from an effluent oio* of a steam plant and from offshore Haters of Catallna Island Mere analyzed for trace element content. Trace element content of the effluent Hater Has at least 5 times qreater than that of nornal sea xater for cadmium, cooper, nickel, zinc, and chromium. Livers of fish from the effluent Here nearly twice the size of those fron the ocean. Greatest differences in concentration occurred with alumlrun* cadmium* and nickel. Silver, barlun, lithium, and lead shoxed the least differences. The author etal (1970), 4MIC-3S31 Stapleton (1968), ANIC-5980 ------- Copper Copper Copper Copper Copper Copper Copper Paral abrax FH Catal Ina ? (dorsal clathratus Island, Cal. muscle residua) Paral abrax FH Scattergood Z (ventral elathratus Steam Plant, muscle LosAngeles, residua) Cal. Paral abrax FN clathratus Paral abrsx FH clathratus Catal Ina 2 (ventral Island, Cat. muscle residue) Scatter-good 6 (gonads Steam Plant, residual losAngeles, Cal. Par a! abrax FH Catal ina 5 (gonads clathratus Island, Cal. residue) Paralabrax FH CatalIna 5 elathratus Island, Cal. (gonads (gravid residue) females) Paralabrax FH Scattergood 5 (liver clathratus Steam Plant, residue) LosAnoeles, Cal. Paralabrax FH CatalIna 6 (liver clathratus Island, Cal. residue) concluded that trace element analysis of tissues could be used to determine the effect of pollutants on marine organisms. same as above same as above same es above same as above same as above same as above same as above same as above Staoleton (1168), AHIC-5980 Staoleton (1468), Staoleton (1965) » Staoleton (106(0 . Staoleton (196.1), AHIC-5980 Staolcton (1 ------- Compound Organise Field Field Study Location Toxlcltv, Active Ingredient, Pp« Experimental Variables! Control led or Noted Comments Reference Copper Capper Copper Paralabrax clathratus Paralabrax clathratus Paralahrax clathratus Selmo galrdnerl FM FN FN BS» Cal. Catallna 1? (heart Island. Cat. residual Scatterqood a (eyebal I Steaa Plant, residue) LosAngeles* Cal. Catallna IsI andf Cal< V Ceyeball residual 0.75 (TZ) a.e.e Corexlt 766* Plmeohales BSA pr one I as 3200 c,d,e,f Corexlt 7664 Corexlt 766% Corexlt 7664 Plmephales prone I as BS* — Biochemical I oxygen deaand Steel head trout (fingerlings) BS* — 180 (MSC) 380,000 15.8 (T4) c.d.e.f c.d.e.f sane as above same as above sane as above Staoleton (1968), Staoleton (I960), AMIC-5980 Staoleron (1968), HIC-S960 RalnbOH trout Mere exposed to Brown, et at eoooer, Dhenol, zinc, or nickel solutions to determine ".S-hour LCSO values for (1970) ,MIC- • Ixtures of cooper and phenol I copoer, 599I> zinc, and phenol I and cooopr, zinc, and nickel. It was concluded that acute lethal toxlcltles of the mixtures could be adequately described by summations of the fractional toxlcltles. Toxlclty of six oil spill dlspersants Has determined along with BOO values. Pond Mater was used as diluent and oil Mas Included In the exoerlment. Oil narked Iy reduced toxiclty of all dlsoersants. Data are given as *nost probable" 96-hr TL sub a. saae as above saae as above milch (1969I.AHIC- 71lllch ------- Corexlt 766I\|. Corexit 7661). Corexlt 766V Coho salmon B3A Hood Canal (flngerllnga) In Hoodaport, »ltu Wash. Pacific oyster (larvae) B3A Hood Canal In Hoodaport, situ Wash. Card luii edule as — UO.O (K) UO.0-80.0 (SB) 3300-10, OJ»U (TZt Corexlt 766V Cra r>g on er anqon BS« — 3300-10,000 ITZ) 776t, appeared to have the least toxlelty .With fair to qood oil dispersion capability. same aa above sane aa above *(contln- One hundred-forty surface active uous ear- agents, solvent enulslflers. pestleldest ation, aea-Dolychlorlnated biohenyls, cure water, and Inorganic, and organic chemicals were dally evaluated against as many as ten aarlne solution organises. The authors noted that nost renewal) published data of this type deal with toxlelty of chemicals to freshwater organises. sam as above a* Icontin- uous aer- ation, sea- water, end dally solution renewal) Tracy, at ai (1969), AKIC-363I. Tracy, et al (1969), AMC-33314. Portnann, et al f19711, •HIC-7701 PortBann, et al (1971). 4HIC-7701 Cerekif 766 Lieanda I Inland* BS» — 1000-3300 (TZI a»(contin- uous aer- ation, sea- wator, and dally solution renewal) seme as above Portxunn, et al (1971). •HIC-7701 Corexlt 766<> Sal no salar loarrl CorelIt 766% Gannarus oceanlcus 8S» — 500 (NTCVt a.e Aroclors IPS", and 1??1 Mere 71tKo Inlxed tap evaluated for toxic effect with Corexlt (1970), or 76f>«. (Height ratio »;! ------- Compound CorexIt 766H Corexlt 6666 Couaaphos Toxlclty, Experimental Active Variables, Field Field Ingredient. Controlled Organism! Study Location Pom or Noted Comments Gammarus BSA — oceanlcus Crangon BSA — crangon 0.19 (SB) a (weeklysol utlon change. seawater) 3300 (TZ) a{ contin- uous B.CC- concentrations down to 0.19 pom. The author notes a possible synerglstlc effect between the two compounds. same as above One hundred-forty surface active agents, solvent emulslflers, pesticides. Reference Mlldish (1970). AHIC-R9 Por tmann, al ation, sea-Pol ych lorlnated blohenyls, pure (1971), MI Rasbora BCFA — heteromorpha and BSA water, and daily solution renewal) 0.046 (T2> a,c,e,f. hard (HW) or SOFT(Stl) synthetic dilution water, or seawater for some species inorganic, and organic chetricals were evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal with toxlclty of chemicals to freshwater organisms. One hundred sixty-four pesticides, wetting agents, and miscellaneous water pollutants showed a wide range of toxlclty spanning 1? orders of magnitude. Knowing the toxicity and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides were nost toxic In hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. 7701 Alabaster (1969), AMIC-5I.Z5 Co-al Norone saxatllls (fingerI Ings) BSA —• 6Z Co-DaI Mercenarla mercenarla (eggs) 9.12 (T2) a,c,d,e,f, All compounds were Investigated Me 11 born p because of thelP probable usaoe In (1971), hatchery production of white bass AH.IC-5ST1 Comnounds that can be used at recommended concentrations were Aouathol, Casaron, Llndane, and Terramycln concentrate. Those that should not be used wepe Acrlflavlne, Raylusclde, Malachite green oxalate, and Malathion. -- The effect of 52 pesticides on Oavls, et al embryonic development of clams and oysters was reported. Synerglstic (1969),AMIC- effeets with solvents were also reported. 5990 Host of the compounds affected ------- k U) Co-ffal Co-Ral Co-Rat Craln* OS* Hercenarla mercenarla (larvael Crassostrea vlrglnlca (eggs) Crassostrea vlrolnlca (larvael Crangon crangon BS» (T 12) 0.11 IT?) greater than l.O (T iv) 330-1000 IT2) Cresol* •genus BS» cataohraetus 10-33 (T2) Crcsols Carclnus aa«nas 10-100 ------- Ceaoound Cresols Creselm Cr»ssauard Crotothane CFOM solvent N Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Organism, Study location Pom or Noted Comments Cardlum edule BSA — Pleuroneetes BSA olatessa Crmngon BSA crangon greater than a«(contin- 100 tT2) uous aer- ation, soa- watcr, and dally solution renewal } 10-33 (T?> a»( contin- uous aer- ation, sea- water, and daily solution renewal) 3.3-10 IT) alcontln- uous asr- same as above One hundred-forty surface active aqents, solvent emulslflers, pesticides. Pol vchlorlnated blphenyls, pure Inorganic, and organic chemicals Mere evaluated aqalnst as many as ten marine organisms. The authors noted that most published data of this type deal with toxlclty of chemicals to freshwater organisms. One hundred-forty surface active aqents, solvent euls 1 f lers, pesticides. Reference Portmann, et al (10711, A«I C- 77 01 Portmann, et • 1 (1471), AMIC-7701 Portmann, et al ation, sea-oolychlorinated blphpnyls, oure (iq71),AHIC— Pasbora 8CFA — heteromorpha and BSA Crangon BSA crangon wator, euid daily solution renewal ) 0.07 (T2) a«,c,e,f. hard (HM)or cnffr ICU1 soil I^HV synthetic dilution Hater, or seawater for some species 33-100 IT?> a»( contin- Inorqanic, and orqanlc chemicals Mere evaluated aqalnst as many as ten marine organisms. The authors noted that most Published data of this type deal with toxlclty of chemicals to freshwater orqnnlsms. One hundred sixty-four pesticides, wettinq aqpnts, and miscellaneous water pollutants Showed a of magnitude. Knowlnq the toxlclty and percentage of all comoonents of a formulation did not result in easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides Mere most toxic in hard Mater and sometimes the opposite was true. Testing the actual material as sold Has found to be essential. One hundred-forty surface active uous aer- aqents, solvent emulslflers, pesticides. ation, sea- polychlorlnat ed blohenyls, oure 7701 Alabaster, tl9&9>,»«IC- Si.?S Portmann, et al (1371), AHIC-7701 water, and Inorqanic, and orqanlc chemicals Here dally evaluated aqalnst as many as fen marine solution orqanlsms. The authors noted that most renewal) published data of this type deal with toxiclfy of chemicals to freshwater organisms. ------- Cr, Nit Cut CN, and Plnephales BSACF Grand River between Zn prone I as (ML) at 1.25-3.75 Hyo»lnq,Mlch oercent (T3) Iqan Cr, Nit Cut CH, and Catostoeus In conncrsonl CS Wolffls. papullfera BSACF Grand River between CHU at 1.25-3.75 Uyonlnq.Hlch percent (T3) I gen 100 (K) A mobile'bloassav unit Has utilized to conduct this study ot Municipal Hastenater containing the indicated toxicants. River wafer Has a,c,e, used as diluent. The conclusion M»S 71IIIch conductIvl reached that synerglstlc or additive (1969), ty. Nit toxic effects occurred since toxlcltv Has AHIC-?9P6 Cu, Cr, greater than that ot any ot the Ions CN, and 7n singly. a,c,e. conductlvi ty. Nit Cu, Cr, CN, and 7n Hunter'a modlum diluted 1:5 saae as above 711llch (1969), ANTC-294J6 All conpounda wore harmful to Worthier, at duckweed to gone decree. Decreased el,(1971), populations were noted at non-lethal AMIC-3233 concentrations and some compounds (Mmlathlon and 2,^-D) caused toratoganlc effects at concentrations as low as 1 ppm. CuCIZ ?H?0 (as Cu) \n Platvonas subcordl- formla a ^^ CuCI? ?H20 (as Cu) Porphrrldlu> L cruentua approx.1.0 (K) appro. 0.5(K) 5SM and NSW SSN and NSM NT stimulated algal tiroHth In FrlcKson, at cultures without added copper and reduced al (19701, toxlclty ot copper at all levels of »Mlc-fc«.9 cooper addition. See information on CuCI2.H20 (as Cu) under authors cited for •further Information. saae as above Erlcfcson, at al (1970), CuCie 2H20 (as Cu) Skeletone»a L — costatua aporox. 0.15 SSM and (K) NSM saae as above Erlckson, et al (1970), CuCI2 2H20 las Cu) ••ohldlnlun L — carterI CuCIZ 2N20 (as Cu) Chactoecros L so CuCIZ 2M29 (as Cu) Cyrlotella L — nana CuC12 2H20 (as Cu) Dunalialla L tortioleeta CuC12 2B20 (as Cu) Isochryala L Salbana less than 8.05 SSM and (K) NSH approx. 0.05 SSM and (K) NSH approx. 0.15 SSM and (K) NSH U50 (5o percent S3K and K) KSW Approx. 0.2 K) SSM and NSW sane as above saae as above saae as above SUM as above sane as above Erlckson, et al (19701, Erlckson, et • I (147«t. Erlckson, at al (1970), Erickscn, et al (1970), AKIC-U49 Erlckaon, et al (1970), AKIC-IA9 ------- > I Compound CuC12 2H20 (as Cu) CuC12 2H20 Us Cu) CuCIS 2H20 (as Cu) CuC12 23120 (as Cu) Cunllate RQ Z* Cunllate RQ Z* Cunllate RO 2* Organism Monochrysls Lutheri Nannochlorls oculata Nltzschla cloaterlum Ollsthodlacus luteus Salmo galrdnerl Rasbora heteromoroha Rasbora heferomorpha Toxiclty, Active Field Field Ingredient, Study Location Pom L L L L BCF» — and BSA BCFA — and BSA BCF4 — and BSA Approx. 0.5 (K) Approx. 0.5 (K) Approx. 0.05" (K) Approx. 0.05 0.9 trz. hardMater) !.<» ITZ, sof tnater) 0.9 (T2, nardHater) Experimental Variables. Control led or Noted Comments SSM nnd NSW SSM and NSW SSM and NSW SSM and NSW a* c e f hard (HH ) or SOft synthetic dilution orseawater for some soecles a,c,e,f , hard(HH) or soft (SHI synthetic dilution Mater, same a a above same as above same as above same as above One hundred sixty-lour pesticides, wetting agents, and MUe range of toxlclty scanning 1? orders percentage of all components of a formulation Hid not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides Mere most toxic in hard Mater and sonetlmes the oooosite xas true. Testing the actual material as sold Mas found to be essential. same as above same as above Ret erence Erlckson, et al (1970), Erlckson, et al (1970), AKIC-uV? Erlckson, et E! (1970), AKIC-U49 Erickson, et £l (1970), Alabaster <1969),A1IC- Alabaster <1969I .AKIC- 51.25 Alabaster (1969) .A1IC- 5425 ------- Cuprlc ammonium sulfate (as Cu) Phormidlum amblguum Cuprlc chloram In Cuorle sulfate Phormldlum anblquum Salve IInus fontlnalIs 16-8 in.) BCFA -- Cuprlc sulfat* Cuerlnol SalvelInus fontlnalls (6-8 In.) Cranqon crangon BCFCH BSA orseawater for some species 0.5-10.0 (16 Percent growth inhibited!!) 0.5-10.0 (100 percent growth Inhibited !<•> 0.038-0.069(59 6 and Zl) Of 7i» chemicals evaluated as alqlcldes, only 1 were more toxic than CuSOU. None Inhibited growth ot mat-forcing algae »or more than 2 weeks. CuSCKf formulated with certain wetting agents was Jiore toxic than CuSOit alone. Coopr chloramine was also found to be more toxic than CuSOU. No wetting agents were found to be inhibitory at the concentrations investigated (0.05 and 0.005 CP">>. Also reoort-d are factors affecting growth of algae in canals to determine whether there were leads to controlling algae by environmental management• No Dractica! environmental »e-ans were found. same as above 0.017-0.033(58 337) 3.3-10 (TZ) a(c«»tfta The seven blood characteristics of brook trout studied were red blood count, hematoerlt, hpmoaloblnt plasma chloride, plasma qlut^mic oxalscetlc transanina<;e« osmolarltv, and total protein. Statistically slonlflcant changes were noted in 5 characteristics after 6 days. Measurable decrease in plasma glutamlc oxaMcetic transaninase was the only change noted after long-tern exposure to lower concentrations. The authors state that fish blood study can be used as a treasure of their physical condition and lonq-ranqe forecasting of reproductive success and survival. atcQ same as above a«(contln- One hundred-forty surface active uous aer- agents, solvent emulsiflers. pesticides, ation, aea-oolychlorlnated blphenylst Pure water, and inorganic, and organic chevieals were daily evaluated against as many as ten marina solution organisms. The authors noted that most renewal) Published data of this type deal with toxlclty of chemicals to freshwater organisms. Otto (197fl», ANIC-89.? Otto (1970), AMIC-892 McKlm, et at (1970). ANIC-3H28 HcKlm, et al M<70) , AtIC-3828 Portmann, et al (1471), AMIC-7701 ------- Compound Co. Zn HI, Cr, Cu, Zn HI, Cr, Organise CH, and Pimeohales crone las CNt and Catostomus commer son I Field Field Study Location BSACF Grand River (ML) at Wyoming, Mich Iqan BSACF Grand River (ML) at Wyoming, Mich Igan Toxlcity. Active Ingredient , Pp- between 1.25-3.75 percent (T3) between l.?5-3.TS percent (T3) Experimental Variables. Controlled or Noted Consents a,c,e, con- A mobile bloassay unit Has ductlvlty, utilized to conduct this study of Kl,Cu,Cr, Municipal wastewater containing the CH, and Zn Indicated toxicants. River water was used as diluent. The conclusion was 'reached that synerglstlc or additive toxic effects occurred since toxlclty Has greater than that of any of the Ions singly. •,0,0, con" sa»e as above ductlvlty. Nl.Cu.Cr, CH, and Zn Reference 711 llch (1969), AMIC-2906 Zllllch (1969) . ANIC-2906 > I ex Fundulus BSA heteroclItus 0.00051-0.00225 a,c,e. (TO and synthetic. seawater CX Cyanides Nereis vlrens BS» — Leoouls BSA aacrochlrus 0.00078-0.0071 (TO 0.11 a,c,e, and synthetic seawater a»e, and synthetic dilution •ater A laboratory procedure based on •Standard Methods Tor 96-hr toxlclty determinations of crude oil and oll-disoersant mixtures was described. The dlsoersanfs varied considerably In toxlclty, ranging from 0.01 to 7.1 ml/1, TL50 for 96 hr. These did not differ significantly from 2 ------- Cyanides Cyclohexlmlde Physa BS» heterostrooha Phormldlum •mblguuB Oalaclda ftasbora heterooorpha BCFA and BSA 620 (TZI Oalapon Oafapon Fish (not specified! Rasbora heteromoroha BCF» and BSA greater than 100-1000 (K> greater than 500 (TZ, hardwater) a»,e, and synthetic dilution Hater same as above 0.5-10.0 (66 percent growth inhlbltadl ,,, bard (HWJ or soft (SWJ syn- the tic dilution water, or sea, water for sona spaeles a'.c.e.f, hard (HW> or soft (SM) synthetic dilution Hater, or seawater (or some Patrick, «t al (1968), ANIC-5720 Otto (1970), AHIC-B92 OT 7i» chemicals evaluated as atgicldes, only 9 Here more toxic than CuSO(». None Inhibited growth of ma t-f orminq algae for more than 2 weeks. CuSOU formulated with certain wetting aaents was more toxic than CuSO alone. Coooer chloramlne Mas also found to be more toxic than CuSO25 Hide range of toxlclty scanning l? orders of magnitude. Knowing the toxlclty and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides were most toxic In hard water and sometimes the ooooslte was true. Testing the actual material as sold was found to be essential. Aooroxlmate toxlcltles of Mawdesley- numerous pesticides commonly used In Thomas Britain were summarized. An excellent ( 19711 ,A1IC- brlef, general discussion of toxlcity 1056 testing is also present. One hundred sixty-four Alabaster pesticides, wettlnq agents, and (1969), miscellaneous water pollutants showed a AMIC-5V25 wide range of toxlcity spanning 12 orders of magnitude. Knowing the toxicity and percentage of all components of a formulation did not result in easy predictability of the toxlclty of a mixture of Materials. Sometimes ------- Compound Organism Field Field Study Location Toxiclty, Active Ingredient, PP» Experimental Variables. Control led or Noted Comments Reference species Oalapon Rasbore BCF* — heteroeorpha and BS« > I Oalapon Cardlum edule BSA — 3 «T3, sot t water) greater than 100 (TZ) a.c,». 1, hard (HH)or soft (SHI synthetic dilution water, or sraMater tor so>e species a«( contin- uous aer- ation, sea. water, and dally solution renewal ) Oalapon Crangon crangon BSA greater than 100 (TZI pesticides Mere most toxic In hard Mater and sometimes the opposite Mas true. Testing the actual material as sold was found to be essential. same as above alabaster a«{contin- uous aer- ation, soa- water, and daily solution renewal) One hundred-forty surface active •an»nts. solvent emulsIflers. pesticides. .polychlorlnated blphenyls. cure Inorganic, and organic cheirlcals Here evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal with toxlclty of chemicals to freshwater organisms. sane as above Portm»nn, et al (1971), AMIC-7701 Portmann, et al Cig71), •«c-rroi Oalapon Platlcthys flesus BSA — greater than 100 (TZI a«(contin- uous aer- ation, sea- water, and daily solution renewal) sane as above Portmann. et al (1971), AMIC-7701 DBP Palaenonetes BCF Nadlakensls O.OB (residue) a* Magnification of DOT and Aldrln tagged with C-14 occurred rapidly. Johnson, et al ------- 08 P ODD «C-1* label led) Palaemonetes, BCF KadtakenIs Sorghum ha I oanse L (Mod- el •oo sr •tarn) O.OOOl (SB3) 1 Ib per A (NTE) a,c»g, standard reference water and sand > 000 fC-lt labelled) Estlqmene acrea L (Mod- el ecosT •tea) 1 Ibper A CK-NTEI standard reference water and sand Bloloqlcal magnification factors of 2900 to 11»»100 depending on the species Mere found for ODT, and ZZ,HOD to IM.DOO for Aldrln. Harked degradation of DOT as determined by analysis for ODT •etabolltes occurred. The authors conclude that aauafIc Invertebrates Influence Quality and Quantity of Insecticide residue passed via the fish food chain. same as above U97i),A1IC- 3S20 This snail laboratory model ecosystem procedure was develooed to study pesticide biodegradabiI 1ty and ecoloolcal maqnl»leaf Ion. The food-chain pathways In this system Mere? (1) sorqhuir - caterplller (larva), (?) caterolller (excreta) - flerloqonlum, (3> Oedoqonlum - snall< d) Estlamene (excreta) - diatoms* C5) Diatoms - plankton, tfi) Plankton - Culex (larva), (7) Culex - Cambusla. The fish is the too of the food chain. Using isotoplcally labeled orstlcide^ (1 Ib/acre application rate), residues Mere determined for only selected organisms (snail, mosquito, and fish) and water. Reoroduclbl11ty appeared to be good. The authors state that the method gives a good estimation of the potential toxlclty of pesticides and their breakdown products to a variety of organisms and is suitable for computer modeling. sane as above Johnson,et at (1971), AMIC-3S20 Metcalf, et al (1971), AMIC-K.95 Metcalf, et al (1971), 000 (C-l label ltd) Physa soo L (Mod- el ecosr sten) 5.6 (residue) standard reference water and sand same as above Metcalf. et at (1971). AMIC-H95 ------- Coeoound 000 (C-l* labelled) ODD (C-l* labelled) ODD CC-1» labelled) 000 (C-lt labelled) 000 (C-l» labelled! 000 IC'lt labelled) ODD ------- ODD'(C-1» label!•«) H»t«r X (Hod- •1 0.006 (residue) standard reference water and •and ••• as above detcalf, at al (197H, •HIC-U95 000 fo.0") •nqullia rostrata FRl St. John, N.B., Can. 0.19 (residue) — 01 000 , 4MIC-371S S(n«ol«s of Hiiter, silt, hot ton Houbry, et debris, bottom organisms, and fish were »l taken in 1966 from a creek adjacent to an (1968),HIC- orchard which had heen treated in 3753 1963-10&5 with various chlorinated hydrocarbon pesticides. No residues were found In water samples. Silt samples contained 0.003-0.013 ppm endrln and 0-0.005 po* dteldrln. Endrln residues of 0.011-D.075 pan and 0.(IO?-I).006 pp* dleldrln were found In debris samples. Oesolte United control data, residue analyses indicated that contamination of the environment studied was United. ------- > H ODD 000 ODD 000 000 000 000 Organism Phlnlchthys atratulus Gamnarus so* Salvel Inus fontlnalls Semotl lus atromacul atus Cottus balrdl Stalls sp. (larva) Car ass lus auratus Field Field Study Location FS Knlqhts CreeK, Oun County, Misc. FS Knlqhts Creek, Oun County, wise. FS Knights CrreK, Oun County, Nlsc. FS Knlqhts CreeK, Oun County, Misc. FS Knlqhts CreeK , Oun County, Wise. FS Knlqhts CreeK, Oun County, Misc. L — Toxiclty, Experimental Active Variables, Ingredient, Controlled Ppa or Noted Comments 0.78 -- sane as above (tat residue) 0.007 (Hhole — sane as above bodyresldue) residua) 0.26-1. flii -- saae as above (fat residua) 0.53-0.67(f at — same as above residue) O.V-0.<>7 (fat -- saae as above residua) 0.003 -- sane as above (Hholebody residue) 0.1-0.8 a Goldfish Mere exoosed to (residua) Increasing concentrations of DOT and Reference Moubry, et al <196«), AMIC-3753 Moubry, ------- ODD ODD 000 DOO Palaemonetes BCF ka4IaVensIs (adult) Daphnla maqna BCF (adult) Pal»emonete« BCF — Kadlakensls (adult) 0.0* (residue) a* 0.0001 (SB3) 0.0001 (SBJ) JOnnson, at 81(1971), Johns on, et al (10711, Archoplltes FL Clear Lake. 316 Cflash Interruotus Cat. residue! sa>e as above saae as above same as above Johnson,et al (1971), »Hic-3s?o Residue analysis results mainly Linn, et al for TOE in fish, birds, and plankton from, (1969),' 1959 through 1965 were reported. The AMIC-5521 residues primarily resulted from application of DOT to farmland and for gnat control. In some cases, data for a single animal In one year Here given. Primary emphasis Mas on largemouth bass and white catfish. The general level of TOE contamination in birds and fish declined markedly from 1958 to 1965. This decline correlated directly tilth strict limitation by permits of DOT applications during the latter years. V/l 000 000 000 Orthodon FL •ierolepi- dotua Pomoxls FL nlgromaeulatu s •echnophorus FL oeel . •HIC-55?! ------- Comoound 000 000 000 000 000 000 ODD 000 000 Organism •rehoolltes Interruotus Ictalurus catus Ictalurus catus Lavlnla exl llcauda Lenomls cyanel lus Leo om Is cyanel lus Mlcrooterus salmoldes Mlcroot^rus sal mo ides Perca f 1 avescens Field Field Study Location FL Clear Lake, Cal. FL Clear Lake, Cal. FL Clear Lake, Cal. FL Clear Lake, Cal. FL Clear Lake, Cal. FL Clear Lake, Cal. FL Clear Lake, Cal. FL Clear Lake, Cal. FLR 93 sampling Mass. Toxlclty, Active Ingredient, 3,972 (fat residue) 1.3-1S<» (flesh residue) 220-2.350 (fat residue) less than 1-2 (flesh residua) 2 (flesh residue) 103 (fat residue) 0.2-111 (flesh residue) 28-1.37 (fat residue) 0.2«.-5.7 Experimental Variables, Control led or Noted Comments Reference -- same as above Linn, etal AMIC-5521 -- same as above Linn, et -- same as above Linn, et ANIC-5521 -- same as above Llnn,et al (1969). AMIC-5521 -- same as above Linn, et al (1969),«MIC- 5521 same as above Linn, et al (1969) , 4MIC- 5521 sane as above Llnn.et at same as above Linn, etal (1959), AMIC-5521 ™ Fish Indigenous to Massachusetts Lynan, et a: and DOT metabolites during 1965-1967. AMIC-3839 Generally there Has an Increase In oestlclde content during the three year period. 000 Leooals FLR 93 samollng 0-6.T same as above Lyaan, et at ------- ODD DOO 000 090 000 000 ODD 000 OOO OOO 000 000 gibbosus Catostomus FLR FLR FLR FLR letalurus nebulosus Cyprlnus carolo Esox niger Noteniqonus FLR Senotilus FLR corporal Is FLR •aerochlrus Anhlonlltes FLR ruoestrls Seaotllus FLR atronaculatus Mlcrooterus FLR dolomieui • losa psudo- harengu FLR FunduIus FLR hetroelItus stations In Mass. 93 saaoling stations in Mass. 93 saMoling stations in Mast. 93 sanotlnq stations in Mass. 93 sampling stations in Mass. 93 sanpllnq stations in Mass. 93 S4niol inq stations in Mills. 93 sainDl ing stations in Mass. 93 saopling stations in Mass. 93 sampling stations in Mass. 93 sanDling stations In Mass. 93 saiiDlinq stations In Mass. 93 sanoling stations In Mass. (residue) 8.03-12.5 (residue) 1.2 (residue) 0.?«.-!.9 (residue) 0.30 (residue) — B.15-2.7 (residue) D.07-1,.3 (residue) (residue) 0.30-10.8 (residue) o.ie-o.61. (residue) 0.20-0.90 (residue) 0.88 (residue) 1.7-3.6 (residue) sane as above sane as above saae as above saae as above ja»e as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above (198), MIC-3839 Lyaan. et al (19M), IMIC-3839 Lywsnt et al (1968). »HIC-3839 Ly»an. et al <1«68) t MIC-3839 ly»an, etal (1951), 4MTC-3SJ9 Lyn^nt «t al (1968). •MIC-3839 Lynn, et at (196M. »MIC-3839 Ly«an, et al Lynan, et al (196S) i •HIC-3839 Lyman, et al (19S8>< tMIC-3839 et al (196S). •HIC-JSJ9 lynan, et al (19fi8) , »MIC-3839 Lvoan, et al (1968), AMIC-3839 000 NotroDls FLR 93sa«Dllnq 0.8-2.0 saae as above Lyaan, et al ------- CD Conoounl 000 000 000 ODD ODD Organism cornutus Roccus amerlcanus Pomoxls nlgro- maculatus Leoomls aurl tus Phinichthys atratulus Cyprlnus carpio Field Field Study Location stations In Mass. FLR 93 sampling stations in Mass. FLR 93 sampling stations in Hiiss. FLR 93 sampling stations In Mass. FLR 9* samollnq stations In Mass. FR St. Lawrence Plver, Toxlclty, Active Ingredient, Ppm (residue) O.I.-1.3 (residue) 10.7 (residue) 0.1.6 (residue) O.VO (residue) 0.38(0.1.0 Don max tissue Experimental Variables, Control led or Noted Comments Reference (19MI, AMIC-3839 -- same as above Lyman, et (1968) . AHIC-3839 same as above Lyman, et (IQftft) , AMIC-3839 same as above Lyman, et ( 196(1) . AMIC-3839 ~- same as above Lyman, et ( 1968) , AMIC-3839 -- Residues of Onn were measured In Fredeen, nater, mud, molluscs, and fish during and al (1970) al al al al et , Montreal, residue) Canada after ODD aoollcatlon In 1967. Samoling AHIC-53". DOlnts Here above the point of aoollcatlon and 10 and 0 DDK Plver, max tissue Montreal, residue) Canada St. Lawrence 0.3X0.5? pp> River, max tissue Montreal, residue) Canada St. Lawrence 0.3S (0.<><>PD* River, max tissue Montreal, residue) Canada sane as above same as above sane as above Fredeen, et al (1970) .ACIC- Fredeen, et al (1Q70). AMIC-5J1. Fredeen, et al (1978), 4MIC-53". ------- 000 000 000 OOD ODE IC-1V labelled) F.SOX luclus FR Amblootltes Plsldlum sp. FR Caopeloea sp. FR Sorqhu» ha loans* L Uiod- el ecosr staa) St. Lawrence 0.3S (1.31 River, pommax tissue Montreal, residue) Canada St. Lawrence 0.34(0.25 pp» River, max tissue Montreal, residue) Canada St. Lawrence 0.38 (O.OOlppm River, max tissue Montreal, residue) Canada St. Lawrence 0.38 (O.ZZppm River, max tissue Montreal, residua) Canada 1 IB par A (NTEJ a.e.g. standard reference Mater and sand OOE IC-lt labelled) Estlqaene aerea L (Mod- el eeosy •torn) 1 Ibper A (IC-NTE> a.c,q, standard reference Mater and sand sane as above sane as above same as above same as above Fredeen, et at 11970), AMIC-531. FreSeen, et al 1, 4MIC- Fredeen, et al (1970), •MIC-53* Fredeen, et al (1970), AMIC-53H This snail laboratory model ecosystem procedure was (level ooed to study cestlcide blotleqradabl 11 ty and ecological magnification. The food-chain oathwavs In this system were! (1) sorqhuw - caterpllier (larva), (2) caterolller (excreta) - Oeioaonlu", (3) Oerloqonlun - snail, (i») Estlqmene (excreta) - diatoms, (5) Diatoms - plankton, (6) Plankton - Culex (larvae), (7) Culex - Ranbusia. The fish Is the too of the food chain. Using Isotoplcally labeled oesticldes (1 Ib/acre application rate), residues Mere determined for only selected organises (snail, mosquito, and fish) and Mater. ReoroduclblI 1ty appeared to be good. The authors state that the method gives a good estimation of the potential toxlclty of pesticides and their breakdown products to a variety of organisms and Is suitable for computer modeling. same as above Metcalf, et al (1971), 4MIC-K.95 Metcalf, et al (1971), AMIC-1U95 OOE IC-1* labelled) Physa spp X Ufed- (residue) ., standard same as above netcalti al et ------- Compound OOE (C-lf. labelled) OOE IC-1* labelled) OOE (C-lV labelled) OOE CC-1* labelled) OOE JC-1* labelled) OOE IC-1* labelled) Organism Daoftnla maqna Culex ololens qulnque- fasolatua Oedogonlum cardlacum Gambusla afflnls Diatoms (Kavlcula, Cosclnodla- CU3, Dlp- lonesa, and Olatoraella} Protozoa (Suclearla, Coleps, Vortlcella, and Paxamaeium) Field Field Study Location al »eoay- stea) L (Mod- el e co ays tern) L (Mod- el eeosy atea.) L — (Mod. el eeosy stem) L * * (Mod. el ecosy atom) 1 (Mod. el ecosy a tea) L (Mod- el ecoay stem) Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments reference Hater and sand 1 Ib per A a.ctq,sfan same as above (K-NTE) dard reference Hater and sand 169. 9 (residue) a,c,q< same as above standard reference Hater and sand 1 Ib per A a,c,g, sane as above (NTE) standard reference Hater and sand 19.8 a,c,q1 same as above (residue) standard reference Hater and sand 1 Ib per A a,c,9, same as above (NTE) standard reference Hater and sand 1 Ib per A a,c,q, sane as above (NTEI standard reference Hater and sand Reference (1971) ,«MIC- 195 "etcalf. et al (1<»71J, »NIC-li»95 Metcalt. et al (1971), AHIC-19S Hetcalt, et al (1971) , AMIC-195 Hetcalf, e» al (1971), HtC-l95 Metcalt, et al (1971), AMtC-ll.95 Me Teal f, et al (1971), AMtC-l95 ------- Dor IC-l labelled) Rotirera L (Aaplanchnop- (Hod. us, Kotomat- el t, Buclarla, ecosy Scardlum) stem) DOC IC-lfc labelled) Hater L (Hod. el •COSTS t«m) 1 Ib per A (NTEI 0.008 (rasldua) a,e,q« standard reference water and sand «»o.E» standard reference water and sand saae as above saae as above Mefcalf, et •I(1971), ANIC-H.95 Metcalf. et al (19711. oor to.o-i Anquitla FRl St. John, 0.5 {residue) rostrata N.B., Can. E DOC ID.P-I DOE lo.O-) oor lo.o-) DOE ID. 0-1 DOE lo.o-) not io.o-> OOE lo.o-l DOC lo.o-> Esox nlqer Sal»o salar Clupea harenqus Seonber scoabrus Mytl lus edulls Gadus "Orhua Urophycls tenuls Hlppo- glossoidea FRL FRL FRL FRL FRL FRL FRL FRL St. John, N.R. , Can. St. John, N.B., Can. St. John, N.B., Can. St. John, N.P., Can. St. John, N.R., Can. St. John, N.P. , Can. St. John, St. John, N.R., Can. 0.16 (residue) 0.22 (residue) 0.06-0.21. (residue) 0.07 (residue) 0.0?(resldue) 0.01 (residue) 0.02 (residue) 0.01 (residue) PCBs were found In hlqher concentrations than orqanoch)orine pesticides In all fish analyTrrt. Th authors point out that PCB Is less toxic In an acute sens* than organochlorlnes, that little Is Known of sublethal PCB effects, and that More Knoxtedqe of PCB distribution and effects Is needed. sane as above sane as above saae as above sane as above sane as above sane as above save as above sane as above Zltko(1971), AMIC-3715 7ltKo (1<»71> 371S ZltHo (1971) 3715 3Tltho(1971) 4MIC-371S 371S Dlatessoldes AMIC-3715 Zltko C1971). AMIC-3715 DOE lO.D-t Sebastodes FRL St. John, trace sane as above 71tko(1971), ------- > Coaoound ooe ooe ooe ooe ooe ooe ooe one one ooe ooe Organise aarlnus Carp Channe 1 catfish Radhors* sucker Gizzard shad Spotted sucker Blueqltls Redbreast sun fish Striped aullet Blue catfish Dock bass Freshwater drua Field Study FRL FRL FRL FRL FRL FRL FRL FRL FRL FRL FRL Toxlclty, experimental Active Variables. Field Inqradlent, Controlled Location Po« or Noted N.fl., Can. (residue) NIsc. states 0.03-2.93 — residue (SB) Misc. states 0.0<>-<>2.3 residue (SB) Hlsc. states 0.03-0.36 residue (SB) Hisc. states 0.27-1.5", residue (SB) Hlsc. states 0.29-0.1.5 residue (SB) Misc. states O.Dt-O.Bl residue (SB) Misc. states 0.02 residue ~ (SB) Misc. states O.OR-<,.55 residue (SB) Misc. states 1.87 residue (SB) Misc. states 0.08-0.60 — residua (SB) Misc. states 0.26 residua — (SB) Coaments saae as above saae as above saae as above saae as above saae as above saae as above saae as above siae as above saae as above saae as above saae as above Reference •HIC-3711 Henderson, et al 11,07 Henderson, et al (1971), »MIC-1<»07 Henderson, et al (1971), Henderson, et al (1971), • 1IC-11.07 Henderson, et al I19'l>, »MIC-1<»07 Henderson, MIC-1'»07 Henderson, et al (1971), Henderson, etal (1971), Henderson, et 3IC19M), «MIC-1<»07 Henderson, MIC-H.07 Henderson, et al 11971), AMIC-1407 ------- OOE OOF Bloater FRL Misc. states l.OT-3.52 residue CSB) lake FRL uniteIsh Misc. states 0.3* residue (SB) sane as above sane as above Henderson et aidant, »MIC-1<«07 Henderson, etal (1971), OOE lake trout FRL Misc. states 0.0-fl.98 • residue (SB) sane as above Henderson, (1171), K OOE ooe OOE OOF HMte crapple FRL Misc. states 0.03-9.23 residue (SB) Biqaoutn FRL buttalo Saatlnouth FRL buffalo Flath«ad FRL catfish Misc. states 0.19-0.62 residue (SB) Misc. states O.V6 residue (SB) Misc. states 0.82 residue (SB) sane as above sane as above saae as above same as above Henderson, et • I (19711, Henderson, et at Henderson, et al 11971). »Mic-i«.n7 Henderson, etal (1971). OOE Goldeye FRL Misc. states 0.03-0.29 residue (SB) same as above Henderson, et al tl<)71), »MIC-1<»07 DOE oor ooe Hal I eye Sauaer FRL Misc. states 0.05 residue (SB) FRL Misc. states 0.36 residue (SB) Flannelaouth FRL Misc. states 0.13 residue sucker (SB) sane as above same as above saee as above Henderson, et al 107 Henderson, et al (1971), 4MTC-H07 Henderson, et al (1971), AMIC-1487 ooe ooe • lack bullhead FRL Misc. states 0.03-0.0<> residue (SB) tthlta bass FRL Misc. states 0.13 residue (SB) saae as above sane as above Hendersor»»et al (1971), »MIC-107 Henderson, et al(1971), ------- Conoound OOE OOE OOE OOE OOE OOE OOE OOE DOE OOE OOE Orqanls Black crapple Larqescale sucker Saul mouth bass Northern squaii fish Chlselnouth Klanath sucker RalnboH trout Brldqellp sucker •rctlc qrayl Ing found •hltef Isn Lonqnose sucker Toxlelty, Experimental Active Variables. Field Field Ingredient, Controlled Study Location Ppa or Noted FRL HIsc. FRL Misc. FRL HIsc. FRL Misc. FRL HIsc. FRL HISC. FRL Misc. FRL MISC. FRL HIsc. FRL MISC. FRL HIsc. states 0.40-0.94 residue (SB) States 0.12-0.47 residue (SB) states 0.30-0.94 residue (SB) States 0.48-1.87 residue (SB) states 0.14-0.70 residue (SR) states 0.02 residue (SB) states 0.08-0. SO residue (SB) states 0.15 residue (SB) states 0.25 residue — (SB) states O.Z7 residue (SB) states 0.01-0.94 ~ resldue (SB) Comments saae as above saae as above saoe as above sane as above save as above sane as above saae as above saae as above sane as above saae as above saee as above Reference •MIC-1407 Henderson.et at (1971), MIC-I497 Henderson, et al (1971), •MIC-1407 Henderson, et al (l«7l). Henderson, et a) I197H, •NTC-1407 Henderson, etal Ctfl'l), •NIC-14D7 Henderson, etal (1971), •MIC-14B7 Henderson, et al (1971), •WIC-1497 Henderson, et al (1971), •MIC-1407 Henderson, etal (1071), •MIC-1407 Henderson, etal 11971), •MIC-1407 Hen Person, et al (14711, •HIC-1407 ------- OOE WMt« sucker FRL Misc. states 0.05-1..8? residue (SB) DOC Yellow perch FRL Misc. states 0.03-2.1.1 residue (SBI The Bureau of Sport Fisheries continued Its fish Monitoring orogra« by collecting 147 composite fish sanoles fro 50 nationwide monitoring stations durlnq the fall ot 1464. Fish were analyzed for residues of 11 orqanochlorlne Insecticides, llplds. and PCB-s. same as above Henderson. et al •1971). 1MIC-IV07 Henderson, etal (19T1), r Ml OOE OOE DOE OOE DOE OOE Chain pJeKerel FRL Misc. states 0.06 residue CSS) Mhlte catfish FRL Misc. states 0.38-0.86 residue (SB) Mhlte perch FRL disc, states 0.6«.-10.9 residue (SBI Goldfish FRL Misc. states 1.Z4 residue (SBI Puaptilnseed FRL Misc. states 0.33 residue ------- Compound Field Field Study location Toxlcity. Active Ingredient, Pom Experimental Variables, Controlled or Noted Comments Reference ODE DOE oor DOE ODE ODE ME Slat Is so. FS (larvae) Gawmarus so. FS Salvellnus FS fontlnallt Scootllus FS atromaeulatus Cottus bairdl FS Rhlnlchthys FS atratulus Enqraulls FH •ordax Knlqhts CreeK, Dun County, Wise. Knlqhts Creek, Oun County, Misc. Knlqhts Creeh , Dun County, Misc. Knlqhts Creek, Oun County, Misc. Knlqhts CroeK, County, MlfSC. Oun 0.005 (Hholebody residue) O.OKwhole bodyresldue) reaidua) 0.3-l.Mfat residue) 1.0Z-1.53(fat residue) 0.6-0.7 (fat residue) 0.011-0.075 pom and 0.003-0.006 ppm dleldrln were found In debris samples. nesoite limited control data, residue analyses Indicated that contamination of the environment studied xas limited. same as above same as above same as above Knlqhts 1.92(fat CreeK, Oun residue) County, Misc. Pacific 0.06-0.17(res Northwest Idue) Coast, Grays Harbor, Mash. same as above same as above same as above Houbry, et al Noubry, et a I (1468), Houbrvt et a I (1968), Houbrv, et al (1468), Houbry, et al (1«6«), Houbry, et at (1<>68>. AHIC-3753 Pesticides from the Columbia Stout River Into Puget Sound apparently 11968), contaminated fish const It ut inn commercial «NIC-378I> catches in Pacific Northwest waters. Residues In these marine products were substantially lower than the FDA tolerance for beef (7 pom). Fish from locations near the mouth of the Columbia River had higher pesticide content than ones caught farther away. ------- Hash. DOE our OOE ODE DOE ooe DOC ODE OOE Sohastodes FM f 1 av 1 -Jus Sehastodes FM ftavlfius Platlehthys FM stet latus Gadus FM •acroceohalus Cancer FH Cancer FM •aqlster Parophrys FM vetulus Herlucclus FM eroductus Herlucclus FM oroductus Paclf Ic Northwest Coast, Hecate Strait. B.C. Paclf Ic Northwest IlMaco,Wash. Pacific Northwest Coast, Rlalne, Hash. Pacific Northwest Coast, Blalne. Pacific Northwest Coast, destruction Island, Hash. Paelf Ic Northwest Coast, I)wacor Hash. Pacific Northwest Coast , Rlalne, Hash. Pacific Northwest Coast , Sarasota Passage. Hash. Pacific Northwest 0.07-0.08 (residue) (residue) O.OZ(resldue) 0.01 (residue) 0.039(resldue> 0.03-0.0e as above sane as above sane as above sane as above saae as above sane as above sane as above Stout Stout (198), Stout (1968). AMIC-3784 Stout (1968), AMIC-37BI. Stout (19681, Stout (1968) , Stout Stout (1968), «MIC-378 Stout (1968). ------- Compound ODE DOE DOE oor DOC DOC ODE Organism Her lucclus produc tus Her lucclus produc tus (f Ishmeal) Sebastodes alutus Carasslus auratus Trlturus erlstatus Rana temporarla Daphnia maqna (adult) Field Field Study Location Coast t Fort Susan, Wash. FH Pacific Northwest Coast, Caee Foul Heather, Ore. FN Pacific Northwest Coast, Aberdeen, Wash. FH Pacific Northwest Coast. Hecate Strait, B.C. L — L BCF — Toxlclty, Active Ingredient, Pon 0.07(resldue) O.Z7 (residue) 0.01 (residue) fc.7-8.2 (residue) O.Z3-0.fH (residue) 0.001-0.01 •icrogram (residue) l.S (residue) Experimental Variables, Control led or Noted Comments same as above sa.«e as above sane as above a* Goldfish were exposed to Increasing concentrations of DOT and residues determined after 21 days of exoosure* Host DOT ha1 been converted to ODE. Phenobarital had no significant effect on Insecticide residues. — DOT caused hyperact Ivlty In exoos'ed tadpoles. This caused Increased caoture lunges of newts thus Increasing the predatory efficiency of the newts. DDT had no apparent effect on the newts. ~ save as above a Magnification of DDT and Aldrln taqqed with C-l,100 depending on the species were Reference 4MIC-378I. Stout (19M). ANIC-37** Stout (19681, AHIC-378* Stout (196S), •MIC-378* Young, etal (19711 , AHIC-3796 Cooke (1971) , ANIC-381* Cooke (1971), AHIC-3SH Johnson, et al (1971), AMIC- 3830 found for DOT, and 22,800 to 1 ".1,000 for Aldrln. narked degradation of DDT as determined by analysis for DOT metabolites occurred. The authors ------- DOC Gaonarus faselatuv lalultl BCF — 0.* (residue) a* conclude that aquatic Invertebrates Influence quality and quantity of Insecticide residue passed via the fish food chain. saae as above Johns on v et at (1971). AKIC- 3830 DOE 09E Palaeaonetes BCF kadlakensis (adult) Hexaqenla bltineata (nyaph) BCF — 0.7 (residue) a* I.I. (residue) a> saae as above saea as above Johnson, et al (1971), Johnson, et al (19M) t § OOF ooe Isehnora vertically Inaiadt BCF ~ Llbetlula sp. BCF Inniadt 8.2 (residual a* O.OZ (residue) a* saae as above saae as above Jchnson, al 3820 Johnson, et al (19711, 4HIC-3?1) ooe ChlrononuS 8CF sp. I larval 0.1 (residue) »• saae as above Johnson, et al 38ZO ooe Daohnla vaqna BCF (adultt 0.0001 (SB3) a sane as above Johnson,et al (1971), ooe DOC ooe ooe Ganearus fasclatus (adult) BCF ~ Palaenonetes BCF kadlakensls (adult) Hexaqenla blllneata (nynoh) Ischnura vertical Is (naiad) BCF — BCF ~ 0.0001 ISB3) a» 0.0001 (SB3) a* 0.0001 (SB!) a* 0.0001 (SB3) a* saae as above saae as above saae as above saae as above Johnson,«t al (19711, a«IC-3S20 Johnson,«t al (1971), AHIC-3820 Johnson,et al (1971), 4MIC-3823 Johnson, «t al (1971), »MIC-38?0 ------- Compound OOF DOE ODE Organise Llbellula sp. (naiad) Chlronomus sp. (larva) Hlcropterus Field Fl«ld Study Location 8CF BCF — FL Clear Lake, Toxlclty, Active Inqredlent. PD« 0.0001 (SB3) 0.0001 (SS3) 0.3-9 (flesh Experimental Variables. Control 1 ed or Noted a» a* — Comments Peference sane as above Johnson, et al (1971), ANIC-3820 same as above Johnson, et al (1071), AMIC-382D Residue analysis results mainly Linn, et OJ o ODE Mlcropterus FL sal no Ides Clear Lake, Cal. 82 Itat residue) tor TDF In fish, birds, and olanhfon fron AL(1969), 19S9 throuqh 1965 Here reoorted. The AHIC-5521 residues urlmarlly resulted Iron aoollcatlon of DOT to Tarmland and Tor gnat control* In some cases* data for a slnqle animal in one year- xore qlvcn. Primary emphasis was on larqemouth bass and Hhlte catfish. Th«. general level of TOE contamination In birds and fish declined markedly from 195ft to 196S. This decline c-prrelated directly with strict limitation by Demits of DOT apollcatlons durlnq the latter years. same as above Linn, et al (19691 .AMIC- DOE OOE OOE DOE Aechmophorus FL occidental Is Larus sop. FL Larus FL del attar ensls Perca FLR llavescens Clear Lake, Cal. Clear Lake, Cal. Clear Lake, Cal. 93 samolIng stations In Mass. 33-3,360 (tat residue) 300-<»OZ (residue) 9?-2700 (fat residue) 0.35-3.6 (residue) same as above same as above same as above Fish Indiqenous to Massachusetts freshwater streams Here analyzed for DOT and DOT metabolites durinq 196S-1967. Generally there Mas an Increase in pesticide content during the three year period. Linn, et AL(l<"i9>, AMIC-55?! Linn, et at 11969), AMIC-55?! Linn, et al (1969),A1IC- 5521 Lyman, et (1968), AMIC-3S39 al ------- r H U) ODE DOE OOF DOC one DOE Ltoomls qlbhosus Catostomu* eownersonl Ictalurus nebulosus Cyprlnus carplo ESOK nlqer FLR FLR FLR FLR FLR Notnlqonus FLR ervsolvueas 93 sanpl 109 stations In Mass. 43 sanollng stations In Mass. 93 sane) Ing stations In Mass. 93 sanding stations In Mass. 93 saniDl Ing stations In Mass. 93 sa»Dl Inq stations In 0.16-3.9 fresldue) (residue) D.9 (residue) 1.6-U.8 (residue) o.g ------- Compound ro DOE DOC DOE OOf 00r OOE OOC OOF Organism Notrools cor nut us POCCUS amerlcanus Pomoxls nl£po~ •teulatus Fundulus dlaphanu Notropls ana tost anus Leoomls aur Jtus Phlnlebthys atratulus Cvprlnu carple Field Study FLR FL* FLR FLR FLR FLR FLR FR Field Location 93 sampling stations In Mass. 93 sampling stations In Mass. 93 sampling stations In Mass. 93 sampling stations In Mass. 4J sampling stations In Mass. 93 sampling stations In Nass. 93 sampling stations In Pass. St. Laurence Plver, Toxlclty, Active Ingredient, Pom 0.50-2.6 (residua) tt.3k-l.it (residue) 1.9* (residue) 2.35 (residue) 0.53 (residue) O.it6 (residue) 0.8-0.50 (residue) 0.36(0.32 ppm max tissue Experimental Variables, Controlled or Noted Comments — same as above same as above ™ same as above ~ same as above same as above same as above same as above -- Residues of DDO Mere measured Hater, mud, me II uses, and fish during Reference lyman, et al (1468), AMlC-^839 Lynan, et al (146), AMTC-3839 Lyman, et al (1958). AHIC-383<» UVSP, »t at (J968), AMIC-3S39 Lyman, et al (19&8), AHIC-3839 Ly«an,et al (1968) , AHIC-S839 Cyan, et al (14<>«), ' AMIC-3839 In Fredeen, et and al (1470) , Montreal, residue) Canada after 000 application In 1967. Sampling ANIC-53fe points »<>re above the oolnt of application and 10 and <»S mi doMnstream. Resllues from unKnoHn sources Here detected uostrean. Downstream residues Here more than tMice those obtained upstream (0.156 versus 0.369 ppm). The highest concentration In an Individual fish was 1.81 ppm. oor ooc Amelurus nebulosuv P«rca flavescens FR FR St. Lawrence 0.38(0.12 ppa Plver, max tissue Montreal, residue) Canada St. Lawance 0.38 (O.Olppm River, max tissue Montreal, residue) Canada same as above saae as above Fredeen, et al (1470). ANIC-53i» Fredeen, et al (1970), •NIC-53* ------- DOE DOE OOE ooe OOf Esox luclus FR tebloollte* rupestrl* FR PlsMlum sp. FR Caeoeloma sp. FR Catostomus Connerson I FR h to DOT (C-l* labelled) Oaphnla maqna BCF (adult I St. Lawrence 0.38 (0.<»3 River. ppmmax tissue Montreal, residue) Canada St. Laurence 8.310.05 ope River, max tissue Montreal, residue) Canada St. Laxrence 0.38 (0.0>iDDa River, max tissue Montreal, resldu) Canada St. Lanrenee 0.38 <0.09pom River, «ax tissue Montreal, residue) Canada St. Laxrence 0.38(0.3? op River, eax tissue Montreal, residue) Canada —• 6.7-9.2 (residue) DOT (C-lt labelled! Culex plotens RCF — (larva) DOT tC-lt labelled) Daphnla oaqna BCF — (adultl 13.9 (residue) a* 0.0001 (SB3) a* same as above saae as above saxe as above same as above same as above Maqnlf(cation of DOT and Aldrln taqqed xlth C-IU occurred rapidly. Bloloqlcal magnification factors of ?900 to 1ft, 100 dependlnq on the species nere found tor DOT, and ?Z,ftOO to 11.1,000 for Aldrln. Marked deqradatlon of DOT as determined by analysis for DDT metabolites occurred. The authors conclude that aquatic invertebrates Influence quality and quantity of Insecticide residue passed via the fish food chain. same as above Fredeen, ef al (1970). Fredeen, et al Fredeen, ef al (1970), Fredeen, et al (1970), Fredeen, ei al (1970),^TC- 53", Johnson, er al (1971), «HIC-38?0 seme as above Johnson,«t al (1471), 4HTC-38ZO Johnson,t al (1971), DOT (C-lt labelled) Cammarus BCF — tasclatus (adult) DOT (C-l labelled) nrconeetes BCF — nals (adult) 0.0001 (SH3) a* 0.0001 (SB3) a* same as above same as above Johnson,t al (1971), 4HTC-JS20 Johnson,et al (1971), Amc-3820 DOT (C-1V labelled) P«l»e«onetes BCF kadlakensls (alult) DOT «C-1 label led! Hexaqenla RCF blllneata 0.0001 (SB3) a* O.OOOKSB3) a* saae as above saaa as above Johnson, et al (1971), AHT.C-3B20 Johnson,et al (1971). ------- Compound DOT (C-l* label ledl DOT (C-m labelled) DOT (C-l«. labelled! DOT (C-l* labelled) DOT (C-l* labelled) DOT (C-l* labelled) DOT (C-l* labelled) DOT (C-l* labelled) Field Field Oraanlsm Study Location (nynoh) Slphlonurus BCF sp (nymph) Ischnura BCF — vert leal Is Inalad) LI Del tula sp. BCF — (naiad) Chlronotus BCF — sp. (larva) Cut ex Plolens BCF (larva) Gavmarus BCF ~ faselatus (adult) Orconectes BCF — nals (adult) Pala««on«tes BCF — kadlakensls (adult) Toxlclty, Active Inqredtent, Pp. 0.0001 ISB3) O.OOOKSB3) 0.0001 (SB3) 0.0001 (SB3) 0.0001 (SB3) 1.3-1.7 (residue) O.Z (residue) 0.3-0.5 (residue) Exo«rt««ntal Variables. Controlled or Noted Comments a* same as above a* sane as above a* same as above a* same as above a* same as above a* same as above a* same as above a* same as above Reference AMTC-382H Johnson, et al (1971), ANrC-3»»0 Johnson, et al 11971), AMIC-7S70 Johnson, et al (1971), HIC-3«?0 Johnson, et al 11971), »MIC-»21 Johnson, et al (1971), »MIC-3»?0 Johnson, et al (1971), HIC-X8'9 Johnson, t al (1971), NIC-3B?0 Johnson, et al (1971), 4HIC-38ZO ------- DOT IC-1% labelled) Hexagenla BCF -- blllneata (nymoh) DOT IC-1» labelled) Slphlonurus BCF — sp. (nvmoM DOT (C-l» labelled) Ischnura BCF — vertical Is (naiad) DOT IC-lt labelled) Libel lula sp. BCF 0.3-1.7 (residue) 1.1 (residue) 0.2-0.1. (residue) O.OU-0.1 (residue) save as above sae as above same as above same as above Johnson, et at (19711, »MIC-3»?0 Johnson, et al (107U, Johnson, et al (1971), Johnson, et al (1971), DOT (C-t* labelled) Chlronomus sp. (larva) DOT IC-lt labelled) Estl ------- ON Compound DOT IC-1* labelled) DOT IC-1* labelled) DDT IC-1* labelled) DOT IC-1* labelled) DOT IC-1* labelled) DDT IC-1* labelled) DOT IC-1* labelled) DOT IC-1* labelled) Orqanlsa Protozoa (Huclearla, Coleps, Vortieella, and Paramecium) Rotifers (Aaplanchnop- ua, Notomat- ta, Euclarls, Scardlum) Hater Physa spp Oaphnla naqna Culex plplens quinque- faseiatua Oedogonlue cardlecue Ca.busla •ffinls Field Field Study Location I. (Mod- el a co ay stem) T. « (Hod- el a COST a tan) L (Mod- el ecoar •tea) L (Mod- al •COST •tern) L — (Mod- el ecogr stem) I* •— (Mod. el ecosys teal) L "" (Mod- el •tea? I ~ (Mod- el •OOST •teal) Toxlcity. Active Inqredienf , Ppi» 1 tb per A (NTE) 1 Ib per A (NTE) 0.00 (residue) ?e.9 (residue) 1 Ib per A IK-NTCI 8.9(resldue) 1 Ib per A (NTE) 5. 2 (residue) Experimental Variables. Control led or Noted com«ent a.c.q, same as above standard reference Hater and sand a.c.q, sane as above standard reference Mater and sand »,c,g, sane as above standard reference water and sand a.c.q, sa»e as above standard reference Hater and sand a,c,q, sane as above standard reference Hater and sand a,c,q, save as above standard reference Mater and sand a.c.q. sea* as "above standard reference Mater and sand a.c.q. see* es above standard reference Mater end •end Reference Hetcalf, et al (1971). AMIC-1'»9'; Metcalf, et 81(1971), AMIC-l"»9S Metcatf, et al (1971). AIIC-1't'W Metcalf. et al (1971) , AMIC-U95 Metcalf, et al (19711. AMIC-l^ Hetcalf, et al (197H, ANIC-195 Hetcalf. et 81(1971), ANIC-l'.OT Hetcalf. et el (1971). •mc-i«/s ------- DOT IC-l«t labelled) DOT JC-1 labelled! (ItavlcuLa, (Mod- Coaclnodla- al cua, Dip- ecosy lonaaa, and at«m) Olatoaalla) S»lweI Inus fontinlls BCFCM — H U) ODT labelled) DOT to,o-» lInus fontlnal Is Rasbora heteromorpha BCFCH — BCFA and BSt DOT (olus DOT analogs) LlmnephlI us rhombleus I larvae) FS 1 Ib per (NTE) 0.000003 (0.0?56ppm accumulation 120 d) a,e.g. standard reference water and sand sane as above Metcalf, et al (1971), »HIC-1«.95 0.0US mg par Kg a (1.92PPM accumulation 120 d) This study was an attempt to evaluate, under laboratory conditions, the relative Importance of food and water as sources of DDT for fish and to relate these observations to natural environments. To simulate conditions in Lake Michigan, fish were exposed to water containing 3 ctus or minus 0.3 pot ODT, and others were fed 3 plus or minus 0.15 ppm DOT (0.01»<< mg/Hq/day) for 120 days. Whole hody accumulations were determined throughout the test by measuring C-l* radioactivity in fish. The re-suits show that fish accumulated 3.5 percent of the DOT available in the water and 35.5 percent of that available in food. It is concluded that the food chain Is the major source of ODT in fish. same as above Hacek, et al (1970), et al AMIC-8i.li 0.03 (Tl) Knights Creek• Dun County,Wise. 0.02". (whole body residue) a»,c,e,f. One hundred sixty-four Alabaster hard (HH) pesticides, wettlnq grns» and (1969), or miscellaneous water pollutants shoxed a AMIC-5U25 SOTTISH) wide range of toxlcity sosnninq 1? orders synthetic of magnitude. Knowing the toxiclty and dilution percentaoe of all co-noonents of a water, or formulation did not result in easy seawater predictability of the toxiclty of a for some mixture of materials. Sometimes species pesticides were most toxic in hard water and soiretimes the opposite was true. Testing the actual material as sold was found to be essential. Samoles of water, silt, bottom Houbry, et debris, bottom organisms, and fish were al (19681, taken In 19fi6 from a creek adjacent to an »»IC-3753 orchard which had been treated in 1963-1965 with various chlorinated hydrocarbon pesticides. No resloues were ------- Comoound Organism Field Field Study Location Toxlclty, Active Ingredient, Experimental Variable. Control led or Noted Comments Reference DOT (otus DOT analogs) DOT (olu« DOT analogs) DOT (olus DOT analogs) DOT (otus DOT analogs) ODT (olus DOT analogs) DOT (olus DOT analogs) DOT (olus 01T analogs) DOT (olus DOT analogs) DOT (olus DOT analogs! Stalls sp. FS (Iftrvae) Canoarus SO SalvelInus fontlnalls FS Senotllus FS atromarulatus Cottus balrdl FS Phlnlchthys FS atratulus Salvellnus FS fontinalIs Semotllus FS atromaculatus Cottus balrdl FS Knlqhts CreeKt Dun County, Misc. Knlqhts Creek. Dun County, Wise. Knlqhts CreeK. Dun County,Misc. Knlqhts CreeK, Oun County,Wise. Knlqhts Creek, OunCounty, Hlsc. Knlqhts CreeK, Oun County,Hlsc. Knlqhts CreeK, Oun County,Wise. Knights CreeK, Oun County,Hlsc. Knlqhts CreeK, 0.016 (whole body residue) 0.001-0.013 (whole body residue) 0.01.2-0.155 (Hhol« body residue) 0.061-0.076 (whole body residue) 0.03«), amc-3753 Moubry, et al (146ft) , AMIC-3753 Moubry, et a I (14681. »HIC-3753 Mouhry,et a) (196S) , 4MIC-3753 Noufry, rt al (19681, &MIC-3753 Noubry. et al (1968), 4HIC-3753 Houbry, et al (11681, Moubry, et al (1968), 4MIC-37S3 MouS>ry, et al (1968), ------- DOT to I us DOT analogs) Phlnichthys atratulus DOT fplus 20 percent Rasbora non-l»nlc heteromorpha ••ulslfler, 60 percent naphtha) FS BCFA and 8S» DunCounty, wise. Knights ?.» (fat Creek, Oun residue) County,Misc. 0.11 CT2) AMIC-3753 r \o 09T (olus ?Q percent Rasbora non-Ionic hetero«oroha eeulsitler, 60 percent naphtha. In acetonel BCFA and USA 0.02 (T2) a«,c,e,f, hard (KW) or soft ISW) syn- thattc dilution water, or aeawater for some spedes hard (HW) or soft ISW) syn- thetic water, or aeawater for some species seme as above vi et a I (19&»), One hundred sixty-four pesticides, wetting agents, and miscellaneous water oollutants showed a Hide range of toxiclty scanning 1? orders of magnitude. Knowing the toxiclty and percentage of all components of a formulation did not result in easy predictability of the toxlcity of a mixture of materials. Sometimes pesticides were most toxic In hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. same as above Alabaster (19f-9>, Alabaster (1964), DOT lotus ?•> percent Rasbora agents) heteromorpha BCFA and USA 10.7 (Tl) DDT fplus 3 percent eaulslfler, « percent naphtha) Vasbora heteromorpha BCFA and BSA 0.11 CT3) a,c,e,f , hard (HW) or soft synthetic dilution water, or seawater for some species a,c,e,f , hard (HH> or soft (SKI synthetic dilution water, or seawater ------- Toxiclty. Active Field Field Ingredient, Comoound Organism Study Location Ppm OOT (Dlus 77 percent fiasbora 8CFA — 8.0 CT3) China clay, f hetero»orpha andBS percent calcium A sul fate) OOT (olus 77 oercent Pasbora BCFA — 0.001 or soft ISH) synthetic dilution Hater, or seawater torsome species Httc,o,r, same as above bard (ITW) or »of t (SO ayn- thetlc water, or aeawater for sone •pecles a'.c.e.f.K Rloassays conducted .l.n.and simultaneously Indicated Trot DDT Has magnesium, considerably more toxic to fathead sul fates, minnows under static conditions than Iron. under continuous flow conditions. calcium Decreasing oxygen and increasing Reference Alabaster (1969). SMIC-SUZS Alabaster C1969). AMIC-^fcZS llneer. e al (1970) AMIC-5S09 OOT <»,o~-> Plm«onales proaelas (3 ca) 8CF» — greater than 0.0V (tit a»,c,.f.h .l.n.and maqneslu, sul fates. Iron. metabolites may have enhanced DDT toxiclty. An Identical study with Endrin resulted In only sliqhtly higher toxiclty under continuous flow conditions. Average pH, oxygen, and ammonia nitrogen nere foltoued throughout the experiments. The results xere comprehensively discussed taking into consideration many contributing factors. same as above Llneer, et al (1970), AMIC-5509 ------- calclu* DOT le.e-t tnqullla r«»trat» FRL St. John, M.B., Can. 0.29 (residue) — f DOT lo.o-» DOT DOT IO,o"l DOT Co.D~> FSOK nlqer FRL St. John, N.n., Can. Saleo salar FRL St. John, H.R., Can. 0.08 (residue) — O.oa (residue) — Cluoea harenqus Scoaber seonbrus FRL FRL St. John, M • n • f C 8H • St. John, N.R., Can. 0.05-0.15 (residue) 0.07 (residue) — ftasbora BCF* ~ heteroaorpha and BS* 0.013 (Tl) av,c,e,f, hard (HH) or SOFT(SW) synthetic dilution •ater, or seawater for son* soeeles DOT (0,0", C-t* labelled) Gamhusla afllnls • ^^ o.oooo<»i(SBZ) q) PCR"s »r« found In h'lqher concentrations than orqanochlorlne oestlcldvs In all fish analyzed. The authors point out that PCP Is less toxic In an acute sense than orqanochlorlnes, that tittle Is known of sublethat PCS effects, and that wore knowledge of PC8 distribution and effects Is needed. sane as above sane as above sane as above sane as above •NIC-3715 ?ltko 3715 Zltko 3715 One hundred sixty-four pesticides, netting agents, and •iseellaneous water oollutants showed a wide ranqe of toxlclty sonnlnq 12 orders of •aanltude. Knowinq the toxlclty and percentage of all coiioonents of a formulation did not result In easy predictability of the toxlcity of a •Ixture of materials. Sometimes pesticides were most toxic In hard water and soiretloes the opposite was true. Testlnq the actual material as Sold was found to be essential. DOT-reslstant mosauitofisn were collected fro* a cond at Salinas, California. Smaller fish (100 •, AMIC-371S Alabaster Murohy (197H, AHIC-180S ------- "i Plus 20 Rasbors BCFA — percent o,o~ODT» hetvrooorpha and BSA DOT lo,o~, plus 20 Salmo trutta BCFA — percent o,o"OOT» (alevln) and BSA DOT (o,o~, olus 28 Rasbora BCFA ~ pereent o>p*OOT) heteroaorpna and BSA o.aoon«.i(o.oi-o a .Ob po" Hhole body residue 2 dl 0.0031 a,c««.t. (T2,herd«ater) hard (HH) or soft (SH) «yntnetlc dilution water, or seattater tor so»e soecles 0.0005<» •>,€,«, f, (TZ,soTt«at«r) hard (HW) or soft UW) syn- thetic water, or •eavater for some •peel e a 0.0035 (T2) a>,e,e.t. hard (HH) or sott (SWI synthetic dilution Hater, or seaiiater tor some species 0.017 IT?) a,c,e,f. hard (HH) or sott CSHI sane as above One hundred sixty-tour pesticides? wettlnq sqenls, and miscellaneous vater pollutants showed a nidi" ranqr ot toxielty soannino 17 orders of naqnlturte. Knoxlnq the toxlcity and percentage of all conoonenfs of a formulation did not result in easy predictability of the toxlcity of a mixture of natvrials. Sometimes pesticides Mere most toxic In hard Hater and sometimes the ooooslte MBS tru. Testlno the actual material as sold Mas found to be essontl'al. sane as above same as above same as above Reference Murohy (1971). AMIC-1005 Alabaster (1969), AMIC-5^25 Alabaster (1969). ANIC-^25 Alabaster (1969) . AMIC-SU21; Alabaster (I960) , AHIC-5<>25 ------- DOT DOT (18 percent) heteromorpha BCFA — and BSA 0.17 (T2> VjJ DOT OUT Fish (not specif Ie-1) Unite sucker FRL greater than 0.0001-0.001 (Kl disc, states 0.09-2.90 residue I SB) synthetic dilution water, or seaMater tor some species a>,c,e. f. hard (HU) or soft (SH) synthetic dilution xater, or seaxafer tor some soecles % a'.c.e.t• hard (HH> orsolt (SKI synthetic dilution water, or seaiiater Tor some species sane as above Alabaster (1969), saae as above Alabaster (196r AMIC-1056 Henderson,et a I (1971), AHIC-H07 DOT Redhorse sucher FRL Misc. States t.02-0.25 residue (SB) sane as above Hendprson,et al DOT Gizzard shad FRL Misc. states 0.13-0.IS residue (SB) same as above Henderscn, etsl (1971), DOT Spotted sucker FRL Misc. states 0.1<» residue (SB) same as above Henderson, etal (1171), AHIC-1I.(I7 ------- 1 Coaoound DOT DOT DOT DOT DOT DOT DOT DOT DOT DOT DOT Organise Striped aullet Blue catfish Pock bass Freshwater drua Bloater Lake Mhlfeflsh Lake trout Mhlte craeola flleaouth buffalo Saaltaouth buffalo Flatneatf catfish Field Study FRL FRL FP.L FRL FRL FRl FRL FRL FRL FRL FRL Field Location Misc. Misc. Hlsc. MISC. MISC. HlSC. MISC. MISC. MISC. HiSC. Misc. states states states states states states states states states states states Toxlclty, CxDeriaental Active Variables, Ingredient, Controlled Poa or Noted 0.30-1.12 residue (SB) O.Ot residue (SB) 0.06-0.«>9 ~ resldue (SB) 0.31 residue — (SBI 0.59-1. 80 — residue (SB) 0.20 residue — (SB) 0.01-O.VS — residue (SB) t. 04-0. 20 — residue (SB) n. 11-0. si residue (SB) 0.50 residue (SB) 0.6 residue — (SB) saae as saaa as saae as saae as saae as saae as saae as saaa as saae as saae as saae as Coaaents above above above above above above above above above above above Peference Henierson,et al (197t>, Hen-Jerson, etal (1971), «MIC-t«t57 etal U97t), etal (19711, t al (jo'l), 4MIC-1I.07 etal (197H, Henderson, etal 119711, at (19711, Henderson, et at (l«7l>. at (19711, •HIC-11.07 Henderson, et al (1471). AHIC-1407 ------- DOT Co Move F»L Misc. 0.0?-0.3<. residua (SB) sane as abov Henderson, t s Ml 971), ANIC-11.07 ODT Hal I eye FRL Misc. states O.Od-O.ZO residue (SB) sane as above Henderson, t al (1971). AM.IC-1«.07 DOT Sauqcr FRL Misc. states 0.18 residue (S3) sane as above Henderson,et 31(1971), AMIC-t<.07 DOT Flannelnouth FRL . sucker Misc. states 0.19 residue (SB) sane as above Henderson,et 81 (1171), AMIC-H.07 \n DOT DOT OUT Black FRL bullhead Misc. states Mhl-te bass FRL Misc. states Black crDDle FRL Misc. states 0.01-0.03 residue (SB) O.?l residue (SRI 0.22-0.25 residue (SB) sane as above same as above sane as above Henderson, et al (1971), Henderson, et al (l«'l), AMIC-IU07 Henderson, et al (1971), AMTC-li.97 DOT Larqescale FRL sucker Misc. states 0.05-0.45 residue (SB) sane as above Henderson,et al (1971), AN!C-1<.07 DOT •>nallnouth FRL bass Misc.' states residue (SB) sae as above Henderson»«t al (1971), ANIC-11.07 ODT Northern FRL SduaNtIsh Misc. states fl.05-0.10 residue ISB) sane as above Henderson,et al (1971), AMIC-1<»07 DOT Chlselnouth FRL Misc. states 0.07-0.09 residue ISB) sane as above Henderson, etal (1971), AMIC-H07 DOT Klanath sucker FRL Misc. states 0.02 residue (SB) sane as above Henderson, etal (19711, AMIC-ldO? DOT Rainbow trout FRL Misc. states 0.03-0.07 residue (SB) sane as above Henderson,et al (1971), AHIC-H07 ------- CoBoound DOT DOT DOT f* DOT H DOT DOT DOT DOT DOT DOT DOT Field Orqanls* Study Brldq-llp FRL sucker •re tic FRL grayllnq Pound FRL whltef ish Longnose FRL sucker Vel low perch FRL Chain FRL olckerel HMte catfish FRL White perch FRL Goldfish FRL Blueqllls FRL Redbreast FRL sunf Ish Toxiclty, Exoerl mental Active Variables, Field Ingredient, Controlled Location Ppm or Noted Misc. states 0.39 residue — (SB) Misc. states 0.21 residue ~ (SB) Misc. states 0.31. residue (SB) Misc. states 0.01-0.10 residue (SB) Misc. states 0.03-2.56 residua (SB) Misc. states 0.08 residue — (SB) Misc. states 0.21-0.31 residue (SB) Misc. states 0.63-1.30 residue (SB) Misc. states 0.65 residue (SB) Misc. states 0.0<»-0.2<» — residue (SB) Misc. states 0.03 residue — — (SB) Comments sane as above same as above same as above same as above saee as above same as above same as above same as above same as above same as above sane as above Reference Henderson, etal (1971), AHic-i'.n'' Henderson, etal (1971), SHIC-li.07 Henderson, etal 119711, Henrterson.et al (1071), AMIC-K.07 Henderson, et al (1971), Henderson, et al (1971), SMIC-11.C7 Henderson, et al C197D, AMIC-1J.07 Henderson, et al (19711, Henderson, et al 107 Henderson, etal (1971), AMIC-11.07 Henderson, et al (1971), ------- DOT DOT DOT DOT DOT DOT DOT DOT DOT Pumofclnseed FRL Largemouth FRL bass Broun FRL bullhead Carp Channel catfish FRL F«L Gambusla 85 •ftints Misc. states 0.23 rasldue (SB) Misc. states O.OS-1.57 residue (SB) Misc. states 0.06-0.1.2 residue ISB) Misc. states 0.01-0.96 residue (SB) Misc. states O.OZ-5.07 residue (SB) 0.0* pob (SB) Wolffla papullfera Salve IInus tontlnalls (1.15 q> BCF« — 100 (K) 7.1, SalvelInus tontlnalls BCF» — 11.9 (Tit) Hunter's medium dllutod 1:5 ae, C,d, e,f,l,O, aulfato, copper, Iron, and Chronlua a,c,d, e.f.l.o, sulfato, copper, saute as above sane as above sane as above same as above same as above Henderson, et al (19?!) > AMTC-K.H7 Henderson, et al (1071), Henderson, «t at (1<»M>, A--hr Murohy period at ?(l C thin at •» r. yt was shown [1971>,AwiC- that only live fish take UP nOT, that 178 uptake was related to resoiration rate and that small fish are more efficient than larger fish In removing PflT from water. One Implication of this study is that at warmer Temperatures HOT is taken up more rapidly, thus suggesting that thermal releases be carefully controlled. All compounds ware harmful to Worthley, et duckweed to aons degree. Decreased al (1971), populations wore iiotoU at non-lethal AMIC-3233 concentrations and some compounds (Malathion and e,l\.-D) caused terstogenle effects at concentrations as low as 1 ppm. Four Insecticides were evaluated Post, etal on four fish species at two body weights. (1971), Standard method bloassay orocedures were AH.IC-181? followed. Symotomology was also reoorted. Generally, toxlclty was significantly different at the two body weights, i.e., more toxic at trie lower body weight, except for Malathion. well-defined experimental conditions were said to result In truer measurement of toxlclty. sa«e as above Post, et al (1971), AMIC-181Z Iron, and cltro.-nlum ------- Coeaound Field Fl«ld Orqanlsa Study Location Toxlclty, Active Ingredient, Pp» Experimental Variables. Controlled or Noted Convents Reference DOT Salvo ctarkl (0.33 0) BCF» ~ B.0001 IT4) DOT Salvo elarkl BCFA 11.29 q) 1.37 (TO DOT Sal mo qalrdnerl 10.1 ql RCF» 0.0092 IT4I e,r,l,o, aulfate, copper, manganeae, Iron, and Chromium sane as above Post, et al (19M), 8,f,l,0, copper, Iron, and eiiromluai •0,0, d, •ff.l.O. aulfata, copper, Iron, and chromium saae as above saoe as above Post, et al (1971), •HIC-1S12 Post, et al (19711, AMIC-1812 DOT DOT ftOT Oncorhynchus kisutch 18.5 9> Oncorhynchus kisutch (1.65 9> BCFA — 0.011 (TO a,. save as above BCFA — 0.019 Artela spp. L ~ 0.00001 and 0.000001 (sublethall eopper, manganese, iron, and chromium a«.e.d, »»f,ifO« sulfate, copper, nangenase, iron, and chromium saae as above Arteaia sop oooulations exposed in 19R6 to the indicated DOT concentratlons and studied for up to ------- DOT Sebastodes sp. FO nor DOT DOT DOT DOT DOT DOT DOT DOT DOT PanufIrua Interruotus Paralabrax nebulIfer Anlsofreals davidsonl FO FO FO PlaelOMtapon FO putenruv Haliofls rufeseens FO Strongylocent FO rotus franclseanus Hlnnltes FO •uitlruqosls Haliotls corrugate Kellctla fcelletll FO FO Plants fulgae F and hlahvr aouatlc Pacific Ocean, Cal. 0.1.6 (liver residue) bacKqround. Brine shrlno nauolll were apparently most sensitive to DOT conoared to older stages. Cyclic coexistence of pesticide residue and vulnerable stage of life cycle Influenced succeeding generations. Samples of marine animals Here Hunson collected fro three locations off the (1972). coast of Southern California and analyzed AMIC-3096 for residues of chlorinated hydrocarbons. The data suggest that Kellet~s nhelk nould be a good Indicator organise for studying the regional distribution of chlorinated hydrocarbons. Pacific 0.037 (nusde Ocean, cat. residue) Pacific Ocean, Cal. Pad f le Ocean, Cat. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. 0.71 (I iverresldue) 0.%(liver residua) 8.21 (liver residue) less than 0.1 (liver residue) 0.07-0.073 (gonad residua) 0.032 (gonad residue) 0.0<«Z (digestive gland residue) 0.077 (residue) saae as above save as above save as above sane as above saae as above save as above sane as above sane as above save as above Hunson Munson(ig73). Munsontl97j), 4NIC-3096 Hunson (l^Z), »MIC-3fl<)6 Hunson (197Z), ANIC-304B Munson (1972), »MIC-J09% Munson (1972I, AHIC-309S Hunson (1<»7?I. 3096 Various 0.01 to 0.7<» oonds and (residue) streaasln Plant, Invertebrate, fish, and Dlaond, •ud samples were pooled, homogenized, and al analyzed for DOT. Birds Here analyzed AMIC-3291 ------- Compound Field Field Organism Study Location Toxlcity, Active Ingredient, Ppm Experimental Variables. Control led or Noted Comments Reference plants) Maine DOT DOT DDT DOT DOT Invertebrates F (Cimbarus bar ton I, freshwater mussel'., and s»al ler anlf»at«t Fish F (Satvnl tnus font Inalls and Sevotl lus atromaculatus prtmarl ly) Birds F (H«aac»ryle alcyon, Mernus merganser. and Lophortytes cucul latus) Muds F Llmneohllus FS rhonblcus (larvae) Various ponds and streams In Maine Various ponds and streams In Maine Variousoonds and streams In Maine Various ponds and streams In Maine Knights Creefc , Dun County, Wise. 0.03 to Z. (residue) 0.21 to 9. (residue) «.Z to 10. (residue) 0.03 to 0. (residue) O.OKxhole residue) ti »i> 1 83 body Individually. The data represent the range of DOT concentration over a 10-year oerlod after one aoolIcatIon. Highest concentrations were found immediately after and 1 yr after anollcatlon with considerably less txo years and after. However, the residues even after 10 years •ere still Hell above those in brooks never treated This study further demonstrated the persistence of DOT in the environment and Its tendency to spread and concentrate In food chains. sane as above same as above same as above same as above Olmond, t Olmondt et al (1971), •MIC-3Z91 al ondf et (1971), Dlmond, et al (19M>, AMIC-3291 Samples of Mater, silt, bottom Mpubry, et debris, bottom organisms, and fish Here al (1965), taken In 1966 from a creek adjacent to an &MIC-J7SJ orchard which had been treated In ------- r H DOT DOT DOT DOT DOT DOT DOT Stalls so. FS Ilarva) Gammarus so. FS Salvelinus FS fontlnalis Semotllus FS atronaculatus Cettus balrdl FS Rhlnlchthys FS atratulus Sal welinos L fontlnal Is 119.2 c«) Knlqhts CreeH, nun County, Misc. Knlqhts Creek, Dun County, HIsc. Knlqnts Creek, Dun County, Misc. Knlqhts Creek, Oun Countyt Misc. Knlqhts Creekt Oun County, Misc. Knlqhts Creek, Oun County, Misc. 0.01 (Hhole body (residue) 0.03(Hhole body residue) 0. «.-!.* Ifat residue) 0.1-0.6(tat residue) 0.5-1.5 (fat residue) 0.10 (tat residue) 0.1-0.3 (SB1) 193-1965 Hlth various chlorinated hydrocarbon pesticides. No residues Here found in water samples. Silt sanoles contained 0.002-0.013 DDK vndrln and 0-0.On; pom dleldrln. Endrin residues of 0.011-0.025 DP and 0.002-0.006 DO* dleldrln Mere found In debris samples. Oesolte llnlted control data, residue analyses Indicated that contamination of the environment studied Has Halted. saae as above saae as above sane as above sane as above sane as above saae as above Moubry, et al (1Q68), •1IC-3753 Houbry, et a I (t«6>, AMIC-3753 Moubry, et at (1968). tloubry, et al (196S). Moubry, et al (1961), 4MIC-375X Moubry, et al (I'?.). AMIC-3753 Neurophyslologlcal function of brook trout Has affected by ?<»-hr exposure to DDT as determined by measurement of electrical activity of lateral lines. Partially exposed lateral lines of freshly Killed fish were fitted Mlth electrodes. DOT caused the lateral line nerve to become hypersensitive to experimental stimuli and affected behavioral responses of fish to tenoerature. • Anderson fl«6S>, AMIC-3764 ------- Comooun4 OrganIso Field Field Study Location Toxlclty, Active Ingredient, Pp» Experimental Variables. Control led or Noted Comments Reference DOT rv> DOT DOT DOT DOT Oncorhynehus klsutch (?.9 9> 0.33 (T31I Oncorhynehus L kisutch (7.1. Oncorhynehus L klsutch (15.01. q) Salvelinus fontlnalls (110-180 q) 1.3 (T65) 2.6 (T106J 0.02 (SB) Parophrys vetutus FH DOT Herlucclus product us FH Pacific Northwest Coast. Blaine, Hash. Pacific Northwest 0.01 (residue) — 0.01-0.06 (residue) A diet containing DOT fed to coho Buhler, et salmon resulted in median survival times al directly proportional to body Height. (197J Suoolemental feeding orolonqed lifesoan, 371 but mean survival time remained a direct function of body lelqht. Smaller salmon Here more susceptible because Hold content apparently failed to provide for storaqe detoxification of DOT. Considerable addition! data are presented. same as above same as above Brook trout conditioned to I iqht and shock rescontf to both by the propeller-tall reflex. Exposure to DOT resulted In markedly delayed ability to learn. The authors state that DOT spoarentlv affects the CNS and may cause adverse effects on such behavioral activities as territorial defence and migration. Pesticides from the Columbia River Into Puget Sound aooarently contaminated fish constituting commercial catches In Pacific Northwest waters. Residues In these marine products were substantially loner than the FDA tolerance for beef (7 pom). Fish fro* locations near the mouth of the Columbia Plver had higher pesticide content than ones caught farther away. same as above Buhlert et al (1970),AHIC- 3701 Buhler. et al Ct970»,AMIC- 3781 Anderson.et al (1970), AMIC-3782 Stout (196S), AM.IC.-37a!. Stout (1968), ------- DOT DOT DOT DOT DOT DOT DOT DOT DOT Herluce lux predue tus HerluceIu« product us MeMucclus croductus Ifishaenl) Sebastodes alutus Platlehthys stetlntus FH FH FH FH Gadus FH •acrocephalu* Sebastodes flavldus Sebastodes I lavtdus Pfaephales FH FH BCF* Coast* Sarasota Passage* Hash. Pacific O.Ot-0.09 Northwest (residue) Coastt Fort Susant Hash. Pacific Northwest Coast* Cape FoulHeather, Or. Pacific Northwest Coast, Aberdeen Hash. Pacific Northwest Coast, Hecate Strait, B.C. Pacific Northwest Coast, Blalne, Hash. Pacific Northwest Coast, Blalne* Hash. Pacific Northwest Coast* Hecate Strait. B.C. Pacific Northwest Coast, IlwaeoHash. O.OKresldua) O.It (residua) — O.It (residual -- O.ll(resldue) — (residua) O.OOH-0.05 (residue) O.OI.-0.19 (residue) 0.018 (TO sane as above «aaa as abova sane as abova sane as abova saa as abova saae as above same as abova saae as above 1MIC-378V Stout (196S). »MIC-378<. Stout (19f.8», •Hic-srs* Stout (1968), 4MIC-378* Stout (19«i9», •HIC-578* Stout (193), Stout Stout (1968). •MIC-378 Stout (1968). HIC-378« LAS acted svnerglstlcalIv with Solon etal ------- Compound DOT DOT DOT Toxtclty, Experimental Active Variables, Field Field Ingredient, Controlled Organism Study Location Ppn or Noted Comments prone) as Car ass 1 us L — auratus Car ass I us L -- auratus Sl»o L qalrdner I (186-788 q) oarathion to cause less survival of fatheds but had an Indeterminate effect with OPT and no svnerqistle effect with Endrln. 1,5-180 (SR a Goldfish were exposed to 5-?0) Inereasinq concentrations of DDT and residues determined after ?1 days of exposure. Most DDT had been converted to ODE. Phenobarital had no siqnlflcant effect on Insecticide residues. 0-0.1 a* ' same as above (residue) 15 (SB 6 hr) »* In aquarium water, I* opm DOT caused no apparent el ect roohysi ol oq leal differences in lateral line preparations. Reference (1969) . AHIC-3785 Young, et al (1971), AMIC- 379«- Younq, et (1971) , AMIC-3796 Bahr, et 3808 al al DOT DOT DOT DOT Sal mo qalMnerl Trl turus crlsfatus Pans temporarla Ran a teaporarla I •«• 0.1-2.0 (NTE, Intravenous) 0.67-1.<> (residue) 0.05 (SB 5-19 hr) 0.5-1.2 • Icrograii (residue) However, tremors antl byperexcl taM 11 ty were observed after 1 hr. Neural discharge was not affected by intravenous Injections, but tremors occurred at concentration levels of 0.5 pon and above. The authors eonclule that spontaneous activity of the lateral >Ine Is not a sensitive Index for DOT neurotoxle effet. same as above Bahr, et al (1971),»MIC- 3808 DOT caused hyperactIvlty In CooKe exoosed tadpoles. This caused Increased (1971), capture lunges of newts thus Increasing »MIC-3S1<, the predatory efficiency of the newts. DOT had no apparent effect on the newts. sane as above same as above CooKe (1971), AMIC-381W CooKe (1971), AHIC-381* ------- DOT DOT Carasslus 9SA auratus (8-15 Car ass 1 us BS» auratus 18-15 1.0 (SB H.5hr> a.q* 1.0 (T 10 hr> expospd to DOT were killed Aubln, et and brain electrical activity recorded by al(19K9)» means of Aq-AqCI bioolar electrodes. A«.IC-3S35 After ?.5 hr exposure, fish dlsolaved complete loss of balance and swam continuously on their sides. Amplitude and freauency of spontaneous electrical activity Mere altered. This coincided with permanent loss of balance. The authors state that this is the first record of a change in fish EEC following DOT poisoning. sane as above Aubln. et at C1«»69),«HIC- DOT Sal mo salar L DOT DOT DOT DOT Salv«tInus fontInalIs (yearlInq) Salw«lInus fontInalIs Endomychura craveri (eqqs) tmlonyehgra craveri (eggs) Western U.S., Pacific Ocean, Panama* Hexlco,and Antarctic Western U.S., Pacific Ocean• 0.02-0.20 a».q« (sai) 0.02-0.20 (SSI) O.I. (SBI a»,q« 39 (residue) 0.31-2. ------- I ^3\ Comoound Orqanlsn IT Thalasseus eleqans (eqgs) JT Laru* heermanl («qg«) JT Pomoxis annul »rl* IT Pomoxl<; nigro- Ba.cula.t-.ia- )T Leoomls •aeroehlrus 9T Pyqoscells ade 1 1 ae Toxlclty, Experimental Active Variables. Field Field Inqredlent< Controlled Study Location Pom or Noted Comments Panama, Mexlcotand Antarctic F Western 5.0 (residue) -- sane as above O.T., Pacific Ocean, Panama, Kazioo>and Aatartlca F Western <»t (residue) ~ saae as above U.«J., Pacific Ocean, Panama, Mexico, and Antarctic F Western 1.83 (whole — saae as above U.S., body residue) Pacific Ocean, Panama, Hoxlco, and Antarctic F Western 7.10 (whole -- same as above U.S., body residue) Pacific Ocean, Panama, Mexico, and An tar tic F Western 5.9 (Hhole body — same as above U.S., residue) Pacific Ocean, Panama, Mexico, and Antarctic F Western 0.128 — same as above U.S., (residue) Reference Rlsebrouqh, et al (1<>6M. AMIC-3W. Blsebrougn, et al (146ft), AHIC-38M. Sls»fcrouqh» et al (1968) , AMIC-3SH "Isebrouqh, et al (1968), AMIC-38M. RIsebrouqh, * t at <19«>8) , AHIC-38Vli »lsebrouqh> et al ------- DOT DOT DOT DOT DOT 00 T (eqgs) Aechmorohorut F occidental is FuI manus qlaclalis PutfInus ereatoous' Puf f inus qriseus Pufflnus F tenulrostrls Oeeanodroma homochroa Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama* Haxlco, and Antarctic Western U.S., Paclf1C Ocean, Panama* Mexico* and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., PaclfIc Ocean, Panama* Mexico* and Antarctic Western U.S.. Pacific Ocean* Panama, Mexico, and ?&.<. (flesh residue) 0.1.1-17.5 (whole body residue) 3.0 (Hhole body residua) 2.3-12.3 (Hhol« body residue) 39 (whole body residue) 99.3 (whole body residue) sane as above sane as above same as above same as above sane as above same as above Slsebrouqh. et al Risebrouoh, et al (196S), Rlsebroucrh, «t al (1968), AHIO384* Risebrouoh, et al (t9f.fl). Rlsebrouqh, et al (1968), "Isebrough, et al (1968), AMIC-38<.* ------- > Field Coaioound Organism Study )T Pelecanus F oce I Cental Is (eqqs) )T Freqata F paqnlf 1C ens (eqgs) )T Sula F leucogaster )T Phalacrocorax F penici llatus (eqqs) )T Phalacrocorax F oelaqlcus (eqgs) JT Anas F cyanootera Field Location Antarctic W«tern U.S., Pacific Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S.. Pacific Ocean, Panama, Mexico. and Antarctic Western U.S.. Pacific Ocean, Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments 10.0-11.5 — same as above (residue) 0.0087-0.03 — same as above (residue) 8.2 (residue) -- saae as above 0.326 ~ same as above (residue) 0.128 ~ same as above (residue) 10.9 (Hhole — same as above body residue) Reference Rlsebrouqh, et al MIC-lU Rlsebrouqh, et al (19681, AMIC-38H Rlsebrouqh, et al ( 1968) , AMIC-S8^ Rlsebrouqh, et al (1968), ANIC-3S«i«( Rlsebrouqh. et al (1968), A MIC— 38fc^ Rlsebrough, etal (1968) AMIC-3M> ------- DOT DOT 6 VO DOT DOT DOT DOT EI anus teocurus fwqgs) Acclolter cooper 11 Aaulla chrysaetos (eqqs) Pandlon hallaetus Falce cotumbarius Falco sparverlus Panama, Mexico, and Antarctic Western Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., PaclfIc Ocean, Panama, Mexico, and Antarctic Western U.S., PaclfIc Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama. Mexico, and Antarctic Western U.S.. Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pad Me Ocean, Panama, Mexico, and Antarctic 0.31.-9.0 (residual 25.2 (whole body residue) 2.0 (residue) same as above same as above same as above 55.0 (whole body residue) 2-9 (whole body residue) 0.01. (whole body residue) sae as above same as above sane as above RIsebrouqh, et al (19S8), Rlsebrough, et al (198B), P. isebrouqh, et al (1968), Rlsebrouqn, et al (196M , SMIC-38«.l» Plsebrouqh, et al (19SS), AHIC-38I.I. Rlsebrouqn, et al (1968), AKIC-3S ------- Comoound Organism DOT Fat co soarverlus (eqqs) Toxlclty, Experimental Active Variables, Field Fl-ld Tnqrdlent, Controlled Study Location Ppm or Noted Comments F Western 0.2 (residue) — - sane as above U.S., Pacific Ocean, Panama, Mexico, and Antarctic Reference Rlsebrouqh, etal (19<>8), AMIC-381,1. DOT DOT DOT DDT Nyctlcorx nyctlcorax (eqqs) Larus F occidental Is (eqqs) Strna for^terl (eqqs) Hy ------- DOT DOT DOT DOT DOT DOT Url» »8lge (eqqs) Ptychoranphus F aleutleua Synthllboraao F hus antlquun Cerorhlnca •onocerata Zenaldura •aeroura Tyto alba DOT Sturnella neqlecta Western U.S., Pacific Ocean, Parana, Mexico, and Antarctic W«a-t«rn U.S.. Pacific Ocean, 191 (residue) — saae as above Rlsebrough, et al Maxlco, and Antarctic Western U.S., Pacific Ocean * Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panana, Mexico, and Antarctic Western U.S.. Pacific 5.8 (Hhole body residual 0.75 (whole body residua) 2.7 (whole body residue) 0.19 (whole body residue) 1.3-6.6 (whole body residue) 0.3-3.3 (whole body residueI sane as above sane as above sa»e as above sane as above sane as above saae as above Rlsebrouon, et al (1968. AHIC-38* Risebrouoh, et al (19681, AMIC-JSMi Risebrouqn, et al (1968), AHTC-38<><> Risebrouqh, et al (1968). ------- Compound DOT DDT DOT DOT DOT Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Orqanlsa Study Location Ppa or Noted Comments Falco F peregr Inus (•99> Falco F pereqrlnus (1 Mature! Faleo F peregrlnus 11 •••tire) Falco F oereorlnus ladult) Falce F oereqrlnus Ocean, Pana«a, Hexlco. and Antarctic Western 0.02 (residue) — U.S.. Pacific Ocean, Panama, Mexico, and Antarctic Western 1.9-396 (flesh — O.S., residue) Pacific Ocean, Panama, Mexico, and Antarctic Western 6l.-5.ODO (fat U.S., residue) Pacific Ocean, Pnnana, Hexlco, and Antarctic Western 85-137 (flesh U.S., residue) Pacific Ocean, Panaaa, Mexico, and Antarctic Western 3,600 (fat U.S., residua) Pereqrjne falcons, falcon nrey. and other predator species were collected widely and analyzed Tor DOT, DOE, PCB, and it few other pesticides to a lesser degree. PCB and DDT were found to be widely dispersed globally. pen was found to be a powerful inducer of heoatic enzymes that degrade oestradlot. Reductions in thlcKness of ego shells. eggshell weight, and water retention occurred. All affect hatching success. The authors state that the oer«grin« aay be the first species entlrpated by global eon tan I nation. sa»e as above saa,e as above sane as above saae as above Reference AMIC-38I><> Rlsebrouqh, et al (1968), »HIC-5««.i. Rlsebrouoh, et al C19SM,A«IC- 381.1, Visebrough, et al (l<»6«t. AMIC-38",!. Rlsebrouqh, et al (1968). AMIO38«t Rlsebrough, et al ------- oar DOT r DOT DOT DOT taduttt Podleaps casplcus LooHelanla ••tanla Halocyptena •Icrosoaa PIzonyx vlvesl Ictalurus ounctatus Pacific Ocean, Panaaa, Mexico,and Antarctic Western U.S., Pacific Ocean, Panaaa, Hex I co, and Antarctic Hestern U.S., Pacific Ocean. Panaaa, Mexico, and Antarctic Western U.S., Pacific Ocean, Parian a, Maxleo, and Antaretie Western U.S.t Pacific Ocean, Panama, Mozloo, and Antarctic O.Z6-12.1 (•hole body residue) 4.2 Cnhole body residual 3.Z iNhole body residue) 0.71 (nho(e body residual save as above RIsebrouq^, et al (19681. sane as above et al C196S), saae as above et al (19681, saae as above et al (19651, ns» — 0.016 a, Orqanochlorlne Insecticides were Hacek, et al synthetic the nost toxic coaoounds, (1970), test Hater orginochosohates Interne.1lat»>, earhanates AHIC-SS10 the least toxic. Proxn trout »as the species nost susceptible to orqanochloPlr.es, coho salmon the nost susceotlble to carbaiates, and goldfish Mert> the least susceotlble of all species. Safe concentrations established by hioassays xith salaonids or centrarchlds Mould likely be safe for cyorinlds and ictalurlds. Safe levels for Ictalurlds or cyprlnlds Mould probably be hazardous for centrarchlds and salaonlds. The use ot qoldflsh In bloassays Mas dlscouraqed. ------- > g COBBOund 'DOT DOT DOT DOT DOT DOT DOT DOT DOT DOT DOT Field Field Organise Study Location Slto trutta BSA Oncorhynehus BSA -- Kisutch Perca BSA flavescens Ictalurus BS» •«las Crasslus BSA ™ aurst us Cyorlnu* USA — - earplo PImeohales BSA •- prone! as l«ools SSA Mcroehlrus LeDomls 8S* •Icrotophus Mlcrooterus BSA — salHoIdxt SslMO BSA — galrdnrrl Toxlclty, Active Ingredient, Pp« 0.003 (T<>t 0.00 0.009 (Ti>) 0.009 (Tit) 0.031 (T) 0.007 (Tl.) Excerlnentat Variables, Control ted or Noted a, synthetic test water a. synthetic test water a, synthetic test Mater a, synthetic test water a» synthetic test water 9, synthetic test water a, synthetic test water a, synthetic test water a, synthetic test water ». synthetic test water at synthetic test water Comments sane as above same as above saae as above sane as above saae as above saae as above sane as above same as above same as above saae as above saae as above Deference Macek, T at (1970), »NIC-«:MO HaceK, et al (197Q1, ANIC-5S10 Mace, et al(1970). •MIC-5S10 MaceK, e» al (1°70). AMIC-5510 M»cH, et »l (1970), »MIC-S«;ID MaceK. et al (1970) , «HTC-5510 Hacek, et al (19701 , AMIC-SS10 NacK, et al (197m , AMIC-5510 Hacek, et »l (1970), AHIC-5510 HaceK, et •1(19701, AHIC-5510 NaceK, et •1(19701, AHIC-9S10 ------- DOT Pa I ae<on« tes kadlakensls (resistant) BS — 0.0037-0.0068 DOT DOT Pa I aemone tes- BSA kadlafcensls (non— resistant) Tctalurus eatus FL Clear Lake, Cal. 0.0026 IT1) less than 1 (flesh residua) DOT 00 T DOT P«rca flavescens Lepomls glbbosus Catostomus commersonl FLR FLR FLR 43 sanipt Inq stations In Mass. 0.06-13.2 (residue) 93 samol Ing 0-9.1 stations In (residue) Mass. 43 sampling 0-11.2 stations In (residua) Hass. Bloassays Mere conducted with Naqvl, et al shrlmn from three areas of Intensive (1970)» pesticide use and from an unexposed area. 4MIC-5519 Previously exposed shrimp Mere from 1 to ?"? times more resistant than unexposed shrimp. Both types of shrimp Mere also exposed In caaes to Maters of the contaminated areas. Susceptible shrimp suffered 66 percent more mortality than did resistant shrimp. The toxiclty of the insecticides ranked In descending order was as follows: most toxic, Endrln, DOT, Methyl parathlon, Parathionl medium toxiclty, Guthlon, Llndane, Toxaohene, Strobanei lease toxic Chlordane, Sevin, and Heptachlor. same as above Naavl,et al (1970), AMIC-S519 Residue analysis results mainly Linn, et for IDE In fish, birds, nd plankton from L11969), 11S9 through 1965 x^re reported. The HIC-55?1 residues primarily resulted from application of DDT to farmland ar.d for qnat control. In some cases, data for a single anliral In one year Here given. Primary emphasis Mas on larqeirouth bass and Mhlte catfish. The qeneral level of TD£ contamination In birds and fish declined markedly fro 195S to 1965. This decline correlated directly Mlth strict limitation by permits of DOT applications during the latter years. Fish indigenous to Massachusetts Lyman, et al freshwater streams Mere analyzed for OOT (1968), and DOT metabolites during 1965-1967. «IC-3»39 Generally there Mas an Increase In pesticide content during the three year period. same as above sane as above Lynan, et al (1968), A1IC-3839 Lyman, et a! 11969). AMIC-3639 ------- Compound DOT DOT DOT DOT DOT DOT DOT DOT DOT DOT DOT Orqanlsn Tctslurus nebul osus Cyorlnus carplo Esox nlqer Not»m 1 oonus erysoleucas Semotl lus corporal Is Leoomls nacroehlrus Amblopl Ites ruoestrls Seiotl lus atpo^acul atus Mlcrooterus dolonlrul Alosa paeudo- harangua Fundu 1 us heterocl 1 tus Field Study FLR FLO FLR FLR FLR FLR FLR FLR FLR FLR FLR Field Locat Ion 93 samollnq stations In Mass. 93 sampling stations In Mass. 93 sampling stations In Mass. 93 sampl 1 ng s tat 1 ons In Mass. 93 sampling stations In Mass. 93 satnpl Ing stations In Mass. 93 sampl Inq stations In Mass. 93 samel Ing stations In Mass. 93 sampling stations In Mass. 93 sampling stat 1 ons In Mass. 93 sanpl Ing stations In Mass. Toxlclty, Experimental Active Variables, Ingredient, Controlled Pp» or Noted 0.32 (residue) 0.3-1.0 (residue) 0.02-1. D (residue) 0-1.1 (residue) 0-2.8 (residue) 0-2.1. (residue) 0.<>-8.3 (residue) 0.02-0.3 (residue) 0.2-B.6 (residue) 0.3<» (residue! — 0.7-2.8 (residue) Comments sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above Reference Lywan, et al (19S8). ANIC-3839 (1968), AMic-3839 Lyan, »t al (1968) , Lvman, et al (19681. Lyman, et al ANIC-3S39 Lyman. et al Lvman. et al AHIC-3839 Lyman, ft al (196S), AHIC-3839 Lyman, et al 4HIC-3S39 Lyean, et al (1968). AMIC-3839 DOT Notrools FLR 13 sanollno 0.1-3.1 sane as above Lynan, et al ------- DOT DOT DOT DOT DOT DOT DOT DOT cornotus Roccus «t at <19«.R) . AMIC-3S39 Lysn, t al et al , AHIC-JS39 Lyxan, et al Lvoan, et al Lyman, et al In studylnq control ot black fly, tne Indicated aauatlc soecles were studied at a series of six sanollnq stations. Mater Quality was unaffected hy the DDT aopllcitlon. No caoed fish died, hut Mild ones did apparently resulting from inaestlon of dead Invertebrate larvae. Invertebrates were collected by bottom sampling and bv drift nets, and fish by nettlncj and anqlinq. Fish mortality could always be related to at least a ten-fold Increase in DOT residues In the fish. DOT caused high bottom fauna mortality by direct contact. Caddisfty larvae Here more affected than stonefly and mayfly larvae. The author stated that DOT larvicidlnq for black fly control was not successful because of bar to non-tarqet organises. sane »s above Hatfleld (1969), AHIC-5770 Hatfletd (1969), AMIC-5770 ------- Coaoound DOT DOT Organise Simula* venustu* (larvae) Botto* Invertebrates Field Field Study Location FS Bobby "s Rrook, Labrador, Can. FS Robby~s Brook , Labrador, Can. Toxlclty, Active Inqredlent, Pp« 0.1 (SB) 0.1 CK) Cxoerlnental Variables, Controlled or Noted c,d,e,9 c«d,a,g DOT DOT DOT 590 (SB) •acrochlrus (liver •Itochondria) Cooeoods (Cyelons talcusoMus, Cyclops varleans, Cyclops vernalIs, Eucycloos agllls. Kacrocyclops albldus, OrthocyclODS •odestus) Cooepods (Cyclops blcuspldus, Cvcloos varlcans, Cyclops vernal Is, Eucycloos FL State and College, 8S» Hiss. 0.05 IK?) FL and BSA Befzontt Hiss 0.05 191 oercent K2I Connents sa«« as above save as above Reference Hatfleld I196<>>. »«IC-5TTO Hatfleld (1«69), AMIC-5770 Oxygen uotakr by blu?1" mitochondria was inhibited in the or«sence of DOT and ^uccinic acid. Increased hvdrolyslt of &TP also occurred in the presence of Mq and Hn ions. ihe author states that the primary effect oT DDT ancears to be Inhibition of electron flow fro«. succlnlc acid to the cytochroae chain. The response of pesticide-resistant aouatle orqar.ls«s to various pesticides was co«oared to the resoonse of non-resistant softies. Pesticide-resistant soecies wr' collected at Pelzonl and non-resistant soecies at State College. CoO«BOd«;. clams, snails, and sludae Hor«« fro* Belzonl were considerably »ore tolerant to oestlcldes than the non-resl«tant orqanlsms. The authors note that the effect of increased tolerance 1" th* orqanlsas Is an Increase In tn« a»ount of pesticide residues available to anlaals of Mqher trophic levels. save as above Hlltlbran (197U, 4MIC-59T5 Naqvlt «t (1969), Naavl, et al (19691, 4NIC-5979 Macro cyclop* ------- DOT DOT DOT DOT DOT DOT albldus, OPthocveloo* nodestus) Tub If ex tublf»x Crassostre vlrglnica I tarvac) FL •nd BSi AetTonl, Hiss. 3.0 (NTE) 0.031. ITlfc) 8SA Gambusia a«fInls (female, «i.3 c«, 1.9 q) Leblstes BS« retIculatus (nale, 1.8 », 0.? 9) Tllapla BS» nossamblca (.<> en, 1.3 Kuhtla BS saidvlcensls U.3 en, 1.5 0.02 (Tl>) 0.003 (T4I 0.007 (T? pesticides on Davis, et al embryonic development of clans and oysters Has reported. Synerqlstlc (1969)••NIC- effects with solvents Here also reported. 5990 Most of the compounds affected develocnent more than survival. Some, however, drastically reduced larval growth. The authors point out the necessity of evaluatlnq the effects of pesticides on all life stages of an orqanisi* and note the oosslbillty of selecting chemicals for oest control that Hould not have serious effect on shell fish. The five fish suedes are Nunoqana. et commonly found In streams and estuaries al (1970), In semi-tropical areas. G. af'lnls Mas the most tolerant. Varied sensitivity to the toxicants Here found. K. sandvlcensis MBS the most sensitive fish studied. The standard method procedure Has fol totted. sane as above sane as above sane as above NunogaMa* et al (19TO), aMIC-6567 NunogaHa, et al (1970), Nunooawa, et al (1970), »MIC-656T DDT Stolephorus BSA purpurea (3.6 em. fl.lt ql 0.001 (T 12hr) a.c,d,e.f, 1, salt nater sane as above et al (1970), NIC-»>567 ------- I Toxlclty, Active Field Field Ingredient. Compound Organism Study Location Ppm DOT Carclnus BSA — 0.3-1.0 (T2> maenas DOT Card I urn edule BSA ~ greater than Experimental Variables, Control led or Noted Comments a (con tin- One hundred-forty surface active uous aer- agents, solvent enulslf iers, pesticides, ation, sea- aolychlorlnated blohenyls, pure water, and Inorganic, and organic cheirlcals were da^y evaluated against as nany as ten marine solution organisms. The authors noted that most renewal) Published data of this type deal xlth toxlclty of chemicals to freshwater organisms. 10 ae(contin- same as above uous aer- ation, sea- water, and daily solution Reference Portmann, et at 11971), AHIC-7701 Portmann, et al (1971), «TC-7701 renewal) DOT Pleuroneetes PIatessa as 0.003-0.01 m> a«(contin- uous aer- ation, sea- water, and daily solution renewal) save as above Portnann, et al 11971), AHTC-7701 DOT Freshwater drua Ft DOT Goldfish FL Oret Lakes 0.6Z (-hole (Ontario, body residue) Huron, Erl«, Superior, Michigan) Great Lakea (Ontario, Huron, Erie, Superior, Michigan) 0.70 (whole body residue) Fish fron lake Nlchiqan contained Relnert 2 to 7 tl»es more POT (and DOT analogs) (ig7fl),«MIC- and ni«ldrin r«>sl<1uvs than fish from fhe 196 other Great Lakes. Fish fro Lake SuOTlor Invariably had the loxest accumulations of both chemicals. The compounds tended to concentrate in fat (oils). Considerable additional data are presented. The author noted the need to reduce pesticide usage to a minimum and to replace these Insecticides with less persistent materials. same as above Relnert (1970), 1HIC-196 ------- DOT Klyl FL Great Lakes (Ontario, Boron, Brie, Superior. Michigan) 3.38 (whole body residue) sane as above Relnert (197DJ, •HIC-19S DOT Lake herring FL Great Lakes l.tt-3.91 (Ontario, (whole body Huron, residue) Erie, Superior. Michigan) saae as above Relnert (1970) , 196 DOT Lake trout FL Great Lakes 6.6t-7.(>i> (Ontario, (whole body Huron, residue) Brie, Superior. Michigan) sane as above Relnert (1970),HIC- 196 DOT Lake white fish FL Great Lakes (Ontario, Huron, Brie, Superior, Michigan} D.<.5-5.0? (Hholebody residue! saae as above Relnert (1970),«MIC- 196 DOT Rock bass FL Great Lakes (Ontario, Huron, Erie, Superior, Michigan) O.ltO (whole body residue) sane as above Relnert (1979), •HIC-19S DOT Round FL Great Lakes 0.57 (whole whiterIsh (Ontario, body residue) Huron, Erie, sane as above Reinert (1970). •MIC-196 aupai-xur, Michigan) ------- Field Field Co»oun4 Organise Study Location Toxlclty, Active Ingredient, PDH Experimental Variables, Controlled or Noted Connents Reference DOT Sea laoorey FL Great Lakes (Ontario, Huron, Brie, Superior. Michigan) 1.27 (whole body residue! saae as above Relnert (1970), AMIC-196 DOT SI lay sculoln FL f s Great Lakes (Ontario, Huron, Erie, Superior, Michigan) 0.22-2.33 (whole body residue) save as above 'elnert (1970) , DOT Soottall shiner FL Great Lakes (Ontario, Huron, Erie, Superior. Michigan) 0.25 (whole body residue) saae as above Relnert (1970), AMIC-196 DOT Nine-coined FL Great Lakes n.^3 (Hhole stickleback (Ontario, body residue) Huron, Erie, Superior, Michigan) sane as above Relnert (1970), AMIC-196 DOT Stonecat FL Great Lakes (Ontario, Huron, Brie, Superior, Michigan) 0.28 (whole body residue) saae as above Relnert (1970), AHIC-196 ------- DOT Troutoerch FL Great Lakes (Ontario, Huron, Krle, Superior. Michigan) 0.9* (Hhole body residue) sane as above PeJnert (1970), •HIC-196 DOT Malleye FL Great Lakes 1.13-6.03 (Ontario, (whole body Huron, residue) Brie, Superior, Michigan) sane as above Relnert •1970), •MIC-196 DOT Hhlte bess FL U) Great Lakes (Ontario, . Huron, Erie, Superior, Michigan) 1.89-2.76 Iwho I* body residue) sane as above R«Inert (1970), 4MIC-196 DOT Mhlte perch FL Great Lakes (Ontario, Huron, Krle, Superior, Michigan) it.'Si (whole body residue) sane as above ffelnert (1970). •MIC-196 DOT Uttlte sucker FL Great Lakes (Ontario, Huron, Brie, Superior, Michigan) 0.37-1.1. (•hole body residue) saee as above Relnert (1070), 196 DOT YeII en oereh FL Great Lakes (Ontario, Huron, Brie, Superior. Michigan) 0.87-2.93 (•hole body residue! saee as above Beinert (1970),AMIC- 196 ------- Comoound Field Field Organism Study Location Toxlclty, Active Ingredient, Pom ExoerlBcntal Variables! Control led or Noted Comments Deference DOT Fiierald shiner FL Great Lakes 0.9 ------- Huron, Erie, Superior. Michigan) residua) DOT Brown FL Great Lakes 0.28 (hole — bullhead (Ontario, body Huron, realdue) Erie, Superior. Michigan) sane as above Reinert (1970),ftMIC- 196 DOT Carp Ft Great Lakes (Ontario, Huron, Brie, Superior. Michigan) 1.93 (Hhola body residue) saae as above Reinert (1<»70>. 4MIC-196 DOT Channel catfish FL Great Lakes (Ontario, Huron, Brie, Superior, Michigan) ft.90 (xhole body residue) sane as above Reinert (1970). •HIC-196 DOT coho sal-on FL Great Lakes 0.72 (whole (flesh) (Ontario, body residue) Huron, Erie, Superior, Michigan) sa«e as above Reinert (1970).»MIC- 196 DOT Coho sol won (eqos) FL Great Lakes (Ontario, Huron, Brie, Superior. Michigan) 2.12 (whole body residue) saae as above Reinert (1970),»MIC- 196 ------- Coaoound Field Field Orgnnls" Study Location Lake Michigan) Toxlclty. Active Ingredient, Ppn Experimental Variables, Control led or Noted Comments Reference DOT Cvorlnus carplo FR DOT DOT DOT DOT DOT DOT Catostotus FR commersonl Amelurus FR nebulosus Perca FR f lavescens Csox luclus FR «»bI oolites FR ruoestrls Ca«pelom» sp. FR St. Lawrence 0.3(1(0.33 Don River, max tissue Montreal, residue) Canada St. Lawrence 0.38(1.33 apu River, max tissue Montreal, residue) Canada St. Lawrence 0.3MD.1? Don Piver, aax tissue Hontreal, residue) Canada St. Lawrence 0.38 (0.?Sppm River, max tissue Montreal, residue) Canada St. Lawrence 0.38 (0.38 River, ppi»«ax tissue Montreal, residue) Canada St. Lawrence 0.38(0.02 POM River, nax tissue Montreal, residue) Canada St. Lawrence 0.36 <0.">0po» River, nax tissue Montreal, residue) Canada Residues of ODD were measured In Fredeen, et water, irud, molluscs, and fish durlnq and at (1970), after 1)00 application in 1967. Sa«0ling •MIC-53't points were shove the point of apotlcatlon and 10 and <•? «i downstream. Residues fro* unknown sources were detected upstream. Qownstreao residues were more than twice those obtained upstream (0.156 versus 0.369 ppn). The hlqhest concentration in an Individual fish was 1.R1 ppm. sane as above same as above same as above sane as above sane as above sa»e as-above Fredeen, et al (1970).A1IC- Fredeen, et al (1970). AHIC-S3I. Fredeen, et al (1970), AMIC-531. Fredeen, et al (1970), AHTC-S3* Fredeen, et al (1970),«HIC- 53«. Fredeen, et at (1970), ANIC-53ii DOT Cyprlnodon BSA 0.015-0.02 (K> a. Sensitivity of three generations Holland, et ------- DOT f 3 00 VP 00 VP 00 VP 00 VP DDVP varleqatus (90-70 ••) seaNater tonthle Trout Creek, 9.012-0.068 Hasatch (Kl County,Utah Streaa flow (.•bee rohlta (fry) BSA 11.? CT7> a,e,d,e,f Labeo rohlta BSA fflnq.rllng) Trichoqaster BSA fasclfttus lyounq) Trlchogaster BSA faselitus (a>lult> Chnna punc tutus tfry) BSA 22.* tT7) 1.8 «T7I ?.«. (T7) 0.8 IT7J a,c,d,e,f a.c,d,c,f a,c>d,«,T of sheepshead nlnnoMs to DOT and Endrln al 119701, Mas determined. Sensitivity to DOT AHIC-726 varied seasonally. Fish Mere bred in ponds 15m X 5m X t.25m exposed to pesticides In aauarla, and survivors used for breeding. The results for DOT Mere not entirely clear due to the seasonal variability. Increased and decreased sensitivity Mere recorded for the Fl generation at different tines. Increased sensitivity for the F7, and decreased for the F3. The authors stated that incorporation of DOT in ova via llnids •ay have caused increased sensitivity. Endrln toxicity MBS decreased in the Fl and Increased In the F? generation. Complete deoopulatlon Has found Sonstelle at the collection station ?ODD m 11969), downstream from aoplicatlon point. AMIC-96* Insect mortality Mas Independent of DOT concentration In areas of turbulent floM, thus mortality Has not directly related to HOT concentration in this field situation. Repopulatlon Mas Incomplete after 57 MK. DDVP and Phosohamldon Mere shoMn Konar to be selective toxicants that can be (1969> ,AM,IC- used for eradication of undesirable 553 animals fro ponds Mlthout injuring carp. OOVP seeeed superior since less Mas needed. It Mas not influenced by turbidity, and It detoxified more rapidly than Phosohamldon. sane as above Konar «!<169l,AHtC- 5U53 saae as above Konar(19691, saae as above save as above Konar (19691, A1IC- 51.57 Konar (1969» , AHIC-51.53 OOVP Puntlus BSA 6.2 (T7> saae as above Konar ------- Comoound OQVP OOVP DOVP OOVP OOVP OOVP OOVP OOVP OOVP OOVP OOVP Field Field Organism Study Loeatloi sophore (adult) nabas BS — testudineus Hetaropnaus- BS* — tea foaailis Esomus BS* — danrlca (Try) Esomus BS* danrlca (adult) Notoneeta sp. BS* — Dytlscus sp. BS* — - (1 arvae) Dytlscus sp. BS* ~ (adult) Spha»rodma BS -- annul a turn Panatra BS* fl liforuls Anisootera BSA ~ (nvmohsl Cytilster sp. BS* Toxlclty, Exoerlmental Active Variables, Inqredlent, Controlled n Pom or Noted 11.7 (T7) a.c.d.e.f 17.8 (T7) a,c,d,e,f 2.8 (T7) a,c,d.e,( 18.? (T7) a.c.d.e.f 0.001 (T7) a,c,d,e,l 0.06<. (T7I a.c.d.e.f 0.35 (T7) a.c.d.e.f 0.085 (T7) a.c.d.e.l 0.13 (T7) a.c.d.e.l 0.15 (T7) a.c.d.e.f 0.21 (T7> a.c.d.e.f Comments same as above same as above same as above same as above same as above same as above same as above same as above same as above same as above same as above Reference (199) ,»HIC- Konar (1969) , Konar Konar (1969) ,MIC- Konar (1969) .AHIC- Konar (1969) , Konar (1969), MIC- 51.53 Konar 51.53 Konar Konar (1969), AMIC-51.53 Konar (1969),HIC- 51.53 Konar (1969), AHIC-St.53 ------- ODVP Neoa so. BSA — 0.27 (T7) a,c, a,e,d,»,f Sao* as above Konar (1969). OOVP 00 VP Hydroonllus BSA SO. Volvox BSA — 0.39 (T7t a,c,d,e.f 5.0 (NTE) a,e,d.e,f sane as above sane as above Konsr (1969), A1TC-5I.53 Konar (1969). 00 VP Pandorlna BSA 5.0 (NTE) »,e,d,.l sane as above IConar (1959), s 00 VP 00 VP OOVP Closterlun BSA Brachlonys BSA Gastrotrleha BSA 5.0 (NTE) a.c.d.e.f 9.0 (NTE) a,c,d,e,f .0 (NTE) a.c.d.e.f same as above sane as above sane as above Konar Konsr (1969) , AMIC-5U53 Konar (1969). OOVP OOVP DOVP Cvorls BSA Cyclops BSA — Nauollus BSA — 1.0 (K> 0.5 (K> 0.5 (K) a,c,d,e,f a.e.d.e.f 9,c,d,e,f sane as above sane as above sane as above Konar (1969), AMIC-5I.53 Konar (1969), AMIC-SU53 Konar (1969). AHIC-51,53 OOVP DOVP Daohnla BSA — Cerlodaphnla BSA 0.5 (K) 0.5 (K) a,c,d,e,f a,c,d,e,f sane as above sane as above Konar (1969), AHTC-S4.5J Konar (1969). AHIC-5W53 ------- Compound OOVP OOVP OOVP DOVP OOVP OOVP OOVP OOVP OOVP OOVP OOVP MVP Field Field Organise Study Location Dlaptomus 8SA — Nandus nandus BSA — •Ufa rlta 8SA Apohlonou BSA — cuchla Mystus BSA — vitatus tlry» Mystus BSA — vitatus (adult) Puntlus BSA sophore lfry> Chann* BSA — punctatus (1 Inqert lnq> Cnanna BSA — punctatus (adult) Mastocembelus BSA — pancalus Hacroqnatnus BSA ~ acu lea turn Cttanna L — punctatus Toxlclty, Active Ingredient, Ppm 0.5 (K) 2.6 CT7) 2.8 (T7) 3.1, (T7) 2.3 CT7) 6.6 1.0 (T7) 1.8 (T71 2.9 (T7> 2.6 (T7) 3.6 «T7I 20 (SB1) Experimental Variables, Control led or Noted Comments a,c,d,e,f same as above a,c,d,e,f same as above a,c,d,e,f same as above a,c,d,e,f same as above a,c,d,e,f same as above a,c,d,e,f same as above a,c,d,e,f same as above a,c,d,e, f same as above a,c,d,e, f same as above a,c,d,e,f same as above a,c,d,e,f same as above a* Snakehead fish eqgs Here unaffected by OOVP concentrations of Reference Konar (1969), AMIC-SWS Konar (1989), Konar Konar AHTC-SI.53 Konar (1969) , Konar (1969), Konar (1969), AMIC-SI.53 (1969),»1tC- Konar (I960) ,ASIC- 553 Konar (1069), AMIC-5»S3 Konar (19S9). AMIC-"il,53 Konar less (1969), AMIC- ------- Oecamethonlu dl bromide leqq) Channa punctafus (hatch!lnq«) Neqaprlon brevlrostrls L — BSA .5 IT2) 90 .0 ppm and stopped at 5.Q ppm or more. Eggs and hatch!Ings survived Hell at 0.1 ppm DOVP. same as above Konar •HIC-6T8S Baldridqe (1969). MIC-383? « Data fro study of drug effects on younq lemon sharks Here treated mathematically to demonstrate applicability of classical rate theory to the study of chemical shark deterrents. Incaoacltatlon (narcosis) xas the orlnary parameter timed for effectiveness. This Has usually quite rapid for the more effective druas. The effect o« 57 pesticides on Davis, et «l embryonic development of clans and oysters Has reported. Svnerglstlc (1969)«»MIC- effects Hlth solvents Here also reported. 5990 Most of the compounds affected develocment more than survival. Some, honever, drastically reduced larval growth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an organise and note the possibility of selecting chemicals for pest control that Mould not have serious effect on shellfish. same as above — Approximate toxlclties of numerous pesticides commonly used in Britain were summarized. An excellent brief, general discussion of toxlclty testing Is also present. «(contin- One hundred-forty surface active uoua aer- agents, solvent emulslflers, pesticides, ation, sea-DO I yen lorInated blohenyls, pure water, and Inorganic, and organic chemicals ner« evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal tilth Davis, et al (1169),»HIC- 5990 HaHdeslev-Th om«s(197t) AMIC-105% Port»ann, «t al (1971), AMIC-7701 ------- Toxlcity, Experimental Field Field Coaoound Organise Study Location Oeraol Crangon BSA — crangon 0«rol Pandalv* BSA — •ontagul Oa Oe Tana ?? Rasbora BCF* — hateroKoroha and BS» Oa Oe Tana (llauld) Rasbora BCF* — heteroaorpha and BSA Active Variables, Ingredient, Controlled Poa or Noted solution renewal) 100-330 «TZ) a«(contin- uous aer- ation, sea- uator, and daily solution renewal) 108-330 a,c,c,r. hard IHHIor soft (SH) synthetic dilution Hater, or seanater t or soae species Conaents toxlclty of chemicals to. freshMater orqanlsos. saae as above sane as above On hundred sixty-tour DesticldeSf wetting agents, and alscel taneous Hater pollutants shoxed a wide ranqe of toxlclty soannlnq 12 orders of miqnltude. Knowlna the toxiclty and • percentage of al 1 comoonents of a formulation did not result In easy predictability of the toxlclty ot a •Ixture of Materials. Sonetlnes pesticides Here nost toxic in hard Hater and sotet lines the opposite Has true. Testing the actual material as sold Has found to be essential. saae as abova Reference Portnann, et al (19711, «HIC-r7«l Portaann, et al 11971), •MIC-77C1 Alabaster, (19691, AHIC- 5?5 Alabaster, (1969), AMIC- 525 ------- Da Oe Tana (liquid! Rasbora heteronorpha 8Cf» •nd BSA 0.02 CT2 In acetone! Oe 0« Ten* (oast) Rasbora heteroaorpha RCFA and BSA 10.7 (Tl) 0 0* Tan* (xettable) Rasbora heteronorpha BCFA and BS* 0.001 IT2 tin acetone) Oa 0* Tana (••tfabta) ffasbora heteronorpha BCF* and flS* 8.2 IT2) afc,«,f , hard (HW) or soft (SH) synthetic dilution ••atari or seanater for son species a,c,e,f. bmrd (HW) or soft (W) thatia dilution vater, or MMmter tor some •paeles hard (HW) or soft (SHI synthetic dilution Mater, or seaxater for some soecles hard IHW)or soft (SH) synthetic dilution natr, or saaHater for soaa spaclas saaa as abova Alabaster, fl<96 ANIC-892 ------- Comoound Organism Field Field Study Location Toxlclty, Active Ingredient, Exo«rI mental Variables, Control led or Noted Comments Reference Olazlnon Pasbora heteromorpha BCFA and OS* l.«»S IT1) Placlnon Olcamba papulifera. Gammarus tasclatus BSA 100 (K) greater than 100.0 IT3) a»,c,e,f, hard (HW) or soft (SO syn- thetic water, or aoawater Tor son* speclea Euntor'i medium diluted 1:5 a» Olcaajba Paleomontes BS» kadiakens Is greater than 100.0 (T2) more toxic thar CuSO» miscellaneous wafer oollutanrs showed a AHIC—5>?5 wide ranoe of toxlcity scanning 12 orders of magnitude. Knowing the toxlclty and formulation did not result in easy prcrtlctabl11tv of the toxicity of a mixture of materials. Sometimes pesticides were most toxic in hard water and sometimes the ooposite was true. Testing the actual material as sold was found to be essential. All compounds were harmful to duckweed to sons degree. Decreased populations were noted at non-lethal concentrations and some compounds (Kalathlon and 2,l).-D) caused teratogenio effects at concentrations as low as 1 ppn. Of the aquatic weed herbicides evaluated, Dlclone was the most toxic, Daphnla was generally the most sensitive IV] organism. All of the Crustacea were affected by much lower concentration levels of herbicides than Indicated by the TL sub SO values. All of the animals represent Important food chain links. sane as above Sanders «1970),AHIC- kiorthley, et al (1971), AKIC-3233 Sander Olcamba Olcaaea •sell us 8S» brevlcaudus Orconectes BS» nals greater than 100.0 (T2) greater than 100.0 IT?) same as above same as above Sanders 11970),AMIC- 53 Sanders (1970>,AHIC- S3 Oleaaba Oaohnla aagna BS* — greater than sarnie as above Sander* ------- loo.o (1970),HIC- Olcamba Cypridoosls BS vldua greater than 100.0 ITZ) sane as above Sanders (1970),»1IC- Oicamba Olcapthon Leoonis BS* •acrochlrus Mercenarla •ercenarla (eggs) l-O.O tti) 5.7 (T2) OIeMot>«nll Cal llhacfIs sp. (nymoh, 8-12 «•> 8S» 10.3 (Tl>) Sanders (1970)t AMIC-WS3 ~ The effect of 5? pesticides on Davis, «t al embryonic development of clams and oysters MBS reported. Synergistic (1969)»AHIC- effects Mlfh solvents Here also reported. 5990 Most of the compounds affected develocment more than survival. Some, however, drastically reduced larval gronth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that Hould not have serious effect on shell fish. — same as above Davis, et al (1969),HIC- 599D a,c,e,f. One hundred sixty-four Alabaster hard (HM) pesticides, netting agents, and (1969), or miscellaneous Hater oollutants shoned a AHIC—5»?5 SOFT(SH) Hide range of toxlcity spanning 12 orders synthetic of magnitude. Knowing the toxlcity and dilution percentage of all components of a Hater, or formulation did not result in easy seanater predictability of the toxlcity of a for some mixture of materials. Sometimes species pesticides Mere most toxic in hard Mater and sometimes the opposite Has true. Testing the actual material as sold xas found to be essential. ««,b»,c,f. The toxlcity of herbicides Olouat Wilson, et 1,1, and and Dichlobenll to aquatic invertebrates al (1969), fllllca, and fish Mas determined in aquaria ANIC-5<>52 Calcium, containing substrates natural to each nagneslura. soecles. Dlouat was nulte toxic to H. sodium, azeteca but not as toxic to other potassium, organisms. Olchlohenll Has less toxic to M. azeteeus but considerably more toxic ------- Toxlclty, Exoerimental Active Variables, Field Field Ingredient, Controlled Comoound Organism Study Location Po» or Noted Comments blcarbon- to th> remaining organism than OiQuat ate. Hud lessened the toxlcltv ot both, but carbonate, more so for Olquat. Oichtobenll had a SUlfate, sublethal narcotizing effect on the Iron, organisms that resulted In dissolved Immobilization. It Has concluded that solids, both herbicides could adversely affect conduc- certain fish food organisms. tanee Olchlobvnll RalUbRctls BSA — 7.* (S8«.) *,b«,c,r, same as above so. Cnymoh, 1,1, and 8-1? ••) silica, calcium, magnesium. sodlun, potassium, blcarbon- ata, carbonate. sulfate, iron. dissolved solids, conduc- tance Olchlobenli Leoonls BSA — lit. 7 (Tit) a»,b»,c,f, sane as above •acrochlrus 1,1, and silica, calcium, oagnesium, sodium. potassium, bicarbon- ate, carbonate. sulfata. iron. dissolved solids, conduc- tance Reference Nllson, et at (1969), »MIC-5 ------- OleMobenll Libel lull ip. ASA (naiad. 16-24 qreater thanlOO a»,b»,c,f, (T 1-M 1,1, and silica, calcium, magnesium, sodium, potassium, bicarbon- ate, carbonate, sulfate, Iron, dissolved solids, conduc- tance sa>e as above Wilson, «t al (1969), OlcMobenll Libellul» so. BSA (nlad, .16-?«t ••I greater ThanlOO »»,b»,c,f, tse l-«»t 1,1, and silica, calcium, magnesium, sodium, potasslua, bicarbon- ate, carbdhate, solTata, iron, dissolved solids, conduc- tance sane as above Mil son, et al (1969), MIC-5«>52 Olchlob«nl! 13.0 (TV) so. (larva, 15-2D ••» a»,b«,c,f, 1,1, and silica, calcium, magnesium, sodium, potassium, bicarbon- ate, saee as above Milton, «T al (19691, ------- Toxlclty, CxDerlmental Active Variables. Field Field Ingredient, Controlled Conoouno Organise Study Location Po« or Noted carbonate, sulfate, iron, dissolved solids, conduc- tance Olehlobenll Llnmeohl tus BSA — 13.BO (SB) ».b»,c,f, so. (larva. ^J; •nd 1S-?0 «•> silica, calcium, magnesium, sodium, potassium, bicarbon- ate, carbonate, aulfate, Iron, dissolved solids, conduc- tance Olchlobenll Hlcrooterus BSA -- 1Z.5 ITU) •.,b»,c,f, salHoldes 1,1, and silica, calcium, magnesium, sodiun, potasaiua, bicarbon- ate, carbonate, sulfate, iron, dissolved solids, conduc- tance Connents same as above sane as above Reference Wilson, et at (196S), Wilson, et al (1965), ------- Dletilobenll Myalella •zeteca (adult. -• BSA — 8.5 (TO > I Dlchlooenll Hylelta azteea ••dolt, k-« Mt BS» — 2.8 csav) OlcMebcnll Enallaq** sp. BS» (nal»d, 16-7* •a) 12.3 (SBl) 1,1, •iliea, calcium, nagneaiua, sodlun, potassium, bicerbon- at«, carbonate, aulfata. Iron, dissolved solids, conduc- tance •,b«,c,r, 1,1. and silica, calcium, •agneslun, •odium, potassium, bicarbon- ate, carbonate, sulfate. Iron, dissolved solids, conduc- tance a,D».e,f, 1,1, and silica, calcium, magnesium, sodium, potassium, bicarbon- ate, SMC »s sbove Mllson, et al Il, •HIC-Sl.52 as above Wilson, et saae as above Wilson, et • I (19691, ------- I ToxIclTy, Experimental Active Variables, Fl^ld Field Ingredient, Controlled Compound Organls" Study Location ._ Pp» or Noted Comments carbonate, solfata. iron, dissolved solids, conduc- tance DlcMobenll Fnallaqaa SP. BSA — 20.7 tT«»> m»fbV,c,r, sa«« as abov« (naiad, 16-Z* 1,1, and ••) silica, calcium, magnesium, sodium, potassium, bicarbon- ate, carbonate, sulfate. Iron, dissolved solids, conduc- tance Reference Wilson, «t al (1969), «HIC-S«.52 DlcMobonll Olchlobenll Olehlobenll Dlchlobcnll Gamnarus fasclatus RSA 18.0 (T2), 10.0 a» Orconectes nals Paleonontes BSA kadlakensls •sellus BSA brevlcaudus 9.0 (T2I 8» BSA — Of the aquatic weed herbicides evaluated, Olclone was the most toxic, Oaonnla was qenerally the most sensitive orqanlsm. All of the Crustacea Mere affected by much lower concentration levels of herbicides than indicated by the TL sub SO values. All of the animals represent Import ant food chain links. same as above Sanders (t<970>. Sanders 3 ------- Olehlobenll Dlchlobenll Olchlobenll Dlehlone Daohnla magna BS» — Cyorldopsls BSA vldua Leoomls BSA •acroehlrin Sal«o BCFA galrdnerl and BSA 10.0 CT21 7.a a,c,e,f, bard IHWJ or soft ISW) syn- thetic dilution water, or seawater for some opeeles OleMon Gammarus BSA fasclatus 0.21. (T2), 0.10 a* Olchlone Olehlon* Olchlon* OieMon* Palconiontes Asrltus BS» Orconectes BSA nals Daphnla «aqna BSA — fl.1.5 (T2) 0.20 (T2) 3.2 IT2) 0.025 (T2> san« as above sane as above sane as above Sanders 11970) , AMIC-1,53 Sanlers same as above sane as above same as abova One hundred sixty-four pesticides, wetting agents, and miscellaneous water pollutants shooed a Hide range of toxlcity scanning 12 orders of magnitude. Knotting the toxlcity and percentage of all eoitoonents of a formulation did not result in easy predictability of the toxlcity of a mixture of materials. Sometimes pesticides Mere most toxic in hard Mater and sometimes the ooooslte was true. Testing the actual material as sold Has found to be essential. Of the aauatlc Meed herbicides evaluated. Olclone was the most toxic. Daphnia Mas generally the most sensitive organism. All of the Crustacea Mere affected by much lower- concentration levels of herbicides than Indicated by the TL sub SO values. All of the animals represent Important food chain links. same as above AMIC-«t53 Sanders I19TO) , AHIC-i.53 Alabaster (1959), AHIC-5V25 Sanders <1970>, AMIC-1.53 Sanders C197P), ANIC-1.53 Sanders <197t» • AMIC- same as above Sanders ------- Compound OrqanlSM vldua Field Field Study Location Toxlclty. Active Ingredient. Ppa Experlaental Variables. Controlled or Noted Coaioents Reference (19701. Olchlon* leooals •acrochlrus BS» — 0.12 sane as above Sanders <197d>, OlcMorfenthlon •asbora BCFA heteroporoha and BSA 1.9 (T2) i Oichtorfenthlon ftasbora BCFA heteroMorptta and BSA Z.I IT1) •»»»f. One hundred sixty—four bard (HW) pesticides, wetting agents, and or soft Mlscellaneous water oollutants showed a wide range of toxlclty soannlnq 1? orders of Maqnltude. Knowlnq the toxlclty and percentage of all covoonents of a (emulation did not result in easy predictability of the toxlclty of a Mixture of Materials. SoMetiws pesticides Mere most toxic In hard Mater and soMetiaes the opposite was true. Testlnq the actual Material as sold Mas found to be essential. saae as above Alabaster (1969), ffn- thotio dilution KBtor, Or •mtrator fOr aXNM •paelea hard (HW) or soft (Stf) fjn- thotie ••tor, or •ewtmtor for aoo. Alabaster 11469). ANIC-5W25 Oletilorfenlhlon Rasbora BCFA heteroBorpha and as (.73 ITZ) Dlchlore«hen (Na «altl Salao qalrdnerl BCFA and BS* O.Z2 tT2> hard'(Hw) or aoft (SO «jn- tfaatlo dUutloa «atr( or •eawater for-aoa« •p«oi« a,c,e,f, hard IHMIor saae as above Alabaster (1969). saae as above Alabaster 119691. ------- Olchlorophen INa «alf> Rasbora heteromorpha 8CFA and BSA 9.19 (T2t soft (SH> synthetic dilution water, or seawater for son species a»,c,e,f, bud (HW) or soft (SO syn- thetic water, or seawater for tome •pecle* sane as above Alabaster (1969).A1IC- I Olchlorvo* Rasbora heteromorpha BCFA and RS* (TZ) Oleldrln 115 percent Rasbora N.O.I hat«ro»orpha BCF» •nd BS» t.a Dlaldrln Dial OrIn Fish (net specified) Poocllla latlolnna BCr» — hard (HW) or SOFT(SH) synthetic dilution water, or seaitater for so«« species a>,c,etf. hardCHW) or soft (SHI synthetic dilution •ater, or seauatar for so»e species qreater than B.D01-0.01 (K) 0.003 (partial a* K?) On» hundred sixty-four pesticides, M»TTlnq sqents, and miscellaneous Hater oollutants showed a Hide range of toxlcity soanninq 12 orders of maqnltude* KnoH(n<\| thi* toxlclty and percentage of all coxoonents of a formulation did not result In easy predictability of the toxlcity of a •Ixture of Materials. Sometimes pesticides Mere most toxic In hard water and soretlaes the opposite was true. Testing the actual Material as sold was found to be essential. sane as above Alabaster (1969), Alabaster Approximate toxlcltles of Nawdeslev- numerous pesticides conaonly used In Thoaas(197t) Britain were summarized. An excellent AMIC-1056 brief, general discussion of toxicity testing is also present. Studies ware conducted with fish Lane, «t al weighing 2-5 g in saawater at a (1970), ------- Compound Field Field Organise Study Location Toxtclty, Active Ingredient, Experimental Variables. Controlled or Not« ------- (SB) ctal (1971), Oleldrln Larqe»outh bass FRL Hlse. states 0.01-1.59 residue (SB) same as above Henderson, Ft al (1971), »MIC-l«i07 Oleldrtn Brown bulI head FRL Misc. states 0.01-0.25 residue ISB) sane as above Henderson,et •I (1971), AHIC-1<.7 Oleldrln Carp FRL Misc. states O.fll-O.S* residue (SB) same as above Henderson, etal (1971), r Dleldrln Oleldrln Channel . FRL Misc. states 0.01-0.36 catfish residue (SB) Rdhorse FRL Misc. states 0.01-0.1? sucker residue (SB) sane as above same as above Henderson,et al (1971), »MIC-H.t»7 Henderson, et al (1971), Oleldrln Gizzard shad FRL Misc. states 0.05-0.50 residue (SB) sane as above Henderson,et al Dleldrln Sootted sucker FRL Misc. states 0.30 residue (SB) sa«e as above Henderson,et al (1971), Oleldrln Blueqllts FRL Misc. states 0.01-0.9; residua (SB) sane as above Henderson,et al (1971), »MIC-1<»07 Oleldrln Redbreast FRL Misc. states 0.01 residue sunfish (SB) same as above Henderson, et at (1971), •MIC-1W07 Dleldrln Striped mullef FRL Misc. states 0.02-0.39 residue (SB) same as above Henderson, et al (19711, 4MIC-1I.07 Oleldrln Rock bass FRL Misc. states 0.07 residue (SB) same as above Henderson, et al (1971), 4MIC-1U07 Oleldrln Bloater FRL Misc. states O.fl?-0.37 same as above Henderson,et ------- Conoound Oleldrin Oleldrin Oleldrin Oleldrin Oleldrin Dleldrln Oleldrin Dleldrln Dleldrln Oleldrin Dleldrln Organise Lake nnltef Isn Lake trout White crapole Blqiiouth buffalo SnallHOuth buffalo Flathead catfish Goldeve Ha II eve Sauger Flannelnouth sucker Freshwater drum Field Study FRL FRL FRL FRL FRL FRL FRL FRL FRL FRL FRL Toxlclty, Experimental Active Variables, Field Ingredient, Controlled Location Pp or Noted Conaents residue (SB) Misc. states 0.03 residue -- saae as above (SB) Nlsc. states 0.02 residue — saae as above (SB) Misc. states 0.02-0.27 — saae as above residue (SB) Misc. states O.fl-0.42 ~ saae as above residue (SB) Misc. states 0.12 residue — - saae as above (SB) Nlsc. states 0.03 residue — saae as above (SB) Misc. states 0.01-0. OS -- saae as above residue (SB) Misc. states 0.01-0.03 — saee as above residue (SB) Misc. states 0.01 residue ~ saae as above (SB) Misc. states 0.01 residue -- saae as above (SB) Misc. states 0.0l\|. residue — ••»«> >» above (SB) Reference al (1971). H enters on, et • 1 I107i>, AMIC-H.07 Henderson, etal (1971), AMIC-H»0T Henderson, «t al »MIC-1«»07 Henderson, et Hi (1971), AMIC-1»07 Henderson, et el 11171), AMIC-ll.07 Henderson, et el (1971), »Mir-iuo7 Henderson, et al (1971), AMIC-1V07 Henderson, et al (1971), Henderson, et al (197U, AMIC-1W07 Henderson, et al (1971), AMIC-IVOT Henderson, et •1 (1971), AKIC-IU07 ------- Oleldrln Black FRL HIsc. states 0.01-0.03 bullhead residue (SB) sane as above Henderson,et 81 (1971), MIC-11.07 . Oleldrln Oleldrln White bass FRL Misc. states 0.02 residue (SB) Black crapole FRL Misc. states 0.02-0.36 residue (SB) saae as above save as above Henderson, et 81(19711, MIC-1<.07 Henderson,et al (1 ------- Coaioound Dieldrln Dleldrln Dleldrln Dleldrln Eleldrla Dieldrln Dleldrin Oleldrln Dleldrln Field Field Organise Study location Ict&lurua FRLO Iowa punctatua Ictlobus FHLO Iowa cyprlnellus Cyprinua FRLO Iowa carpi o Hicropterus FRLO Iowa sal no Ides Carplodea sp HILO Iowa Pomoxia FRLO Iowa nlgronaculatua Pomoxls FRLO Iowa annular! a Stlzostedlon FRLO Iowa vl treuii Tsox luclus FRLO Iowa Toxlclty, Active Ingredient, 0.03H.6 ( accumulation, SB) 0.028-0.614. (accumulation, S3) 0.015-0.56 (accumulation, SB) 0.11-0.08 (accumulation, SB) 0.313 (accumulation, SB) 0.012 (accumulation, SB) 0.059 (accumulation, S3) 0.01-0.06 (accumulation, SB) 0.05 (accumulation, SB) Expert Mental Variables, Controlled or Noted Consents JSdlble fleah of flah collected from rivers, lakes, ponda, and reservolra waa analysed. Flab taken in areas receiving agricultural runoff showed bigheat accumulation, especially In bottom feeding flab. — Sane aa above — sane aa above — sane aa above same as above same aa above same aa above sane as above -- saee as above Reference Horrls, et al (1971), AKIC-1US2 Morris, et al (1971), AKIC-114.52 Korrla, et al (1971), Morris, et al U971 j. Korrla et al 11971), Korrls, et al i 1971), AK1C-1U52 Horrla, et al (1971;, AKIC-U.52 Horrls, et al tl97t>. Horrls, »t et 152 ------- Dleldrin Dleldrfn Dieldrln Dieldrln Xctalarus PRLO low* •elas Lepomls FHLO Iowa Bacrochirua Esoz luclus PRLO low* Roccua FRLO Iowa 0.098 (accumulation, SB) 0.01I4.-0.03U (accuaulatlon, SB) 0.05 (accumulation, SB) 0.091-0.175 (accumulation, SB) aua as above aaaa as above MOM as above sane as aboTa Korrls, et al (1971), AMIC-U4.52 Korrls, et al (1971). AKIC-ll;52 Korrls, et •1 (1971). AHIC-11^2 Morris, et al (1971), I Oleldrln 011drln Oleldrln Anacystis nidutans Oleldrln Oleldrln lloatui Leptodlus f I or I (Janus (larvae) a ^^ l_ •••» P»nopnus ncrbstll Clarviif) Llaneohllus rhOBblcui (Iarvael • —^ FS 0.5-1.8 (qrowth a»,c»,r Inhibited) SN 0.5-1.0 (groMth e,c.r Inhibited) SH 5-10 ppb(K) ~ 5-10 DPb (K) — O.OBZ(Mhole Creek, Oun body residue) County, Misc. Batterton, etal Batterton, et al (19711, Metabolic products of Al ------- Comooun* Organism Field Field Study Location Toxlclty, Active Ingr«di«nt, Ppm Exoerlmental Variables, Control led or Noted Comments Reference Oleldrln 01 eldrIn 01 eldrIn Oleldrln Oleldrln Oleldrln Oleldrln Oleldrln Oleldrln Stalls so. FS (larvae) Gamaarus sir* FS Salvellnus FS Iontlnalls Senotllus FS atromaculatus Cottus balrdl FS Rhlnlehthys FS atratulus Salvellnus FS T ontlnalls Semotllus FS atromaculatus Cottus balrdl FS Knights Creek, Dun County. Misc. Knights Creek , Dun County. MISC. Knights Creek, Dun County,Misc. Knights Creek, Oun County, Hlsc. Knights Creek, Oun County, Misc. Knights Creek, Dun County,Wise. Knights Creek, Oun County,Misc. Knights Creek« Oun County. Wise. Knights Creek, Oun 0.01T (nhotebody residue) 0.005-0.01! (xholebody residue) 0.008-0.011. (uhole body residua) 0.006-0.013 (whole body residue) 0.007-0.017 (whole body residue) 0 (Mholebody residue) 0.18-0.?6(fat residue) 0.17-0.3* (tat residue) 0.3-0.7 (fat residue* 0-0.005 DDK dleldrln. Fndrln residues ot 0.011-0.0?5 opin and O.OOZ-0.006. DP* dleldrln were tound In debris samples.' OesDlte United control data, residue analyses Indicated that contamination of the environment studied Has United. same as above sane as above same as above same as above same as above sane as above same as above same as above same as above Moubrv, et al (H6S), tMIC-3751 (•oubry, et al <1"6). AHIC-37SJ Houbry, «t al Koubrv, et al (19SB) .AHIC- 3751 Houbry, et al (11691, 4HIC-375J Moubry, et al (19SA1, Moubry, et al (1968), 4MIC-375J Noubry, et al (1968). AMIC-37SJ Moubry. «t al (1968). ------- Dleldrin OlelOVln fthlnlehthys atratulus Leooals cyanel I u FS County, Mice. Knights ( (fat CreeK, Dun r«sldu«> County.Mlsc. L — 1.106 (K9I Ololdrln Oleldrln Oleldrln leooals cyanIIus L — cyanelIus Fa Ico F peregrlnus (eggs) Woctorn o.s.. Pacific $.7 (blood resIduo) 10.1 (brain recldu) 0.11 (roslduc) — Haxloo, and Antarctic SOKO as above Tho blood and brains of groon sunflsh that dld duo to exoosurc to Oicldrln were analyzed for this ch«ntcal« Survlvlnq »Ish had less Ololdrln In blood and brains than dead fish. Severity of ooisonlng syaptoas also correlated with Oleldrln concentration. Extraction efficiency froa blood and brains Mas quite good (92-95 percent). sane as above sa«e as above •NIC-3753 Moubrv, «t at (1968) i •HTC-S753 Haqan, et al (1971J, Hoqan, et al Hogan, et al f H7H.MIIC- 382". Hereqrlne falcons, falcon prey, 3ist>rouo,h( and other predator species Mere collected et al Mldely and analyzed for DDT, OOF. PCR. (1468). and a feM other pesticides to a lesser (MIC-3BM degree. PCR and OPT Mer* found to be Mldely dispersed globally. PC9 MBS found to be a powerful Inducer of hepatic enzymes that degrade oestradlol. Reductions In thickness of egg shells. eggshell weight, and Hater retention occurred. All affect hatching success. Tho authors state that the peregrine aay bo the first species entlrpated by global contamination. Olaldrln •quit a chrysaetos (eggs) Western U.S.. Pacific Ocean. Panana, Mexico, and Antarctic 0.007 (residua) sane as above Risebrough, et al AMIC-38«.<. ------- ro Conoound Olelarlr. Dletdrin Oleldrln Orqanisn Fa Ice peregrlnus denature) Falco pcreqrlnus (adult) Falco pereqrlnus (adult) Field Field Study Location F Western U.S., Pacific Ocean, Panama, Hexlco,and Antarctic F Western U.S., Pacific Ocean, Panama, Hexico.and Antarctic F Western U.S., Pacific Ocean, Parian a. Mexico, and Antarctic Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppn or Noted Comments 0.07-1.6 (Tat -- sane as above residue) 0.31-3.7 (flesh — sane as above residue) O.I.1.-62.5 (fat — sane as above residue) Ref erence Rlsehrouqn, et al (196S), AMIC-38H Rlsefcrou^n, et at (1968), AHIC-3»«t<. Rise&rouqh, et al (1968). ANIC-36i.il 01 el dr In Olcldrln Oleldrln Oleldrln Endonychura craverl (eqqs) Petecanus occidental Is (eqgs) Sula leucoqaster leqqs) Fa I CO Western U.S., Pacific Ocean, Panama, Mexico,and Antarctic Western U.S.. Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ooean, Panama, Mexico, and Antarctic Western O.Ot (residue) — same as above 0.06-0.16 (residue) O.Od-0.18 (residue) sane as above sane as above Rlsebrouqh, et il sale as above AHIC-3M.I Rlsebrough, et al (196SI, AMIC-38I.^ Rlsebrouqh, et al (!<»*), tMTC-38l»l> Rlscbrough, ------- peregrlnus (Immature) Oleldrln > Oleldrln Oleldrln Oleldrln U.S.. Pacific Ocean , Panama.Mexlc o. and Antarctic (flesh residue) Chlamydotheca BSCH — arcuata and Chlamydotheca a Hh) 0.021.5 (Tl) 0.00001-0.001 (1.9-126 ppb residue 33-8 HK) 0.39 (A3 oercentKZ) et al (1968) 381.". KaHatskl. et al (14711. NIC-550S The organisms «er» exposed to O.ni and O.J oob of the toxicants for Hecks after which time the amounts each tueeK H»re Increased ten-fold over the Initial amounts. Ulothrlx occurred spontaneously In the test tanks. The results shOH that chronic accumulations In Chiamyrtotheca exceeded levels which were toxic In acute tests. Residues In Chtanydotheca ranged fro* 12.000 to 260.000 tines greater than the theoretical concentrations in the Materi those in Ulothrlx Mere 7^^-3,000 tlaes exposure levels. same as above save as above The response of Naavl. et al- pesticide-resistant aquatic organises to (1969). various pesticides was compared to the «HIC-5979 resoonse of non-resistant species. Pesticide-resistant species Here collected at Relzonl and non-resistant species at State College. Copepods. clams, snails, and sludge worms from Belzonl Here considerably more tolerant to Pesticides than the non-resistant organisms. The authors note that the effect of Increased tolerance in the organisms Is an Increase in the aaount of pesticide residues available to animals of higher trophic levels. KanatsVcI, et al(l«7l), «MIC-550(> KawatsKl, at a I (19711, ------- Compound •Oleldrln Oleldrln Oleldrin Oleldrln Oieldrln Oleldrln Organise Tublfex tublfex Pnysa qyrlna Physa qyrlna Copepo«1s (Cyclops bicusoldus. Cvclons varicans. Cyclop-; vernal I«s, Eucyctoos sgllls. albMus, Orthoeyel ops •odes tut) Coo»po B5A AHIC-5979 FL Belzonl, 0.40 (39 -- saae as above Naavl, et and Hiss percent K2> al(1969), BSA t1IC-5979 L — ».&<» (T2) — The effect of 52 pesticides on Davis, et a embryonic development of clams and oysters t»as reported. Synerqlstlc (1969), AMIC effects Hitn solvents Here also reported. Most of the compounds affected develornent «ore than survival. Soae, however, drastically reduced larval qroxth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an organise and not the possibility of 5990 ------- Dleldrln Dleldrln Oleldrln Dleldrln Oleldrln Dleldrln Oleldrln Oleldrln CP assostrea vlrqinlca (larvae) Ganbusla •f finis (foal. cut 1.9 8SA greater than 10.0 0.031 ITI>) .3 BSA BSA Lehlst« reticulatus (male, l.a cm, 0.7 g) TMaoia •ossanblea (3.1. cm, 1.3 9> Kuhlla BSA sandvlcensls («».3 cm, 1.9 9> Stolephorus BSA purpurea 13.6 cm, 0.* g> Agonus BSA cataohractus 0.007 (Tl>) 0.010 (T«.l 0.002 (T<>) O.D05 (T 12 HR) 3.3 IT2) Carelnus BSA — 0.01-0.03 (TZ> selecting ehcmlcats for pest control that Mould not have serious effect on shellfish. same as above Davis, etal (1969), a,c,d,e. The five fish species are •ff»l» commonly found In streams and estuaries al (1970). (Honolulu In seml-troolcal areas. C. affinis Has tap the most tolerant. Varied sensitivity to wator) the toxicants Mere found. K. sandvicensls Mas the most sensitive fish studied. The standard method procedure Has folloned. et a,c,d, e.JT.i. (Honolulu tap water] a,c,d, (Honolulu tap water) a.Cid.e,ft l.salt Hater a>c,d,e,f , 1, salt Hater a«(contin- uous aer- ation, sea- water, and daily solution renewal) same as above same as above same as above same as above a«( contin- uous aer- ation, sea- water, and daily One hundred-forty surface active agentst solvent enulsIfters« oestlctdeSt polychtorlnated blohenyls, pure Inorqanlc* and organic chenicals Mere evaluated against as many as ten irarlne organisms. The authors noted that most published data of this type deal with toxlclty of chemicals to freshHater organisms. same as above NunoaiHa, et al (1970), AHTC-SSS7 NunooaMS, et al (1970). ANIC-6567 Nunoqanai et al (1979), AHIC-65&7 Nunogawa, et al (1970). AXIC-6567 Portrann, et al (1971), »«C-7701 Portmann, et al (1971), AHIC-7701 ------- CoHOound Field Field Organism Study Location Toxiclty, Active Ingredient, Ppm Experimental Variables, Controlled or Noted Comments Reference solution renewal ) Oleldrln Cardlum edule BS» •— areater than a(contin- uoug aer- ation, sea- vator, and daily solution renewal ) same as above Portfann, «t al 11971), •HIC-7701 Oleldrln Crangon eranqon BS» 0.01-0.03 (T?) •«(contin- uous aer- ation, sea- wator, and daily solution renewal) same as above Portmann, et al (1971), 4HIC-7701 Oleldrln Freshwater drum FL Oleldrln Aleutf FL Great Lakes (Ontario, Huron, Erie, Superior, Michigan) D.0<» (whole body residue) Or eat Lakes- 0.09-0.97 (Ontario, (Hhote body Huron, residue) Erie, Superior, dupanor, Michigan) Fish from Lahe Mlchlqan contained Pelnert 2 to 7 times more DOT (and DDT analogs) (1970),AHIC- and (Heldrln residues than fish from the 196 other Great Lakes. Fish from Lake Suoerlor Invariably had the lowest accumulations of both chemicals. The compounds tended to concentrate In fat (oils). Considerable additional data are presented. The author noted the need to reduce pesticide usage to a minimum and to replace these Insecticides Mlth less persistent materials. same as above Reinert <1970>,»tIC- 196 Oleldrln American smelt FL Great Lakea (Ontario, o.oz-o.io (MhoI* body same as above Relnerr (1970), ------- Huron, Erie, Superior, Michigan) residue) 196 Oleldrln Bloater FL Great Lakes D.03-1.07 (Ontario, (whole body Huron, residue) Brie, Superior, Michigan) sane as above Relnert (1970),»NIC- 196 Oleldrln r ro Broxn FL Great Lakes 0.00 (Hholebody bullhead (Ontario, residue) Huron, Erie, Superior, San* as above Relnert (1970).AMIC- 196 OUpfJXJ.OZe Michigan) Oleldrln Channel FL Great Lakes 0.07 (whole catfish (Ontario, body residue) Huron, Erie, Superior, Michigan) same as above Relnert (1970),»MIC- 196 Oleldrln Coho salnon (flesh) FL Great Lakes (Ontario, Huron, Erie, Superior, Michigan) O.OKxhole body residue) sane as above Reinert (1970),»HIC- 196 Oleldrln Coho salnen (eqqs) FL Great Lakes (Ontario, 0.0<» (whole body residue) sane as above Reinert (1970),AMIC- 196 ------- COHDOUIV) Field Field Organise Study Location Toxiclty, Active Ingredient, Pom Exoerlmental Variables, Control led or Noted Comments Reference Huron, Erie* Superior, Michigan) Oleldrln Gizzard shad FL Great Lakes (Ontario, Huron, Erie, Superior, Michigan) o.o<»-o.09 (whole body residue) sane as above Reinert (1970), 196 Oleldrin Klyl FL Great Lakes 0.28 (whole (Ontario, body residue) Huron, Erie, Superior, same as above Reinert (1970),»HIC- 196 dupanoz", Michigan) Oleldrin Lake herring FL Great Lakes 0.02-0.07 (Ontario, (whole body Huron, residue) Erie, . Superior, Michigan) same as above Reinert 11970),»WIC- 1S6 Oleldrin Lake trout FL Great Lakes (Ontario, Huron, Erie, Superior. Michigan) 0.05-1.13 (whole body residue) same as above Reinert (1970),«HIC- 196 ------- Oleldrln Lake Ft Great Lakes O.oz-o.W whltetlsh (Ontario, (Hhott body Huron, residue) Brie, Superior, Michigan) saae as above Relnert 11970),MIC- 196 Dleldrln Rock bass FL Great Lakes o.oz (whole (Ontario, body residual Huron, Brie. Superior, Michigan) saae as above Relnert (1970),AMIC- 196 r 10 8 Dleldrln Round whiterIsh FL Great Lakes (Ontario, Huron, Erie, Superior, Michigan) 0.03 (whole body residue) saae as above Relnert t!970»,»HIC- 196 Dleldrln Sea tanprey FL Great Lakes (Ontario, Huron, Brie, Superior, Michigan) 0.02 (whole body residue) saae as above Reinert .At1IC- 196 Oletdrln SI lay sculaln FL Great Lakes (Ontario, Huron, Brie, Superior, Michigan) 0.0 (whole body residue) sane as above Relnert (1970),»MIC- 196 Dleldrln Nlne-splned stickleback Great Lakes (Ontario, O.OZlHhole body residue! saae as above Relnert (1970),AHIC- ------- Compound Field Field Orqinls* Study Location Huron, Brie, Superior. Michigan) Toxlelty. Active Ingredient, PD» Exoerlnental Variables, Control led or Noted Comments Reference 196 Oieldrln f g ualley* FL Great Lakes 0.08-0.13 (Ontario, (whole body Huron, residue) Erie, Superior, Michigan) sane as above Relnert (1970),»MIC- 196 Oieldrln ~MtrtT« bass FL Great Lakes O.Oit-0.10 (Ontario, (whole body Huron, residua) Brie, Superior. Michigan) sane as above Relnert (19701,AMIC- 196 Oieldrln White perch FL Great Lakea (Ontario, Huron, Brie, Superior. Michigan) 0.10 (whole body residue) save as above Relnert (19TO),nIC- 19 Oieldrln White sucker FL Great Lakes (Ontario, Huron, Brie, Superior. Michigan) 0.02 (whole body residue) sane as above Relnert (1970),»MIC- 196 ------- Oletdrln Vet I OH perch FL Michigan! Greet Lakes (Lake Ontario, LaKeHuron, LakeErle. Lake Superior, Lake Michigan) 0.03-0.07 (Hhole body residua) Dleldrln Wolffla papullfera. Olethyl-OL-tartarate Plnephales 8S» — proaelas Olethyl fumarate Olethvl fumarate Olethyl aaleate Olethyl succlnate Olfolatan Pimephales proar I as Plaephales proaelas Plmephales proaelas Plmephales proaelas Dlfolatan 100 (K) 650.0 CTI.) Hunter's medium diluted 1:5 a,d,e,o, and Fe BS» — 8CFA BSA BSA Brachydanlo L rerlo (larvae) "..5 Z.S (Til.) 18.0 (Ti>) 1VO.O (Td) 1.0 (T 30 aln) and Fe and F« and Fe a,d.«,o. •nd Fe Rasbora 8CF» hetereaerpha and BSA 0.032 (Tl) a'.c.e.f, hard (HH> or SOFT(SH) synthetic dilution saae as above Relnert tt970)tHIC- 196 All compounds were harmful to tforthley, et duckweed to sone degroe. Decreased al (1971), populations were noted at non-lethal AKIC-3233 concentrations and some compounds (Malathlon and 2,li-D) caused teratogenlc effects at concentrations as low as 1 ppm, Malathlon and Its hydrolysis Mender products Here evaluated with the finding (19.69) ,AHIC- that one such product (diethyl fuaarete) 3787 Mas more toxic than Malathlon to fathead •Innows. Synrrqlsm occurred between Malathlon and two products of hydrolysis. Continuous exposure resulted In Increased toxiclty. sane as above Render (1969),MIC- 3/8T sane as above Bender (19>9), above sax as abov» Bender (14I>9) 3787 Bender(iq«q) HIC-37«7 Folpet, OHolatan, and Captan Abedi. et Mere found to be toxic to zebraflsh altl'Jf.B). larvae xithln 90 nln. Dlfolatan Mas aost AHIC-3717 toxic while Raptan was least toxic. Effects observed Here cessation of heartbeat and loss of plqment at Ion. The authors recommended this as a sensitive, raolr) bloassay for these and related coapounds. One hundred sixty-four pesticides, wetting agents, and alscel laneous Hater pollutants showed a Hide ranqe of toxlcity spanning 12 orders of aagnltude. Knowing the toxlcity and percentage of all components of a Alabaster (19S3), Hater, or formulation did not result In easy ------- Coaoound Organise Flald Field Study Loot Ion Toxlclty, Active Ingredient, Pp« Experimental Variables, Controlled or Noted Comments Reference Olfolatan Rasbora BCFA heteromorpha and BS« 0.017 CT2) Oloanln Rasbora BCFA n«feromorpha and BSA 3.3 (T2) Dlmecron Puntlus tleto — 0.1.1 (TV) Olaethoate Fish (not specified) greater than 10-100 ------- OlawTheat Sal mo galrdnerl dCF* and BSA 9 I TZI Olmthoate Carclnus aaenas BSA — greater Than 3.3 CTZI OlMthoat Car ill urn edule BS* — H.3 (TZI «,C,e,f, hard (HW) or soft (StfJ thatle water, or •••water for aomo •pacles a«(centln- uoua cer- ation, sea- water, and daily solution renewal) a«(contin- uous aer- ation, sea- water, and dally solution renewal) One hundred sixty-four Alabaster pesticides, wetting agents, and (1969), miscellaneous water pollutants showed a ANIC-^?5 wide range of toxlclty spanning 1? orders of mannltude. Knowing the toxlclty and percentage of all components of a formulation did not result In easy predictability of the toxlclty ot a mixture of materials. Sometines pesticides were most toxic In hard water and sometimes the opposite was true. Testing The actual material as sold was found to be essential. One hundred-forty surface active Portmann, agents, solvent emulslflers, pesticides, 81(1971), polychlorlnated blphenyls, nure ANIC-7701 Inorganic, and organic chenlcals were evaluated against as many as ten marine organisms. The authors noted that most published data ot This type deal with toxlclty of chemicals To freshwater organisms. same as above Portmann, « al (1071), ANIC-7701 OlMthoaTe Crangon crmngon BSA — 0.0003-D. (TZI 001 ««(contin- uous aer- ation, sea- water, and daily solution renewal) saae as above Portaann, et al (1971), AN.IC-7701 OlMtttoate Panda I us aontaqul BSA — greater Than 0.03 (TZI a»( contin- uous aer- ation, sea- water, and daily solution renewal) same as above PorTmann, etal (19711, AH1C-7701 ------- ro Toxiclty, Experimental Active Variables, Field Field Ingredient, Controlled Compound Organism Study Location Ppm or Noted Comments Dlmethy lailne Crangon BSA — crangon greater than a(cor.tln- 100 (T2I uous aer- Cne hundred-forty surface active aqents, solvent emulslfiers, pesticides. at ion, aea-ool ychlorinated blphenyls, pure Olnethylphosphorodlt PImephales BSA hole acid oromelas Dloethy 1 phosohorodlt Plmephales BCFA -- hole acid oromelas OlmethylohosDhorothl Plmephales BSA onic acid prooelas Dimethyl formamlde Cranqon BSA — crangon water, and «4n 4 1 XT OAixy solution renewal) 23.5 (Ti») a,d,e,o, and Fe 21.0 (Tli>) a»,d,o,o. and Fe «»2.5 (T4) a»,d,e,o. and Fe greater than a»(contin- 100 (T2> uous aer- inorganic, and organic chevicals were organisms. The authors noted that most published data of this type deal with toxlcity of chemicals to freshwater organisms. Malathion and its hydrolysis products were evaluated with the finding that one such product (dlethyl fumarate) was more toxic than Malathion to fathead minnows. Synergism occurred between Malathion and txo products of hydrolysis. Continuous exposure resulted in Increased toxlcity. same as above same as above One hundred-forty surface active agents, solvent emulslfiers, pesticides. ation, sea-ool ych lorlnitcrt blohenyls, Dure water, and daily solution renewal) Inorganic, and organic chemicals were evaluated against ns many as ten marine organisms. The authors noted that most published data of this type deal with toxicity of chemicals to freshwater organisms. Reference Portmsnn, «t al (1971), AMIC-77D1 Pender (1959) , AMIC-37B7 Bender (1969) , &MIC-3787 Render (1969), AHIC-3787 Portmann,et al (1971), AMTC-7701 OlMthyl phosohate Plmephales prone I as BSA 11.0 (T<>) a,d,e,o, and Fe Halathlon and Its hydrolysis products were evaluated with the finding that one such product (dlethyl funarate) was more toxic than Malathion to fathead minnows. Svnerglsm occurred between Malathion and two products of hydrolysis. Continuous exposure resulted In Increased toxlcity. 8ender(1969>, AHIC-37ST ------- 01•thy I ohosohlte Plmephales croneI as Dimethyl Phormldlum ?»J.6-tefrachlorot«r aiblguum eohth«tte BSA L — 235.0 «T«.) o.5-in.o (33p»rcent growth Inhibited l and F« to Dlmlt Tublfex tublfex Ft and 8SA Belzonlt Hiss. 0.90 (NT?) OInltrobutyl phenol Ganmarus fasclatus BSA 1.8 (T> Olnltroohenylether Phorcldlum amblquu L — 0.9-10.0 (66 percent growth Inhibited 1I>1 same as above Of 7i» chemicals evaluated as alqlcldest only 9 Here more toxic than CuSO<«. None inhibited qrowth of mat-forming algae lor more than 2 weeKs. CuSO» formulated with certain Hettinq agents was more toxic than CuSDi. alone. Cooner chloramlne was also found to be more toxic thar CuSO^. No wettlnn aqents Here found to be inhibitory at trie concentrations Investigated (P»05 and 0.005 Bom). Also reoorted are factors affecting qroith of alqae in canals to determine Mhether there were leads to controlling »ln»p by environmental managetrent. No practical environmental means were found. The response of pesticide-resistant ^nuatic organist's to various pesticides vos comoared to the re^non^e of non-re<:I; tant species. Pesticide-resistant species xere collected at Oelzonl and non-resistant species at State College. Copepods< CMmst snallSt and sludqe Morms Irom Belronl Mere considerably more tolerant to oesticldes than the non-resistant orqanisms. The authors note that the effect of Increased tolerance in the organisms Is an Increase in the amount of pesticide residues available to animals of higher trophic levels. Of the aquatic Heed herbicides evaluated. Dlclone xas the most toxic, Oaohnla Mas generally the most sensitive orqanlsm. All of the Crustacea Mere affected by much lower concentration levels of herbicides than Indicated by the TL sub SO values. All of the animals represent important food chain links. Of 7<> chemicals evaluated as alqlcidest only 9 Here more toxic than CuSO".. None Inhibited gronth of mat-forming algae for more than ? MeeKs. CuSOit formulated with certain netting agents MBS more toxic than CuSO". alone. Copoer chloraolne was also found to be B«nder(1969>< AHIC-V8T Otto 11970). &MTOS92 Naavl, et at USf>t), AHIC-5979 Sanders 11978), Otto (1978) i AHIC-89Z ------- Compound Organism- Field Field Study Location Toxiclty, Active Ingredient, f»r>« Fxoerlmental Variables. Control led or Noted Comments Reference •ore toxic than CuSOfc. No wetting agents •ere found to be Inhibitory at the concentrations Investigated (0.05 and 0.005 com). Also reported are factors affecting arowth of a Icae In ctnals to determine whether th«re were leads to controlling algae by environmental Management. No practical environmental means were found. 3- Olnocao OInoevo Fish (not seed fled) R»shor» RCFA heteromorpha and RSA greater than 0.01-0.1 (K> 0.11 ITZt Olnocao Rasbora BCFA heteromorpha and BSA 0.07 (TZJ »•»«»•.t, hard (HW) or «oft (WJ «yn- tbatle uatar, or •eavater Tor aoma •paola* «»,c.e,. hard (HW) or soft {») syn- thetic dilution watar, or ••awater for some •paclaa Anproxiniit* toxlcltles of Hawdeslev- nuwerous pesticides connonly used In Tnonas Britain wpre summsr 1 i» ------- Olphen»id Olphenaaid Olohenavld Gaimarirs fasclatus BSA — Paleomontes 8S» KadlaKensls Asellus BSA brevlcaudus greater than 100.0 (T2t 98.0 (T2) greater than 100.0 (T?) Of the aquatic H«d herbicides evaluatedt Olelone «as the most toxlcf Daohnla Has generally the most sensitive orqanlsn. All or the Crustacea xere affected by much lower concentration levels of herbicides than Indicated by the TL sub SO values. All of the animals represent Important food chain linHs. sane as above sane as above Sanders (1970). AHIC-WS Sanders 11970) « ANIC- 80.0 (TZ) 1.0 (Tll>) a» sae as above same as above sane as above sane as above San-lers (Iflroi. (.55 Sanders Sanders AHIC-l.53 Sanders (J<)70) , A'HC-'.SJ 70 CTZJ ~ The effect of 52 pesticides on Davis* et at embryonic development of clans and oysters Has reported. Synerqistlc C1969).AMIC- effects Hlth solvents Mere also reported. 5990 Most of the compounds affected develocment more than survival. So«e, hOMevPrv drastically reduced larval qronth. The authors point out the necessity of evaluating the effects of pesticides on all life staqes of an orqanlsn and note the possibility of selecting chemicals for oest control that Mould not have serious effect on shell fish. atc ------- > I Toxlcity, Experimental Active Variables, Field Field Ingredient. Controlled Compound Organism Study Location Pom or Noted Comments Reference SOFTCSWJ synthetic dilution Hater, or seanater for some species Olouat Caltibactls BSA — 16. (T») ••&»»«», SP. {nymoh, 1,1, and 9-12 mm) silica, calcium. magnesium, sodium. potassium. bicarbon- ate, carbonate, sulfate, iron, dissolved solids. conduc- tance Dlouat Ena Magma so. BSA — greater than a»,b»,C,f, (naiad. 16-2* 100 IT) 1,1, «"» mm) silica. calcium, magnesium. sodium. potassium, bicarbon- ate. carbonate. solfate, iron, dissolved solids, conduc- tance Hide range of toxlcity spanning 12 orders of magnitude. KnoHlnq the toxlcity and percentage of all components of a formulation did not result In easy predictability of the toxlcity of a mixture of materials. Sometimes pesticides Here most toxic in hard Rater and sometimes the oooosite Has true. Testing the actual material as sold Has found to be essential. The toxlcity of herbicides Olquat Wilson, et and Oichlobenll to aquatic Invertebrates al f 19%9> , and fish Has determined In aquaria AHTC— SV5? containing substrates natural to each soecies. 01 qua I Has quite toxic to H. az«teca but not as toxic to other organisms. Dlchlohenil Has less toxic to H. azrtecus but considerably more toxic to the remaining organism than Oiauat Hud lessened the toxicltv of both, but more so for Diquat. Oichlobenll had a sublethal narcotizing effect on the organisms that resulted In Immobilization. It Has concluded that both herbicides could adversely affect certain fish food organisms. same as above Wilson, et al (1969), AMIC-SfcS? ------- Olouat Hyal«l 1» azteea (adult, <»-8 8S» — o.os m> a,b,c,f, 1,1, and silica, calcium, magnesium, sodium, potassium, blcarbon- ate. carbonate, sulfate, iron, dissolved solids, conduc- tance saae as above Wilson, et at (19691. • MIC-5W2 I Otouat Libellula sp. BSA (naiad, 16-?". greater than 100 (Tl»t a«.b»,c,f, 1,1, and silica, calcium, magnesium, •odium, potassium, bicarbon- ate. carbonate, sulfate. Iron. dissolved solids, conduc- tance sane as above Wilson, et at (19691. Olouat LleneoMlus so. (larva. 1S-70 ••) as — 33 (TV) «,b«,c,f, 1,1, and silica, calcium, magnesium, sodium, potassium, bicarbon- ate, carbonate, sulfate, iron, sane as above Wilson, et al (1969). AMIC-51.5? ------- Toxlelty, Active Field Field Ingredient. Compound Organise Study Location Ppn Experimental Variables. Controlled or Noted Consents dissolved solids, conduc- tance Reference Olouat Tendluedldae BSA — (larvae. 7-10 greater than 100 (T4»> a,b»,c,f, 1,1, and silica, calcium, magnesium, sodium, potassium, bicarbon- ate, carbonate, sulfate. Iron, dissolved solids, conduc- tance same as above Wilson,et al (19491, Oiquat Oiouat Roccus BSA — saxatitls (fIngerlInqs) Hya arenaria f Nomlnl CreeK, Va. 80 0.35 (SB) a«,c,d,e, Striped bass f Inqerl Inqs Here Wellborn f,p, and aooarently nuch more sensitive to (1969). Iron therapeutic and herblcldal compounds than AMIC-5723 many freshwater fish. Consistent absence of Diauat In Haven edible Parts of clans and oysters Mas 11959) , recorded. Residues In Intequnent of clam S97g siphons MBS believed to be due to soil particles trapped In folds of tissue. No Dlauat Mas found in water due probably to rapid adsorption by silt and bottom mud. Residues persisted for nearly one year In bottom mud. Olouat Crassostrea vlrglnlca Nonlnl Creek. Va. O.J5 (SB) same as above Haven (1969).AHIC- ------- Olouat DIguat Myrloohlllum splcatu* No«lnl Creek, Va. 0.35 (1.0-70 percent K36) same as above Card turn «dule BS» — greater than 10 a«(contin- One hundred-forty surface active IT?) uous aer- agents, solvent emulsl'lers, pesticides, atlon, ssa-polychlorlnated blohenyls, pure water, and inorganic, and organic eheirlcals were dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. Olouat Crangon crangon BS» — f e greater than 10 a«(eontin- uous aer- ation, sea- water, and daily solution renewal] Olsoersol SO Aqonus cataohractus 8S» ~ 100-330 (TV) a«(contin- uous aer- ation, sea- water, and daily solution renewal) sa»e as above sane as above Haven (I«f69» . AMIC-5978 Portnann, et al Portwann, et al (1971), AMIC-7701 Portnann. et al 11971), AH1C-7701 Dispersal SO Crangon erangon BS» — 3300-10(000 ITZ) atcontin- uous aer- ation, sea- water, and dally solution renewal) sane as above Portnann, et al (1971), Olsulfoton Oluron Fish Inot sptclf14> Hercenarla •ercenarla greater than 1.0-10.0 IK) 2.5 (TZ) Approximate toxlcltles of Haiidesley- nu«i>rous pesticides commonly used In Thomas(1971l Britalr Mere summarized. An excellent AMTC-I056 brief, general discussion of toxlclty testing Is also present. The effect of 52 pesticides on Oavls, et al embryonic development of clams and oysters Has reported. Synerglstlc 11969),AHIC- effects with solvents Mere also reported. 5990 Host of the compounds affected ------- Compound Organism Field Field Study Location Toxlclty. Active Ingredient, Ppm Experimental Variables, Control led or Noted Comments Reference Oluren Oluron Mercenerla •ercenarla (larvae) Cammarus fasclatus BSA greater than 9.0 IT12) 0.70 «T<»> 01-lsobutyl ohenoxyethoxyethyl dimethyl benzyl aaeonlu* chloride Phormldlum emb i guum 0.5-10.0 (16 percent growth inhibited l«t) OI-ft-butyl tin oxide Creoidostomua L terlonls 150 {oral dose, ~ Kl) development more than survival. Some, however, drastically reduced larval growth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that would not have serious effect on shell fish. same as above Davis, et Of the aauittc weed herbicides evaluated, Dlclone was the most toxic, Daohnia was generally the most sensitive orqanlsm. Alt of the Crustacea were affected by much lower concentration levels of herbicides than indicated by the TL sub 50 values. All of the animals represent imoortant food chain links. Of 71, chemicals evaluated as alglcldes, only 9 were more toxic than CuSOi. None Inhibited growth of mat-forming aloae for more than ? weeks. CuSO"t formulated with certain wetting agents was more toxic than CuSO.it alone. Copper chloraiMne was also found to be more toxic than CuSO<>. No wettlno. agents were found to be inhibitory at the concentrations Investigated (0.05 and O.OOS ppm)« Also reported are factors affecting growth of algae in canals to determine whether there were leads to controlling algae by environmental management. No practical environmental means were found. Capsules containing the tin HItchua, et compound were administered to the trout al (19691, by force feeding. The tin comoound was AHIC-5730 effective against the Intestinal fluke but erytnromycin was not. Residue analyses indicated tin was not readily Sanders (19701. AMIC-53 Otto (1970), AMIC-89Z ------- Dl-n-butyl tin oilde Salmo •quabonlta fe U) 01-Systofl 01-Syston 01-Syton OI-Sysfon Mercenarla •ercenarla (eqqs) Mercennrla mereennrle Itarvac) Crassostrea vlrqlnlca (eqqs) Crassostrea vlrqlnlea (larvae) L — L — 01 IN. M d\|ethyl cocoaIne salt of •n do that I (ethyl bis) (?-ethylhexy«) phosphl na te7-oxabicy ele I?.?.II heptane-?,3-dlcarbo» yllc acid) Phormldlum amb1quua 100-600 (oral — dos«t NTC1 5.28 IT2) 1.39 9.86 ITZ) 3.67 (TIV) 8.5-10.0 CNTE> — 01 IN, N dimethyl Phormldlua L trldecyl amlne) salt of endothall ONOC Fish Cnot — ~ 0.5-10.0 (0 percent growth Inhibited 1<») than absorbed by tissue outside the Intestinal tract and that the coaoound was raoldly eliminated. Tissue residue and retention tine studies Here reeoaaended for drug clearance purposes. save as above save as above sane as above saae as above sane as above Of 7it chemicals evaluated as •Inlcldes. only 9 »»re wore toxic than CuSOit. None Inhibited growth of mat-formlnq algae for nore than 7 weeks. CuSCKt formulated with certain wetting aqpnts was nor toxic thin CuSO". alone. Conner chlorarlne was also found to be more toxic than CuSQ<»« No wetting agents Mere found to be Inhibitory at the concentrations Investigated (C.05 and 0.00"5 Dp«). Also reoorted are factors affecting growth of algae In canals to determine whether there were leads to controlling aloae by environmental •anaqevent. No practical environmental •cans Here found. same as above Hltchuo* et al Cl-»69>, •MIC-57S9 Oavls> et al (19691.AHIC- 5998 Davis, et al (1969).AHIC- 5993 Davis, et al (1969>,A«»IO 5990 Davis, et al (19691,AHIC- 5990 Otto I19T9). AHTC-89Z Otto (1970). ftHIC-89? Approximate toxlcitles of Naitdesley- ------- rv? Comooun'l Dobs JN Dobs JN Oobs JN Dobs JN Oobs 095 Toxicity, Active Field Field Ingredient, Organism Study Location Pom seed fled) 1.0-10.0 (K) Carclnus BSA -- qreater than •aenas 100 (T2> Cardlum edule BSA — qreater than 100 Cranqon BSA — qreater than eranqon 100 Pandalus BSA — qreater than •ontaqul 100 (T2) Csrclnus BSA -- qreater than maenas 100 Exoerl mental Variables, Control 1 ed or Noted Comments numerous pesticides commonly used in Britain Here suinmar l?ed. An excellent brief, general discussion of toxlcity testing is also present. a(contin- One hundred- forty surface active uous aer- aqents, solvent emulslf lers, pesticides. ation, sea ool vch lorlnated blohenyls. cure wato™, tmd Inorqanlc, and organic chemicals were dally evaluated against as many as ten marine solution organisms. The authors noted that most removal) published data of this type deal with toxlcity of chemicals to «resh»ater organisms. a«(contln- same as above uous aer- ation, sea- water, and daily solution renewal ) atCccntin- same as above UCM3 aor- etion, soa- vc tor, and drily solution renewal ) a(contin- same as above uous aer- ation, 363- water, and daily solution renewal } a(contin- sarre as above uous aer- ation, sec.- wntor, and daily solution Reference rco-os (1171) ,S-I 10-^5 Por t r 3nnt si (1971) , ATC-7701 Por t r.S'-n, 31 (1971), AMIC-7701 Por t-iann. al (I'i7!) , ANIC-7701 Por Tyann, etsl ( ) t er ------- renewal) Dobs »S5 Cardiua edul« BSA — (TZ) o(contin- uous aer- ation, sea- watcr, and daily solution renewal) same as above Portmann, et al U9M>, AKTC-770-. Dobs Crangon crangon BSA — greater than 100 (TZ) r 18 vn Debs 055 Panda I us •ont»qul BSA greater man 100 (TZ) a«(contin- uous aer- ation, sea- water, and daily solution renewal) a»(contin- uous aer- ation, aea- water, and daily solution renewal) sane as above as above Portnann, et at (1971), A1IC-77P1 Portnann, et el (19M1, Debs OSS Platlcthys fIvsus BSA 10-30 ITZ) a(contin- uous aer- ation, 3CC- wator, and daily solution renewal) same as above Portmanr, et al (1971), ANIC-7701 Oodlne acetate Oonlclde A (not soclf le-1) Mercenaria •ercenwla (eggs) greater than 0.1-1.0 (K) greater Than 10.0 (T2> Approximate toxiclties of Nawlsl«y- nur»»rous pesticides commonly used In Tho»as(1371] Britain were sumi"a>-izpa. An excellent AllC-lOS'i brief, general discussion of toxicity testing is also present. The effect oT 52 pesticides on Davis, etal embryonic development pf clap* and tl9'i<»», oysters was reported. Synerqistjc AMIC-5993 effects with solvents were also reported. Most of the compounds affected development more than survival. Sone, however, drastically reduced larval ------- COBDOurv) Field Field Organism Study Location Toxicitv. Active Ingredient, Pom Experimental Variables, Control led or Noted Comments Peter ence Oonlelde * OOHlcide G IU CO ON Do»lcl<1e G Oo»pon OoKpon Mercenarla mercenaria (Iarvae) Mercenaria nercenarla (eqqs) Mercenarla merceoarla (larvael Rashora heteroxoroha BCFA and as A 0.75 (TlZ) less than 0.25 (T?) less than 0.25CT1?) (TZ) Sal no SCFA — gairdnerl and 8SA 179 growth. The authors ooint out the necessity ot evaluating the effects ot Desricldes on all life stages of an organism and note the possibility of selecting chemicals for pest control that Hould not have serious effect on she!If ish. same as above a,c,o,r, hard (KV) or soft (SW) syn- thetic dilution water, or seawotcr for soaie species sane as above seme as above Davis, et a! < 1969! ,t«TC- SS?1 Oavls, et Dsuis, et al I bard (IIU) or soft {3W> syn- thetic water, or soawater for some opeclea One hundred sixty-four pesticides, wettinq agents, and miscellaneous water oollutan»s showed a wide ranoe of toxicity snannlnq 12 orders of magnitude. Knowing the toxicity and percentage of all conoonents of a formulation did not result in easy predictability of the toxicity of a mixture of materials. Sometimes pesticides were most toxic in hard water and soiretimes the opposite was true. Testing the actual material as sold was found to be essential. same as above 41abaster AMIC-si?5 Alabaster AMIC-5«.?5 ------- DoxeMc fCIO?) Carclnus •aenas BSA 500 (T2) OoxcMe (CIO?) CaPdlum edule BSA a«(contir.- One hundpert-f opty surface activ UOUs aer- aqents, solvent emulsl f 1 eps, pesticides, ution, sea-Potych lorlnated biohenyls, Pure water, ar.ci inopqanic, and orqanic chemicals »»pe daily evaluated aqalnst ?s msny as ten mapine solution opqanlsms. The authors noted that nost 1'enewal) published data at this type deal Kith toxlelty of chemicals to fpeshwater opqanisms. «t a«-(contln- uous aer- ation, sea- v.-atcr', and daily solution renev:al ) sa"e above tMIC-7701 et al A1IC-/7C1 Oexclde fCIO?) I ro ro -4 Doxctd* «:i^nated as CV, on, Cl, On, AQ, PC, MM, TN, HP, an1 NA with no fuPtnep descpjotion of theip chemical natuPe OP source. Only a few hioasssys wepe conducted with shPimo. Molluscs and «chlnodepms wepe suggested as suitable test anlirals. The authops stated that the method could be used to test any ppoduct fop toxicity in seaxateP. al (19711, AtIC-7731 et al (1973) ------- o Compound 00 00 OSS OTHC Field Field Organise Study Location Fundulus BS* ~ heterocl 1 tus N«r«ls vlrens BSA — Nereis vlrens BS* — - Palaemonetes BCF -- kadlaKensls (adult) Toxlclty, Active Inqredlent, Pp« 0.0005 mi O.OOOZ-0.001 mt 13.5 (T(.) 0.07 (residue) Experimental Variables. Control led or Noted Comments a'.c.e, sane as above and synthetic seaiiater a»c»e, same as above and synthetic seaHater 8.c,e, sane as above and synthetic seawafer a* Magnification ot POT aid Aldrln taqqpd with C-l ------- Oylox 0.8. Granular Coccus saxatills tfingerlIngs) 8SA — Sal no galrdn«rl BCFA and BSA Cconat 13046 Rasborn n«teronorpha BCFA and BSA 0.19 CT2) tC-9» Rasbora h«t«romorph» BCFA and BSA Pesticide-resistant species were collected at Relzoni and non-resistant species at State College. Cooepods, clans, snails, and sludge worirs Iron Relzoni were consid»rinfv more tolerant to pesticides than tie non-resistant organisms. The authors note that the effect of Increased tolerance In the organisms Is an Increase In the amount of pesticide residues available to animals of higher troohic levels. S.2 (Tl») a«,c,d,e,f Strloed bass flnqerlinos were Hellborn ' ,p and apoarently much more sensitive to (1969), Iron therapeutic and herbicldat compounds than AMIC-57?! many freshwater fish. 2050 (T2) a,c,e,f. One hurdrert sixty-four alabaster hard (HH) pesticides, Hettlnq agents, and or miscellaneous «at«>r oollutants showed a SOFTtSM) wide range of toxlclty spanning 12 orders synthetic ot magnitude. Knowing the toxiclty and dilution percentage of all comconenfs of a water, or formulation did not result in easy seawater predictability of the toxlclty of a forsome mixture of naferijis. Sometimes species pesticides were most toxic In hard water and sometimes the ooooslte «as true. Testlnq the actual material as sold Has found to be essential. a,c,e,f. One hundred sixty-four Alabaster hard (HH) pesticides, Hettino aoents, and (1969), or miscellaneous water oollutants showed a AMIC-5U2S SOFT(SM) Hide range of toxicity soanninq 1? orders synthetic of itnqni tude. Kno«lno the toxlclfy and dilution percentage of all co^oonpnts of a water, or formulation did not result in easy seawater predictability of the toxlclty of a for some mixture of materials. Sometimes species pesticides were most toxic in hard water and soretires the opposite was true. Testlnq tne actual material as sold was found to be essential. l.Z IT2, a,c,e,f. One hundred sixty-four tlabast«r h»rdwat«r> hard (HH) pesticides, wetting agents, and (1969), or so)t miscellaneous water oollutants showed a AMIC-5t?5 (SM) wide range of toxicity spanning 12 orders synthetic of magnitude. Knowing the toxicity and dilution percentage of all comoonents of a water, or formulation did not result in easv ------- Compound Orqanlsm Field Field Study Location Toxlclty, Active Ingredient. Exoerlnental Variables, Control led or Noted Comments Reference EC-98 Rasbora BCFA heteromorpha and BSA 1.2 (T2, softMater) E»col M-146 IS percent olvs Z> percent F«col N-9IIX) Rasbora BCFA heteromorpha and BSA 10 IT2> Eacol 7«? Rasbora BCFA heteromorpha and BSA 6.0 c.e,ff .hard (HWJ or soft ISH) syn- thetic dilution water, or aaawater for aoaa apeolaa predictability of the toxlclfy of a mixture of materials. Sometimes pesticides Here mo^t toxic In hard Mater and sometimes the opposite Mas true. Testlnq the actual material as sold Mas found to be essential. sane as above Alabaster 11969), AMIC-5<,?5 One hundred sixty—four pesticides, HCttlnq agents, and miscellaneous Mater pollutants showed a Mlde range of toxlclty soanninq 12 orders of maqnitude. Knowinq the toxiclty and percentage of at I eooon»nts of a formulation did not result in easy predictability of the toxicity of a • Ixture of materials. So-neti»cs pesticides Mere most toxic in hard Mater and sometimes the opposite Mas true. Testing the actual material as sold was found to be essential. sane a above Alabaster •1969), R1IC-5I.2S Alabaster (1969), CHIO Crassostrea vlrglnlca 16.S IT?) The effect of 52 pesticides on eabryonlc development of clans and Oavls, et at (1969). ------- t»qo«> EHTO Cvpilan Crassostrea vlrolnlea (larvae) Cranqon crangon 30.0 IT1U iofl-330 take* «pi II'ussK USA l.B-3.3 (T. mC-7701 Cndosultan Fish (not soeclfled) greater than 0.000001-0.0000 1 (K) Approximate toxicltles of HaHdeslev- numerous pesticides commonly used In Thomas (1971 Britain were summarized. An excellent AMIC-1856 brief, general discussion of toxlclty testing Is also present. ------- Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Comoound Organism Study Location Pom or Noted Comments Reference Cndosutfan Rasbor» BCFA — 0.000003 tT2> a,c,e,f, heteromorpha and hard (HH) BSA or soft ISH) synthetic dilution water, or seawater tor some species One hundred sixty-four Alabaster pesticides, wettlna agents, afd (1969), miscellaneous water oof lut^nrs showed a ANIC-S'i?': wide ranqe of toxlcitv spmnin-j tires pesticides were most toxic in nard water and soffetlmes the ooooslte wai true. Testlnq the actual material as sold was found to be essential. Cndosulfan AgonuS cataohractus BS» — 0.03-1.0 (T2) a«(oontin- . One hundred-forty surface active "or UOUs aer- nqents, solvent euulsIflers, pestlcidss, al ation, sea-PO'vch'orlnated biohpryts, oure water and Inorqanlc, and orqanic cn^t^icals wore ^ally evaluated aqalnst as many as ten marine solution orqanisms. The authors noted that most renewal) Published data of this tyoe deal with toxlelty ot chemicals to freshwater orqanisms. AMIC-7701. Cndosulfan CardIurn edul« BS» greater than 10 ao(cor.tin- IT2) uoua aar- atlon, sea- water, and daily solution renewal) same as above Portmann. et a I (19^:>, »MIC-?7C1 Cndosulfan Crangon crangon BSA 0.01 (T2) a«-( contin- uous aer- ation, sea- water, and dally solution renewal) same as above Portma^i, et at (19?1), Cndothall Rasbora heteromorpha 8CFA and BSA (TZ1 •»»t'» One hundred sixty-four hard (HW) pesticides, wettlnq aqents, and OF soft miscellaneous water oollurants showed a (SW) »jn- wide range of.toxiclty scanning iZ orders Alabaster (t969>. ------- Cndotnall > IU u> CJ Endofhall Cndothall Cndofhall Endothal Endrln Endrln tlMjttC dilution water, or seawater for soxe spa tiles Hercenaria •ercenarla (eqqs) 51.0 (T2) Hereen««rl8 •ercenarle II arvne) Crassostrea L vlrqlnlca 12.5 (T12) 28.2 CT2) Crassostr«» L vlrqlnica (larvae) Fish (not specified) Fish (not specified) an»cystls nlrtulans greater than 10-100 (K) oreater than — 0.0001-0.001 (K) 0.5-1.0 (qroMth a,c»ir inhibited) SM of maqnltude. Knowinq the toxicity and orc»ntaoss ioi 11 ty of selecting chemicals for oest control that would not have serious effect on shell fish. sane as above same as above same as above Approximate toxlcitles of numerous pesticides commonly used in Britain were summarized. An excellent brief* general discussion of toxlclty testing Is also present. same as above Metabolic products of Aldrln, Oieldrin, and Endrln can be as toxic as the parent compounds, as shown by 00 measurement. Davis, et al (1969), »Mi:- navis, et al ( 19691. Davis, et al 1199) ,»1IC- •5990 Mawdesley- Thonas (1971), AMIO 1056 Hawdesley- ThOB«S(1971 AHIC-1056 Batterton.et al ------- ro Comnound Ff\ttf I n coor i n Cndrln Endrln tnar In Endrln Endrln Field Field Organism Study Location quadrup- lleatun Salvellnus BCFA — fontlnalls (1.15 q> Salvellnus BCFA — fontlnal Is (2.01. q> Salno clarkl BCFA — (0.3? a) Salno ctarfcl BCFA — (1.30 q> Sal no BCFA ~ qalrdn»rl (!.?<> q» Toxlcity. Cxoer I mental Active Variables. Ingredient t Controlled Pom or Noted Comments 0.51.0 (growth a»c»r Inhibited) SM 0.355 {TH a«,c,d. s,r,i,o, aulfate. copper, manganese, Iron, and chromium 0.59 (Ti.) a«,c,d. e,r,l,o, suirata, copper, nanemese. iron, and chronlum 0.00001 CK> »,c,d, e,r,l,o, oulfate. copper. manganese. iron, and chromium 0.00002 (Tli> a«,c,d. e.r.l.o. aulfato, copper, manganese. Iron, and chromium 0.00 Of, (T«») »,c,d. e,r,l,o. aulfate. copper. manganese, Iron, and chromium sane as above Four Insecticides Mere evaluated on tour fish species at two body weights. Standard method bloassay orocedures were fol lowed. SyfflDtomotogy was also recocted. Generally, toxlcity Mas significantly different at the two body weights. !.«.» more toxic at tne lower body weight, exceot for Hatathlon. Well-defined exoer inental conditions were said to result In truer measurement of toxlcity. sane as above sane as above sane as above sane as above Reference AMIC-K.71 Bat ter t on • «t al (19711. AMIC-1«.M Post, et al (1971), AHIC-1813 Post, et al (1971) , A1IC-1812 Post, et al (1971) , AMic-iai? Post, ct al (1971). AHIC-181? Post, et al I197D , AMIC.-IIZ ------- En-in llmneohllus rhombIcus (larvae) .Knights 0.003 (whole CRFEK, body residue) OunCounty, Misc. \J\ Endrln Endrln Endrln Endrln Slalls so. FS (larvae) Gannarus so, FS Plmephales BCFA orone I as Carass1us BCF auratus Kniqhts 0.009 Creek, Dun (wholebody County,Wise, residue) Knights CreeKt Dun County, Misc. 0.013-0.035 (unoI(body residue) 0.25 DPb (U) a»,e 0.00<»3 (oral a,c,q dose o«r day,S8 i, mo) endrln Oncorhynehus BCF Klsulch (1.50 0.76 IT) Samoles of xater, silt, bottom Houbry, et debris, bottom orqanlsus, and fish Mere a( (1^68), taken In 1966 troi» a creek adjacent to an SHIC-3753 orchard which had been treated In 1«!<>3-1?SS with various chlorinated hydrocarbon pesticides. No residues Here founr) in Hater samnles. Silt sanotes contained 0.003-0.013 DDK endrln and 0-0.01)5 cpm dleldrln. Endrln residues of 0.011-0.025 oom and 0.007-0.006 opn diaMrln Here found In debris samples. nesolte United control data, residue analyses Indicated that contamination of the environment studied was United. sane as above sane as above Moutry, et a I Moubry, et al (148). SMIC-37S3 a«,e.d. e,f,l.o, aulfato, copper, nanconese. Iron, and chromium ISS acted synerglstleally with Solon, et al parathlon to cause less survival of fatheds but had an Indeterminate effect (1969),AMIC- nith ROT and no synerqlstic effect with 37<5 En»1rln. No effects Here noted at lower Grant, et al concentrations while higher doses caused (1970), some mortality, lowered growth rat?, AH.IC-3S26 decreased thyroid cell height, decreased qanetogenesls, lowered total body fat, less vaeuot Izatlon of liver cells, elevated serus Na concentrations, osmo-regutatory disturbance, and other effects. The-authors note that sublethal sane as above Post, et al M971) , 4MIC-181? ------- ro LO O\ Compound Endr in Endrln Endrln Endrln Endrln Toxicity, Experimental Active Variables, Field Field Ingredient, Controlled Organism Study Location Ppn or Noted Comments Enrfomyc^ura F Western 0.17 (residue) — • craverl U.S., (eqqs) Pacific Ocean, Panama, Mexico, and Antarctic Pelecanus F Western 0.07-1.13 •occidental Is U.S.. , (residue) (eggs) Pact f Ic Ocean, Panama, Mexico, and Antarctic Sula F Western 0.01-0.06 leucoqrster U.S., f residue) (eggs) Pad f ic Oc»an, Panama, Mexico, and Antarctic Pandion F Western 0.?5 (residue) hallaetus U.S.. (eqqs) Pacific Ocean, Panama, Mexico, and Antarctic Gaibusla L — 0.05-0.* (SB 3 — • Minis hr) (resistant) effects could adversely affect fish poou 1 at 1 ons. d t" 1 * 1 1 t d widely and analyzed tor HOT, DOE, PCB, and a few other oestlcides to a lesser degree. PC?) and DOT were found to be widely dispersed globally. PCS was found to be a powerful inducer of heoatic enzymes that degrade oestradlol. Reductions in thickness of eqg shells. eggshell weight, and water retention occurred. Alt affect hatching success. The authors state that the peregrine nay be the first species entlroated by global contamination. sa»e as above sane as above sane as above Endrln resistant mosauitoTlsh exhibited no consistent change in rate of oxygen consumption. The susceptible Reference et al (19SSJ , ANIC-38i> Rtsebrouqh, et al (1968), AMIO38M» Rlsebrougn, et al (1968), »HIC-38<.«. Rlsebrouqh, et at (1968), AllC-JSkW Mrlngvale. et al (1968), ------- EnrtrIn fnurln Caxbusla L (susceptible) Plueohales proud as (3 8SA 0.00001-0. (SB 3 hr) 0.00077 IT2> a«,c,e,f, k,l,n, and na(-- noslun, sulfates, iron, calcium IU Cntfrln Endrtn Plmephales crone I as H en) Pala«nonet«s Hadlakensls (resistant) H.00057 (TZ> a,e,e,f, lc,l,n, and nag- neslun, sulfates, Iron, calcium BS» ~ 0.0028-0.0137 at higher concentrations. Some nortallty occurred at .02-.075 oo» In susceptible tlsh and at .Ml po« In the resistant strain. saae as above Hclnqvatet et al Ploassays conducted simultaneously Indicated that DDT was conslri«>raMy nore toxic to fatnead minnows under static conditions than under continuous «I on conditions. Decreasing oxygen and increasing metabolites may have enhanced DDT toxic!ty. An identical study «lth Endrln resulted in only sllqhtty higher toxiclty under continuous flow conditions. Average pH, oxvqen, and anmonia nltroqen were foil owed throuohout the oxperlnents. The results nere conprehensl«ely discussed taking into consideration »»ny contributing factors. same as above AMIC-5V75 Linear, et al 5S09 Llncer, et al (1470), Bloassays Her* conducted Kith shrlmo fron three areas of intensive pesticide use and from an unexoosed area. Previously exoosed shrimp Here from 1 to ?5 times more resistant than unexposed shrimp. Both types of shrlno Here also exoosert in cages to waters of the contaminated areas. Susceptible shrimp suffered fit percent more mortality than did resistant shrlmo. The toxicity of the Insecticides ranHed in descending order xas as follows: nost toxic, Endrln, DDT, Methyl paratnlon, Parathloni medium toxiclty, Cuthlon, Llndane, Toxaohene, Strobanet lease toxic Chlordane, Sevln, and Heptachlor. Naavl, et (1970), AHIC-S519 al Fndrin Pala«en»tes USA — 0.0009 (Tl) sane as abova Naovi.et al ------- Compound Endrln Field Field Organise Study Location kadlaKenvls (non- resistant) Gambol 1 » U — at finis (resistant) Toxlcity, Active Ingredient, fom D.5-? (SB6-9) Experimental Variables, Control led or Noted Comments ~ Resistant nosqul t of ish Her exposed to Endrln for varyina periods of time then fed to susceotible green Reference (1970), ANIC-S519 Ferguson, et al (1967), ANIC-5976 ro Endrln Endrln Gambusla affinis (resistant) tenon i s cyanellus (susceptible) L — (whole body residue) greater than 1 (k ------- En-In r NO Endrln Cndrln Endrln Endrln Endrin Cndrln Cooroods (Cvcl or>s blcusoldus. CycloDs vaplcns« Cyclons vernal Is, Eueyclops aql Us, Macro eyclops albldus. Opthoeycloos modulus) Tub If ex tublfex Physa gyPlna Physa gyplna Euoepa slngieyl Leoomls •acPochlPus FL and BSA FL and BSA FL and BSA FL and BSA FL and BSA BSA Belzonl, 0.08 (20 Hiss percent K2> Belzonl, 6.D CNTE) Miss. State 0.55 State 0.075 (K3) Col lege. MISS. 0.0001 ------- Compound Cndrln Organise Crassostrea vlrglnlca leqgs) Field Field Study Location L — Toxlcity, Active Ingredient, Ppa 0.79 (T2) Experimental Variables, Controlled or Noted Coaaents — - saae as above Reference Davis, et al C19S9),A1IC- Cndrln Cndrln Crassostrea vlrqtnlca (larvae) Lepoals aacrochlrus L — 8S» — greater than 1Q.O 0.001-0.002 (Kl Cndrln Cndrln Cndrln Cndrln Cndrln Leooals alcroloohus Leooals •aerocMrus Lepovls •aeroehlrus lepovls aaeroehlrus Leooals •aeroehlrus BS« — FP FP FP Orlft wood Far> Ponds, Indiana Orlftnood Far* Ponds. Indiana OrlftHood Fara Ponds* Indiana 8CF» — 1.001-0.002 CKt O.DO". (K2> 0.001 (K21) 0.046 (Kl) 0.002 (Tit saae as above Davlst et • 110599!) Lab. tests Mere folloxed by tests He^eynolds In oonds to eradicate fish. Cndrln (1969),»HIC- toxlclty persisted In one oond study (W6 108 Dob) rven after the pond had been mptled and refilled twice. In oonds. Cndrln tbxlclty varied widely. The author stated that this cheolcal MBS too danqerous for use as a pesciclde except In extrenely Isolated Instances. saae as above saae as above sane as above saae as above Cndrln absorbed by bluegllt In lethal and sublethal exposures Has deteralned by electron caoture gas chro«tograDhy. Absorotlon Has Measured at varying tlaes uo to 24 hr. The authors stated that a teaoorarv decrease In absorption at the sublethat concentration level suqoests the fish •ere aetabolizlnq and excreting the Endrln. McReynotds (I960), •HIC-1D8 Hc9eynolds (11^91, •HIC-108 HcRevnolds (19fi9), AMIC-1B8 HcReynolds (1<>69) , »HIC-1B8 Bennett, et 81(1970), AMIC-19S ------- Endrln Endrln Cndrln Endrln Cndrin Endrln eolchlorhydrln Leoomls BCFA •acrochirus Lepomis BCFA •acrochirus Leoomls •acrochlrus Leoonls •atrochlrus lepomis •acrochlrus Cyorlnodon varlegatus (50-70 ••) BCFA — BCFA — BCFA — BSA Rasbora BCFA heteromorpha and BSA 0.0002 (SSI) o.noo? 10.04-0.13 DO •uscle residue) 0.0002 (0.60-0.70 pp» qut residue) 0.000? (0.80-1.0 DO* IIver residue) 0.0002 (0.80-0.30 OP" whole body residue) 0.001 (K) sane as above same as above sane as above sane as above same as above Bennett,et at (1970),AMIC- 195 Bennett, et al (1970), AMIC-19S Bennett, et al (1970), AMTC-195 Bennett, et al (1970), AMIC-195 Bennett, et al (1970), AHIC-195 36 (T2) a", Sensitivity of threi- generations seaxater of sheeosheacJ minnoMS to 03T and Fndrin Nas determined. Sensitivity to ODT varl«d seasonally. Fish were bred In ponds 15m X 5» X 1.25* exposed to pesticides In aquaria, and survivors used for breeding. The results for DOT Here not entirely clear due to the seasonal variability. Increased and decreased sensitivity Mere recorded for the Fl generation at different times. Increased sensitivity for the F2, and decreased for the F3. The authors stated that Incorporation of DDT in ova via lioids •ay have caused increased sensitivity. Endrin toxlcity Has decreased in the Fl and Increased in the F? qeneratlon. a,c,e,f. One hundred sixty-four hard pesticides. Netting agents, and or miscellaneous Hater pollutants showed a SOFT(SH) Hide range of toxlcity scanning 1? orders synthetic of magnitude. Knowing the toxicity and dilution percentage of all components of a Mater, or formulation did not result in easy seanater •predict jbl 1 1 ty of the toxlcity of a for so«e mixture of caterlals. Some tines species pesticides were Most toxic In hard Mater and sometimes .the opposite Mas true. Holland, et al (197C), AMIC-726 Alabaster (1969). ------- Coeoound Eotam Eterlne fulfat Field Field Organise Study Location Gammarus BSA — Negaorlon BSA brevlrostrls <1-I kg) Toxiclty, Fxperlmentat Active Variables, Ingredient, Controlled Ppm or Noted Comments Testing the actual material as sold was found to be essential. 23.0 (Ti.) a* Of the aquatic weed herbicides Oaohnla Mas generally the most sensitive organism. Ill of the Crustacea Mere affected by much lover concentration levels of herbicides than indicated by the TL sub 50 values. All of the animals reoresent Imoortant food chain links. 11 (NTE 3 hr) a,c,e Data from study of dru? effects on young lemon sharks were treated mathematically to demonstrate Reference Sanders 1 1070) • AMIC-W3 <>aldrldge(19 69), AM.IC-3832 Ctsolvene Carclnus •aenas 9S» 10—33 (T2) Csselvene Cardlua «dule BS» — 33-100 (T2> applicability of classical rat* theory to the study of chemical shark deterrents. IncapacItatlon (narcosis) was the primary parameter timed for effectiveness. This Mas usually guite raold for the more effective drugs. a»(contin- One hundred-forty surface active Portmann, et UOU3 nor- agents, solvent emulslflers, pesticides, al ation, sea-DOlychlorlnated biphenyls, oure (1971),»MIC- water, and inorganic, and organic cherlcats Mere 7701 daily evaluated against as many as ten marine solution organisms. The authors noted that most- renewal) oublIshed data of this type deal with toxlclty of chemicals to freshwater organisms. sane as above Portaann, et al 11971),»HIC- 7701 uous aer- ation, soa- woter, and daily solution renewal) Csselvene Crangon cranqon BS» 10 (TZ) a«(contin- uous aer- ation, sea- water, and sane as above Portnann, et al (197H, •HIC-7701 ------- daily solution renewal) Essolvene Ostrea edulls BSA ~ 33-100 (T2J a»( contin- uous aer- ation, aea- wcter, and solution rcne-.ral) same as above Portnann, «t al (19711. AMIC-7701 Cssolvene Panda I us •ontaqui BSA 10 (TZt a»(contin- uous aer- ation, sea- wa tqr, and dally solution renewal) sane as above Portrann, et al (1971), AMIC-7701 C*0 solvent FC-1S5 Cranqon cranqon BS» 10-33 (T2> Cthanedlol Cranqon cranqon BSA qreater than 100 IT2> Cthanolamlne Cranqon eranqon 8S» — greater than 100 (T2> ac( contin- uous aer- ation, sea- water, end solution renewal ) a«(contin- uous aer- ation, sea water, er.d daily solution renewal) a (contin- uous aer- ation, S3Q- water, and daily solution renewal) One hundred-forty surface active aq«nts» solvent emulsIflers, pesticides, ooIvchI orInated blrh^nvls, pure Inorganic, and organic cnrfflcals were evaluated against PS many as ten marine organisms. The authors noted that most published data of this type deal with toxlclty of chemicals to freshwater organisms. One hundred-forty surface active aq-nts, solvent emulslflers, pesticides, .DOlychlorInated biohenylsi our* Inorganic, and organic chemicals w»re evaluated against as many as ten marine organisms. The authors noted that Host published data of this tyce deal Hlth toxlclty of chemicals to freshwater organises. same as above Portiann, et al (1<>71>, AHJC-7701 Portinann, et al (1971), AHIC-7701 Portmann, et al (1971), AHIC-7701 ------- Conoound Ethanol .Organise, Sett* Field Field Study Location • m^ Toxlcity, Active Ingredient, Ron ?8SO (SB 6 hrl Experimental Variables, Controlled or Noted Comments a* The effects of ethanol and Reference Raynes. et soIendens tthlon Pashora heteromorpha BCFA and BSA 0.53 (T2) OP soft ISM) a?a- tbetie dilution water, or •eawmter for ' Ethlon Tublfex tublfex Ft and BSA Belzonl, Hiss. 1.50 tNTE) Ethoeeen S-25 Pas bora heferomorpha and 9.39 m, hardxater) hard (HW; or soft (SH) ayn- bourbon en the aggressive response of al Siamese fighting fish were determined. (1968), AHIC Cthanol Increased all I snow 5712 (aggressiveness) and bourbon and bourbon congeners decreased It. The authors tentatively concluded that the delayed effect of the congener resulted fro<« involvement of a different Dhyslological mechanism and that this nay be related to hangover effects in nan. One hundred sixty-four Alabaster pesticides, wetting agents, and M96. AMT.C- alscel laneous water pollutants showed • 525 wMe range of toxlclty spanning 1? orders of magnitude. Knowing the toxlcitv and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. So«e times pesticides Mere most toxic In hard water and so»«tjmes the opposite was true. Testing the actual •af«rj«l • sold «»» found to bt ------- Cthoneen S-Z5 Rasbora heteronorpha <5CFA and as* 0.68 (TZ, softxat«r) Cthylene phosphite Pineohales crone fas BS« — 34.0 (U) Cthyl parathlon Cardlum edule BS» —• 3.3-10 ------- Compound Organise Field Field Study Location Toxlclty, Active Ingredient, PD« Experimental Variables, Control led or Noted Comments Reference £-311. Fenac (Ha salt) > Fenac (Na saltl Fenac (Na salt) Fenac (Na saltl Fenac (Na salt) Fenac (Na salt) Coho salmon BSA Hood Canal, 0.01 (X) (fingerlings) In Hoodsport, situ Wash. Tracy, et al (19t>9), Gammarus faselatu? OS* Paleomontes karl I ak»n% J^ As11 US brevlcaudus Orconectes nals BSA BSA BSA Daohnla aaqna BSA Cyoridoosis vidua BSA greater than 100.0 CT2) greater than tno.D IT?) greater than lOO.O(TZ) greater than 100.0 (T?) greater than 100.0 (T?> greater than 100.0 (T7) with fair to good oil dlsoerslon caoabi lity. sane as above Of the aquatic Heed herbicides Sanders evaluated. Old one was the most toxic, (1471), Daohnla Has generally the most sensitive AHIC-WJ organ l«mi. All of the crust.irea Here affected by much lower concentration levels of herbicides than Indicated by the TL sub 50 values. All of the animals reoresent important food chain links. same as above S; same as above same as above sane as above same as above Sand«--s(ig70), AHIC-1.53 1.53 Sanders (1970 1, •lic- it "53 Ssnders Fenac (Na salt) Fenoproo Lenonls •acrochlrus BSA Rasbora RCFA heteroaorpha and BSA 19.0 (T2) 37 a same as above Sanders (1970, AHIC-53 a>,Cfe,ft One hundred sixty-four Alabaster bard (Htfj pesticides, netting aqents, and J19A9), or soft miscellaneous nater pollutants showed a A1IC-5<.?5 (SH) syn- • wide range of toxlclty spanning 12 orders thetic of magnitude. Knowing the toxlcity and dilution percentage of alt components of a water, or formulation did not result in easy seawater predictability of the toxlcity of a ------- Fcntln acetate PandaI us montaqul BSA — for soMe Mixture of Materials. Sometimes species pesticides Mere most toxic In hard water and sometimes the oooosite was true. Testing the actual Material as sold Mas found to be essential. greater than 33 a»(contin- One hundred-torty surface active (T2) UOU3 aer- aqents, solvent enutslflers, oestlcldes, ation, sea-Polychlorinated blohenyls, cure water, and Inorganic, and organic cheirlcals Mere dally evaluated against as many as ten marine solution organ ISMS. The authors noted that Most renewal) published data of this type deal xlth toxlclty of chemicals to freshwater organ isms. Portaann, et at (1971). ANIC-7701 Fenuron Mercenarla mercenarla (eqqs) greater than 10.0 (T2) The effect of 52 pesticides on Pavls> et embryonic development of clans and al(1969). oysters Mas reported. Synerglstlc 4NIC-5990 effects Mlth solvents Mere also reported. Most of the compounds affected development more than survival. Some, hoNever, drastically reduced larval qroMth. The authors ooint out the necessity of evaluating the effects of pesticides on all life staoes of an orqanlsir and note the oosslbillty of selecting chemicals tor pest control that Mould not have serious effect on shell fish. Fenuron Ferrle eh I or I do Ferric sulfate Ferrous chloride Mercenarla Mercenarla I larvae) Carasslus auratus Carass1us auratus Carass1us auratus \| ^^ Ferrous sultate las »croneurla Fel L BS» greater than 5.0 «T1?) 5-10 5-10 (KV) 5-10 16 (T9) as above Davis, et al(19S9), AMIC-5990 Iron salts Merc most harmful shlv Immediately after dissolving, resulting (1978),»MIC- In gill blockage (reversible), absorption 5<>36 In digestive tract, and Iron precipitates In epithelium' and renal tubules. a,c,d,e,f same as above same as above EpheMerelta (Mayfly) Mas the most Warnlck, et Ashley (1970), A1TC-5I.36 shley(1970). sensitive aquatic Insect of those at(1969), studied, and copper the most broadly ANIC-3767 toxic metal. The authors suggest that ------- Compound Field Field Organism Study Location Toxlclty, Active Ingredient, Pom Experimental Variables. Controlled or Noted Convents Reference Ferrous sulfate las Ephemera 11a BSA Ferrous sulfate (as Hydropsyche BSA Fe) Ferrous sulfate Carassluv L auratus Flnavol FSK Cr»nton ASA cranqon 0.32 ITM 16 (T7) 9-10 (1C.) 180-330 CT21 Flnasol 0<5RZ Cranqon crangon BSA — 3300 (T<») a«c,d,e«f ,c,d,e,f aquatic Insects nay not be as sensitive to heavy netals as fish. sane as above a&tcontin- uous aer- ation sea- water, and sane as above MarnlcK, etal 11069). AMTC-3767 Warnick, et 81(1969). ANIC-3767 Iron salts Here most harmful Ashley Immediately after dissolving, resulting (1970). In qill bloeKaa (reversible), absorotion in dlqestlve tract, and Iron orecloltates In eolthellum and renal tubules. solution renewal) ae(contln- uoua aer- ation, sea- water, and dally solution renewal ) One hundred-forty surface active agents, solvent eiuls i Tiers, oestlcides, Dolvchlorinated blohenyls, oure Inorganic, and organic chemicals were evaluated against as nany as ten marine organisms. The authors noted that nost published data of this type deal with toxlclty of chemicals to freshwater organlsns. »•• » above Portmann, et at (1971), AHIC-7T01 Portmann, at al (1971), AHIC-7701 Flnasol SC Cranqon crangon BSA — 33-100 (T2> a(contin- uous aer- ation, sea- water, and dally solution renewal) sane as above Partmann, et al (1971). AMIC-7701 Flack o.p. Fly dip BCFA — 0.73 (T2) ,c,e,f, One hundred sixty-four Alabaster, ------- hetaroMorphe and BS hard pesticides, wetting aqents. and (19S9),»MIC- (HM)or Miscellaneous Hater ooltutants showed a 525 soft (SN) Hide ranqe of toxlclty soannlnq tZ orders synthetic of naqritude. Knowing the toxlclty and dilution percentage of all covoonents of a Hater, or foraulatlon did not result In easy seawater predictability of the toxlclty of a for SOMO Mixture of Materials. SonotlMes species pesticides Here Most toxic in hard Hater and socetlMcs the opposite Has true. Testlnq the actual Material as sold Has found to be essential. Fluoresceln sodlua Sal MO galrdncrl BS» — 1.J7Z (TV) Fluorwsceln so<1IUM Ictalurus ounctatus BS ~ Z.Z67 «T> Th« dyes Rhodanlne B and Fluoresceln sodlu Here found to be relatively non-toxic in poa concentrations while antlaycln Has toxic at pob levels. The author states that neither dye at field use concentrations should slqnlfIcantly Influence the activity of ntlycln « aqalnst fish. sane as above «arKIng (1969), HarKlnq <19691,»HIC- Fluorescein sodlt» LepOMls BS* aacrochlrus saae as above Marl, Ing t19691,»"IC- FluoroMIl Rasbora BCF* heteroaorpha and BS* 3,500 (TZI hard (HM) or SOFTtSU) synthetic dilution Hater, or Fluoroklli Salao qairdnerl BCF* and BS* 1.S90 (T2) for son* species 8tCt«tft hard (HHI or SOFT(SW) synthetic dilution •»ter, or seaitater One hundred sixty-four pesticides, Hettlnq aqents, and Miscellaneous Hater pollutants showed a Hide ranqe of toxiclty spanning 12 orders of Magnitude. Knowing the toxicity and percentage of all conoonents of a formulation did not result In easy predictability of the toxlclty of a Mixture of Materials. Sonetlnes pesticides Here Most toxic In hard water and sOMetlMes the opposite Has true. Testing the actual Material as sold Has found to be essential. save as above Alabaster (1969), Alabaster (1969), ------- ro VJI o Conoouni) Fluorofcllt Fellzoll Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Orqanise Study Location Ppn or Noted Comments for some species Platessa BCFA — 1,200 (TZ> a».c,e,f. vulgar Is and hard pesticides, wetting agents, and (1969!, or soft miscellaneous water pollutants showed a AHIC-S<>?S ------- Formaldehyde Salvo trutta BCFA and BSA 90 ro Ml Formaldehyde Crangon eranqon 8SA — 330-1000 (T2> Formaldehyde Plstlcthys f I esus BS» — 100-330 (T2) (SW) ayn- wide ranqe of toxlcltv spanning 12 orders thetic of maorltude. Knowing the toxlclty and dilution percentage of all components of a water, or formulation did not result In easy seawater predictability of the toxlclty of a tor some mixture of materials. Sometimes speclea pesticides Mere most toxic In hard Mater and sometimes the opposite was true. Testing the actual material as sold was found to be essential. sane as above a,cte,f, hard (HH) or soft (SH)synthe tic dilution water, or seawater for some species ai>(contln- One hundred-forty surface active uous eer- agents, solvent emulsltiers, pesticides, atlon, sea-DO'vch'orlnated blphenyls. Pure water, ftnd Inorqanlc. and organic chenlcals were dally evaluated aqalnst as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. a(contin- uous aer- ation, sea- water, and dally solution renewal) same as above Alabaster (1969). AHIC-51.25 Portrann, et al (1471), ANIC-7701 Portaann, et al (1971), AHIC-7701 Formal In Sal no galrdnerl 200-1.00 (SB. -6 hr) Caudal arterial blood samples were taken at selected time Intervals evaluated for acid-base balance and for gill. Kidney, and liver function by measuring 0? consumption, total CO?, HC03, Cl(minus), Ca(Z plus), blllrubln, whole blood pH, and Vitamin C depletion. Formal In treatments seemed to be a more severe stress to rainbow gelscff ofele data and discussion are presented. Hede»eyer and (197l),AHIC- 3287 ------- ro \J1 IU Toxlclty. Experimental Active Variables, Field Field Ingredient. Controlled Compound Organise Study Location Ppm or Noted Comments Formalin Oncorhynchus L — klsutch foff9l in Tracblnotus BSA — enrol Inus (Juvenile) Fora* 1 In Roccus BSA — saxatllls (f Inqerl Ings) Formic acid Care Inus BSA — •aenas 200-400 (SB, f 4-6 hrl and •ul fate. sodium, calcium. potassium. Bagnesium, carbonate. bicarbon- ate. salinity 18 (T4I a»,e,dfa. f,p, and Iron 80-90 IT2I a(contln- uous aer- same as above In this study of pompano salinity MBS controlled at 10, ?0, and 30 ppt and investigated as a variable. Acrltlavln, formalin, and potassium permanganate Mere slightly more toxic at the highest salinity, while copoer sulfate was slightly less toxic. These compounds are used as prophylactic bacterial treatments. All appeared to he reasonably safe to use excepte possibly potassium permanganate. Striped bass finger linos were apparently much more sensitive to therapeutic and herblcldal compounds than •any freshwater fish. Pne hundred-forty surface active agents, solvent emulslfiers, pesticides. atlon, aaa-oolychlorinated blphenyls, pure wator, and daily solution renewal ) Inorganic, and organic chewlcals Mere evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal with toxlclty of chemicals to freshwater organisms. Reference Wedemever (1071), AMIC- B l^dsonQf »jt al (1971), AMIC-5570 Mel Iborn (1969), AMIC-S7?3 Portmann, et al (1971), AMIC-7701 Formothlon Puntlus tlcto -- 0.16S ITt) Fervothlon Rasbora heteromorph* BCFA and BSA l.Z (TZ) a,c,d,e,f Of the pesticides Investigated, Bhatla the most toxic was Klofos followed in 11971),A1IC deereaslng order by Sumlthlon, Malathion, S?J Formithion, Olmecron, Sevln, and BHC. The author cites the need for more selective pesticides nontoxic to fish or antagonistic agents for reducing fish toxlclty. a,Cte,f, One hundred sixty-four Alabaster hard (HW) pesticides, wetting agents, and (1969), or soft miscellaneous Mater pollutants showed a AMIC-5?S (SU) syn- Hide range of toxlclty spanning iz orders tfaotlc of magnitude.• Knowing the toxiclty and ------- Furfural •.asbora BCFA — heteromorpha and 8S» 23 (T2> to ^jj f»0m Steel head trout (fingerlIngs) BS» 65.0 (T«O F.O. 300-B Camlen CM Coho aalnon B3A (fingerllnga) in altu Cardtun edule 8S» Hood Canal, Hoodaport, fc.O (K) 33-100 (T2) Cam! en CM PandaI us montagal BS» 10-33 IT2I dilution water, or seawater for some species a.«,c,e,f, hard (HW> or soft (SM) syn- thetic dilution water, or seawater for aona •peolea percentage of all conoonents of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides Here most toxic In hard Mater an<1 sometimes the opposite Has true. Testing the actual material as sold xas found to be essential. One hundred sixty-four Alabaster pestlcidesi netting agents! and (19691, miscellaneous nater pollutants showed a niC-5l»25 Hide range of toxiclty spanning 1? orders of magnitude. Knowing the toxlclty and percentage of all comoonents of a formulation did not result In easy predictability of the toxiclty of a mixture of materials. Sometimes pesticides were most toxic In hard Hater and soiretlmes the opposite H«S true. Testing the actual material as sold was found to be essential. Evaluation of 11 oil dlsoersants resulted In a ranKlng for each and a recommendation for use according to the ranklnq. Ranking Has based on toxiclty and oil dispersal effectiveness. Corexlt 77fiit appeared to have the least toxlclty with fair to good oil dispersion capability. MM • above Tracy, et al (19691, »«.IC-383«. •(contln- un* hundred-forty surface active uous eer- agents, solvent enulslfiers, pesticides, atlon, sea-POlychlorlnated blphenyls, pure water, and Inorganic, and organic chemicals were daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. «»(contln- s»»e as above uoua aer- ation, sea- water, and daily solution Trmcy, et al (1969J. AKIC-3&3U. Portmann, et al C1971>, AHIC-7701 Portmann, et al (1971), A1IC-7701 ------- £ Coaoound Gael en 0 Gael en 0 Caelen 0 Gael en OVt Caelen OS* Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Organise Study Location Pom or Noted Consents renewal ) Cardlua edule BSA — 33 CTZ) a«(contin- sane as above uous aer- ation, sea- water, and doily solution renewal) Cra no on BSA — 10 CT2I M.f „«•«.«„ »•• »« above cranqon * contin- uous aer- ation, sea water, and daily solution renewal ) Panda 1 us BSA — 10 IT?) a(contin- »•* »« above •ontaqul UOU3 aer_ ation, sea- wcter, and daily solution renewal ) Carclnus BSA — 10-33 IT?) a,«(contin- saae as above ram as uous aer- ation, soa- wcter, and daily •olutlon renewal) Cardlu* edule BSA — 10-33 IT?) a«(contln- sa»e as above uous a or- ation, sea- water, and daily Reference Portnann, et al (19711, ANIC-7701 Port»ann, et al (1971), 1MIC-7701 Port«ann, et al (197H,AHIC- 7701 Portnann, et al (1971), AHIC-7701 Portnann, et al (1971), AHIC-7701 ------- solution renewal) Gaalcn OS* Cranqon cranqon BSA 10 (T2) a»(contin- uous aer- ation, sea- water, and daily solution renewal} sane as above Portnann, et al (1971), ANIC-7701 Gail en OS* Ostrea edulls BSA ~ 15-55 (T2) a(contin- uous aer- ation, s=a- water, arid doily solution renewal) sa»e as abov« Portwann, et al (1971), AMIC-T701 vn vn Ganlen PRX Cranqon cranqon BSA 330-1000 (T<>> a«(contin- uous aer- ation, sea- wator, and daily solution renewal) same as abov« Portnann, et al (1971), 4MIC-7701 Ganl«n Crangon crangon BSA 100-330 (Tit) a(con;in- uous aar- ation, sea- water, and daily solution renewal) sa»e as above Port»arS IT2) a,c,e,f. One hundred sixty-four hard (HH) oestlcldrs, wettlnq agents, and or iKlscel laneous Mater pollutants shooed a SOFT(SH) Mlrle range of toxlclty soanolng 12 orders synthetic of magnitude. Knowing the toxlclty and dilution percentage of all comoonents of a Hater, or formulation did not result In easy seaxater predictability of the toxlclty of a tor some mixture of materials. Sometimes species pesticides were most toxic in hard water and sometimes the ooooslte xas true. Testing the actual Material as sold was Alabaster (1969), ------- Compound Gesapax Toxicity, Active Field Field Inqredient, Orqanlsm Study Location Ppm Pandalus BSA — 33 (T21 pontaqul Experimental Variables, Control I ed or Noted a( contin- uous aer- agents, ation, 3ea-polychl< One hundred- forty surface active jrinated blohenyls, pur> Reference Portwann, et al (14711, AMIC-7701 Glob terranycln pet Roecus tabs saxatllls (f logerlInqs) BSA O\ GtoQuat C Crangon cranqon RSA 100-300 (T2) Cramoxone 11J7) H (J.F. Rasbora heteromorpha BCFA and BSA 17 UZ, hardnater) Graoxon« 11371 U (J.F. Rasbora BCFA heteromorpha and BSA «>6 (TZ, softwater) water, and Inorcjanic, and organic cheTlcals xere daily evaluated aqalnst as many as ten marine solution organisms. The authors noted that nost renewal) published data of this type deal wltK toxlcity of chemicals to freshwater orqanlsms. a or soft (SW) synthetic dilution Mater, or seaHater for some species a,c,e,f, hard (HH> or soft (SM) synthetic dilution One hundred-forty surface active agents, solvent emulslflers, pesticides, pelyehlorlnated biphenyls, cure Inorganic, and organic cheirlcals Here evaluated against as nany as ten marine organisms. The authors noted that most published data of this type deal «ith toxlcity of chemicals to freshxater organisms. One hundred sixty-four pesticides, wettinq agents, and miscellaneous Kater pollutants showed a wide ranqe of toxicity spanning 1? orders o' maqnitude. Knowinq the toxlcity and percentage of all components of a formulation did not result in easy predictability of the toxicity of a mixture of materials. Sometimes pesticides Mere most toxic in hard Hater and sometimes the opposite was true. Testing the actual material as sold Has found to be essential. same as above Portmann, et al M97D, AMIOT701 Alabaster AMIC-SI.2S Alabaster (196 <»», AHIC-5VZ5 ------- Granoxon* IJ.F. 1511 Rasbora h«t»ro«ornha BCFA anil 8S» 570 «49>, ANIC-5U25 same as above Alabaster (1969), AMIC-5U25 The effect of 5? pesticides on Davis, et embryonic development of clams and al(1969)» oysters Has reported. Svnergistlc A1IC-S990 effects Hlth solvents Here also reported. Most of the compounds affected development more than survival. Some, hoH»vpr, drastically reduced larval qronth. The authors point out the necessity of evaluating the effects of pesticides on all life staoes of an organism and note the possibility of selecting chemicals for pest control that would not have serious effect on shell fish. Crlseofulvln Gulf agent 1009 Mercenaria mercenaria (larvae) Crangon cranqon BSA — less than 1.0 «T12I 330 same as above a(contin- un* hundred-forty surface active uous aer- agents, solvent efflulsiflers, pesticides, atIon, sea-PO\|vchlorlnated blphenyls, pure water, and Inorganic, and organic chemicals Here daily evaluated against as many as ten marine solution organisms. The authors noted that most Davis, t al(l969>, A1TC-S990 Portnann, et al H971), AMIC-7701 ------- Coaoourxl Organism Field Field Study Location Toxlclty. Active Ingredient, Ppm ExoerlMental Variables, Control led or Noted Comments Reference Guthlon Ictalurus BSA — Ounctatus 3.29 (T<»1 ro VJ1 CD Guthlon Cuthlon Cuthlon Guthlon Cuthlon Cuthlon Ictalurus •el as Carass1us auratus CynrInus carplo BSA BS — RSA — Plmeohales BSA promelas Lttnomls BSA maerochlrus leoonls BSA •Icrolophus 3.50 .27 8.695 (Tl>) 0.295 tT<>) 0.022 \|T<»> 0.052 (T<>) renewal) published data of this type deal tilth toxlclty of chemicals to freshwater organisms. a, OrganochlorIne Insecticides were HaceK, et synthetic the most toxic conpounds, aU1970)» Testwater organochosphates Intermediate, carbamates AtlIC-5510 the least toxic. Brown trout Has the species most susceptible to orqanochlorlnest coho salmon the most susceptible to carbamates, and goldfish were the least susceotible of all species. Sate concentrations established by bloassays with salmonids or centrarchlds MOUM imely be safe for cyorlnids and Ictalurids. Sate levels for Ictalurids or eyorlnlds would probably be hazardous for centrarchids and salmonids. The use of goldfish In bioassays was discouraged. synthetic test Mater synthetic test Mater a, synthetic test water a, synthetic test water a, synthetic test water a, synthetic test water same as above same as above same as above same as above same as above same as above HaceK, et al (19T0), AHIC-5510 Hacek, et al (19701, AHIC- 5510 Macek, et al (19731. Hacek, et al (1970), Hacek, et aUl<>70>, Hacek, et at (19701. AM.IC-5510 ------- Cuthlon Guthlon Cuthlon Cuthlon Cuthlon Cuthlon Mlcropterus BSA salnolife Cuthlon Cuthlon S»l«o qalrdnerl 8SA Saleo trutta BS» ~ Oneorhvnchus BSA klsutch Perca 8SA ftavescens Palaemonetes BSA kadiakensis freslstantl 0.009 ) O.D17 ITI 0.013 CT«.J a. synthetic test water at synthetic test Hater synthetic test water a, synthetic test Hater synthetic test Hater sane as above same as above sane as above sane as above sane as above MaeeK, et altl«70), Macek, et at (1970), 4MIC-5513 MacrV. t at 119TO)t ftKTC-5510 Mscek, et 81(1970), Macek. et a1(l970), (Tl) Bioassays were conducted with Naovl* et a! shrlno tron three areas of Intensive (1970), pesticide use and from an unexoosed area. AMIC-5519 Previously exposed shrimp Here fro" 1 to 26 tines more resistant than unexposed shrimp. Both types of shrimp were also exposed In caqes to naters of the contaminated areas. Susceptible shrimp suffered 66 percent more mortality than did resistant shrimp. The toxiclty of the Insecticides ranked In descendlnq order Has as foil oust nost toxic, Endrin, DOT, Methyl parathlon, Parathlonl medium toxiclty, Cuthlon, Lindane, Toxaphene, Strobanei lease toxic Chtordane, Sevin, and Heptachlor. Palaevonetes BSA — kadlakvnsls (non- r« olatant) TubIfex tublfex Ft and BSA Belzonl, Hiss. 0.0089 (Tl) 1.00 (NTE) same as above The response of pesticide-resistant aauatlc orqanlsos to various Pesticides Mas compared to the response of non-resistant soecles. Pesticide-resistant soecles were collected at Belzonl and non-resistant species at State College. Copepods, clans, snails, and sludge worms from Belzonl Here considerably more tolerant to pesticides-than the non-resistant NaavU et 11970). AMIC-5519 • I Naavl, etal 11969), AMIC-5979 ------- Compound Organism Field Field Study Location Toxlclty, Active Ingredient, Ppm Experimental Variables, Control led or Noted Comments Reference CutMon Cuthlon CutMon Horcenarla mercenarla (eggs) 0.86 (T2) Mercenarla •ereeniirla (larvae) Crassostrea L vlrqlnlea (eggs) 0.86 (TtZ) 0.62 (T21 Heptachlor eooxlde Brown bullhead FRL Misc. states 0.3<. residue (SB) Heptachlor eooxlde Caro Heptachlor eooxide Channel catfish FRL Misc. states 0.0<> residue (SB) FRL Misc. states 0.03 residue (SB) orqanlsns. The authors note that the effect of Increased tolerance in the organisms Is an Increase In th« amount ot pesticide residues available to animals of higher trophic levels. The effect of 52 pesticides on Oavls, et al embryonic development of clans and oysters was reported. Syneralstlc (1969) effects with solvents were also reported. S990 Most of the compounds affected develocment more than survival. Some, however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stages ol an organism and note the possibility of selecting, chemicals for oest control that would not have serious effect on shellf ish. same as above sane as above The Bureau of Sport Fisheries continued its fish moni tor Inq oroqra"" by collecting H»7 composite fish samples from 50 nationwide monitoring stations during the fall of 1969. Fish were analyzed for residues of 11 orqanochlorlne Insecticides, liplds, and PCB-s. sane as above same as above Davis, et al S990 Davis, et al U9«.9I.»MIC- S990 Henderson, et al (1971), Henderson,et al (1971), AMIC-li.07 Henderson, • t al ------- (191). HeotaeMor eooxlde HcBtacMor epoxld Small mouth buffalo Fa I co oei-»grlnus (Immature) PRL HIsc. states 0.16 residue (SB) Western D.S., Pacific Ocean, Panama, Mexico, and Antarctic 0.09 (Mhole body residue! Meotachlor eooxlde Heotaehlor Fa I co oeregrlnus (adult) Gizzard shad FRL Western 0.18-1.0 (whole U.S., body residue) Pacific Ocean. Panamai Mexico,and Antarctic Misc. states fl.i»5 residue (SB) He»taehlor Heotacnlor Blue catfish FRL Rasbora BCF* heteromoroha and BS* disc, states 0.22 residue (SB) 0.05 (TZ) same as above Henderson, et al (1971I. HIC-1<,97 Peregrine falcons, falcon crey, Rlsebrough, and other predator soecies Here collected et al Hldely and analyzed lor DOT, ODE, PCS. (1968), AMIC- and a few other pesticides to a lesser 38<»I> deqree. PCR and DOT Mere found to be widely dispersed globally. PCB was found to be 9 powerful inducer of hepatic enzynes that deqrade oestradiol. Reductions in thickness of egq shells, eggshell weight, and water retention occurred. All affect hatching success. The authors state that the perqrine may be the first species entlrpated by global contamination. s«e as above Rlsebrougn, et al (1968), The Bureau of Sport Fisheries eontinuod its fish monitoring proqran by collecting li>7 composite fish samples from 5Q nationwide monitoring stations during the fall of 196g. Fish were analyzed for r»sldues of 11 orqanochtorlne insecticides, llplds? and PCS-s. sane as above Henderson, eta I Henderson, etal (1971), AMIC-H.97 a,c,e,f. One hundred sixty-four Alabaster brd (HW) pesticides, wetting agents, and (1969), or soft miscellaneous wafer pollutants showed a AMIC-5b?5 (S4) syn- wide range of toxiclty spanning 12 orders thetlc of magnitude. Knowing the toxiclty and dilution percentage of all components of a water, or formulation did not result In easy •eaumter predictability of the toxiclty of a ------- Covoound Field Field Organism Study Location Toxlclty, Active Ingredient, Pp» Experimental Variables, Control led or Noted for some mixture of species pesticides Consents Reference Materials. Sometimes were most toxic In hard water Heotachlor Heotachlor Lepomls cyan11 us (Resistant) BS» 1.96 (T2> Leoomls cyanellus (Susceptible) BS» 0.07 (T21 and sometimes the ooooslte Has true. Testlnq the actual material as sold was found to be essential. Green sunflsh from BelzonI, Miss. Ninchew, et were resistant to Chlordane, Heptachtor, al(197»), Llndanp, and Strobane, but not to MIC-5«t71 Parathlon. Golden shiners fro™ the same location were resistant to Llndane and Strobane, tolerant to Chlordane and Heptachlor, and susceptible to Parathlon. Lack cf resistance to Parathlon indicated lack of agricultural usaoe of orqanochosphates in that area. Resistant fish were compared to susceptible ones collected at Starkvllle. sane as above Hlnchew, et al (10701, Heptachlor Heotachlor Notemlgonus crysoleucas (Resistant) Noteilgonus crvsoleucas (Susceptible) BS» BSA (T3) 0. ------- Hepfachlor Keptachi or Heptachlor u> Heptachlor Palaeonet«s KadlakensJs (non- real slant) Het«ropneU3- tos fossills Aphlpnous cuchta BSA 0.01.06 (Til 1.0 (S3 2 hr,K — <•«. hr) Medium toxlcity, Guthlon, Llndane, Toxaph«ne« StrobaneJ lease toxic Chlordane, Sevln, and Heptachlor. same as above Epldernal lesions of catfish barbels were moderate to severe after exposure noted. Barbel curllnq and Inactlvatlon were associated effects. Naavi, «t 81 Konar BSA 2.0 (K31 »,c,dte,f Konar All bloassar animals xere collected locally sooarently near Muzaffarpur. Bihar, India. The bloassay «MIC-i.<.» consisted of a simple \| ar (8-llter) with dally solution renexal (except for plankton studies In xhlch solutions «re not renewed). A safe apallcatlon rate of 0.813 Ib/acre was suggested for survival of Host aquatic species. Anabus trstudlncus BSA 0.5 (K3> a.e.d.e, f sane as above Konar I19TO) . Heptachlor Heptachlor H«pt»cMor Channa ounctatus (frvl Channa punctitus (adult) Esenius danrlca BSA BSA — BSA 0.001 (Kilt Z.O (K2I 0.2 (Kt) a.ctd,e,f same as above sane as above sane as above Konar (19701 . AMIC-M.8 Konar I197P) , Heotachlor Heptachlor Heteropnoua- tea foasllis Mry) BSA 0.016 (K2> a,c,d,,f H«tropnau«- BSA tes fossllis (adultt 1.0 (K2> a,c.d,e,f sane as above sane as above Konar (19ro),AMIC- Konar (1970) , AM!C-i>ii8 ------- s Coapound Heptachlor Heptachlor Heptachlor Heptachlor Heptachlor Heptaehlor Heptachlor Heptachlor Heptachlor Heptachlor Heptachlor Field Field TJrqanlsa Study Location Oaphnla BS A Oiaptoeus BSA — — Gastrotrlcha BSA — Naupl lus RSA Pandorlna BSA — - Volvox BSA — Anlsoptera BSA -- (nynphs) Belostoaa BSA — Indlca Cybister SB. BSA — Oytlscus sp. BSA (larvae) Oytlscus SB. BSA — (adult) Toxiclty, Active Ingredient. Poa 0.1 (K) 0.1 IK) 0.1 (NT) 0.1 (K) 0.001 (K) O.OD1 (K) 0.01 (K5) 2.0 (K3) 0.1 (K3) 0.05 (K2) 0.1 (K3) Experimental Variables. Control led or Noted a.c.d.e.t a.c,d,e, t a.c.d.e.f a,c.d,e, t a,c,d.e,f a.c,d,e,f ,,c.d...r a.c.d.e.f a.c.d.e, f a.c.d.e.f a.c.d.e.t Comments save as above saae as above sane as above sane as above saae as above saae as above saae as above sane as above saae as above saae as above saae as above Reference Konar (1970). AHIO ttft Konar Konar (1970) . Konar (1970), Konar AMIC-«i<.S Konar (197(1) , AHIC-H8 Konar (19711). Konar (1970), Konar (1970). A1TC-H8 Konar (1970), »HIC- Konar (1970). ------- k vn Hepfechlor Heotachlor HeptaeMor Heptachtor Meotacnlor Heotachlor Hepfaehlor Heotachlor HepfaeMor Heptacntor HeptacMor Heotachlor Heptachtor HeotacMor Heptaehlor Hydroohllus BSA -r sp. Neoa so. BSA Notonecta so. BSA — Ranatra BS» fillfornls BSA annulatun Hystus - BSA vlttatus Nsndus nandus BSA ~ Puntlus BSA Trlcho a,c,d,,t 0.007 (K3) a.c.d.e.f 0.5 (Kit 0.1 (ICH 0.3 (K3I 0.1 (K) Cyorls BSA 0.1 (K) 0.1 (Kl) a.c.d.c.r a.c.d.e.f 0.1 (NTEi a.c.d.e.r a.c.d.e,f 0.001 (K) a.c.d.e.f a.c.d.e.f a.c.d.c.f sane as above sane as above sane as above same as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above same as above sane as above sane as above Konar(1970J, A1IC-8 Konar (1970», 41IC-UI.8 Konar (19701, AMIC-lt8 Konar 11973), Konar (1970) ,A«IC- Konar (1970),AHIC- Konsr (1970) , Konsr (1970) , AMIC-«.l(8 Konar (1970) , Konar (1970), f.1.8 Konar (1970). ------- f & Compound Meptachlor Meotachlor Hexachl orobenzene Hexacnl orobenzene Hexach 1 orobenzene Hexachl orobenzene Hexachl orobenzene H« xach f or odl me thy 1 cut Ton* Toxlclty, Experimental Active Variables. Field Field Ingredient, Controlled Organism Study Location Ppm or Noted Comments Labeo rohlta BSA — 0.0? (Kl> a,c,d,e»f same as above (early f inserting) Labeo rohlta BSA ~ 0.20 (K2) a,c,d,e,f same as above (late f Inqer ling) Anqullla FRL St. John, 0.01 (residue) — rostrata N.R., Can. Esox nlqer FRL St. John, 0.03 (residue! -- N.B., Can. Salmo salar FRL St. John, 0.002 N.B., Can. (residue) Cluoea FRL St. John, 0.003-0.006 harenqus N.B., Can. (residue) Scomber FRL St. John, B.001 scombrus N.B., Can. (residue) Phormldlum L — 0.5-10.0 (NTE) — ambiquum PCB""s were found In higher concentrations than organochl or ine pesticides In all fish analyzed. The authors point out that PCB is less toxic In an acute sense than orqanochl orines, that little Is Known of sublethal PCB distribution and effects is needed. same as above same as above same as above same as above Of 7i» chemicals evaluated as alqlcides, only 9 Here more toxic than Reference Konar (197B»,»MIC- U<.B Konar (1970), AHIC- <>t8 Zltko (1971), AMIC-S71S ZltHo(197U, AMIC-371S ZltKo(1971), AMIC-371«: Zltko (1971), AMIC-3715 ZltKo (1971), AfIC-3715 Otto<1978) , AHIC-89Z CuSO<>. None Inhibited growth of mat-forminq algae for more than ? weeks. CuSOi. formulated xlth certain netting agents Has more toxic than CuSOl> alone. Cooper chloramne Has also found to be more toxic than CuSnit. No netting agents Here found to be Inhibitory at the concentrations investigated (H.05 and 0.005 ppm). Also reported are factors affecting growth of algae in canals to determine Hhether there Here leads to controlling alga* by environmental ------- Hexedecanol (Preoarat »lfol HV IB) Copeoods 8SA (NTE) Hexadecanol (Praparat Alfol HV 10) Mexadecanof (Praparat Alfol HV > 10) TO Hexad»eanol Cr» (Praparat Alfol HV -1 10) Hexadecanol (Praparat Alfol HV 101 Hexadecanol (Praparat Atfol HV 10) Hlllvale Fly dip Oaohnla BSA — TublMclds BSA — LeblstM BSA retlcutatus Salmo 9SA qalrdnerl Gerrls BSA — Rasbora BCFA heteromorpha and BSA (NTE) INTO (NTE) (NTE) (Suffocation) 2.1 (Tl) »,c,e,f. bard (HV) or aoft {«) ayn- thetio water, or aeawater for >on« •peclai Hlstaalnc phosphat Ncqaorlon brevlrostrls (1-3 ko) BSA kt (NTE 2 nr) a,c,« •anageeent. No practical environmental means were found. The formulation was applied to fann the Hater surface at concentration levels (1971),AMIC- to yield a more or less continuous 3079 •onomolecutar layer. Gerrls and other surface-oriented aauatlc Insects as Hell •s Insect larvae that surface to breathe and hatch could not maintain themselves at the surface and therefore sank and suffocated. same as above "ann same as above same as above sane as above same as above 3079 Hann (1971 3079 ,AHIC- Mann(1971) AMIC-3079 Hann I1S71),AMIC- 3079 Mann tl«71),AMIC- 3079 Alabaster, 11969),A1IC- One hundred sixty-four pesticides, wetting aqents, and miscellaneous water pollutants shotted a wide ranae of toxlclty spanning 12 orders of magnitude. Knotting the toxicity and percentage of all components of a formulation did not result In easy predictability of th« toxlclty of a mixture of materials. Sometimes pesticides xere most toxic In hard water an-1 sometimes the opposite was true. Testing the actual material as sold Has found to be essential. Data from study of drug effects Batdrldqe on youncj lemon sharK% wore treated fllft^l, mathematically to demonstrate AMIC-3132 applicability of classical rate theory to the study of chemical shark deterrents. ------- Conoound Field Field Organism Study Location Toxlclty, Active Ingredient, PDH Experimental Variables. Control led or Noted Comments Reference Hobstone OSD Crangon cr angon BSA 1.0-3.3 (T2> Hoc SC 178D Cranqon cranqon BSA 330-1000 (T2> Holl-Cne» 622 Steethead trout (tInqerlInqs) BS — 3.2 (W Boll-Chen 622 Houqhtosolv* Coho salmon BSA (ringerllngs) In altu Hood Canal, Hoodsport, Wash. Cranqon crangon BSA — 0.1 (K) 10-33 (T2> Tncaoacltatlon (narcosis) Has the primary parameter timed for effectiveness. This nas usually qulta rapid for the more effective drugs. ac(contin- One hundred-forty surface active Portmann, et uous aer- agents, solvent emulslflers, pesticides, al (1971). ation, sea. poI yenlorlnated blohenyls. oure AMIC-7781 water, and inorganic, and organic cheolcals Here dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) oubllshed data of this tyoe deal Hith toxlclty of chemicals to freshwater organ Isms. a-(contin- One hundred-forty surface active Portmann, «t uous aer- agents, solvent emulslflers, pesticides, al (1971), ation, sea-oolych lorlnated biphpnyls, oure ANIC-7701 water, and Inorganic, and organic chemicals Here daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) oubltshed data of this type deal with toxlclty of chemicals to freshwater organisms. -- Fvatuatlon of 11 oil dlsoersants Tracy, et resulted In a ranking for each and a alfl969). recommendation for use according to the ANIC-383<> ranKina. Ranting Has based on toxiclty and oil dispersal effectiveness. Corexlt 776". appeared to have the least toxlclty with fair to good oil dispersion capabl 11 ty. same as above Tracy, et al (1969), a«{contin- One hundred-forty surface active uous aer- agents solvent emulslflers, pesticides, ation, sea-Polychlorlnated blphenyls, pure water, and Inorganic, and organic chenlcals Here daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal Kith toxlcity of chemicals to freshwater Portmann, et al (1971). AHIC-7701 ------- organisms. Hydrochloric acid Brook trout OH 3.5 (SBlt) Hydrochloric acid r VO Hydrochloric acid Hydrochloric acid Hydrochloric acid Hydrochloric acid Hydrochloric acid Hydrochloric acid Hydrochloric acid Br»chycentrus 8CFA americanus (larva* and nymphs) BCF» — BCFA — Cohemerella suhvar la (larvae and nymphs) Hydropsyche bettenl (larva* and nymphs) Taenlopteryx BCFA maura (larvaa and nymphs) Boreria vlnosa (larva** and nymphs) Acroneurla lycorlas (larva* and nymphs) Stenonema rubrum (larvae and nymphs) Ophlogomphus BCFA ruplnsulensls BCFA — BCFA — BCFA — Excessive mucin accumulated in Vaala. et al the gill region of exposed trout. No evidence of enhanced hemoooiesis or (1969)AMTC Increased red cell destruction Mas found. 5709 The authors concluded that one of the reasons for trout deaths In acid water is that compensatory erythrooolesis does not occur or Is not rapidly Initiated. pH 1.21-1.8 a.c.d.e PH a«c,d,e •».35-5.05>8 a,c,d,» (T pH Z.90-3.7<» a.c.d.e tauatlc Insects generally Here tolerant of acid conditions for at least one weeK. Th* organisms died .at pH values be I ox those normally found In streams. The authors point out that ecological factors In streams may cause different results. Research on long-term effects on nolrtng, growth, reproduction, and survival Mas recommended. seme as above pH 3.15-3.1.1 a.c.d.e PH 3.31-3.71 a.c.d.e same as above same as above same as above same as above same as above same as above 811, et al »>1IC-5988 al Bel I, et (1969), AKIC-5988 Bel 1 , et al (19S9I, Bell, et al (1969). AHIC-5988 Bel I, et al (1969), AMIC-5988 Bel I, et « (1969), A1IC-5988 Bel I, et al (1969), AMIC-5988 Bel I, et al (1969). ------- Compound Hydrochloric acid Hydrochloric acid Hydrochloric acid Toxiclty, Experimental Active Variables, Flold Flald Ingredient, Controlled Organism Study Location Poa or Noted Comments (larvae and nymphs) Isogenus BCFA — frontal is 1 larva and nymphs) Pteronarcys BCF» — • dorsata (lrvae and nymphs) Carclnus BSA ~ maenas PH 3.20-<».0 to test the effect of hydrogen sutflde on al (1970), Pike eggs and sac fry and the effect of AMIC-5516 oxygen concentrations on hydrogen sulfide toxlclty. Eggs subjected to hydrogen sulflde produced a higher oercentaae of sac fry with anatomical sailor-nations. Sac fry hatched from eggs held at the higher hydrogen sulfide concentrations were smaller than the controls. Sac fry subjected to hydrogen sulflde showed decreased gronth rates at the higher concentrations. The level of dissolved oxygen was significant only in relation ------- Hydrogen sulfl, Daphnla was generally the most sensitive AMIC-<>53 organism. All of the Crustacea were affected by much tower concentration levels of herbicides than indicated by the TL Sub 50 values. All of the animals represent Important food chain links. Of 71. chemicals evaluated as Otto (1970) alglcldes, only 9 were more toxic than AMIC-892 CuSOi>. None inhibited growth of mat-forming aloae for more than 2 weeks. CuSOfc formulated with certain wetting agents was more toxic than CuSO ------- Coaoound HZS1F6 (as FLUOPIOE* ZAA latin* brushneed killer 10 lallne orast gronth regulator (Regulox) latine verqlclde •eedklller D Toxicity, Experimental Active Variables, Field Field Ingredient. Controlled Organism: Study Location Pp* or Noted Comments Plmephates BCF — promelas woirria i> papullfara Sal mo BCF* ~ galrdnerl and USA Sal mo BCF* — galrdnerl and as* Sal mo BCF* — galrdnerl and as* 0.8-0.13 (NT) a,c,d,e,f ,r»,s 100 (X) Hunter's medium diluted 1:5 27 CTZ) a,c,e,f. hard tHil) or soft (SVO synthetic dilution Hater, or seaHater for some species 56 IT21 a»,c,,T, hard (HH) or soft (SH) synthetic dilution water, or aeawater tor some spades 3.3 (TZI a'.c.e.f. hard(HH) or soft ISMI synthetic dilution Hater, or seauater for some soec las same as above All compounds were harnful to duckweed to aorae decree. Decreased populations were noted at non-lethal concentrations and some compounds (Kalathlon and 2A-D) caused teratogenlc affaeta at concentrations aa low aa 1 ppm, One hundred sixty-four pesticides, netting aqents,_and miscellaneous Hater pollutants showed a Hide range of toxicity spanning 12 orders of magnitude. Knowing the toxicity and percentage of all comoonents of a formulation did not result in easy predictability of the toxicity of a mixture of materials. Sometimes pesticides Here most toxic in hard Hater and sometimes the opposite Has true. Testing the actual material as sold Has found to be essential. same as above same as above Reference Arthuret al U971), ANIC-3290 Worthley, at al (1971), WUC-3233 a Alabaster (196g> ,AMIC— 5iZ5 alabaster (1969), HIC-5<.?5 Alabaster tl9S9).AMIC- 51.25 ------- lodoacetic add Phormldlum •e-blquum L — O.f-10.0 (100 percent growth Inhibited 1O Toxynll Na Basher BCFA heteromorpha and BSA 68 (TZ, hard-water) loxynll Na Rasbora BCFA heteromorpha and BSA 3.3 (T2, softwater) hard (HM)or soft (SHI synthetic dilution water, or seaiiater for son* species atcte,f. hard (HM)or soft tsu) synthetic dilution Hater, or seatiater for son species Gammarus faiclatus BS» — 19.0 Of 7it chemicals evaluated as alqlcides, only 9 Mere mart toxic than Cu<>0<>. None inhibited qrowth of mat-forming algae for more than ? HeeHs. CuSO ------- Compound Field Field •Organism Study Location Toxlclty, Active Ingredient, Ppm Experimental Variables. Controlled or Noted Comments Reference ' Iron I Iron Iron Iron Iron Iron Iron Paralafarax clathratus FH Paralabrax elathratus Paral abrax elathratus Paratabrax clathratus Par at abrax clathratus Paralabrax clathratus Paralabrax elathratus (gravid FH FM FH FH FH FN Scatterqood <>>> (dorsal Steam PI ant i Muscle Los Angeles, residue) Cat. Catallna 3? (dorsal Island, Cat. muscle residue* Scatterqood ------- females! ro -a vn Iron Iron Iron Iron Iron Iron Iron Iron Paralsbrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paratabrax clathratus Paralabrax clathratus Paralabrax elathratus Paralahrax clathratus Iso-oroovl Rasbora Z,«»» dlnI tro-6-sec-bu heteromorpha tylphenyl carbonate FH FM FH FH FH FH FM BCFA and BSA Scattergood 160 (liver Steam Plant, residue) Los Angeles, Cal. ratalIna 205 (liver Island, Cal. residue) Scatterqood 72 (Integument 5t«am Plant, residue) Los Angeles« Cal. Catallna 77 I Integument Island, Cal. residue) Scatterqood <> 80 (heart Steam Plant, residue) Los Angeles, Pal. Catallna 6 same as above same as above same as above same as above same as above same as above same as above same as above Staoleton (1968), AMIC-S980 S tao I « ton a,c,e,t. One hundred sixty-four hard (HH) pesticides, wetting agents, and or soft miscellaneous xater ool lutants shotted a (SVO wide range of toxlclty scanning 12 orders synthetic of magnitude. Knotting the toxlclty and dilution percentage of all comoonents of a Hater, or formulation did not result In easy seawater predictability of the toxlclty of a forsoma mixture of materials. Sometimes species pesticides Here most toxic In hard Mater and sometimes the oooosite Has true. Testing the actual material as sold Has found to be essential. Staole.ton (196S1 , AHIC-59SQ Staoleton (l^sa), AMIC-5990 Staot eton (1968), AHIC-5980 Staol eton (196M, Staoteton AMIC-5980 Staoleton (19f>8) , AMIC-5980 Alabaster (1969), AHIC-5%25 ------- I Ori Comoound I.C. I. Summer sheep dip Jansol v-60 Jansol v-60 Jansol v-60 Jan-Sol v-60 Jan-Sol v-60 Toxlclty. Active Field Field Inqredlent, Organism Study Location Pom Rasbora «CF — I..1 (T2I heteromorpha and BS* Pimephales BS* -- aporox. 56.0 promelas (Ti») Pimephales BSA — approx. 7.5 promelas (HSCI Biochemical L — 350.000 oxygen demand Steel head BS* — 35.5 CT1 trout (f Inqerl Inqs) Coho salmon BSA Hood Canal, 0.8 (K) ( f 1 nqer 1 1 nqs ) In Hoodsport, situ Wash. Exoerlmental Variables, Control led or Noted Comments a'.c.e.f. hard ) Bioassays Here conducted at 12 C. Harking The toxlclty of Juqlone to rainbow trout (1970),A1IC- and blueglI Is .Mas not altered 5517 ------- 5- a Juglone Juqlon* Juglone Ju9lon* Esox luclus BSA auratus Cyorlnus cvolo Catostomus co»i»»rsonl BSA — BS* BSA 0.0271 ITVI 0.080 (T significantly In Maters of different tenoerature or hardness. Standard (oH 7.1.) and buffered (DH 9.0) solutions of Juglone aaed for one Meek effectively killed ralnbOH trout although acoroxlmately three tines as much Jug I one Has r'-julred at the hlqher oH. Juqlon* Is ea;Ily reduced to less toxic components by factors In the natural environment. However, Juqlone Is sufficiently persistent to eltnlnat* target fish. sa«e as above sane as above same as above save as above Marking (1975) , AfIC-5517 Marking (19701 , AMIC-5517 Harking 11070). SMIC-5S17 Marking Juglone Jugfone Juglone Jug) on* Ictaluru* ••las Ictalurus punctatus l«ools cyan«!I us BSA — BSA — BSA lepoitls BSA •aerochlrus 0.0757 0.0367 (TV) 0.01.69 (T«l 0.01.29 (TV) sane as above sane as above sane as above sane as above Harking (1970) , AMIC-SS17 Marking (19701 , AMIC-5517 Marking (197D). AHIC-S517 Marking (197C) , Kartex Kelth«ni> eoccus saxatilis (finq»rlIngs) Tublfex tublfex BSA FL Relzonl, and Hiss. 3.0 (Ti,) 0.50 (NTC1 a,ctd,e,f Strioed bass ftnqerllngs ner* He)(born ,D and apparently much nore sensitive to (1969). iron therapeutic and herbicldal compounds than AHIC-5723 •any freshwater fish. The response of pesticide-resistant aquatic organisms to Naqvl. »t at (1969). ------- Compound Organise) Field Field Study Location Toxlcity, Active Ingredient* PD» Experimental Variables, Controlled or Noted Comments Reference 8SA Ketoendrln Ketoendrln Kief es Anaeystls L nl <1u I ans Agmenellum L — qimdrup. lleatwT Puntlus tlcto — — 0.5-1.0 (growth a»c»r Inhibited) SH NTt 0.00017 m> a».c»,r SH a.c,d,e,f various pesticides was compared to the resoonse of non-resistant species. Pesticide-resistant species were collected at Rplzonl and non-resistant species at State College. Cooepods, clams, snails, and sludge worms from Belzonl were considerably more tolerant to pesticides than the non-resistant organisms. The authors note that the effect of Increased tolerance In the organisms Is an Increase In the amount of pesticide residues available to animals of hlaher trophic levels* Metabolic products of Aldrln, Oleldrln, and Endrln can be as toxic as the oarent compounds, as shown by 00 measurement. same as above AHIC-5979 Batterton, al (1971), AHIC-1%71 Batterton, et al(1971) AMIC-1J.71 Of the pesticides Investigated, Bhatia the most toxic Has Klofos followed in (1971),IHIC- decreaslnq order by Sunlthion, Nalathlon, 523 Formlthlon, Olnecron, Sevln, and BHC. The author cites the need for more selective pesticides nontoxlc to fish or antagonistic agents for reducing fish toxlclty. LAS Plmeohalos BCFA promelas Lauryl ether sulfate Cardlurn edule 8SA (plus ethylene oxide) 3.5 CTi.) (T2) a».e al L»S acted synerqjstleal I/ with Solon, «t parathlon to cause less survival of (1969), fatheris but had an Indeterminate effect »MJC-37S5 with DDT and no synerglstlc effect with Endrln. at-(contin- One hundred-forty surface active Portmann, et uous aer- aqents, solvent emutslflers, pesticides, al aticn, aea-POlychlorlnated blphenyls, pure (1971),AMIC- water, and Inorganic, and organic chemicals Here 7701 dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxiclty of chemicals to freshwater ------- organism. Lauryt ether sulfate Cranqon (plus ethylene erangon oxide) BS» — qreater thanlOO a«(contin- (T2> uous aer- ation, sea- water, and dully solution renewal) same as above Portn>ann,et •I (1971), »NIC-7701 Leuryl ether sulfate Carelnus (elus ethylene vaenas OK loci BS» —• greater thanlOO a«(contln- CTJI uoua aer- ation, sea- water, and daily solution renewal) same as above Portmann.et el 11=171), AKTC-7701 Lauryl ether sulfate Panda I us lotus ethylene nontagul oxide) BS — greater thanlOO. a«(contln- (TZ> uous aer- ation, sea- water, and dally solution renewal) sane as above Port»ann,eT al (1471), AHIC-77B1 Lead arsenate Lead carbonate Fish Inot specif led) Carass1us auratus greater than 10-100 (K) 110 IT7) Lead nitrate (as lead) Cardluei edule 8S» — greater than 500 (T2) Aporoxlmat* toxlcltles of nunerous oestlcldes cownonly used In Britain ir«r« sum«arl2* ------- Toxlclty, Active Field Field Ingredient, Compound Organism Study Location Ppm Lead nitrate (as Pandalus BSA — 375 CT2) leadl tiontaqul Experimental Variables, Controlled or Noted Comments Reference renewal) published data of this type deal with Toxlclty of chemicals to freshwater organisms. e(contin- same as above Portmann, et UOU3 aer- at (1971). ation, sea- HHT.C-7701 water, and daily solution renewal) lead nitrate Car ass 1 us L — auratus 6.6 (T7I a,c Lead sulfate (as Pbl Lend sulfate (as Pbl Lead sulfate (as Pbl Lead Acroneurla BSA Ephemerella BSA — Hydroosyche BSA — (T1U) 16 (T7I 3? (T7> a,c«d«e« f In addition to toxlclty data. Heir, et al conditioned avoidance response was (1970), studied at sublethal concentrations. The AMIC-739 lowest concentration of metal resulting In significant impairment was! arsenic, O.int lead, 0.071 mercury, 0.0031 and selenium, 0.25. Deleterious effects occurred at metal concentrations approximately similar to potable water standards. Ephemerella (mayfly) was the most HarnleK, et sensitive aguatic Insect of those studied, and copper the most broadly toxic metal. The authors suggest that aquatic Insects may not be as sensitive to heavy metals as fish. a,c,d,e,f sane as above a»,c,d,e,t same as above al(1969>, •MIC-3767 Varnlck, et al(1969), AHIC-3767 HarnicK, et al 11969), ANIC-3767 Coregonus FL Moose Lake, 0.5 (residue) cluoeaformis Can. Concentrations of 13 toxic elements in dressed fish from heavily industrialized and non-industrialized areas were determined. Only mercury exceeded regulatory Halts, and concentrations of most elements Mere essentially the same in fish from both Uthe, et (1971), AHIC-3819 al ------- artas. Lead Lead Coregonus FL clupeaformls Esox luclus FL Lake Ontario* Can. Moose Lake, Can. 0.9 (rasI due I 0.5 (residue) same as above sane as above Uthe. et al (1971), Uthe, et al Lead Esox luclus FL Lake St. Pierre, Can. 0.5 (residue! sine as above Uthe. et Lead Lead Lead Lead Esox luclus FL Osnerus •ordax Perca flavescens Paralabrax clathratus FL FL FH Lake Erie, Can. Lake Erie, Can. Lake Erie, Can. Seattergood Steam Plant, Los Angelas, Cal. .9 (reslduel 0.5 (residue) 0.5 (residue) 2.1 dorsal muscle residue) Lead Lead Paralabrax clathratus Paralabrax clathratus FM FH CatalIna 1.3 (dorsal Island, Cal. muscle residue) Scattergood 1.1 (ventral Steam Plant, muscle Los Angeles, residue) Cal. sane as above sane as above sane as above same as above Fish collected front en effluent ploe of a steam plant and from offshore Maters of Catallna Island were analyzed for trace element content. Trace element content of the effluent xater Mas at least 5 times greater than that of normal sea water for cadmium, coooer, nickel, Zinc, and chromium. Livers of fish trow the effluent Mere nearly twice the size of those from the ocean. Greatest differences In concentration occurred Hlth aluminum, cadmium, and nickel. Sliver, barium, lithium, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on marine organisms. sane as above Uthe, et al (1971), »MIC- 3819 Uthe, et al «1971),A1IC- 3819 Uthe, et al (1971) ,»MIC- 7S19 Staoleton (1968), «MIC-S9M> Staol eton (196S), S tao I eton (196S), AMIC-S980 ------- Conoound Lead Ltad Lead Lead Lead Lead Lead Lead Lead Lead Orqanlsn Paratahrax cl athratus Paralabrax cl athratus Paral abrax cl athratus Paral ibrax cl athratus (qravl ------- Lead Llndane (aa»» Llndane UI Llndane Paralabrax clathratus Paralabrax elthrtus HHCI Fish (not specified) Lepoals cyanIlus (Resistant) FH Scattergood 2.2 (eyeball Stea Plant, residue) Los Anqeles, Cal. FH Catallna 3.<> (eyeball Island* Cal. residue) greater than 0.01-1.0 (K) 1.93 (TZ> Leoowls cy ane11us (Susceptible) BS» — 0.05 (T2) save as above saae as above Approximate toxleltles of nuwerous pesticides commonly used In Britain Hre suntrnarized. An excellent brlelt qenvral discussion of toxlclty testing is also present. Stapleton (196B). 4MIC-5990 Stapl»ton Haxdesley-Th omas 11971 AMIC-1056 Green sunfish from Belzonl, Hiss. Hinchex, et nere resistant to Chlor^ane, Heptachlor, al(1970)> Llndane, and Strobane, but not to Parathi on. Golden shiners froi the same location Here resistant to Llndane and Strobane, tolerant to Chtordane and HeotacMor, and susceptible to Parathlon. Lack of resistance to Parathlon Indicated lack of agricultural usaoe of orqanochosphates In that area. Resistant fish were compared to susceptible ones collected at Starkvllle. sane as above Mlnche», et Llndane Llndene Notenlgonus erysoleucas (Resistant) Notealgonus crysoleucas (Susceptible) BSA ~ BS« — 3.K, (TZ) 0.19 (TZ) sane as above sane as above Hlnchew, et alJ1979), AMIC-51.71 Ninclex, et al(1970), A1IC-5fc71 'Llndane Ictaturus punctatus BS» •— (TO at Orqanochlorlne Insecticides Here Haeek, tt synthetic the most toxic compoundst al (1 ------- Compound Llndane Llndane r (O Llndane L 1 n4an» L 1 ndane Llndane Llndane Llndane Li Man llndtne Field Field Orqanlsa Study Location Ictalurus BSA — ire las Carassius BSA ~ auratu^ Cyorinus USA — carplo PMephales ASA prone las Leponis BSA •acrochlrus Leoonis BSA — •icrolophus NIcrooterus 6SA — salaoldes Salno BSA — 9alrdnerl Salao trutta BSA Oncorhynenus BSA — klsutch • Toxiclty, Active Inqredlent, PPM 0.064 (T 0.131 (T 0.090 (Tit) O.OH7 ITI.) 0.06(1 (Tit) 0.083 (Tl.) 0.032 (Tit) 0.0?7 ITIt) 0.002 (TV) 0.01.1 (Tit) Experimental Variables, Controlled or Noted Conments a, synthetic test nater a, synthet Ic test Mater a. synthetic test water a, synthetic test Mater a, synthetic test Hater a, synthetic test Mater a, synthetic test Hater a, synthetic test Hater a( synthetic test Hater synthetic test Hater centrarchlds Hould IlKely be safe for cyorinlds and Ictalurlds. Sate levels for Ictalurlds or cyorinlds would and satnonlds. The use of goldfish In bioassays Mas discouraqed. sane as above sane as above same as above saoe •« above sane as above sane as above sa«e as above sane as above sane as above saae as above Reference MacrK, etal AMIC-5510 MaccK, etal (1970) , Macefct et »l (1970). MaceK, etal (1970, AHIC-5510 Mac«k, etal (1970) , HaceK, etal (1970), HaceK.et al (1070) , • M.IOS510 Hacek, etal (1970) , AMIC-5513 Macek, et al (197C), ANIC-S510 (1970) , •HIC-5510 ------- llndane vn Llndane Llndane Llndanc Perea ftaveseens Pataewonetes 3S» kadlaken>> 0.01I.-D.0373 (TH at same as above "acek. et»l synthetic (19701, test water Aiic-5510 a* Rioassays were conducted with Naqvi, et al shrimp from three areas of intensive (1970), pesticide use and from an unexoosed area. AHIC-5519 Previously exposed shrimp Here from i to 2^ tlires wore resistant than unexoosed shrimp. Both types of shrimp were also exposed in cages to Haters of the contaminated areas. Susceptible shrimp suffered 66 percent more mortality than did resistant shrimp. The toxlclty of the insecticides ranked in descending ord-r Has as follows: most toxic, Endrin, COT, Methyl parathlon, Parafhiont medium toxlclty, Guthlon, Llndane, Toxanhene, Strobanoj lease toxic Chlordane, Sevln, and Heotachlor. Pa Iaemone tes k»<11alnsl« (non- resistant) Moron* saxatllls (finger IInqs) BS» — BS» O.OOS1 (Tl) 0. ------- ,._ Llndane Llndane Llndane Organism Coo»oi'1s (Cycl oos bieusoldus. Cyetoos var leans. Cycl oos vernal is. Eucycloos aql 1 is. Macro cyclops al bidus, Orthocycloos modestus) Tubif ex tublfex Mercenaria mercenarla (eqqs) Field Field Study Location FL flelzonl. and Miss BSA FL Relzonl, and Miss. BSA L -- Toxlclty, Active Ingredient, Ppm 0.60 (87 percent KZJ <..« (NTE) greater than 10.0 (TZt Experimental Variables, Control led or Noted Comments Reference -- • same as above Naovi, et al ( 1°69) , AMIC-5979 same as above Naavi, et al (19f>9) , ANIO59T9 ~ The effect of 2 nestlcides on Davis, et embryonic develooment of clams and al(l°69). effects xlth solvents xere also reported. Host cf the co^Dounds affected develocwent more than survival. Some, however, drastically reduced larval grOHth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life staqes of an orqanism and note the oossiblllty of selecting chemicals for pest control that would not have serious effect on shell fish. Llndan LIndane Llndane Mercenarla oercenaria (larvae) Crassosfrea vlrqinlca (eqqs) Gamhusla affinis {female, 4.3 BSA greater than 10.0 (T12) 9.1 (TZ) 0.13 (T<») Oavls, et same as above — sane as above Davis, et al <19S9).A1IC- 5990 a,c,d, The five fish species are Nunoqana, et 8,f,l, commonly found In streams and estuaries at (1970), (Honolulu in semi- trooical areas. G. afflnls Has AMIC-6567 ------- f Llndane Lind&ne Lindajie Lindana Linear alxytate sulfonate Linear alkylate sulfonat* C«l, 1.9 ql Lehlstes retIculatus (male, 1.8 cm, 0.2 ql Tllapla nos salable* (3.^ cm, 1.3 0) Kuhlia BSA aandvlcensla (U.3 em. 1.5 a) otolephorus BSA purpurea (36 en, O.It- G) 8SA BSA 0.05 (T<0 0.06 0.00^ (T 12 hr) Pimeohales crone I a? BCFA BCFCH — 0.63 (NTE) prooel »s tap the most tolerant. Varied sensitivity to water) the toxicants were found. K. sandvicensis was the most sensitive fish studied. The standard nethod procedure Has foiloHed same as above ,c,d. »,t,i, (Honolulu tap water) ft,c,d,e,f,l (Honolulu tap water) a,c,d,e,f,l, salt water a,c,d,e;f,i, salt water al (197C), sane as above same as above same as above I.I .n, calc lum, maqnes lum« sol lum, sul fate, beryl I lum, strontium, Iron, boron, barium, a lum 1 num, zinc, CODDPr, cadm 1 um a»,c,d,f ', 1.) in, calcium, maqnesiun, sodium, cotasslun, sul fate, beryl I lun, strontlu»» Iron, boron, barium, aluminum, zinc, tcute and chronic toxlclty studies resulted in a laboratory fish production Index for fathead minnow. Lethality of LAS to nenly hatched fry was the most critical factor Hlth no effect at 0. pom on soawnlno eqq oronuctlon, or hatchabillty at this concentration. A funqus infection of mature wales occurred and was controlled by means of antibiotics. No accumulative mortality occurred. The application factor was calculated to be between 14 and 25 percent. The concentration of 0.63 pom was determined to be the maxinum acceptable concentration of LAS for fatheads. sane as above Kunopawa, et al (1970), AKIC-6567 Jiunogava, et al (197C), AKIC-65o7 Nunogawa, et al (1970), AKIC-6567 Plckerinq, et al (1 ------- Comoound Llnuron Llrostanol LIssaool IPA Lltsaool 1" Toxlcity, Experimental Active Variables, Field Field Ingredient, Controlled Organise Study Location Ppm or Noted Comments copper. cadmium Fish Inet -- — greater than — Approximate toxlclties of spec if led) 10-100 numerous Pesticides commonly used In Britain Here summarized. An excellent brief, general discussion of toxlcity testing is tso present. Rasbera BCFA — 0.04t ITZ1 a»,c,e,f, One hundred sixty-four heteromorpha and hard (HH) pesticides, wettlno anont^. anri BSA or miscellaneous Hater ootlutants showed e SOFTI1W) Hide range of toxlcity spanning 12 orders synthetic of magnitude. Knowing the toxlcity and dilution percentage of all components of a Hater, or formulation did not result in easy seawater predictability of the toxlcity of a species pesticides Here most toxic in hard Hater and sometimes the opposite Has true. Testing the actual material as sold Has tound to be essential. Crangon BSA — 1080-3300 IT2) a«(ecatln- same as above crangon uous aer- ation, sea- water, and daily solution renewal) Crangon BSA — 330-1000 CT2I a»(contin- ••• »s «bove crangon uous aer— •tion, sea- vcter, and daily solution renewal) Reference MaHdesley- Tho»as<1171) AMIC-1056 Alabaster (146QI , AM.IC-542S Portaann, et al (1971). AMIC-7701 Portmann, et al 11971), AHIC-77J1 Llssaool NX Rasbora BCFA heteromorpha and B3» 3.S ITZt a,c,e,t. One hundred sixty-four Alabaster hard {HH> pesticides, wetting agents, and 119691, or miscellaneous Hater pollutants shoHed a AMIC-912S SOFTfSM) Hide range of toxlcity spanning 1? order synthetic ef magnitude.. Knonlng the toxlcity and ------- Ll*a0ol NX Crangon eranqon BSA — 1010-3300 IT?) Lithium Paratabrax el athratus FH Seatterqood 6.9 {dorsal Steaa Plantt muscle Los Angeles. Cal. Llthiue Paratabrax ctathratus FH Catallna 6.2 (dorsal Island, Cal. muscle residual dilution oereentage of all components of a Mater, or formulation did not result In easy seaNater Dredictabllity of the toxiclty of a for some alxture of materials. Sometimes soecles pesticides Mere most toxic In hard Mater and soiretlmes the ooooslte MBS true. Testing the actual material as sold Mas found to be essential. a»(contln- One hundred-forty surface active UOU9 aer- aqents, solvent emuls1fiers, pesticides, ation, aea-Oolychlorlnated blphenyls, oure water, and Inorqanic, and organic chemicals were daily evaluated against as many as ten marine solution orianlsms. The authors noted that nost renewal} published data of this type deal with toxiclty of chemicals to freshwater organisms. — Fish collected from an effluent Dloc of a steam plant and fro« offshore waters of Catallna Island Mere analyzed for trace element content. Trace element content of th effluent Mater Mas at least 5 tines greater than that of normal sea Mater for cadmium, coooer, nlcKel, 7lnc, and chromium. Livers of fish from the effluent were nearly tMlce the size of those from the ocean. Greatest differences In concentration occurred ulth alurlnum, cadmium, and nickel. Silver, barium, lithium, and lead shoMed the leist differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on earine organises. sane as above Portn.ann, et al (l^Tll, AMIC-7701 Staoleton (1968), &MIC- 5980 Staoleton NIC-59»0 Llthlua Llthlun lltMua Paralabrax elathratus Paralabrax cIathratus Paral abrax cIathratus FH Scatterqood 6.7 (ventral Steaa Plant, muscle Los Angeles, residual Cal. FN Catallna Island, Cal, Scatterqood SteM Plant, 5.6 (ventral •use Ie RESIDUE! 0.6 (qonads residual saae as above saee as above save as above Staoleton 119(8), 41IC-S9SO Staoleton (1«6B>, AHIC-«i980 Staoleton (1968), ------- Comountf Llthlu Lithium LithluB Llthlu* LIthlua Llthlu- UthlUB Llthlu* Llthlua Lithlua Orqanls* Paratabrax clathratus Paralabrax el athratus (qravld females) Parat abr^x cl athratus Paral abraic el athratus Paral abrax clathratus Paralabrax el athratus Paralabrax ct athratus Paralabrax el athratus Paralabrax el athratus Paralabrax clathratus Field Study FN FN FN FN FN FN FN FN FN FH Flld Location Los Ang«l«s< Cat. Carat Ina Tstandt Cat. Catal ina Island, Cal. Scatterqood Ste»» Plant, Los Anqeles, Cal. Catal Ina Island, Cal. Scatterqood Strain Plant, Los Angeles, Cat. Catat Ina Island, Cal. Scatterqood Stean Plant, Los Angeles, Cal. Catal Ina Island, Cal. Scattergood St«aa Plant, Los Angeles, Cal. Catal Ina Island, Cal. Toxicity, Cxeerlaentat Active Variables, Ingredient, Controlled PPH or Noted 8. (gonads -- residue) 7.7 (gonads residue) 5.8 (liver residue) 7.J (liver residue) 6.8 (Intequnent -- residue) 7.7 (Integuaent ~ resldue) 7.6 (heart residue) 8.5 (heart residue) 580 (eyeball residue) l?fc (eyeball — residue) Comments sane as above sane as above same as above saae as above sa«e as above sane as above saae as above sane as above sae as above sa»e as above Reference AMIC-Sq&O Staoleton (19M) , A1IC-q ------- AKIC-5980 Lubrol APNS Car dl urn edule BSA — Lubrot »PNS Crnqon crangon BSA — 10-33 IT2) a«lcontin- One hundred-forty surface active UOU5 acr- aqents, solvent emulslflers, pesticides, ation, sea-polychlorlnated biohenyls. Pure water, and Inorganic, and organic cherlcals were daily evaluated aqalnst as many as ten marine solution orqanlsms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. 33-100 (T2> «(eontln- same as above uous aor- ation, sea- wator, and dally solution renewal) Portmann, et al J1971), AHIC-7701 Portmann, et al (1971), AHIC-7701 Lubrel L Ravbora heteroeoroha OCFA and BSA 16 CT2, hardwater) Lubrel L Pasbora heteromorpha BCFA and BSA 1Z.5 tlZ, softwater) Naqle Power Plmeohales orone I a* BSA H..O (T<»> hard (HM) or soft (SH> synthetic dilution Mater, or seaitater for some species s,c,e,f, hard (HHI or soft (SH) synthetic dilution water, or seawater for some species c,d,e,f One hundred sixty-four pesticides, wettlno aqents, and miscellaneous water pollutants showed a wide rarqe of toxlclty spanning 12 orders of magnitude. Knowing the toxlcity and percentaqe of all components of a formulation did not result in easy predictability of the toxicity of a mixture of materials. Sometimes pesticides were most toxic in hard water and sometimes the ooposlte was true. Testinq the actual material as sold was found to be essential. same as above Alabaster «1969), AHIC-6U2? Toxlclty of six oil spill dlsoersants was determined alonq with 800 values. Pond water was used as diluent and oil was Included in the experiment. Oil markedly reduced toxlclty of all dlsoersants. Data are Alabaster (1969), AMIC-54Z5 Zilllch (1969),AMIC ?909 ------- Compound Field Field Oroanlsm Study Location Toxlclty, Active Ingredient, Pom Experimental Variables, Control led or Noted Comments Reference Magic Power Poner Hegneslum Magnesium Magnesium Hagnesluf Plmeohnles prone las BSA — 2.7 (MSC) Biochemical L oxygen deeand Paral abrax clathratus ParaIabrax clathpafus P»ra1abrax clathratus Paralabrax el atnratus ParaIabrax ctethratus 880,000 given as "«ost probable* 96-hr TL sub c,d,e,f sane as above e,d,e,f same as above FM Scatterqood 1670 (dorsal Steam Plant, muscle Los Angeles, residue) Cal. FH Catallna ?190(dorsal Island, Cal. muscle residue) FH Scattergood 1BZO (ventral Steam Plant, muscle Los Angeles, residue! Cal. FH Catallna ?190(ventral Island, Cal. muscle residue! FH Scattergood 1010 (gonads Steam Plant, residue) Los Angeles, Cal. Fish collected from an effluent pipe of a steam plant and from offshore Haters of Catallna Island Here analyzed for trace element content. Trace element Content of the effluent Hater was at least 5 times en-eater than that of normal sea Hater for cadmium, cooper, nickel, zinc, and chromium. Livers of fish from the effluent Here nearly twice the size of those from the ocean. Greatest differences In concentration occurred Hlth aluminum, cadmium, and nlcKel. Silver, barium, lithium, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on marine organises. sane as above 711 IIch (19 ------- •Ugneslun Hagneslun Hagneslu* Nagneslua Paralabrax Clathrafus Paralabrax clatnratus (gravid feiales) Paralabmx elathratus FH FH FH Paralabrax FH elathratus Catal Ina ?<.?(! (gonads Island, Cal. residua) Catal Ina l«tZO Island, Cal. taonads P«sldU«» Seiittergood 690 (liver Stea* Plant, residue) Los Angeles, Cal. Catal Ina 100 ( liver Island, Cal. residue) sane as above saae as above same as above sane as above Staoleton (1968). AMIC-5980 AMIC-S98C Staoleton Slacleton 6S). Naqnesiu" Haqneslu Hagneslu* Paralabrax FH Scattergood 730 (Intequaent elathratus St»a» Plant, residue) Los Angeles, Cal. Pamlabrax FH Catal Inn 840 (Integunent clathratus Inland, Cal. residue) Par at abrax FH Scattergood 1Z80 (heart elathratus Steam Plant, residue) Los Angeles, Cal. Paralabrax FH Catal Ina 9<>0 (heart elathratus Island, Cal. residue) sane as above sane as above save as above same as above S t a o I e t o>\ aiIC-5980 Staoleton Staoleton I19SM , Stsoleton (t9SS) , Naqneslua Hagneslua Halachlte qreen Par at abrax elathratus Paralabrax elathratus FH FH Rasbora BCFA heteronorpha and BSt Scattergood 10SO (eyeball Stea» Plant, residue) Los Angeles, Cat. Catal Ina 1<»70 (eyebal I Island, Cal. residue! O.fcfe (Tl, nardNater) saae as above same as above a,c,e,t. One hundred sixtv-'our hard I!H) pesticides, netting agents, and or soft Miscellaneous water oollutants showed a (SW) wide range of toxlclty scanning 12 orders synthetic of magnitude. Knowing the toxlclty and dilution percentage of all comoonents of a Hater, f emulation did not result In easy Staoleton (196), •MIC-59S9 Staoleton AHIC-5980 Alabaster(19 69). ------- CoMoound nrqanisa Field Field Study Location Toxlcitvt Active Ingredient, PPM ExperI mental Variables, Control led or Noted Comments Reference Malachite areen Pasbora BCFA heteromorpha and BSA 0.0« (Tl, sottnater) Malachite areen Sal no qalrdnvrl flCFA anr, hardlHW) or soft (SHI synthetic dilution Hater, or seawater for some species same as above alabaster (1959).AIC- 51,25 sa«e as above Alabaster synthetic dilution same as above Alabaster (1969),AHIC- 525 ------- Malachite green fU Malathion Malathion Halafhlon Morone saxatllls ------- Coeoound Halatnion Malathlon Halathlon Halatrtlon Malathlon Field Field Orqnnls Study Location Salvellnus BCF* — f ontlnal Is (2.13 g) Sal«o elarKl BCF* ~ (0.33 q> Sal»o elarkl BCF* — (1.25 q) Sal»o BCF* — qairdnerl (0.1.1 q) Oncorhynchus BCF* — Kisutch (1.70 q) Toxlclty, Fxoerimental Active Variables, Ingredient, Controlled Pom or Noted Convents toxlclty. 120.0 (T<>> a«,c,d, sane as above e.r.l.o, aulfat. copper. annconase. iron, and chromium 0.15 (Ti>) a»,c,d, same as above •,f,i,o. auirate, copper, manganaia, iron, and chromium 0.20 (TO a«,c,d, saae as above e,r,l,o, aulfate, copper. manganese. iron, and chromium 0.12 (TO a»,o,d, sane as above e,f,i,o, auirate, coppor. manganese. iron, and chromium 0.269 (Tit) a«,e,d, sane as above e,r,i,o, aulfat. copper. nangoneaa. iron, and chromium Reference Post, et 4LI1971), 4MIC-181? Post, et (1971), 4HIC-1S1? Post, et (19711, MIC-1»12 Post, «t (197H, •MIC-1812 Post, et <1971! , »MIC-1812 al al al al Malathlon Cyorlnus L carplo 0.010 (SB) This study «as conducted to determine whether comoonents ot tissues fron various fish would Interfere xlth CLC determinations for Malathlon. Good NIC-37?8 ------- He lathIon RalatMon Halathlon Catostomuv cOMcrsonl Prca Esox nlq«r L — 0.010 (SB) 0.010 (SB) 0.010 (SB) recovery (80-96 percent) Mas obtained Mlth best recovery from shin. flesh, and gills. Recovery Has less successful In liver, brain, and blood. The author recommends the GLC orocedure as simoler than the us of activated charcoal. San* as above same as above sa«e as above ffaoab (19SS)t •HIC-3728 Raoab (1"6!» , • "IC-372IJ Raaab (I960), Helatnlon Halath\| on Notelionus L crysoleucas Piaephalas promelas 0.010 (SB) 16.0 CTI.) sane as above Raasb (1968) a.»,d,e,o, Halathlon and Its hydrolysis and Pa products were evaluated with the finding that one such oroduct (dlethyl tumarate) Has more toxic than Halathlon to fathead minnows. Syrterqls* occurred between Halathlon and two products of hydrolysis. Continuous exposure resulted in Increased toxiclty. Ha lath ion Ha lathIon Pimephales prone I as BCF» — Punt Ius tieto — — 11.0 (Tl a,d,e,o, and Ft a.c,d,e,f sane as above Bender (1969>>HIC- 3787 Bender (1919.) 3787 Of the pesticides investigated, the most toxic was Klofos fol loved in decreaslnq order by SUB it hi on, Halathlon, Formlthlon, Oimecron, Sevln, and PMC. The »uthor cites the need for more selective pesticides nontoxic to fish or antaqonistic agents for reducing fish toxiclty. Bhatla (1971) , A>1IC- Ha lath Ion Rasbora BCFA heteroaorpha and BS» 8 (T2> l.«,C,a,f, One hundred sixty-four hard (Htf) pesticides, nettlna agents, and or soft miscellaneous water ooltutants showed a tSW) syn- Hide range of toxiclty scanning 12 orders thetic of magnitude. Knowlnq the toxtclty and dilution percentage of all components of a water, or formulation did not result In easy Alabaster (1969), ------- Toxlclty, Active Field Field Ingredient, Compound Orqanlsm Study Location Pom Experimental Variables, Control led or Noted seawater species prertlctabll 1 ty pesticides were Comments of the most toxlcity toxic In ot a es hard water Reference Ha lath Ion Ictalurus punctatus BSA 6.97 (T<>) ro Matathlon Halathlon Malathion Ictalurus vet as Carasslus auratus Cyorlnus carpio BSA 8SA BSA 1Z.90 (T4) 10.70 CU) 6.59 CT<») and sometimes the opposite Has true* Testing the actual material as sold was found to be essential* a, Orqanochlorlne Insecticides were MaceK,et al synthetic th« most toxic compounds, (1970), test water orqanochosrhates Intermediatet carbamates 4MIC-5510 the least toxic. Brown trout Has the species most susceptible to orqanochlorInes, echo salmon the most susceptible to carbamates* and qoMfish Mere the least susceotlbte of all species. Safe concentrations established by bloassays ulth salmonids or centrarchlds would lih<-ly be safe for cyorinlds and Ictalurids. Safe levels for Ictalurids or cyorlnlds Hould probably be hazardous for centrarchids and salmonids. The use of goldfish In bloassays was discouraged. a, synthetic testnater synthetic test water a, synthetic test water same as above sane as above sane as above HaceH, et 81 C197PI, 4MIC-5510 NaceK.et al Mace, et al (197C), tMIC-5510 Halathlon Pl«ieohales BSft promelas 8.65 (T<>) a, synthetic test water same as above "acen.et al <19T0) . Malathlon M»lath Ion Leoomls macrochlrus BSA — Leoomls BSA •icroloohus 0.103 (Ti.) 0.170 synthetic test water a, synthetic same as above same as above aceK,et al (iq70), •HIC-SS10 HaceK.et al (1970>, ------- test water ANIC-5519 Halathlon Hatathlon Halathlon Halathlon Halathlon Halathlon Halathlon Halathlon Nalathlon HlcroPterus 3SA salnoldes Salmo galrdneri 8SA ~ Salmo trutta BSA Oncorhynchus BSA klsutch Perca IIaveseens BSA — O.ZB5 (Ti.) 0.170 IT4) 0.300 (Tit) 0.101 (Ti.) 0.263 (T«.) at same as above MaceK.et si synthetic (1970), test water a, synthetic test Hater a, synthetic test Mater synthetic test water sane as above same as above sane as above NsceH, etal (1973), HaceK, et al(197Q), Haeek.et (197T), AMIC-5510 al Morons saxatlIIs (f InqerlInqs) BSA Cyprlnus carplo 5 (S8«t) a, same as above KaceH, etal synthetic (1970), test Hater AMIC-SSIO a,c,d,e,f. All ccmoourHs were Invest iqated Wellborn p because ot their orobsble ussq* In (1971), hatchery oroductlon of Hhlte Ba^s. AHTC-S571 Conmounds that can be used at recommended concffn tra t I ons Here Aquathol, Casaron, Llndane, and Terranycln concentrate. Those That should not be used Here Acrlflavlne, Raylusclde, Malachite qreen oxaltte, and Malathlon. ~ Malathlon residues In carp Bender (1969) » occurred primarily in the liver and flesh ANIC-5731 Hlth lesser amounts In the brain, blood, and qills. Retention tine Has relatively brief Hlth most of the residue passing on or belnq metabolized within 1-2 days. Metabolism In the fish foreaut, degradation biochemically, and lack of uptake due to ION permeability Here cited as possible explanations lor the results obtained. Lack of persistence in fish couoled Hith slOH hydrolysis In the environment seem to Indicate that this compound has desirable characteristics regarding safety to humans. Cyprlnus carplo Copeoods FL State J.6-66.6 (residua) 0.025 (K3) sane as above The response of Pender(l<»69), AMIC-5731 Naavl, et al ------- Compound Halethlon Hetathlon Hatatnlon Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Org»nls« Study Location Ppm or Noted Comments Reference (Cyclops and College, blcusoldus, 8SA Hiss. Cvcloos var leans. Cyclons vernal is. Fucycloo* aqllls, Hacrocyclops albldus. Orthocyclops modes tusl Conenods FL Relzonl, 0.025 (13 — (Cyclops and Miss percent KZ1 blcuspldus, RSI Cycloos var leans. Cyelons vernal Is, Fucyeloos aqilis. Kacro cyolops albldus. Or t hoc vetoes •odestusl Tublfex FL Relzonl, 3.0 (NTE) tunlfex and Hiss. BSA Crassostrea L — 9.07 CTZ) — vlrqlnlea IC99SI oestlclde-reslstant aquatic orqanisus to (1969), various pesticides Mas compared to the «MIC-S979 r»soonse ot non-resistant species. Pesticide-resistant species were collected at Pelzoni and non-resistant species at State College. Copepods, clnms* snails, and sluHae Morn« froi* Belzoni Here considerably nore tolerant to pesticides than the nan-resistant organisms. The authors note that the effect of Increased tolerance In the organisms Is an Increase In the amount of pesticide residues available to animals of higher trophic levels. same as above Naavl, et al (1969), •HIC-5979 same as above Nsavl, et al (1969), AMIC-59r ------- M»lathi on Malathlon Crsssostrea vlrqlnlca (larva) Cardlu edule 8S» — 2.66 ITU.) 3.J-10 «T2> Nalatnlon Crangon crangen BS» — 0.33-1.0 (TZ) shellfish. same as above a(contln- One hunrtred-forty surface active uoua, aer- agents, solvent vmulslflers. pesticides. atlon, soa-polychlorinatea blphenyls. cure water, and Inorqanlc, and organic chemicals Mere dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal Kith toxicity of chemicals To freshwater organisms. a»(contln- same as above uoua, aer- ation, sea- water, and dally solution renewal) Davis, et al Portmann, et al U971), AMIC-7701 Portmann, et al (1971), AMIC-7701 Kalathlon Halelc >eM Wolffia papullfera Plnephnles prometas BS» Manazon Hancozeb Fish (not specified) Fish (not SD'Cifled) 100 (K) 5.0 greater than 100-1000 (K) greater than 1.0-10.0 (K) Huntera All compounds were hnrmful to Worthier, et medium duckweed to some degree. Cecressed 61 (1971), diluted populations were noted at non-lethal AMIC-3233 1:5 concentrations and some compounds (Halathlon and 2,L\|.-D) caused teratogenlc effects at concentrations as low as 1 ppn. a,d,e,o» HalatMon ana It; hydrolysis Bender and Fe products were evaluated iiith the finding (1969) .tire- that one such product (diethyl fumarate) 3787 was more toxic than Nalathion to fathead minnows. Synerglsn occurred between Malathlon and two oroducts of hydrolysis. Continuous exposure resulted in Increased toxlclty. Approximate toxlcltles of numerous pesticides commonly used in Britain were summarized. n excellent brief, general discussion of toxiclty testing is also present. sane as above Hawdesley- Thomasm A1IC-1056 Haw-lesley- Thoas(197l> Naneb Fish (not specified) greater than 0.1-1.0 (K) Approximate toxlcitles of Mawdeslev- numerous Destlcldos commonly used In Thomas Britain were summarized. An excellent (1971) ,AMIO brlef. general discussion of toxlclty 1056 testing Is also present. Haneb Agonus BSA — 0.33-1.0 (T?) One hundred-forty surface active Portaann, et ------- Toxiclty, Experimental Active Variables, Field Field Ingredient. Controlled Compound Organism Study Location Ppm or Noted Comments eataohractus (contln- aoents, solvent emulslflers, pesticides. uous, aer- pol ychlerlnated biohenyls, pure atlon, sea Inorganic, and organic chenlcals were water, and evaluated against as many as ten marine dally organisms. The authors noted that most solution published data of this type deal with renewal) toxiclty of chemicals to freshwater organises. •neb Asterlas BSA — 33-100 (TZ) •( contln- same as above rubens uoua, aer- ation, sea water, and dally solution renewal) aneb Cardlum edule BSA — 100-330 (TZ) a»(eontln- sane as above uoua aer- ation, sea- water, and dally solution renewal) •»>«b Crangon BSA — 3.3-10 a«(contln- same as above crangon uoua aer- ation, sea- water, and daily solution renewal) angaries* Coreqonus fl Hoose Lake, 0.7 (residua) — Concentrations of 13 toxic cluoeaformls Can. elements In dressed fish fro« heavily Industrialized and non-Industrial Ized Deference al 11971), AMIC-7701 Portmanr, et al (1971), AHIC-7701 Portwann, et al ll^T-u, AMIC-7701 Portmann, et al (1971), AMIC-7701 Uthe, et AL(1971), A1IC-S819 areas Here determined. Only mercury exceeded regulatory Units, and concentrations of most elements were essentially the save in fish from both areas. Manganese Coreqonus Lake 0.7 (residue) same as above Uthe. etal ------- Manganese Manganese Manganese Manganese cluoeaforals fsox luclus FL Fsox luclus FL Esox luclus FL Os«erus •ord»x FL Ontario, Can. Moos* Lake. 3.0 (residue) Can. Lake St. 3.2 (residue! Pierre, Can. Lake Erie, 0.9 (residue) Can. Lake Erie, 0.02 (residue) Can. saoe as above sane as above saae as above sane as above 4HIC-3B19 Uthe, et al (1971), »MIC- 3S19, Uthe, et • HI9M), »1IC-3819 Uthe, et al Uthe, et al Manganese Manganese Manganese Manganese Manganese Perca FL flavescens Paralabrnx FH cl athratus Lnk* Erie, 0.21 (residue) Can. Scatterqood 0.9 (dorsal Steam Plant, nuscle Los Angelas, residua) Cal. same as above Paralabrax FH Catallna 0.6 (dorsal clathratus Island, Cal. muscle residue) Paralabrax FM Scattargood 0.9 (ventral clathratus Steam Plant, muscle Los Angeles, residue) Cal. Paralabrax FM Catatlna 0.5 (ventral clathratus Island, Cal. Muscle Fish collected from an effluent oloe ot a stea™ olant and from offshore Haters of Catalina Island nerp analyzed lor trace element content. Trace element content of the effluent Hater was at test 5 times ore^ter than that of normal sea Hater for caditlum, coooer, nicKel, zinc, and chrowlu". Livers of fls fro* the effluent were nearly twice the size of those from the ocean. Greatest differences In concentration occurred Hlth alurlnum, cadmium, and nickel. Sliver, barium, llthlu, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on narine organises sane as above Uthe, et al (1971), »KIC 3819 Staoleton (1968) , •MIC-5980 sane as above sane as above Staoleton I196M , 4MIC-S9SO S t a o I e t on (1"68), AMIC-598Q Staoletor> (1968) . ------- Comoound Manganese Manganese Manganese Manganese Manganese Manganese Manganese Manganese Manganese Manganese Organism Paral ahrax cl athratus Paralabrax clathratus Paral afcrax cl athratus (qravid f ema 1 es) Paral ahrax el athratus Paral ahrax cl athratus Paral ahrax cl athratus Paral ahrax cl athratus Paral abrax ct athratus Paral abrax clathratus Paralabrax clathratus Field Study FM FM FM FM FM FM FM FM FM FM Toxlclty, Experimental Active Variables, Field Ingredient, Controlled Locat Ion Pern or Noted residue) Scattergood 1.1 (gonads — - Steam Plant, residue) Los Angeles, Cal. Catallna 1.7 (gonads Island, Cal. residue) Catalina 3.3 Island, Cal. (gonads residue) Scattergood 3.<» (liver Steao Plant, residue) Lois Angeles, Cal. Catalina <>.3 (liver Island, Cal. residue) Scatterqoort 0.7 (Integument — Steam Plant, residue) Los Angeles, Cal. Catallna 0.8 (Integument -• - Island, Cal. residue) Scattergood 1.6 (heart -- Steam Plant, residue) Los Angeles, Cal. Catallna !.<• (heart Island, Cal. residue) Scattergood 1.6 (eyeball Steam Plant, residue) Los Angeles, Comments same as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above Pef erence AMIC-S910 StaD I eton (1968) , AMIC-5981 Staoleton (1968) , AMic-sgan Staoleton (1968) , AHIC-^980 Staoleton (19&SI , AMIC-59SO Staol eton (19^8) , AMic-sgso Stjioleton (1968). AMIC-5980 Staol eton I19SM , ATC-5980 Staoletcn (1968). AMIC-5980 Staoleton 11968). AMIC-5988 Staoleton (19681. AMIC-59JO ------- Cat. Manoaoese Paralabrax clathratus FH Catatlna 2.6 (eyeball Island, Cat. residue) sane as above Staoleton (1961, Hanoxol Pasbora heteromorpha 16 (T2> and BSA r vn NCPA Fish (not soeclfl»d> Crassostrea vlrqlnlca (egqs) greater than 10-100 (K) 19.6 (T2) HCPA Crassostrea vlrqlnlca (larvae) 31.3 (Til.) a,c,e,f. One hundred sixty-four Alabaster hard (HH) pesticides, Mettlnq agents, and or soft miscellaneous Mater pollutants shOMed a (SHIsynthe Mine range ot toxlclty soainlno 12 orders tic of magnitude. KnOMlnq the toxlclty and dilution percentage of all comoonents of a Mater, or formulation did not result In easy seaMater predictability of the toxlcity of a for sone mixture of materials. Sometimes species pesticides Mere most toxic in hard Mater and sometimes the opposite Mas true. Testing the actual material as sold Mas found to be essential. Approximate toxlclties of "aMdesley numerous pesticides commonly used In Thomas Britain Mere summarized. An excellent (19M1 brief, general discussion of toxlclty 1056 testing Is also present. The effect of «!2 pesticides on Davis, et embryonic development of clams and (1969), oysters Mas reported. Synerglstlc ANIC-5990 effects Mith solvents »ere also reported. Most of the compounds affected development more than survival. Some, however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life sfaaes of an organism and note the oossiblllty ot selecting chemicals for pest control that would not have serious effect on she!I fish. sane as above Davis, et al (1969),AMIC- 5990 al Mecarb»« Fish (not specified) greater than 0.001-0.01 (K) Approximate toxlclties of MaMdesley- numerous pesticides commonly used in Thonast1971) Britain Mere summarized. An excellent AHIC-10S6 brief, general discussion of toxlclty testlnq Is also present. ------- 10 Conoouni Menazon Toxlcity, Experimental Active Variables, Field Field Ingredient, Controlled Orqanlsm Study Location Ppm or Noted Comments RasborK BCFA — 151, Acroneurla BSA Cohemere11 * BSA Hyrtroosych* BSA Uatersloora L cucul1sta (larvae) Buqula neritina (larvae) Solrorbls lanellosa (larvae) C.aleolarla caesolrosa ? (Tit) z mi 2 (Tit) 0.10 (T 2hr) 0.20 CT 2 hr) O.H (T Z hr) 0.12 (T 2 hrl t,t Fohemerella (mayfly) was the most War-nick, et sensitive aquatic Insect of those al(1969>, studied, and coooer the most broadly »1I! toxic metal. The authors suqaest that aouatlc Insects mav not be as sensitive to heavy metals as fish. ,c,d,e,f a»,c,d,e,t a,c,l, and salinity same as above same as above HarnlcK. et al (199), ANTC-J767 HarnlcK, et al This study was conducted To determine snecles ot marine larvae suitable tor use In test screeninq antlfoullnq chemicals. A. sallna (brine shrino) appeared to have the best potential tor this ouroose. A. sallna larvae sensitivity xas qreatest starting at age 20-AO hr, and tolerated relatively I ox oH (5.0). same as above Wisely, «T al (11S7I, AMIC-S70S salinity a,c,l, and salinity a.c.lt and salinity Wisely, et al sane as above sa«e as above Wisely, et a I II 967) , AMIC-S73 Wisely, et a I (1967), ------- (larva) »MIC-1>70S Mercuric chloride (as Hq) Mercuric chloride las Hq) Mercuric chloride las MI) Mercuric chloride las »ercury) Mercuric chloride las •«rcuryl Hytllus eluli? nlonulatus (larvae) Crassostrea comnerclalls (I arvae) Arteula salIna (larvae) Carclnus •aenas L — BS» — 13.1 (T 2 hr) 180.9 (T 2 hr) 1809 (T 2 hr) 1.2 (TZ) Cardlum edule 8S» — 9.0 (T3> and sailnlty a.CiI, and salinity •.,0.1, and salinity a»(eontin- uoua, aer- ation, soa water, and dally •olutlon renewal) sane as above saee as above sane as above Wisely, et al 11967). a»(contln- uoua aer- ation, aea- water, and dally solution renewal) One hundred-forty surface active aqents, solvent e»ul51 tiers, pesticides, polychlorinated biphenyls, cure Inorqanlc, and organic cheirlcals Mere evaluated aqalnst as many as ten marine organisms. The authors noted that nost published data of this type deal oltn toxlclty of chenlcals to freshwater orqanlsns. saae as above Wisely, et al Wisely, et al (1967), Portanr», et al (1971), • •1IC-77D1 Port»ann, et al (1971). •1IC-7701 Mercuric chloride (as a>ercury> Mercuric chloride las aercury) Crangon cranqon BS* — 0.10-0.33(11.) Ostrea edulls USA — t.2 (T2> a«( contin- uous aer- ation, sea* water, and dally solution renewal) a»(contin- uous, aer- ation, sea. water, and dally solution renewal) sane as above et saae as above a) (1971), »MIC-770t Portwann, et a I (1971), AMIC-7701 Mercuric chloride Pandalus BS» — 0.08 (T2) same as above Portaann, et ------- Comnound fas mercury! Hereurlc chloride (as mercury) Hereurlc chloride Mercuric chloride Mercuric chloride Field Field Organism Study Location •ontaqul Platlethys BSA flesus Carasslus BSA -- auratus Carasslus BSA — auratus Carasslus BSA — auratus Toxicity, Active Ingredient, POD 3.3 (TZ> 0.25 (S81) 0.25 (15 ppm tissue residue 1 d) 0.25 C.O-SO pom tissue residua 100 hr) Variables, Control 1 ed or Noted (continuous aeration. and dally solution renewal > a» (continuous aeration. seaxater. and dally solution renewal) a»,e a»,e a'.e 1 Comments save as above Mercury accumulated rapidly in qoldflsh. The higher the concentration UP to 1.0 pom, the more rapid MBS the accumulation. At higher concentrations. of the mercury beinq found in the mucus. The authors noted that bacterial mefhytatlon occurs In dead fish but only If muchus is present. same as above same as above Reference al (197U, ANIC-7701 Portuann, et al (197U, AIC-77gl HcKone, et al (l°7i». AMIC-11? McKoie, et al (11711, AMIC-l«.S? PcKone, et al (10711. ANIC-li.9? Hereurlc chloride Anbassis BSA safgha (Tl) a». Measurement of residual dissolved Pal lard,et seaxater oxyqen during exposure of fish to al (1969), toxlcarts resulted In data similar to AHIC-300 that obtained froi Z<>- and 8-hr bloassays by the standard vethod. The residual oxyqen method required only S hr to conduct. Variables studied included density per unit votuve, temperature, and fish size. The authors conclude that the residual oxygen method is a quick and reliable procedure for routine monitoring work. ------- Mercuric chloride Carats Ius auratus O.S? IT7) > I Mercury (total) Mercury (total) Mercury (total) Mercury (Total) Mercury (Total) Mercury (Total) Mercury (total) Mercury (total) Mercury (Total) Mercury (total) Salvellnus Fl Cayuqa LaKet 6.2Mresidue) namaycush (1 Ithaca, N.Y. yr) Salvellnus namaycush (11 yr) Salve) Inus namaycush (12 yr) Salvel Inus na»ayeush (? yr) Salvel Inus nanaycush (3 yr) Salvel inus namayeush (w yr) Salvellnus namaycush (5 vr) Salvel Inus namaycush (6 yr) Salvel Inus ramaycush (7 yr) Salvellnus FL FL FL FL FL FL FL FL FL Cayuga Lake, Ithaca, N.Y. Cayuqa Lake, Ithaca, N.Y. Cavuqa Lake, Ithaca, N.Y. Cavuga Lake, Ithaca, N.Y. Cayuqa Lake, Ithaca, N.Y. Cayuqa Lake, Ithaca. N.Y. Cayuqa LaKe, Ithaca, N.Y. Cayuqa Lake, Ithaca. N.Y. Cayuga Lake. 0.58 (residue) 0.57 (residue) 0.27 (residue) 0.37 (residue) d.i.3 (residue) 0. ------- Coaooun4 Mercury (total) Mercury Mercury Mercury Mercury Mercury Mercury Mercury Metasystox Organls* pamaycush (6 yr) Sal vet Inus namayeush (9 yr) Copegonus clupeaf or«ls CoPegonus cluneafopHls Esox lueius Esox luclus Esox lueius Osmepus •opdax PePca f lavescens Rasbora heteromopDha Toxlclty, Active Field Field Ingredient, Study Location Ron Ithaca, N.Y. FL Cayuga Lake, 0.53 (residue) Ithaca, N.Y. FL Hoose Lake, 0.07 (residue) Can. PI 1 aW A fl IT ff»A«l/4iiAl r i_ Lane u.if iresiouei Ontario, Can. FL Hoose Lake, 0.11 (residue) Can. FL Lake St. 0.70 (residue) Pierre, Can. FL Lake Erie, 0.49 (residue) Can. FL Lake Erie, 0.05 (residue) Can. FL Lake Erie, 0.22 (residue) Can. BCFA — 6.5 (T2> and BSA Exoerlnental Variables, Control led or Noted Comments — - sane as above Concentrations of 13 toxic >l«ments In dressed t Ish from heavily Industrialized and non-industrialized areas were determined. Only mercury exceeded regulatory limits, and concentrations of most elements were essentially the same In fish Iron both areas. -- same as above -- same as above •— - same as above -- same as above -- same as above a,c,e,f. One hundred sixty— four hard (HH) Destlcldes, wetting agents, and or miscellaneous Hater oollutants showed a SOFT(SH) Hide range of toxlcity scanning 12 orders synthetic of magnitude. Knowing the toxlcity and dilution percentage of. all components of a Reference (1971) , »»ic-m» Bache, et al (1971) , AMIC-3S18 Uthe, etal (1971) , AMIC-3819 U t ^ ft « c t^ t (19T1) . AMIC-3S19 Uth«, et al (1971) ,4MIC- 3S19 Uthe, et ALI1971), SMIC-3519 Uth. et al (1971),&Mic- 3U9 Uthe, et al (1971), A«IC- 3319 Uthe, et at (1971), SMIC- 7819 Alabaster (1969), AMIC-SfcZS ------- Hethanol Agonus eataohractus 8SA 10,000-33,000 IT2» M«thanol Cardlurn edule flSA 3300-10,000 (T2) water, or formulation did not result In easy seawater predictability of the toxlclty of a for sone mixture of materials. Sometimes species pesticides Here most toxic in hard Hater and soiretlmes the ooooslte Mas true. Testing the actual material as sold Has found to be essential. a(contln- One hundred-Tor TV surface active uous, aer- agents, solvent emuls1fiers, cestlcides, ation, aea-polvchlorlnated biohenyls, bure water, and inorqanic, and organic chenicats Here dally evaluated aqalnst as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxiclty of chemicals to freshwater orqanisms. saute as above «{ contin- uous aer- ation, sea- water, and dally solution renewal) Portmann, et al »1971>, Anic-7701 Portaann, et al (1971), AMIC-7701 dethanol Crangon erangon BS» — 1700 (Ti«> a«(contin- uous aer- ation, sea- water, and dally solution renewal) same as above Portiann, et al I19T1I, AMIC-701 Hethoxycnl or •tritium labelled) Sorghum halpense U (node I ecosy stem) 1 Ib per A atc,q. This small laboratory model (NTE) standard ecosystem orocedur<> was dpvelooed to reference study pesticide blodeqradabl I i ty and Hater and ecological magnification. The food-chain sand pathways In this system Here; (i) sorghum - caterpillar (larva), (2) caterolller (excreta) - Oedooonium, (3) OffdOTonium - snail, (it) Estiqmene (excreta) - diatoms, (5) Diatoms - plsnktcn, (6) Plankton — Culex (larvae), (7) Culex - Gambusia. The fish is the too of the food chain. Using Isotoolcally labeled oestlclrtos (1 Ib/acre application rate), residues Here determined for only selected organisms (snail, mosquito, and fish) and Hater, fetcalf, et al (19711, ------- Compound Orgtnlsm Fluid Field Study Location Toxlclty, Active Tnqredlent, Experimental Variables, Control led or Noted Comments Reference Hethoxychlor Cstlqmene (tritium labelled) acrea L (Hod. •1 1 Ib per A (K-NTE) a,c,q, standard reference Mater and sand Reorodueibl11ty appeared to be qood. The authors state that the method qlves a good estimation of the potential toxlclty of pesticides and their breakdown products to a variety of orqanlsus and Is suitable for computer modeling. same as above Netcalf. et al to Hethoxychlor (tritium labelled) Physa sop (Mod. .•1 •COST 15.7 (residue) a,c,g, standaro reference Mater and sand same as above Hetcalf, et al (1971), Hethoxychlor (tritium labelled! Oaphnla maqna (Mod- •1 «oorr at«n) 1 Ib per (K-NTE) a,e.g. standard reference Mater and sand same as above netcatr, et al (19711. Hethoxychlor Culex plplens L ftritium labelled) mtlaqua- (mode fMO&to* i ecosy stem) O.VS(residue) same as above standard reference Mater and sand Hetcalf, et al (1171). Hethoxychlor Oedogonlum L (tritium labelled) cardlacua (mode I •cosy stem) 1 Ib per A(NTE) a,c,q, standard reference mater and sand same as above Hetcalf, et al (1971), Hethoxychlor Gambusla L (tritium labelled) affinis (mode I •coy 0.33 (residue) a,e.g. standard reference Mater and same as above Netcalf, et al (19711, »MIC-Hi95 ------- ste«O sand ".•thoxychlor (tritium label 14) U) (tritluei labI lad) He thoxychlor (tritium labell«4> HethoxycMor (trltlun labelled) Diatoms L (Kavleula., (node Cosclnodia- I cua. Dip- ecosy loneaa, and st«) MatooallA) Protozoa L (Nuclearia. (node Coleps, I Vortlcellat ecosy and stem) Paraoeciua) Rotifera LInod (Aaplanebnop- el us, Hotoaat- ecosy ta., Euelaria, steel Seardium) Hater L ecosy stenl 1 Ib oer A (NTEJ 1 Ib per A (NTE) 1 Ib per A (NTE1 0.0016 (residue) a.c,q, standard reference Mater and sand otc,g, standard reference Mater and sand a.c.g, standard reference Mater and sand a.c.q, standard reference Mater and sand saee as above sane as above saae as above sane as above Wetcalf. et Metcalf, etal (19711. Hetcalt, etal (1971), Hetcalf, et al (19711. Nethoxyenior Methoxychlor Methoxychlor Chlronoiius tentans llnstar) BSACF — 5.5 (Tl Stenonema candirtui linstar) BSACF — Taenloptervx BSACF nival Is (Instar) 2.1 (Tit) 0.98 (TU c.d.e This chemical Mas evaluated primarily because It is on* of the principal substitutes for DOT. Raoid breaKdcnn of the chemical occurred Mhen llvlnq orqanlsirs Here present. The half-life of methoxychlor Has 7 days in Ann Arbor city nater* but Has fpuch nore raold (less than 1 day) In local creeK Mater and si OH (approximately 200 days) in distilled nater. These studies Mere to be continued to determine long term effects but no data are presented. c.d.e sane as above c.d.e. same as above lender.et al (1971). AMIC-JZ79 Bender, et al(1971), AMIC-3279 Sender.et al (1971), AMIC-J779 He thyIen* bis Phoraldiua L — 0.5-10.0 (16 — 01 7k chemicals evaluated as Otto (1970). ------- Compound thloeyanate Field Field 'Organism Study Location aablguum Toxlclty, Active Ingredient, Ppm percent Experimental Variables. Control led or Noted Comments alqlcides, only 9 Her* nor* toxic than Reference AMIC-M? O) Hethylmercury Hethylmercury Hethy I Mercury Nethylmercury MethyI acreury HethyI mercury Hethylmercury qrowth Inhibited HO Salvelinus FL Cayuqa Lake, 0.07 (residue) n««iaycush (1 Ithaca, N.Y. yr» Salvelinus FL namaycush (2 yrl Salvellnus FL namaycush (3 yr) Satvelinus namavcush ( yr) FL Cayuqa Lake, 0.11 Ithaca, N.Y. Cayuqa Lake, 0.21 Ithaca, N.y. Cayuqa LaKe, 0.3<> Ithaca, N.Y. (residue) -- (residue) (residue) -- Salvelinus FL namaycusn (5 yr) Salvelinus FL .nanaycush (6 yr) Salvelinus FL navaycush (7 yr) Cayuqa LaKe, 0.35 (residue) Ithaca, N.Y. Cayuqa Lak, Ithaca, N.Y. Cayuqa Lake, 0.31 Ithaca, N.Y. (residue) (residue) Cu<:oii. None Inhibited oronth of mat-formlnq alqae for more than 2 weeks. CuSOI. formulated nlth certain Hettinq aqents Has more toxic than CuSOl> alone. Cooper chloramlne HAS also found to he more toxic than Cu30<>. No netting aqents Here found to be Inhibitory at the concentrations investigated (0.05 and 0.105 ppir) . Also reported are factors affectlnq qroHth of alqne In canals to determine nhether there were leads to controllinq algae by environmental management. No practical environmental means Here found. LaKe trout stocKed annually as Bache, et al taqqed finoerllngs Here netted and (1971), analyzed for mercury and methyImercury. A1IC-SS1H Total mercury and the proportion of methy lirercury to mercury Increased Mlth aqe but not sex. same as above Cache, et al (19711, AMIC-3818 Bache, et al (1971), AMIC-SS18 Bache, et al A««IC-381» Bache. et al (1971), AH.IC-1818 Cachet et al (19711, AN.TC-3818 Bache, et al (1971), AHIC-3818 same as above same as above same as above same as above same as above ------- f 8 Hethylmrcury Methylmwreury Hethyl mercury Methyl mercury Me thylo»ntynol Nethyloentynol SalvlInus FL Cayuga Lake, I).SI (residue) namayrush (8 Ithaca, N.Y. yr) Sal vel Inus FL Cayuqa Lake, 0.1.3 (residue) (9 Ithaca, N.Y. vr> Sal vet Inus FL Cayuqa Lake, 0.1.1 (residue) (11 Ithaca, N.Y. yr) Salvel Inus FL Cayuqa Lake, 0.47 (residue) nawaycush (12 Ithaca, N.Y. vr) Sal mo galrdnerl BSA Salno trutta BSA Methyloentynol Methyloentynol Methyl pent ynol Methylpentynol Methylpentynol Sal vel Inus fontlnal is Sal vel Inus namaycush Esox lucius Ictalurus punetatus Leoomts •acrochlrus BSA BSA BSA BSA BSA 870-1260 (Tt>) a,c,f 680-1100 (Tit) atCtf 1100-1200 (TV) a»,C,f 660-1160 »,c,l less than 900 a»c,f IT) 1700-1890 CTJ.) a»,cff l?60-13dO (T«.) a,c.f same as above sane as above same as above same as above MethyIoentynol was tested in 9fi-hour bioassays for Its toxicity to rainbow trout, brown trout, brook trout. laKe trout, northern olke. channel catfish, blueqitlsi MrqemouTh bass, and walleyes Channel cattish were the most resistant and lake trout the ost sensitive. Two-inch rainbow trout, brown trout, and lake trout were more sensitive to methyloentynol than larqer ones in the 96-hour exposures. The druq was more toxic to blueqills and rainbow trout with elevated temperatures. Toxiclty was barely Influenced by changes In Mater hardness. sane as above Pac>e, et al AMIC-38H Pache, et al Bache. et al I19M) , Pache, 'et al (1171), aiic-ms Markinq(19S9> , 4MIC-S«>77 same as above same as above same as above same as above saa* as above "arking (1969), 51.77 Marklnqtl9S9\| Harking(19S9) . AMIC-5I»77 f arking (19S9J.AHIC- 577 »«arklnq(1959) . »«IC-5<»77 Harkinq(1969>, »MIC-5l»77 ------- Conoound M«thyloentynol M«thyloentynol Organism Mlcrooterus salnoldes St Izostedlon vl treun Field Field Study Location BSA BSA Toxicltyt Active Ingredient, Pom 1100-1350 (T<.) 110 (T<>) Experimental Variablest Controlled or Noted Comments a,c,f sane as above a,c,f sane as above Reference :fIC-5<.77 Marking 1199) ,»MIC- SI.77 Hethyl parathlon CO t-> ON Methyl oarathion Leoonls 8SA — cyanelI us (Resistant) Leoomis cvanellus (Susceptible) BSA greater than 5000 (T2) greaterthan •5000 (T2) Green sunflsh Iron Helionl, Hiss. Hinchew, et were resistant to Chlordane, Heotachlor, al (19TO)« Llndane, and Strobanet but not to Par^thion, Golden shiners fron the sa»e location were resistant to Llmlane and Strohane, tolerant to Thlordane and Heotachlor, and suseeotltle to Parathlon. Lack ct resistance to Parathion indicated lack of agricultural usage of organochosohates In that area. Resistant fish Here comoared to susceotible ones collected at Starkvltle. sane as above Hl al Methyl oarathion Methyl oarathion Notem1nonus crysoleucas (Resistant) Notemlaonus crysoleucas (Susceotlble) aSA BSA greater than 6000 (T2) greater thanSOOO ITZ) sane as above sane as above Hlnchex. et al lig7C), al Methyl oarathion tctalurus ounctatus BSA — 5.71 (T4) at Oroanochlorlne insecticides were Hacek, «t al synthetic the most toxic cowoounrts, (1970), test water organochesohates Intermediate, carbaiates AMIC-S510 the least toxic. Prown trout Has the soecies most susceptible to organochlorlnes, coho salmon the »ost susceptible to carbaates, and goldfish Here the least susceotible of all soecles. Safe concentrations established by bloassays with saltonlds or centrarchlds would likely be safe for ------- Methyl oarathion Hefhyl oarathion Methyl oarathion Methyl oarathion Methyl oarathion Methyl oaratnion Methyl oarathion Methyl oarathion Methyl oarathlon Methyl oarathion Methyl oarathion Methyl oaratnlon let alur us BSA •el as Carasslus BSA — auratus Cyorlous BSA — carolo Plmeohales BSA — prone las Lenoml; ' BSA -- macrochlrus Leoonls BSA -- nlcroloohus Microoterus BSA — sal moliles Salno BSA — galrdnerl Salno trutta BSA — Oncorhynchus BSA -— Kisutch Perca 8SA — f lavescens Pataenonetes BSA kadiakensis 6.6". (T<>) 99.00 (TM 7.13 (T«.) 8.90 (T<>) 5.72 (T 5.17 (Tl.) 5.22 (Tl.) 2.75 (Tl.) .7* (Tit) 5.30 (T".) 3.06 (Tit) 0.0025-0.0233 (Tl) a, synthetic test Hater a, synthetic test water a. synthetic test water a, synthetic test water a, synthetic test water a, synthetic test water a. synthetic test water a, synthetic test water a, synthetic test water a, synthetic test water synthetic test water a* cyorlnlds and Ictalurlds. Safe levels for ictalurids or cyprlnlds would probably be hazardous for centrarchlds and salnonlds. The use of goldfish In bloassays was discouraged. sane as above same as above sane as above sane as above same as above sane as above sane as above sane as above sane as above same as above same as above Bloassays were conducted with shrlmo from three areas of Intensive Pacek.et al (19701, SMIC-5510 Maeek. et at •MTC-5S1C MaceX, et at (1970 . AMIC-5510 Hacett. et al AMTC-S510 HaceK, et al AMIC-5510 K^cek* et al Macek, et at (1970) . Hacek, et al (1970) . al (1970), Maeek, et al (1973», AMIC-55H Macex. et al (1970), AHIC-5510 Naovl, et al (1970), ------- Compound Organism (resistant) Field Field Study Location Toxlelty. Active Ingredient, Pp« Experimental Variables, Control led or Noted Comments Reference > U) Methyl parathlon Methyl paratnion Palaemonetes BSA kadlakensls (non- resistant) Tunlf»x tunlfex Ft ant BSA RelzonI, HISS. 0.0037 (Tl) 6.00 (NTF) pesticide us* and from an unexoosed area. AMIC-5519 Previously exposed shrimp were from 1 to 25 times more resistant than unexoosed shrimp. Roth typos of shrimp Mere also exposed In cages to Maters of the contaminated areas. Susceptible shrimp suffered f> percent more mortality than did resistant shrimp. The Toxlelty of the Insecticides ranked in descending order was as foil CMS; mast toxic, Fndrln, DOT, Methyl parathion, Parathlonl medium toxlclty, Guthlon, Lindane, Toxaohene, Strobanet lease toxic Chtordane, Sevln, and Heotachlor. Hevlnfos Basbora heteromorpha BCFA — and BSA 11.9 tTZ) a.c,e,f, hard (HW) or SOFT(SH) synthetic dilution water, or seawater for son* sane as above Naavl, et al The response of pesticide-resistant aauatlc organisms to various pesticides Mas compared to the response ot non-resistant soecies. Pest Ic Ide— r es Is t ant species Mere collected at Pelzonl and non-resistant species at State College. Copepods, clams, snails, and sludQ" Morms from Relzonl Mere considerably morA tolerant to pesticides than the non-resistant organisms. The authors note that the effect of Increased tolerance In the organisms Is an Increase in the amount of pesticide residues available to animals of hloher trophic levels. One hundred sixty-four pesticides, Netting agents, and miscellaneous Mater Pollutants shoMed a Hide range of toxiclty spanning 1? orders of magnitude. KnoMlng the toxlcity and percentage ef all comoonents of a formulation did not result In easy predictability of the toxlclty of • •Ixture of materials. Sometimes pesticides Here most toxic in hard Mater Nadvi, et IJ9S9I, AHIC-5979 Alabaster (19691, AHIC-5i»?5 ------- Ml Ibex ffasbora heteroMorpha BCFA and BSA 3.5 (T2) r UJ WoaSPlM Fundulus BSA heteroelItus Nereis vlrens BSA — Crangon RSA crangon D.0003-0.0006 CT> spades ».c,e,f. hard (HW) or soft (SV) syn- thetic dilution Miter, or saa.va.ter for-aooe apecies a,c,e, and synthetic seawater and sometimes the ooooslte was true. Testing the actual material as sold was found to be essential. fine hundred sixty-four pesticides, wetting agents, and miscellaneous water pollutants showed a wide ranqe of toxicity scanning 12 orders of magnitude. Knowing the toxiclty and oereentaoe of alI components of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides were most toxic in hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. same as above alabaster et al 0.00006-0.floods a'.cte, (Tit) and synthetic seawater same as above LaRorhe.et al J197C), 1000-3300 (T<») Portmann, et al (1971), •MIC-7701 Mobllsol Crsngon crangon BS» 10-33 a«(contln- One hundred-forty surface active uous, aer- aq^nts, solvent enulslf lers. oesticldeSi atlon, aea>polychlorlnated blphenyls, pure water, and Inoroanlc, and organic chemicals were dally evaluated against as itany as ten marine solution organisms. The authors noted that most renewal) oubflshed data of this type rteal with toxlcity of chemicals to freshwater organisms. a«(contin- °ne hundred-forty surface active uoua, aer- agentst solvent emulslf iers, pesticides, ation, aoa-polychlorlnated blohenyls, pure wnter, and Inorganic, and organic cheiricals w,re daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxiclty of chemicals to freshwater organisms. Of the aauatlc weed herbicides Sanders evaluated. Oiclone was the eost toxic, (19>OI, Oaohnla was generally the most sensitive »MIC-»53 organise. All of the Crustacea were Port«»nn, et al (1971), AMIC-7701 ------- Comoound Field Field Organism Study Location Toxiclty, Active Ingredient, Ppm Experimental Variables, Control led or Noted Comments Reference Notinate Paleomontes BSA — kadlahensls 1.0U2) aTfected by much loner concentration levels of herbicides than Indicated by the TL sub SO values. Alt of the animals represent Important food chain links. same as above Sanders (19731 , AMIC-<.53 r 8 Hoi mate Nollnate Hollnate Nollnate Nollnate No Iybdenum Aseltus BSA brevicaudus Orconectes BSA nals Oaphnla maqna BSA Cyprldopsls BSA virtus Lepomls BSA macrochlrus D.<»0 (TZ) 5.6 (TZI 0.60 (T?) 0.18 (T3) 0.1.8 (T2I Paralabrax FN -Scatterqood 0.1 (dorsal elatnratus Steam Plant, muscle Los An9eles, Cal. same as above same as above same as above same as above same as above Sanders (1970) , AMIC-1.53 Sanders Sanders (i°ro) , • HTC-fcSS Sanders Fish collected from an effluent pioe ol a stea1" plant and troii offshore Haters of Catallna Island «ere analyzed for trace element content. Trace element content of the effluent water Has at least 5 times greater than that of normal sea Hater for cadmium, copper, nickel, zinc, and chromium. Livers of fish from the effluent were nearly tuice the size of those from the ocean. Greatest differences in concentration occurred with aluminum, cadmium, and nickel. Silver, barium, I ithiun, and lead shotted the least differences. The author concluded that trace element analysis of tissues could be used to determine the AMIC-4S7 Sand«>-s (19731 , AMIC-i.53 Stanleton (196SI, AMIC-5980 ------- N«lyb4«iHM Holyttdenu* Molyb4nw Purnlahrax FH Cstallna 0.3(dorsal clathratus Island, Cat. Muscle residue) Paralabrax FH Scatterqood 0.2 (ventral clathratus Stean Plant, Muscle Los Angeles, residue) Cal. Paralabrax FH Catallna 0.2tventral elathratus Island. Cal. ousel* residue! effect of pollutants on Marine organises. saae as above sane as above sane as above Staoleton (1968). Alloys') Staoleton (146(1). »MIC-'i980 Stsoleton (IORI>), AHIC-S9S1 NolyMenu* Nolybdenu* Nolybdenm Nolvbdenue Paralabrax clathratus Fn Paralabrax FM clathratus Paralabrax FH clathratus IqravM feaalei:! Paralabrax FH elathratus Paralabrax Clathratus FH Scatteraood 0.7 (gonads Steaa Plant, residue) Los Angeles, Cal. Catallna O.Stqonads Island, Cal. residue) Catallnalsla 0.6 nd, Cal. (qonads residue) Scatterqood 0.2 (liver Steam Plant, residue) Los Angeles, Cat. CatalIna Island, Ca 0. ------- Comoound Organism Molybdenum Pamlhrax clathratus Molybdenum Paralabrax clathratus Holybdenua Paralabrax clathratus Honoxone Sal mo galrdnerl Hono (N, N dliethyl Phormldlum alkyl amine) salt of amblquum Toxielty, Experimental Active Variables, Field Field Ingredient, Controlled Study Location Ppm or Noted Comments FH Catallna 0. ------- Honuron Hercenaria •ercenarla feggs) greater than 6.0 9>« Cardlu edule 9S4 CO 10 greater than 10 a»(contln- one hunrtr<«d-forty surface active IT3) UOUs aer- agents, solvent emulslflers, pestlci9), AMIC-SS^O Portmann, et a I (1971), Portmann, et al J19711, »MIC-77D1 F«s-^^^ Negaorlon brevlrostrls (1-3 Kq) BSA Z0.9 (SB ID »,c,e Data from study of drug effects •in) on younq lemon sharks were treated mathematically to demonstrate aoplIcabl11ty of classical rate theory to the study of chemical shark deterrents. Incaoacltat Ion tnarcosls) was the orimary parameter timed for effectiveness. This was usually Quite raold for the more effective drugs. Psldrldge J1969), ------- Compound 5-2 2Z Organism L«oomls •acroehlrus Field Field Study Location 8SA — Toxlclty, Active Ingredient, Pom 30 (S81» Experimental Variables, Controlled or Noted Comments a.* Little difference In nitrogen excretion rate Has found between treated and control fish. Anaesthesia should Reference Savltx (1969) ,AMIC- 5838 Mystox LSC-P Pasbora HCFA ~ heteromorpha and 8SA 18 (T2. hardwater) Hystox LSC-l> Pasbora heteroworpha 8CFA •nd BSA 5.6 (T2, sortwater) Nystox LSE-L Sal mo qalrdnerl BCFA and BSA 36 (T2> Nystox LSE-P Sal»o ^alrdnerl 8CFA •nd BSA (TZ) have reduced nltroqen excretion but did not. The author believed that Increased •ucus secretion was a possible explanation for the results obtained. a,Ct«,ft One hundred sixty-four Alabaster hiird(NW) pesticides, netting aqents. and 11969) .AMIC- or soft nlscel laneous water pollutants shotted a S ------- Nystox CSL-L Sal «o qairdnerl BCFA and BSA 180 (T2I Hystox LSL-P Salao galrdnerl BCFA and BSA 68 (T?) vn NystOX LSL Rasbora heteromoroha BCFA and BSA 8.Z (T2, hardHater) Nystex ISL Rasbora BCFA and BSA J.5 ------- Compound Field Field Organism Study Location Toxielty, Active Ingredient, Pp« Experimental Variables. Control led or Noted Contents Reference Nabaei Nabae> Naleo Mercenaria mercenarla (larvae) Crassostraa virqlnlca (eqgs) Pasbora BCFA heteromorpha and BS 1.75 CT12) less than 0.5 (T2J 0.76 ITZI bard IHH) or sort Nalce ?«.0 Rasbora BCF» heteromorpha and B5A (TZ) thotle dilution imt«r, or flea.ua ter Cor aoiaa ipaolaa a,e,e,r. hard (HW) or soft development more than survival. Some, however, drastically reduced larval groxth. The authors oolnt out the necessity of evaluating the effects of oestlcldes on all lire stages of an organism and note the possibility of selecting chemicals for oest control that HOuld not have serious effect on shellfish. sane as above Oavls. ct al saae as above 5930 Davis, et al One hundred sixty—four pesticides, wetting agents, and miscellaneous water oollutants showed a wide range of toxlclfy soannlnq 12 orders of magnitude. Knowing the toxiclty and percentage of all components of a formulation did not result in easy predictability of the toxlcity of a mixture of materials. Sometimes pesticides were most toxic in hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. same as above 5990 Alabaster (1969), ANIC-5WZ? Alabaster 11969), thatlc dilution «tt«r, or ------- N»ICO ?J Ratbora BCFk heteromoroha and Haohthenlc acids Leoomls 8SA, •i}crochlrus L 0.28 (T2) a».c,e,f. hard (HH) or SOFT(SW) synthetic dilution Mater, or seaMater for son species 5.6 (T<>> a«,e, and. synthetic dilution miter same as abova Alabaster (1969), Naohthenlc acids Mltzschla 8SA, linear!- L This study Has conducted to determine the relative toxlcltles of ?0 eonaon constituents of Industrial xastes to a fish, an alqa, and an Invertebrate. The exoerlnents Mere conducted over a 10-y«ar period for varied purposes. The authors recommend bioassays Mlth at least three components of the food Meb. sane as above Patrick, et al MQ6>, «C-57?0 Naohthenlc acMs Physa BSA, heterostrapha L same as above N Fundulus BSA heteroclItus »3.1 mi a»,e, and synthetic dilution water 7.1 ITI>) »,e, and synthetic dilution water D.00018-0.OOOSi, a.c.e.and A laboratory procedure based on synthetic Standard Methods tor 96-hr toxlcity seaxater determinations of crude oil and oll-dlspers^nt mixtures Mas described. The dlspersants varied considerably in toxlclfy, ranqlng from 0.01 to 7.1 ml/I, TL50 for 96 hr. These did not differ Significantly from 2iiO hr values. The dlspersants Mere deslqnated as C« no, Cl, 00, AO, PC,' HM, TN, BP. and NA with no further description of their chemical nature or source. Only a feM hloassays Mere conducted xlth shrimp. HollusHs and echlnoderms Mere suqqested as suitable test animals. The authors stated that the method could be used to test any product for toxlcity in seaMater. Patrick, et a I <146 ft). ANIC-5720 Patrick al flif.M AIIC-S7?0 et La"?oche, et al (1970), N* Hebur on Nereis vlrens BSA Hercenarla L •ercenarla (e99S) 0.000007-0.0000 a,c,e, 6 (Tl>> and synthetic seaMater less than 2, m» laoche,et al U970), sane as above The effect of 5? pesticides on Davis, et embryonic rfeveIoonent of clams and 81(1969), oysters Mas reported. Synerqlstlc AMIC-5990 effects with solvents were also reported. Most of the compounds affected development more than survival. Some, ------- Compound Field Field Study Location Toxlclty, Active Ingredient, Experimental Variables, Control led or Noted Comments Reference Neburon Memagon Mereenarla •ercenarla (larvae! Hercenarla •ercenarla (eggs) L — less than (T12I 10.0 (T2I UJ ro OO Ne>ag<>n Meoaycln sul. None Inhibited growth of •at-forming algae for more than 2 weeks. Cu^Ot* formulated Hlth certain wetting agents was more toxic than CuSO ------- Nlcl<l sulfate las nickel> Carclnus aaenas BSA — ?55 CT2I Nickel sulfate (as nickel) Nickel sulfate (as nick I) Cardlua edule BSA —> Crsnqon cranqon BS* greater than $00 (T2J (T2I water, and Inorganic, and organic clericals Mere dally evaluated aqainst as Many as ten varlne aolutlon organisms. The authors noted that most renewal) Dubtlshed data of this type deal with toxlclty of chemicals to freshwater orqanlss« a«(contln- One hundred-forty surface active Uoua, aer- aijents, solvent emulsl t lrs. oestlcldes< atlon, sea-oolychlorlnated blohenyls, cure water, and Inorganic, and orqanlc cheflcals were dully evaluated aqalnst as many as ten ear In* solution organisms. The authors noted that Most renewal) oubllshed data of this tyoe deal with toxlclty of chemicals to freshwater organisms. saae as above »( contin- uous, aer- ation, soa- water, and daily solution renewal) a»(contin- uous aer- ation, aaa- water, and daily aolutlon renewal) saa as above Portnann, at al Cl<)71>, •Mic-rm Port»ann, et al (1S71I, AHIC-7701 Portaann, et al «1<»71I, AMIC-7701 Nickel sulfat* (as nickel! Ostrea edulls BS» 100-150 •.•(contin- uous aer- ation, aaa- wa.ter, and daily aolutlon renewal) saa* as above Porteann, et al (1971), •NIC-7701 Nickel sulfate (as nickel) PandaI us •ontagul BSA 13.9 (T2) a( contin- uous aer- ation, sea- water, and dally aolutlon renewal) saae as above Port«ann, et al (14711, AMIC-7701 ------- Compound Field Field Orqanlsm Study Location Toxlclty, Active Ingredient, Ppm Experimental Variables, Control led or Noted Comments Reference Nickel sulfate (as Salmo NIZ »»us» qalrdnerl (eqqs and sperm) BSA 1.0 (NTE) a,c,f Data were given in mq/l which Has Shan, et at taken to be the equivalent of op. (1971), Fertilization rates Here statistically AMIC-im.1. similar In both test (Cu and Nil and control waters. The rat* of hatching N»S slqnl f leant I v different for eoqs exposed to Cu and the rate of devel ooient was Increased. The authors concluded that In , hard waters neither Cu nor Nl Is likely to Impair fertilization In rainbow trout. U) Nickel tulfate (as Acroneurla BSA Nickel sultate las Cphemerella BSA Nil Nickel sulfata (as Hydroosyche BSA Nil Nickel suitate (as Phormldlum L Nil amblquum 33.5 (T> 6d (TIM 0.5-10.0 (16 percent growth lnhlbltedl<»> atc,d,eif atCtdttf atC(d,ef1 Nickel (Plus coooer. Sal BO lineI galrdnerl BSA — 0.5-1.4 (T2) Ephemerella (mayfly) was the most Warnlck sensitive aquatic Insect of those Studied, and cooper the cno chemicals evaluated as atqlcldes, only q xere more toxic than CuSOU. None Inhibited qrooth of •at-formlnq alqae for nore than 2 necks. CuSOU formulated Hlth certain netting aqcnts Has nor* toxic than CuSO<> alone. Coooer chlorairlne Has also found to be • ore toxic than CuSOii. No nettlnq aqents were found to be Inhibitory at the concentrations Investlqated (D.05 and 0.005 oonl. Also reported are factors affectlnq qronth of alqae In canals to determine whether there Her* leads to controlling alqae by environmental •anaqenent. No practical environmental means were found. RalnbOH trout Here exposed to 8ro»n,»t al copper, phenol, zinc, or nickel solutions (1970), to determine 1.8-hour LCSO values for ANIC-S99* ------- Nickel Coreqonus FL Moos* Lake, 0.2 (residue) elupeaforals Can. £ u> Nickel Nickel Nickel Nickel Nickel Nickel Nickel Fsox luclus FL Esox fuclus FL Esox luclus FL Osaerus FL aordax Perca FL flavescens Coreqonus FL cluoeaformls Paralabrax FH clathratus Moose Lake, 0.2 (residue) Can. Lake St. 0.2 (residue) Pierre, Can. Lake Erie. 0.2 (residue) Can. Lake Erie. O.Z (residue) Can. Lake Erie. 0.2 (residue) Can. Lake 0.? (residue) Ontario, Can. Scattergood 5 (dorsal Steam Plant, Muscle LosAnqeles, residue) Cat. Mixtures of copper and phenol 1 copper, zinc? and phenol I and copper• zinc, and nickel. It was concluded that acute lethal toxlclties of the elxtures could be adeauately described by summations of the fractional toxlclties. Concentrations of 13 toxic elements In dressed fish from heavily Industrialized and non-Industrialized ureas were determined. Only mercury exceeded regulatory limits, and concentrations of most elements were essentially the same in fish froa both areas. saae as above same as above saae as above same as above same as above same as above Fish collected from an effluent pioe of a steam plant and from offshore Haters of Catatlna Island Here analyzed for trace element content. Trace element content of the effluent water Has at least 5 times greater than that of normal sea Hater for cadmium, coooer, nickel, zinc, and chromium. Livers of fish froa the effluent Here nearly twice the size of those fro* the ocean. Greatest differences In concentration occurred Kith atunlnum, cadalua, and nickel. Othe.et at (1971). AMIC-3819 Uthe, et al (1971),AMIC- 3819 Uthe, et • LU971I, 4HIC-3I19 Uthe, et al 3819 Uthe, et al (1971),AHIC- 3819 Uthe. et al C1971),AMIC- 3819 Uthe.et al (19711, AMIC-3819 Staoleton (1968), AMIC-5980 ------- Cecoound Mich! Nickel Nickel Nickel Nickel Nickel Nickel Nickel Nickel Organise Pars! »t>rax elathratus Paratabrax clathratus Paratabrax elathratus Paralnbrax el athratus Paralatirax clnthratus Paralahrax cl athratus (gravid females) Paralabrax cl athratus Paralabrax cl athratus Paralabrax el athratus Field Study FH FM FM FM FN FM FN FN FH Field Locat Ion Catal Ina Island. Cat. Scatter qood Steam, Plant, Los Angeles, Cal. Catal Ina Island> Cal Seatterqood Steam Plant, LosAngeles, Cal. Catal Ina Island, Cal. Catal Ina Island, Cal. Scatterqood St«an Plant, LosAngeles, Cal. Catal Ina Island, Cal. Scatterqood Steal* Plant, LosAnqelcs, Toxlcity, Active Ingredient, Pp» 6.. 7 (gonads residue) 72.2 (gonads residue) 8.6 (gonads residue) 3.9 (liver residue) 7.6 (liver residue) 9 (Integuaent residue) Experimental Variables, Controlled or Noted Comments Silver, barlue, lithium, and lead shooed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on narlne organisms. sane as above ~ sane as above ~ sane as above ~ sane as above -- saae as above — sane as above -- same as above same as above — sa«e as above Pelerence Staoleton IIS^I, AMIC-5980 Staoleton <19<-!O, MIC-5983 Staoleton <1<>6M, »MIC-S9SO Staoleton (1968), ANIC-«;980 Staoleton I1»6M , AHIC-5980 Stapleton (19681 . AHIC-5980 Staol eton (I960. AMIC-S980 Staoleton (196d). ANIC-5980 Staoleton (1968) . AHIC-5980 ------- U) U> Nickel Nickel Nickel MICHI Nickel Nickel Rural ahrax clathratus Paralabmx clathratus Paralabrax clathratus Paratabrax clathratus Paralabrax elathratus Sal no qalrdnerl FM FH FN FH CatalInn Tsland> Ce in.2 I Integument residua) Stuoleton (1968), Scatterqood A.I fheart Steae Plant, residual LosAngeles, Cat. Cat a Una 10.8 (heart Island. Cat. residue) Scatter good 6.<> (eyeball Steam Plant, residue) LosAngeles, Cal. CatalIna Island, Cal. BS» 33.? (eyeball residue) 3?.0 Nicotine Negaorlon brevlrostrls (1-3 kg.) BSA ~ 31. (SB) Nicotine Labeo rohlta L — 1.0 (SB7) Stsoleton (1968), •MIC-59SO Staolcton (1<9S8) , AMIC-5980 Staoleton (19^8), AHIC-59SO Staoleton (1968). saae as above same as above saae as above saae as above same as above a,c,e RalnboM trout Mere exposed to Broun, et al eoooer, phenol, zinc, or nickel solutions (1970), to doternilne fc«-hour LCSO values for AHIC-599«> mixtures of cocoer an4 Dhenoti copoer, zinc, and ohenoli an.4 cooper, zinc, and nlcKel. It Mas concluded that acute lethal toxlclties of the mixtures could be arteauately described by summations of the fractional toxlclties. a,c,e Data from stud/ of drug effects Baldrldge on younq tenon sharks Nere treated (1959), mathematically to demonstrate 3S3? aoollcahlllty of classical rate theory to the study of chemical shark deterrents. Incanacltat Ion (narcosis) MAS the primary parameter timed for effectiveness. This was usually quite rapid for the more effective drugs. a.d.e.t This experiment showed that Konar nicotine could be successfully used to (1970), llve-esotur fish from reservoirs. Fish »MIC-S">35 surfaced and recovered rapidly when placed In freshwater. Fish remaining In test solutions above <» pom did not recover. This chemical Has considerably less toxic to the aquatic Insects studied. ------- CO Comoound Nicotine Nlcotln* Nicotine Nicotine Nitric acid Nitric acid Nitric acid Field Field Organism Study Location Punt 1 us L — soohore Panatra L — - fltlformls Dytlscus so. L Hataropnaus- L tea rossllls Agonus BSA ~ cataohractus Asterlas BSA — rubens jCarcinus BSA — •aenas Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments 1.0 (SB7) a,d,e,f same as above tO (NTE7) a.d.e.f same a* above <>00 (NTE7I a,d,e, f same as above 3.2 (SB 5 hr>, — . epidermal lesions of catfish K in hrl barbels Here moderate to s»v»re after exoosure noted. Rarbel curling and Inactlvatlon Here associated effects. 100-330 (T2) a(eontln- "ne hundred-forty surface active uoua aar- agents, solvent emutslfiers, oestlcldes. atlon, sea- POlych lorinated blohenyls, pure water, and Inorqanlc, and organic chemicals Here dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) oubllshed data of this tyoe deal xith toxlclty of chemicals to freshwater organisms. 100-330 (T2> a»(contln- same as above uous aer- ation, sea- water, and dally solution renewal) 180 (T2I a»(contln- sa.e as above uoua aer- ation, sea- water, and dally solution renewal) Reference Konar i«c-Usn Konar (19701, Konsr (1970) , AMIC-5U35 Konar (1969), AMIC-57?f, Portmann, et al (1971). AMIC-7701 Portmann, et el (1971), AMIC-7701 Portmann, et al (1971), AMIC- 7701 Nitric acid Cardlum edule BSA 330-1000 (T2) « ------- i>9 ErlcKson, et al (197(1), ErlcKson, et al (1970), FrlcKson, et al (1970), MIC-i.<.9 Nltrllotrlae etlc acid Erlckson, et al (1970), ErlcVson, et al (1970), Erlckson, et al (1970), Srlckson, et al (1970), ------- Field Field Compound Organism Study Location Ml trofurazone Hercenarla L — •ercenarla (egqs) Toxlclty, »ctlv« Ingredient, Pom greater than 100.8 CTZ) Experimental Variables, Control ld or Noted Consents — The effect of embryonic development oysters was reported. 52 pesticides on of clans and Synerqistle Reference Davis, et i (1969), 4MIC-5990 > Ml trofurazone Nltroqen (dissolved) Nercenarla •ercenarla (larvae) Oneorhynchus tshauytscha (Juveniles) FR.BS Priest CH Rapids Dam, Mash. greater than 100.D (T12> Super saturation HI tro?en Cdltsolved) Nitrogen (dissolved) Salmo qalrHnerl (adults) Oneorhynchus klsuteh <\|uvenlles) F«, BSCN HcNary Oaa, Hash. Priest RapldsDae, Mash. Supersaturatlon (NTE 35» Super saturation 16-16 percent effects with solvents were also reoorted. Host of the compounds affected develoceent more than survival. Soae, however, drastically reduced larval qrowth. The authors point out the necessity of evaluatlnq the effects of pesticides on all life staoes of an oraanlsK and note the oossibllity of selecting chemicals for oast control that MOuM not have serious effect on shellfish. same as above The nltroq»n qas regime In the Colunbla River Mas studied in 1966 In order to determine whether hlqh levels of dissolved nltroqen nlqht be responsible for losses of adult salaon and poor production of young fish at spawning channels, examinations of dead (uvenlla salmon revealed that most fish had symntoms of "qas bubble disease". Juvenile saloon Keot at sufficient depth to compensate for the Supersaturatlon of dissolved nitrogen were free of symptoms of qas bubble disease. Fish under stress fro* the Supersaturatlon of dissolved nltroqen were very Intolerant to temperature Increases. saae as -above Davis, et al (1969). •HIC-599D Ebel (1969 AHIC-6198 sae as above Ebel (1969). •NIC-6198 Ebel (1969)t •NIC-6198 ------- U) co -j Nitrogen (dissolved) HI, Cu, Cr, CN, Zn (••stenater) Oneorhynchus nerka (adults) Pln«>ohales prone I as FR McNary Oam, Hash. BSACF Grand River (ML) at Wyoming, Michigan Nl, Cu, Cr, CM. and CatostomuS Zn IwasteMater) commersonl Nonyl phenol 1? (olus ethylene oxide) Nonyl ohenol 12 (Dlus ethylene oxide) Carclnus •aenas BSACF Grand River (HL) atiiyoalng, Michigan BS» — Suoersaturatlon (SB35) same as above •oprox. 1.67 percent (T3) between 1.35-3.75 percent (T3) greater than 100JT2) Cardlua edule 8S» 92.6 CT2) fbel AMIC-619S a,c,e, con- A mobile bloassay unit was ductlvity, utilized to conduct this study or NifCUfCr, municipal Mastmater containing the CN, and Zn indicated toxicants. River Mater «»i used as diluent. The conclusion Mas reached that synerglstlc or additive toxic effects occurred since toxlelty was greater than that of any of the Ions singly. 71IIIch (1969), a,cte, con- ductivity, Hl.Cu.Cr, CH, and Zn save as above a(contin- uous aer- ation, sea- water, and dally solution renewal) a«(contin- uous aer- ation, aea. water, and daily •olution renewal) One hundred-forty surface active agents, solvent enulsifiers, pesticides, polychlorlnated blphenyls. Pure Inorganic, and organic chenlcals were evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal with toxlelty of chemicals to freshwater organisms. saee as above <1969>, 1NIC-2906 Portpsni.et al Portmann. et al (1971),AMIC- 7701 Monyl phenol 12 (plus ethylene exlde) Crangon crangon 8S» 89.5 (T2) a»(eontin- uoui, aer- ation, aea- wator, and dally •olution •••• as Move Portnann. et al (1971),MIC- 7701 Nonyl phenol 12 (plus ethylene exide) PandaIus •ontagul BS« — 19.3 (T2) at (contin- uous, aer- ation, a«a- se»e as above Pertnann, et al (19711.AHIC- ------- COB-pound Orqanlsa Field Field Study location Toxlcity, Active Ingredient, Experimental Variables, Controlled or Noted Comments Reference water, and daily solution renewal) 7781 More* Gammarus faselatus BSA — 1.* mi U) Norseman Cranqon crangon BS* — 3.3-10 (TO Pasbora BCFA — hateroaorpha and BSA ITZ) NH 1113 Rasbora BCFA — heteroaorpha and BSA 11 U2I a(contin- uous aer- ation, sea- water, and dally solution renewal) a»,c,e,f, hard (HH1 or SOFTCSHI synthetic dilution •ater, or seaiiater for SOBC spec 1e s a,c,e,f, hard (HM) or soft Of the aquatic urns herbicides Sanders evaluated, Olclone was the most toxic, (1970), Daphnta was generally the most sensitive »HIC-55 orqanisn. All of the Crustacea Here affected by much loner concentration levels of herbicides than indicated by the TL sub 50 values. All of the aniaals represent important lood chain links. One hundred-forty surface active Portaann, et aqents, solvent enulslflers, pesticides, al (1971). •polychlorInated blphnyls» pure ANIC-7701 Inorqanlc, and organic cheaicals Here evaluated against as many as ten narlne ornanisms. The authors noted that Most published data of this type deal with toxlcity of chenicals to freshwater orqanlsns. One hundred sixty-four Alabaster pesticides, Hettlnq agents, and (19591, •iscellaneous Hater pollutants showed a AMIC-51Z5 • He ranqe of toxlcity soanninq 12 orders of aaqnltude. Knowing the toxicltr and percentage of alI components of a fomulatlon did not result in easy predictability of the toxlcity of a mixture of Materials. Sometimes pesticides Mere most toxic in hard nater and sometimes the opposite was true. Testing the actual aaterlal as sold «as found to be essential. _ synthetic dilution •afar, or sane as above Alabaster (19691, ------- 1313 Rasbora BCFA heteromorpha and BSA 5.0 ITZI HueIdol dlazlnon she«p dip Rasbora BCFA heteromorpha and BSA l.M ITU NO seawater for some species «,C,e,f. hard (H¥) or soft (SU) thetlc dilution Mater, or ••mutter • for'aome •peelea «,c,8,r, h»rd (HW) or aoft ISUJ thatle dilution water, or seawator for aome apoelaa Hystatln I — B.5-10.0 (NTE> — aablquua N-»«thvt carbaaata darlvltlva Rasbora BCFA heteromorpha and BSA 0.58 (TZ> hard (HHt or soft (SW) synthetic dilution •atr,or •aaHatar .for tea* saaa as above Alabaster (1969). saaa as above Alabaster, (19691,AMIC Of Tit chenlcals evaluated as Otto alqlelds< only 9 Here more toxic then AHIC-892 CuSOd. Non« Inhlbltel qroMth of mat-fornlnq algae for more than ? necks. CuSOU formulated Mlth certain wetting aqents Has more toxic than CuSOlt alone. Conner chloranine Mat also found to be • ore toxic than CuSO<>. No netting aqents Mere found to be Inhibitory at the concentrations Investigated (0.05 and O.nns ppnl. Also reported are factors affecting growth of alqae In canals to detemlne Mhether there Mere leads to Controlling algae by environmental aanaqenent. No practical environmental •eans Here found. One hundred sixty-four Alabaster Pesticides, wetting agents, and (1969), •iscellaneous Mater pollutants showed a AHIC-5«2S Mlde range of toxlclty spanning 12 orders Of aaqnltude. Knowing the toxiclty and percentage of all components of a formulation did not result In easy predictability of the toxlclty of • •ixtura of materials. Sometimes ------- Compound Organls Field Field Study Location Toxlclty, Active Ingredient, PPM Experimental Variables. Control led or Noted Consents Reference H-351V Crassostrea vlrglnlca feqqsl Crassostrea vlrglnlca (larvae) Mercenarla mercenarla (eggs) less than 0.5 IT2) less than 0,9 • Tli.) less than l.D ITZ) species pesticides w<>re most toxic In hard Hater and sometimes the ooooslte Mas true. Testing the actual material as sold xas round to b<> essential. -— The effect of "!Z pesticides on embryonic development of clans and oysters was reported. Synerqlstlc effects with solvents were also reported. Most of the comoounds affected development more than survival. Some, hoxever, drastically reduced larval growth. The authors point out the necessity of evaluating the effects ot pesticides on all life stages of an organism and note the oosslblllty of selecting chemicals for pest control that would not have serious effect on shellfish. same as above same as above Davis, et al <1969),A1IC- 5998 Davis, et al 11969), AMIC-5990 Davis, et al (19691 .AHIC- 5990 M-J5I* Oetyl phenol 11 lotus ethylene oxide) Nercenarla •ercenarla IIarvael Crassostrea vlrglnlca (eggs) Crassostrea vlrglnlca (larvaet Caretnut •aenM L — BSA — less than 1.0 (Tl?) less than l.D IT2I less than 1.0 (Til.) sane as above same as above same as above greater thanlOO a* One hundred-forty surface active (TZI (eontlnuou agents, solvent emulslflers, pesticides, % polychlorlnated blphenyls, pure aeration. Inorganic, and organic cheelcals were seawater, evaluated against as many as ten marine Davis, et al(l969), AMIC-59°5 Davis, et 81(1969), AHIC-599B Davis, et 8111969). AMIC-5990 Portmann,et al (1971), AHIC-7701 ------- Oetyl phenol 11 (plus ethylene exldel Card I urn edule 85* — 19.6ITZ) and dally organisms. The authors noted that most solution published date of this type deal Kith renewal) toxlelty of chealcals to freshwater organism. a, (contin- uous aer- ation, sea- water, and daily solution renewal) same as above Portnann, et al(1971l, ANIC-7701 Oetyl phenol 11 (plus ethylene oxld) Crangon erangon BSA — 63(Tt) f a«( contin- uous, aer- ation, sea- water, and dally solution renewal) same as above Porteann, et al(1971), AMIC-7701 Octvl phenol 11 (plus ethylene oxldet Pandatun •ontagul BSA — 10.B (TZI a«( contin- uous, aer- ation, sea- water, and dally solution renewal) same as above Portwann, et al«t971), AMIC-7701 Oetyl phenol 11 (plus ethylene exldel Platlethys flesus BSA — 33-100 (T2I a»(contin- uous, aer- ation, sea- water, and dally solution renewal) same as above Portmann, et at C1971)tA«IC- 7701 00 Fundulus heteroelItus BSA — 0.0005 ITfcl a,Cte, A laboratory procedure based on and Standard Methods for 9S-hr toxlelty synthetic determinations of crudp oil and seaHater oll-dlspersint mixtures was described. The dlspersants varied considerably In toxlcityt ranging from 0.01 to 7.1 ml/I, TL50 for 96 hr. These did not differ significantly from ?i»0 hr values. The dlsoersants Here designated as CX, 00, Cl, 00, AO, PC, MM, TN, BP, and NA with no further description of their chrnlcat nature or source. Only a Tex bloassays were conducted Mlth shrimp. HollusKs and echlnoderms Ner* suggested as suitable test animals. The authors stated that the method could be used to test any product for toxlelty In seaxater. LsRoche.et al (1970), AHIC-H5 ------- Comoound 00 Oil herder Toxlclty, Active Field Field Ingredient, Organism Study Location Ppa Nereis vlrens 8SA — 0.0001^-0.0009* (T> Cranqon BSA — 3300-10,000 cranqon (T») Experimental Variables, Control ltd or Noted Comments a,c,e, same as above and synthetic seanater »(eontin- one hundred-forty surface active UOUS aer- aa»nts, solvent emulslf lers, pesticides. atlon, aoa-pol ychlorlnated blohenyls, pure vater, and inorganic, and organic chevlcals w«re daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. Reference LaRoche,et al (1970), ANtC-»«.S Portmann, at al (1971), AMIC-7701 Oil (crude) Palaemonetes BSA — vulgarls greater than 1.0 (TM a,c,e, and synthetic seaiiater ru Oil Icruda oil Bl Fundulus BS» heteroelltus Oil (crude oil 81 Nereis vlrens BS» Oil fr •fined) 0«az«ne Pataeeonetes 8S» vulgar Is Hercenarla •ercenarla 0.0083 (T4> 0.0061 (TV) 0.00005 IT) a,c,e, and synthetic seawafer a,c,e, and synthetic seaMater a,c,e, and synthetic seaitater A laboratory procedure based on Standard Hethods for 96-hr toxlclty determinations of erule oil an ------- U) Oaazene Omazene Oaazene Mercenarle, aereenarla (larvae) Crassostrea vlrglnlea (eggs) Crassostrea vlrqlnlca (Inrva) Orthodlehlorobenten Her can aria aercenarla (egos) 0.3* (T1Z) 0.07S (T2> 0.3* (Tilt) greater titan 100.D IT2) Orthodlchlorobentene Hercenarla aercenarla, (larvae) 0>lne-cop»er Sal BO galrdnerl L — • CM and 65* greater than 100.0 (Tit) 0.1* (Til Most of the compounds affected devetocaent nor* than survival. Some. however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stapes of an organ Is* and note the possibility of selecting cheelcals for pest control that would not have serious effect on shellfish. saae as above Oavlst et al saae as above sane as ahove 5990 Davis, et al C1969),»1IC- 5990 Oavlst et al (1069). »MIC- 5990 Davis, et (1969), »HIC-599D al The effect of 52 pesticides on embryonic development of clams and oysters Mas reported. Synerqlstlc effects with solvents were also reported. Host of the compounds affected develocaent more than survival. Some. however, drastically reduced larval growth. The authors point out the necessity of evaluating the effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that Mould not have serious effect on shell fish. saee as above 0«vls, et al (1969)t ANIC-5990 a,c,e,f. One hundred sixty—four Alabaster hard CHM) pesticides. Netting agents, and (1969), or soft miscellaneous Mater oollutants showed a AMIC-S»?S (SMIsynthe wide range of toxtclty spanning 12 orders tic of magnitude. Knomlng the toxlcitv and dilution percentage of all component of a Hater, or formulation did not result In easy ------- Compound Organise Field Study Location Toxiclty, Active Ingredient, Pom Experimental variables. Cantrolled or Noted Comments Reference seawater for some species Oxygen Leooals eacrochlrus BCF — 0 to saturation »«•• (S8«> o-dlchlorobenzene (58 oereent plus ?0 percent crescyllc acid) Aasbora heteromorpha BCF* and 8SA 9.1 ITZ) o.o-dlethyl o-? pyrazinyl pnosPhorothlate Rasbora BCF* neteroeorpha and BS* hard (HH) or SOFTJSH) synthetic dilution water, orseawater lor son* species a«c,e,t, hard (HH) or soft (SHI synthetic di lution Hater, or seanater for so»e specie predictability of the toxlclty of a mixture of materials. Sometimes pesticides Mere most toxic in hard Mater and soaetlmes the opposite was true. Testing the actual material as sold was found to be essential. Fish 15-29 c« long Mere exposed Burton to gradual hypoxla stress to determine (1970), the effect on skeletal muscle and liver AMIC-63«5 lactate and oyruvate. Tests were conducted at S and 20 C with DO reduced froa saturation to zero over an 8-hour period. Low DO Increased lactic acid concentrations in muscle and liver at both temperatures! pyruvlc acid levels remained constant. Lactic acid levels Mere higher at 5 C than at to C, and fish Mere better able to tolerate low oxygen levels at the lower temperature. One hundred sixty-four Alabaster pesticides, wettlnq aqents, and (1969). miscellaneous water pollutants showed * AMIC-5W5 Mlde ranqe of toxlclty spanning 12 orders of magnitude. Knowing the toxlcity and percentage of all components of a formulation did not result in easy predictability of the toxlcity of a mixture of materials. Soaetlnes pesticides Mere most toxic in hard water and sometimes the opposite was true. Testing the actual material as sold mas found to be essential. same as above Alabaster (1969), ------- Paraouat-di (eethyi) chloride Ratbora BCF* —v heteroaorpha and US* Paraauat Chara sp Jeffarson Count»•» Colo. 32 «T2» •,c,e,f,h ard (HM> or soft saae as abova 1.1MK16I synthetic dilution Mater, or seanater for soaa species a,c,d,e,g, and Hater stage Alabaster tl969»,»1IC- 525 Paraauat almost eliminated Chara sp. In 16 days and gave Initial control of Solroqyra so. The latter recovered Hi thin 3 aos. Fish deaths and other effects occurred within 1.6 Kr. Paraquat Mas recovered froe aud 99 days after application* Indlcatlna that this herbicide can be very persistent. This study xas conducted In 196%. Llvecar exposure of some fish Has one technique employed. Earnest (1971), 4M.IC-5S6* \JI Pareauat Paraauat Paraouat Paraauat Paraauat Mater FL (botteal Mud FL Splroqyra sp FL Chara sp FL Splroqyra sp FL Jefferson County., Colo. Jeffarson County., Colo. Jefferson County., Colp. Jefferson County.t Colo. Jefferson County., Colo. 1.1% (1.5 ppn •,c,d,e,9, aax residue! and Hater hrl stage 1.14 115.9 ppa •axresldue 16 residua 164) a,c,d,e,q, and Hater stage a.c.d.e.g. and Hater stage a,c,d,e,g, and Hater l.l«i (2300 ppa aax tissue raaldua 8d) (1300 ppa a,c,d,e,g, tiaau* and Hater realdn* lul) » stage sane as above saae as abova sane as above sae as abova saae as abova Earnest tl971),»MIC- 556% Earnest (19T1J, •KIC-556% Earnest (19TU, •HIC-S56 Earnest (197H, •HIC-556* Earnest (19711, AHIC-55M Paraquat Paraauat KaInbox trout FL Channel FL catfish Jefferson County., Colo. Jefferson County.i Colo. 1.1 (1.9ppa Max a,c,d,e,g( tlaaue 1 . and Hater raaldua Id) stage 1.1 (1.3 ppa a,c,d,a,gt •ax and Hater tlaaue 1 stage saae as abova saae as abova reeidue Id) Earnest (19711,»MIC- 5561, Earnest (19711, MIC-556% ------- Compound Organise Field Field Study Location Toxlclty, Active Ingredient, Pom Experimental Variables, Control led or Noted Comments Reference > Paraquat Paraquat Paraquat Paraquat Green sun fish FL Jefferson County., Colo. Blueqllls FL Jefferson County., Colo. Mater (top) FL Jefferson County., Colo. Cardlun edule USA — Paraquat Crangon BSA crangon 1.1 (Z.lppm max a,c,d,e,gf t Issueresidue and Hater 16 d> stage 1.1 (1.6 ppmmax a,c,d,e,g, t Issueresidue 8 and Mater d> staqe 1.1U (0.6 pp» a,c,d,e(g, nax residues and Mater hr-l dl stage sane as above sane as above sane as above greater than 10 a»(contin- One hundred-forty surface active (T2) uous aer- agents, solvent emuls1flers, oestlcides, atlon, sea-oolvchlorlnated blohenyls, pure water, and inorganic, and organic chemicals Mere dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal Mith toxlclty of chemicals to freshwater organisms. greater than 10 a»(contin- CT2) nous aer- ation, sea- water, and dally solution renewal) sane as above Earnest (1971), AMIOS56 • Earnest (1971, AMIC-S56I. Earnest (1971), AMIC-55M. Portmann, et al (1971), Porfmann, et al (1971), AHIC-7701 Paratnlon (plus 0.75 Plnephsles BCFA ppn LAS) prone I as Parathlon (plus 0.5 Plneohales 8CF» ppn LAS) oromelas Parathlon (plus t Plnephales BCFA ppn LAS) proneI as 0.8 (Z.5 a»,e LAS acted synergistlcally Mith Solon, et al percent K) parathlon to cause less survival of (1969), fatheds but had an indeterminate effect AMIC-3785 Mith DDT and no synerglstlc effect Mith Endrln. O.S (61.5 a»,e percent K) 0.1 (95 percent a,a K) sane as above sane as above Solon, et al (1969), AH.IC-37S5 Solon, et al (1969), ------- Parathlon (Sesavcx pretreatnent at t ppn) Parathlon (Sesanex pretreatnent at 2 PP«> Parathlon (Sesanex ppetreatnent at Z Oo • I Notenlgonus chrysoleueas Leoonls cyanII us Leoomis nacrochlrus t — 0.20 CtSpercent -- AChE Inhibition) O.?0 (UO percentAChE Inhibition) 0.20 (Wpercent AChE Inhibition) Fish brain AChE activity Has not affected by Sesamex alone but Has significantly Inhibited by parathton. Pretreatirent with Sesamex at 2 ppn resulted In decreased Inhibition of AChe activity by parathlon. sane as above sane as above Gibson, et al (1971). AMIC-3799 Gibson et al <197U , AMIO3T99 Gibson, et a I (1P7D, Parathlon r u> Parathlon Parathlon Parathlon Parathlon Para th Ion leoonl* •acrochlrus (brain tissue) 0.7? (SB 30 nln, invltro) Plnephales BCFA — pronelas Plxephales BCFA ~ oronelas Notenlqonus L ~ chrysolcucas Leponls cyan11us Leoomls L •aerochlrus (T<»t 0.6 (5 percent K) 0.20 (67 percent AChE inhibition) O.?0 (71. percent AChE Inhibition) O.ZO (68 percent AChC Inhibition) This study Has conducted to Gibson, et determine whether brain tissue and al (1969) » handllnq variables ( f reez loq- than Inq) AHIC-378'5 affected AChE assays. AChE Inhibition of ?5 oercent occurred at 750 pnb Considerable variation occurred, i.e., no symotoms Here evident and fish recovered after experiencing 9B oercent AChF Inhibition. The authors reconwend standardization of handling procedures and fish strain. LAS acted synerqistleally Hith Solon, et parathlon to cause less survival of al(1969), fatheds but had an Indeterminate effect ANIC-3785 tilth DDT and no synerqlstlc effect xlth Endrin. sane as above Fish brain AChE activity Has not affected by Sesanex alone but Has significantly inhibited by parathion. Pretreatnent with Sesanex at 2 ppn resulted in decreased Inhibition of AChe activity by parathlon. San* as above sane as above Solon, et al (1969). AHIC-3785 Gibson, et al (19M). AHIC-3799 Gibson, et al (1971), •HIC-3799 Gibson, et •1(1971), AN.IC-3799 ------- Co* pound Parathlon Organise Lepomls cyan! lus IP<>sI«tantl Field Field Study Location BSA — Toxlelty, Active Ingredient, Pp. 0.38 CTZ) Experimental Variables, Control ted or Noted a» Comments Green sunflsh from Belzonl, Hiss. Mere resistant to Chlorrtanw, Heotachlor, LIndane, and Strobune, hut not to Reference MincheN, • al 119701, ANIC-571 Parathion cyanellus fSu«e»ptIbla> BSA 0.31 (T2) Parathion. Golden shiners fron the sae location Mere resistant to LIndane and Strobane, tolerant to Chlordane and Heotachlor, and susc«otlble to Parathlon. LaeK of resistance to Parathlon Indicated lacK of agricultural usaae of organochosphates In that area. Resistant fish Mere compared to susceptible ones collected at Starkvllle. sa»e as above NlncheM, et at(1970), AHIC-«!«.7l Parathlon Parathlon Notemlqonus BSA cry-: Notemlqonus BSA crvsoleucas (Susceptible) Z.SO IT2) 1.90 (T2) sa»e as above saa as above HlncheM, et al(1970), AHIC-5U71 HlncheM, etal (1970), AHIC-571 Parathlon Parathlon Pa I aeiaone tes kadiakensls raslatant) Pataevonetes KadlaKensls (resistant) BSA — BSA — 0.0071 (Tl) 0.0066-0.0116 (Tl) sane as above Naovl. et al (1970), AHIC-5519 Ploassays were conducted with Naavi, et al shriip fron three areas of Intensive (1970), pesticide use and fro an unexoosed area. AHIC-S519 Previously exposed shrimp Mere fron 1 to ?5 times more resistant than unexoosed shrimn. Both types of shrine were also exposed In cages to Maters of the contaminated ureas. Susceptible shrlnp suffered 66 percent more mortality than did resistant shrlmo. The toxlclty of the insecticides ranked in descending order Mas as follows! most toxic, Endrln, DOT, Methyl paratnion. Parathlont medium toxlclty, Guthion, LIndane. ------- •••rath I on Notemlgonus crysoleucas • ^^ •arathlon Tub Hex tub Ifex FL and BS* Belzonl, Miss. r VO Parathlon Cardlurn edule BS* — Toxaohene. Strobanet lease toxic Chtordane. Sevln, and Heotachlor. 0.5 (SB 1-Z) — Fish exposed as Indicated had Butler, et significant or highly significant changes al (1969). In hematocrlt, leucocytes, lymphocytes, ANIC-5977 heteroohlls. and In body Height. No significant changes were noted In body length, or erythrocyte total and fragility. The authors state that effects on hemopoelsls and cell membranes could produce the results reported. Z.OO (NTEt — The response of Naovl, etal pesticide-resistant aquatic organisms to (1969), various pesticides was compared to the »MIC-5979 response of non-resistant species. Pesticide-resistant species Here collected at Belzonl and non-resistant soecles at State College. Cooeoods. clams, snails, and sludge Norms from Belzonl were considerably more tolerant to pesticides than the non-resistant organisms. The authors note that the effect of Increased tolerance In the organisms Is an Increase In the amount of pesticide residues available to animals of higher trophic levels. 3.3-10 (T2I a(eontin- One hundred-forty surface active Portmann, et uous aer- agents, solvent emulslflers. pesticides, al (1971). atlon, sea.polychlorinated blphenyls. pure AHIC—7701 water, and Inorganic, and organic chemicals were daily evaluated against as many as ten marine solution organisms. The authors noted that aost renewal) published data of this type deal nlth Toxlcity of chemicals to freshwater organisms. ParthI on Cranqon crangon BS» ~ I.003-0.01 mi «( contin- uous aer- ation, sea- water, and dally solution renewal) saae as above Portmann, et al (1971). »MIC-7701 •erethlon PI eur onec tes platessa BS B.03-0.10 (T2t a»(contin- uous aer- ation, soo,- watar, and same as above Portmann. et al (1971), »HIC-7701 ------- Toxiclty, Active Field Field Ingredient, Cmoound Organism Study Location Ppa irafhlon Ictalurus 8CF* — 0.8-3.8 (K up nebulosus to 30 dt Experimental Variables, Controlled or Noted Comments Reference daily solution renewal) a,c,d,e, r Catfish blood content of Mount, et al ,9 parathlon Has shown to be directly (19%9), u» ParathIon •CB Ictalurus nehulosus BCF» 10-SO Ibtood residue) corre!atable Mlth Hater content, AHIC-11 lethality, and sublethal symptoms. Freeze-thaning of blood five times resulted In disruption or blood cells and release of unaltered parathlon thus Indicating that this pesticide Is not readily and completely metabolized In fish. ,c»d,e,f same as above Unite sucker FRL Hlsc. states D.27-lt.8 residue (SB) •CB •CB YelloH perch FRL Hlsc. states 0.28-12.6 residue (SB! Chain pickerel FRL Hlsc. states d.%9 residue (SB) The Bureau of Sport Fisheries continued Its fish monitoring program by collecting 11.7 composite fish samples from 50 nationwide monitoring stations during the tall of 1969. Fish were analyzed for residues of 11 organochlorlne Insecticides, Holds, and PCB-s. sane as above same as above Mount,et al (1969) • •MIC-11 Henderson, et al(197t), »t1IC-H.07 Henderson, et alftqril, »MIC-1«.97 Henderson, etal (1971), • HIC-11.07 PCS PC White cattish FRL Hlse. states less than 0.10-2.16 residue (SB) White perch FRL Hlsc. states less than •.10-7.68 residua ISB) sane as above saae as above Henderson, et al (19711. AMIC-1V07 Henderson.et al (1971), «HXC-1«07 ------- Goldfish FRL HlSC. states 9.50 residua (SRI saae as above Henderson, • t »1 i«>o7 PuaoMnseed FRL Hisc. states 2.68 residua (SB) saae as ibov* Henderson, • t si (14711, Mic-i07 Larqeaouth FRL Misc. states less than bats 0.10-8.07 residue (SB) saae as above Henderson, • t al (1971), »MIC-1MI7 KB Brawn bullhead FRL Misc. states 0.3<.-<..00 residue (SB> saae as above Henderson,«T al (1971), PCS Ul VM Carp FRL Misc. states less than o.10-11.r residue (SB) Channel FRL Misc. states less than catfish 0.10-6.77 residue (SB) save as above saae as above Henderson, et al (1471), »MIC-1«.07 Henderson, et «l AMTOl«i07 Redhorso FRL Misc. states less than sucker 0.10-0.2? residua (SB) saaa as above Henderson, et al (19711 , »MIC-1«.07 KB Gizzard shad FRL Misc. states 0.22-0.86 residua (SB) saaa as above Hendrson,et al KB Sootted sucker FRL Misc. states less than 0.10 residua (SB) same as above Henderson,et at (1971), MIC-l«i07 KB BlueqlllS FRL Misc. states 0.39-1.19 residue (SB) same as above Henderson, et al (1971),»HIC- I«i07 KB Redbreast sunfish FRL Hlse. states 0.19 residue (SB) saae as above Henderson, et at(1971), »HIC-1«>07 Strlpad FRL Hlse. states less than aullet 0.10-1.39 residua (SB) saae as above Henderson, et al (1971), ------- u> VJ1 ru Coapound PCB PCB PCB PCB PCB PCB pcb PCB PCB PCB PCB Orqanlsa Blue catfish Rock bass Freshnater drua Bloater LaKe Mhltef Ish LaKe trout Hhlte craoole Blqaouth buffalo Saallaouth buffalo Flathead catfish Col day* Field Study FRl FRL FL FRL FRL FRL FRL FRL FRL FRL FIH. Field Location Misc. Misc. MlSC. MlSC. N1SC. MlSC. MlSC. MlSC. Nlse. MlSC. H\|SC. states states states states states states states states states states states Toxlclty, Exoerlaental Active Variables, Inqredlent, Controlled Poa or Noted less than 0.10 residue (SB) 0.39-l>.10 residue (SB) 1.9d residue (SB) residue (SB) 1.96 residue (SB) residue (SB) 0.83-1.79 residue (SB) less than 0.10-1.21 resldue(SB) 2.66 residue — (SB) 3.»8 residue — (SB) I.1S-Z.35 — residue (SB) Comments saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above Deference Henderson, etal (19M), AMIC -107 Henderson, et al (1971), AMIC-1«.07 Henderson, et al 11171), AHIC-H07 Henderson, et al (1971). SMIC- 11.07 Henderson, et aid1"!), AHIC-11.07 Henderson, et al (1971), AMTC-1U07 Henderson, et al (1971), AMIC-1U07 Henderson, et at (1971), AMIC-11.07 Henderson, et 81 (l?7l>, AMIC-1«.07 Henderson, ANIC-l«i07 Henderson, •t al(197t>. ------- PCB Hal lay* FRL Hlsc. states O.ZZ residue (SB) Sauqer FRL Misc. states 1.09 residue (SB) saae as »bow« saae as above »MIC-1«.07 Henderson, et al 11.07 Henderson.et at <197l>, •CB Flunnelaouth FRL Misc. states 2.1H residue sucker (SB) saae as above Henderson t et U> vn •CB •CB PCB PC8 Black bulI head FRL Hlsc. States 0.15-0.21 residue (SB) MMte bass FRL Misc. states LOW residue (5B» Black crapele FRL Lerqescale FRL sucHer Misc. states less than 0.10-1.83 residue (SB) Hlsc. states less than 0.10-1.16 residue (SB) saae as above sane as above sane as above saae as above Henderson, et »l(l«71>, • HIC-1I.B7 Henderson, f at (1971), »HIC- 1<,07 Henderson, et al (1471), Henderson, et al (1971), • NIC-l«t07 tt Seallaouth FRL bass Misc. states less than 0.10 residue (SB) sane as above Henderson, et at (1971), PCB Northern sauaHfIsh FRL Hlsc. states 0.58-1.19 residue (SB) sane as above Henderson, et at (1971), 4MIC-H.07 •C8 Chlselnouth FRL Hlsc. states 0.71-0.98 residue (SB) saae as above Henderson, et al(1971), «HIC-1«.07 •CB •CB Klaaath sucker FRL Rainbow trout FRL Hlse. states 0.13 residua fSBI Hlsc. states B.ZT-.k8 residua (SB) saae as above saae as above Henderson, et al(197i), • MIC-11.07 Henderson, et •1(1971), ------- Coetoound PCB PCB PCB i V»» Org»f»is« qrldqellp sucker Arctic grayling Pound •hltef Isn Longnose sucker Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Study Location Pen or Noted Consents FRL Misc. states 2.75 residue — sane as above (SB) FRL Misc. states !."»? residue ~ sae,e as above (SB) FRL Hlsc. states 2.62 residue ~ same as above (SB) FRL Hlsc. states 1.53-3.87 — same as above residue (SB) Pet erenee AMIC-1V07 Henderson, et SH19M), ANIC-t«.fl7 Henderson, AHIC-1U07 Henderson, et al (1971), A1IC-1I.07 Henderson, etal (1971), AHIC-1<.07 PCB KB PCS KB PCB PCS PCB Sebastodes FO so. Pacific 1.0 t liver- Ocean, Cal. residue) Sanotes of narlne anlnals Here Hunson collected from three locations off the (1972),»MIC- coast of Southern California and analyzed 3096 for residues of chlorinated hydrocarbons. The data suggest that Kellefs whelk Mould be a good indicator organism for studying the regional distribution of chlorinated hydrocarbons. Parat ahrix nebul 1 f er Anlsotrenus davldsonl Pixel onetaoon pulehru Hal lot Is puf esc ens Stronqylocent rot us franc Iscanus Hlnnltes •ul tlrueosls FO FO FO FO FO FO Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. Pacific Ocean, Cal. 0.2% (liver residue) 0.51 (liver residue) 0.?9 (liver residue) less than 2.0 (qonad residua) 0.12-0.21 fgonad residue) 0.9 (gonad residue) sane as above sae as above same as above sa«e as above sane as above saae as above Munson(1972>, AMIC-3096 Hunson(1973), AMIC-3096 Munson(197Z). Hunson «197?», AMIC-30<»6 Hunson (1972), AMIC-3096 Hunson (197?), AHIC-3096 ------- PCB PCB PCB PCB U) VI vn PCB PCB PCB PCB PCB PCB PCB PCB Hal lot 1« corrugata Kelletla fcelletll Penul Irua InterrupTus Anqultla ' rostraTa S«b»atode8 •arlnus fsoie nlger Salao salar Cluoea harengus Scoaber seoabrus rlytllus edulls Cadus aorhue Uroohyels tenuls FO FO FO FRl FRL FRL FRL FRL FRL FRL FRL FRL Pacific Ocean. Cal. Pacific Ocean. Cal. Pacific Ocean. Cal. ST. John, N.B., Can. ST. John, N.B., Can. ST. John, N.P-. , Can. ST. John, N.B., Can. ST. John, N.B., Can. ST. John, N.B., Can. ST. John, N.B., Can. ST. John, N.B.. Can. ST. John, N.B.t Can. O.OOS (gonad residue) 0.?3 (residue) — 0.16 (auscle residue) 0.71 (residue) — Trace (residue) 0.33 (residue) — 0.<»S (residue) ~ (residue) 0.35 (residue) ~ 0.1 (residue) -- 0.03 (residue) ~ O.OZ (residue) — saae as above saae as above saee as above PCB"s were found In higher concentrations than orgarochlor Ine .pesticides In alt fish analyzed. The authors point out that PCB is less toxic In an acute sense than organochtorlnes, that little is known of sublethal PCD effects, and that aore knowledge of PCB distribution and effects is needed. same as above saae as above saae as above saae as above sane as above saae as above same as above saae as above Munson 3096 Hunson 3(96 Wunson(197?\|« Zltko (1971) i •NIC-3715 Zltko 3715 ZltKo ( 19711. •HIC- 3715 Zltko (1971),V»IC- 3715 Zltko(1971), »«C-3715 Zltko (1971),MIC- 3715 Zltko (1971), »MIC- 3715 Zltko <1971),»MIC- 3715 ZltKo (19711,»HtC- 3715 ------- > vn Coeoound »»C« •C8 »cs •CB PC8 res Toxiclty, Experimental Active Variables. Field Field Ingredient, Controlled Organise Study Location Pp« or Noted Comments Hippo- FRL glossoides plataasoldes F»lco F peregrimis (eggs) Falco F or»gr inus •Immature) Falco F peregrlnus (immature) Falco F oeregr Inus (adult) Falco F oeregrlnus (adult) St. John, 0.03 (residue) N.B., Can. Western 10.2 (residue) — O.S., Pacific Ooaan, Panama, Mexico, and An tare tic Western 0. 16-81. (flesh — U.S., residue) Pacific Ocean, Panama, Mexico, and Antarctic Western 3.3-l,<.20 «»at — U.S., residue) Pacific Ocean, Panama, Mexico, and Antarctic Western 19.7-%1.5 U.S., (flesh Pacific residue) Ocean, Panama, Mexico, and Antarctic Western 3.2-1,980 (fat — U.S., residue) Pacific sane as above Peregrine falcons, falcon prey. an>1 other predator «oecles Mere collected widely and analyzed tor DOT, HOE, PCS, and a tew other oestlcldes to a lesser degree. PCR and DDT Here found to be widely dispersed globally. PCP was found enzymes that degrade oestradiol. Reductions In thickness of egq shells. eggshell weight, and water retention occurred. Ill affect hatching success. The authors state that the peregrine "ay be the first species entlroated by global contamination. saoe as above same as above sane as above sane as above Reference Zltko (1«71», AMIC-ST1S Risebrougn, et al (1968). 4HIC-38M. Rtsebrough, et al (1968), AMIC- 3»<.i. Rtsebrough, et al (19S8), AMIC-38k« Risebrough, et al (1968), AHTC-38 ------- PCS PCS U) vn PCS PCS PCS PCS looaelanla •elanla Haloeyptena •Icrosoaa Plronyx vlvesl Erxlonychura cravert leqgs) Thalasseus efeqans (eqqsl Larus heeraanl (cqqs) Ocean, Panama, Mexico,and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Oc*n, Panama, Mexico, and Antarctic western U.S., ParIfic Ocean, 1.0 (Hhole body residual 0.35 (whole body residue) 0.02 (Mnole body residua) save as above saae as above saae as above Mexico, and Antarctic western U.S., Pacific Ocean, Panama, Mexico,and Antarctic Western U.S., Paclf Ic Ocean, Panama, Haxleo, and Antarctic Western U.S., Pacific Ocean, Panama. Mexico, and Antarctic (residual saae as above 1.5 (residua) saae as above 8.1 (residua) saaa as above 4HIC-38W. Rlsebrouqn, et al I19K8I, INIC-S8S HI safer oug ti* et al (1468), AHIC-38 Rlsebrouqh. et al AHIC-38 Rlsebrou<]h,e t al (19«8I. AMIC-3SHU Risebrouqn, et al (1968), AMIC-38V". Rlsebrouan, etal (19681, AHIC-38M, ------- OJ \J\ CD Comoound PCS PCB PCB PCS PCB PCB Orqanlsn Pomoxls annular Is Pomoxls nlgro- naculatus Leoomls •acrochlrus Pyqoseel Is advllae (eqqs) Futmanus glaclalls Put f Inus creatoous Field Field Study Location F Western U.S., Pacific Ocean t Panama, Mexico, and Antarctic F Western U.S., Paclt Ic Ocean, Panama, Mexico, and Antarctic F Hestern U.S., Paclf Ic Ocean, Panama, Mexico, and Antarctic F Hrstern U.S., Pacific Ocean, Panama, Mexico, and Antarctic F Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic F Hestern U.S., Pacific Ocean, Panama, Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments O.OOt (whole -- same as above body residue) 0.003 (whole — same as above body residue) 0.005 (whole -- same as above body residue) 0.0di» — - same as above (residue) 0.08-6.5 (whole — sane as above body residue) O.it? (whole — same as above body residue) Reference Rlsebrouqh.e t al (1968), AMIC-Sm Plsebrouqh, et al (iqfiM , AMIC-38<>« Rls»brouqh, et al (1968), AHIC-3Sk* Rlsebrovign, et al (1968), ANTC-38H, Rlsebrouqh, et al (1968), Amc-38<> Rlsebrough,e t al (1968), ANIC-38 ------- PCB pee U) vn NO PCS PCS Pu Minus qrlseus PuffInus tenulrostrls Oceanodroma homocnroa Peleeanus F occidental Is (eqqs) Freqata •aqnlfIcens (egqst Sula leucoqaster HexIco( and Antarctic Western U.S., Pacific Ocean Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panana, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico,and Antarctic Western U.S., Pacific Oce an, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic 0.9-1.2 iMhole body residue) Z.I (whole body residual 9.8 (whole body residual 0.010^-0.0231 (residue) 0.0057-0.084 (residue) 0.00<,» (residue) saae as above same as above sane as above same as above sane as above same as above Risebrou9h, et al (1968), »MIC-S8«.<> Rlsebrougn, et al (1966), AMIC-38M PIsebrouqh, et al (1968), Rlsebrouqh, • t al (1968), Rlsebrough, et al (1968), Rlsebrou9nt et al (1968). AMIC-mit pea Phalacrocorax F Western 0.113 same as above Rlsebrough, ------- Compound Organism penlclllatus (eagst IB Phalacroeorax pelaglcus (eggst !• Anas cyanoptera :B El anus tcucurus feggs) :B Ace loiter cooper 11 !• Aoulla chrysaetos (•99) Field Field Study Location U.S.. Pacific Ocean t Panama! Mexico, and Antarctic F Western U.S., Pacific Ocean, Panama, Hexlco,and Antarctic F Western U.S., Pacific Ocenn, Panama, Hexlco, and Antarctic F Western U.S., Pacific Ocean, Panama, Hexlco, and Antarctic F Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic F Western U.S., Pacific Ocean, Panama Mexico, and Antarctic Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppn or Noted Comments (residue) 0.062 — same as above (residue) 0.91 (whole — same as above body rest duet 0.00as<»-0.006<> — same as above (residue) 6.3 (Dhole body — same as above residue) 0.23 (Mhole — same as above body residue) Reference et al (1968), AHIC-38** Rlsebrough, et al (1968). AMIC-SSMi RIsebrouqt, etal (1968), AHIC-38tt Rlsebrouqh, et al (1968). ANIC-38«.» Rlsebrou9n, et al (1968). AKIC-381* R isebrouqn. et al (1968), AHXC-38«t ------- MB MB MB MB MB MB Pandlon ha IIartus Fa I eo coluabarlus Falco soarverlus Faleo soarverlus (e<os> Nyctlcorax nyctleorax (eggs) Larus F occidental Is leq9S> Sterna torsterl (eons) Western U.S., Pacific Ocean, Panana, Mexico, and Antarctic Western U.S., Pacific Ocean, Panana, Mexico, and Antarctic Western U.S., Paclf 1C Ocean, Panana Mexico and 0.003^-0.103 (whole body residue) 0.39 (Hhole body residue) 0.31 (whole body residue) 0.09 (residue) — sane as above sane as above sane as above Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western D.023-0.33 U.S., (resldut) Pacific Ocean, Panama, Mexico, and Antarctic Western 0.023-1.31 U.S., (residue) Pacific Ocean, Panana, Mexico, and Antarctic saa as above same as above saae as above Western U.S., Pacific Ocean, 0.11* (residue) saae as above Rlsebrougn, et al (1968), AHIC-38«t P.Isebrou9h, et al (1968), ANIC-3S«<> PIsebrough. et al (1961), et al Plsebrouqh, et al (1968), ANIC-3««i> Rlsebrough, et al (1968), AHIC-3« ------- Coaoound Organise !8 Hydrooroqne caspla (•qgs) !B Phalaropus lul learlus :• Urla aalqe (eqast IB Ptyehoraaphus aleutlcua JB SyntMlboraap hus antlauua !• Cerorhlnca aenocarata Field Field Study locution Parian a • Hvxlco. and Antarctic F Western U.S., Pacific Ocean , Panama, Mexico, and Antarctic F Western U.S., Pftelf Ic Ocean , Panama, H»xlco« and Antarctic F Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic F Western U.S., Pacific Ocean , Panama, Mexico, and Antarctic F Western U.S.. Pacific Ocean, Panama, Haxlco, and Antarctic F Western U.S.. Pacific Oe»n. Panama, Mexico, and Antarctic Toxlclty, Experimental Active Variables. Ingredient. Controlled Pea or Noted Coaaents 0.11V-1.01 — saae as above (residue! D.10 (whole ~ saae as above body rest duel 5 (residue) ~ sane as above (.16 (whole ~ saae as above body residual D.1S (whole ~ saae as above body residue) 0.16 (whole ~ saae as above body residue! Reference Rlsebrouqh. et al (1968), AMIC-38W Rlsebrougri, et al (1468). AM.IC.-3AM> Risebrough. et al « 11681 , AMIC-38M. RIsebrouqh, et al (1968) , NIC-J8«,V Rlsebrough, et al- (19681. AMIC-38IA Rlsebrough. • t al (1468). ANIC-S8»% ------- PCB PCS PCB ft ZenalduTa •acroura Tyto alba leqqs) Sturnella neqleeta Fundulus heteroclltus CO Western U.S., Pacific Ocean, Panea, Mexico, and Antarctic Western U.S., Pacific Ocean, Panama, Mexico, and Antarctic Western U.S., Pacific Ocean, Pan ana, Mexico, and Antarctic Mo residua — saaa a* above BSA — 0.<>7-0.66 (residue) O.OOZS-0.0261 (residual 0.0003H-O.OOOI. (TV) 8»,e,e, and synthetic seaxater Pebulete Nereis vlrtns BSA — Gammarus BSA fasclatus 0.00068-0.00079 a»,C,e, (T« and synthetic seanater sa«a as above Rlsebrouqh, et at (196$), AHIC-3RI.V Rlsebrouqh, etal (19«S), sane as above Rlsebrouqn, et »l (196S), AMIC-JKM. A laboratory procedure based on •Standard Methods for qK-hr toxlclty deternlnat Ions of crurl* oil and olt-dlspersnt mixtures «as described. The dlsoersants varied considerably in toxlclty, ranqlng fro 0.01 to 7.1 •!/!, TLSO for 96 hr. These did not differ slinl f Icantl y fro* ? ------- Toxlclty, Experimental Active Variables, Field Field Ingredient. Controlled Compound Organism Study Location Poa 9r Noted Comments Reference water, and dally solution renewal) Pentachloroohenol Crassostrea L — less then 0.25 ~ vlrglnlca (T2I teggsl Inorganic. >nd organic chemicals »ere evaluated against as many as ten Marine organisms. The authors noted that most published data of this tyoe deal with toxlclfy of chemicals to freshHater organises. The effect of 52 pesticides on OavlStet el embryonic development of clams and (19691 t oysters was reported. Synerglstle AHIC-5990 * PentacMoroDhenot Penfechloroohenyl •cetate PentacM or ooheny I •cetate •erolln No. 9 Crassostrea vlrqlnlea (larvael Crassosfrea vlrglnlca Crassostrea vlrglnlca flarvael Crangon cranqon L — • M_^ t — 8S« — O.BT1 less than 0.25 — less than 0.025 — effects with solvents Here also reported. Host of the compounds affected develocment more than survival. Some. however, drastically reduced larval growth. The authors point out the necessity of evaluating the effects ot pesticides on all life stages of an organls* and note the possibility of selecting chemicals for pest control that •oufd not have serious effect on Shellfish. sane as above Davit;, et same as above same as above 4NIC-5990 Oavls* et a I (1969). 3.3-10 (T2) Davis, et al (1969). •NIC-S990 Portmann. et al (19711. •Mic-rroi •erthane TubI few tubIfex rt and •.• (MTf» Miss. a(contln- One hundred-forty surface active uous aer- agents, solvent eaulslflers. pesticides. atlon, aea-pol vchlorlnatod blphenyls. pure Water, and Inorganic, and organic chemicals were dally evaluated against as many as ten marine •olutlon organisms. The authors noted that aost renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. — - The response of Naovl. etal pesticide-resistant aquatic organisms to (19691* ------- BS» Petrol It* W-1HVJ Patrollte W-1U39 Phenkapton Phenoberbltal Phenobarltal Phenolic* Steel heal trout I f Ingerllnq) BSA — 35.5 (T Coho salmon BSA Rood Canal, 1.5 (K) (flngerllnga) In Hoodaport, •Itu Hash. Fish Inot specified) Neqaprlon BSA — brevlrostrls (1-3 kq> greater than 1.0-10.0 300 (NTE3.Z5 hr> Carasslus auratus Fish (not specifled) 75 (MTE) greater than 0.1-1.0 (Kl various pesticides Mas compared to the AHIC-S979 resoonse of non-resistant species. Pesticide-resistant soecles were collected at Belzonl and non-resistant species at State College. Cooepodst claws, snallst and sludoe norms from Belzonl Here considerably more tolerant to pesticides than the non-re-sl stant orqanlsns. The authors note that the effect of Increased tolerance In the orqanlsns Is an Increase In the amount of pesticide residues available to animals of higher trophic levels. Evaluation of 11 oil dlspersants Tracy, etal resulted In a ranfelnq for each and a (1969). recommendation for use according to the AHIC-383 ranKlnq. Ranking MBS based on toxlclty and oil dlsoersal effectiveness. Corexlt 776 ------- Comoound Phenols (plus •••on I a and zlnel Toxicity, Active Field Field Ingredient, Organism Study Location Pom Sal mo 8SA — 0.5-2.51, (T2> ga 1 rdner 1 Experimental Variables, Controlled or Noted Comments Britain were summarized. An excellent brief, general discussion of toxicltv testing Is also present. a,e,d,et Rainbow trout were exposed to f»» concentrations of fluctuating levels of Reference (1«7H, AMI 1056 Brown, et 11969), • 1 > Phenols leius coooerl Sal mo qalrdnerl BS» 0.5-1.75 IT2I a.c,e Phenols lolus cooper, ilnet Phenols Salao galrdnerl BS» 0.6-2.1,0 (T2) a.c.e Rashora BCFA heteromoroha and BSA 6.2 CT2, hardwater) a,c,e,f, hard (HW> orsoft (SH) synthetic dilution water, or seawater tor soae seeeles ammonia, phenol, and zinc and to constant mixtures ol the tv~»e. Tests Mlth fluctuating levels of toxicants showed that LC50 values Here similar to those for constant concentrations as long as the oerlodiclty of the fluctuation did not exceed the resistance tine for the poison. Except when zinc predominated In th« mixtures, the fractional toxlcltles could be summed to give the toxicity of the mixture. Rainbow trout were exposed to Brown, et cooper, phenol, zinc, or nlcKel solutions al(19701, to determine and cooper, zinc, and nickel. It was concluded that acute lethal toxlcltles of the mixtures could be adequately described by summations of the fractional tnxlcltles. Brown,et al (1970). same as above One hundred slxtr-four Alabaster oestlcldes, wetting agents, and (1969), miscellaneous water pollutants showed a ANIC-525 wide range of toxicity scanning 12 orders of magnitude. Knowing the toxicity and percentage of all components of a formulation did not result In easy predictability of the toxicity of a mixture of materials. Sometimes pesticides were most toxic in hard water and sometimes the opposite was true* Testing the actual material as sold Has found to be essential. ------- Ptienols Rasbora heteromorpha BCF* and BS» 7.1. IT2, softwater) Phenols Leooals macrochlrus BS», L 13.9 I TO Phenols Phenol* Phenols Nltzschla linear is' BS«, L Physa BS«» haterastrooha L Hercenarla •ercenarla 258 (TSI 9* (Ttl 5Z.6 UZ) ft»,e,e,f, bard (HW) or 30ft (SW) synthetic dilution water or sotwater for some species a»e» and synthetic dilution water atCt and synthetic dilution •ater a«e, and synthetic dilution water saae as above Phenols Phenols Hercenarla •ercenarla IIarvae) Crasiostraa vlrqlnica L — t — 99 (T12t 98.3 ITZI Alabaster (1959), NIC-5Z9 This study HSS conducted to Patrick et d«ternlne the relative toxicltles or It al (196a). coimon constituents of industrial wastes »NIC-57?0 to a Msh, an alga* and an Invertebrate. The experiments Here conducted over a 10-year period for varied purposes. The authors recoavend bloassays Hlth at least three components of the food web. saae as above same as above Patrick, et al (1968), »nIC-97ZB Patrick, et al (1468), AMIC-5720 The effect of 92 pesticides on Davis, et al embryonic development of elans and oysters Mas reported. Synerqlstlc (1989),»MIC- effects with solvents Mere also reported. 9990 Host of the compounds affected develocaent acre than survival. Some. however, drastically reduced larval growth. The authors Point out the necessity of evaluating The effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that would not have serious effect on shellfish. saae as above same as abeve Davis, et al «t969».t«C- 9990 Davis, et at ------- Cemeund Organise Field FUld Study Locatla Toxlclty. Active Ingredient, Ppm Experimental Variables, Control led or Noted Convents R«l«r«nc« •nenols (eqqsl Sal BO qalrdnwl BS» 9. IT2I Phenol* BS» Phenols Phenols Phenols Phenols Phenols Ganbusla af finis (female. t.3 cm, 1.9 ql Leblstes retleulatus (•ale. l.t e«, a.? qi Tllapla aossaoblca (T.I. c», 1.3 qi Kuhlla BS» sandvtcensls «i.3 c«, 1.5 9> Stoteohorus BS» purourva 13.6 ca, I.* gl 26 ITdl •..o.d. •,r»i, (Honolulu tap BSA — BS» Carclnus BSA — si 19 IT) 11 ITVI 8.91 IT12 hr) 96 IT?) »,c,d,e, e.f.l, (Honolulu tap water a,c,d,e,f, 1, sal tnater a,c,d,e,f, I, salt «ater 9990 RalnboH trout Here exposed to Broun, et al coooer, phenol, zinc, or nickel solutions (1970), to detvrolne 8-hour LC50 values for • Ixtures of copper and phenol I coooer, zinc, and phenoll and coooer, zinc, and nickel. It MBS concluded that acute lethal toxlcltles of the mixtures could be adeauately described by summations of the fractional toxlcltles. The five fish soecles are commonly found In streams and estuaries Nunoqax», et • i (iirott In semi-tropical areas. C. affinis Mas AMIC-6S67 the most tolerant. Varied sensitivity to the toxicants Mere found. K. sandvlcensls MBS the aost sensitive fish studied. The standard Method procedure •as followed. ••« above. ^Honolulu saee as above same as above same as above ••(contin- one hundred-forty surface active uous aer- agents, solvent eaulslflers, pesticides, •tlon, sea-polychlorlnated blphenyts, pure water, and Inorganic and organic chealcals Mere • 1 AHIC-6S67 NunooaHi, et al (1970), 1)110-6967 Nunoqawa, et al (1970)* •HIC-6567 NunogaMi, et al (1970). ANIC-6967 Portaann, et al (1971), •NTC-7701 ------- Phenols Cardlua edule BSA greater then Mi (T2t Cranoon eranqon BS» — Z3.5 ITZt Phenols PandaIus eontaqul 17.5 tret dally evaluated against as aany as ten aarlne solution organises. The authors noted that east renewal) published data of this type dal with toxlclty of chealcals to freshwater organises. ae(eontin- ••• •* above uous, aer- ation, aea- water, and daily solution ,renewal) ae( contin- uous, aer- ation, sea- water, and dally solution renewal) a«(contin- uous, aer- ation, sea- water, and dally solution renewal) Portaann, at el U97t>. see* as above »a«« as above Portaann, at al 11971). •HIC-7701 Portaann, at al 11971), Phenels Platlcthys flesus ss» — 33-180 (TZ) a* (con tin. uous, aer- ation, sea- water, and dally solution renewal) save as above Portaann, at al (1971), •HIC-7701 Pnenois tobassls ssfeha BS» — 13.5 \|T1I a. Measureaent of residual dissolved Ballard, et seanater oxyqen during exposure of fish to al toxicants resulted In data similar to (1969>,AHXC- that obtained fro" Zd- and 8-hr 300 bloassays by the standard aethod. The residual oxyqcn aethod required only 8 hr to conduct. Variables studied Included density per unit voluae, teaoerature, and fish size. The authors conclude that the residual oxygen oethod Is a Quick and ------- CoBpound OrganlsB Field Field Study location Toxtelty, Active Ingredient, Ppa Experimental Variables, Controlled or Noted Comments Reference Pnenoxylene Crangon crangon BSA ~ reliable procedure for routine monitoring MorK. greater than 10 a«(contln- One hundred-forty surface active Portaann, et ITZJ uous, aer- agents, solvent emulslfiers, pesticides, al (1971), ation, sea- oolychlorlnated blphenyls, pure AHIC-7701 water, and Inorganic, and organic chemicals Here daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshnater organisms. PhenoKVtol Pasbora heterororoha BCFA — and BSA 135 IT2) a,e,e,f. One hundred sixty-four Alabaster hard (HM1 oestlcldes, Netting agents, and (1969), or soft miscellaneous Hater pollutants shotted a AMIC-525 (SW)synthe Hide range of toxlclty spanning 12 orders tic of magnitude. Knowing the toxlclty and dilution percentage of all components of a Hater, or formulation did not result In easy seanater predictability of the toxlclty of a for some fixture of materials. Sometimes species oestlcldes Here most toxic In hard Hater and sometimes the opposite Has true. Testing the actual material as sold was found to be essential. Pneny I mercuric acetate Pnenyl »ercurie •cetate Brachydanlo rerlo (breeding adults and eqgs) Sal BIO g«lrdnrl 0.2 and 1.0 ppb a,f (01 BCFA and BSA 9.995 IT1) Pnenyl "arcurie Salvo 9alrdnerl BCFA and BSA 0.10* IT?) a,c,e,f, hard (HHtor soft (SH) synthetic dilution Hater, or seaHater for soa species a,e,e,f, hard tHUIor soft (SHI synthetic Eggs Here collected daily from spawning females which Here continuously exoosed to nater solutions of the chemical. Dead and hatched eggs were counted daily with dally Hater renewal and removal of dead eggs. At 1.0 oob the number of eggs released was significantly less, and at 0.2 and 1.0 nob hatching frequency was significantly reduced. One hundred sixty-four pesticides, Hettlng agents, and miscellaneous water pollutants showed a Hide range of toxlcity scanning 12 orders of magnitude. Knowing the toxlcity and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a mixture of aaterlals. Sometimes pesticides Here most toxic In hard Hater and sometimes the opposite Mas true. Testing the actual material a sold Has found to be essential. saae as abova Klhlstroa, et al (1971), AMIC-2707 Alabaster (1969), ANIC- Alabaster (19691,AHIC- 52? ------- Pnorate Ph order •ftosalon* •ttosdrln »h os drin dilution Mater, or seaMater for son* species Fish (not specified* Crangon crangon greater than O.n-1.0 IK) Approximate toxlcltles of numerous pesticides commonly used la Britain Here summarized. An excellent brief, qeneral discussion o» toxlclty testing is also present. BS* —• greater than 10 aofcontln- One huncred-forty surface active fTZ) UOUS,, aor- eqents, solvent evuis if ter-s« pesticides, ation, aea-Po'vchl°rlnated biohenyls, pure water, and inorganic, and organic chemicals Here daily evaluated against as many as ten arlne solution organisms. The authors noted that nost renewal) published data of this type deal Mlth toxlclty of chemicals to freshHater organisms. Handesley- Thomas 11971),AMIC- 10S6 Portmann, et •I (1971), AHIC-7701 Rasbora heteroaorpha BCF and BSA O.I. (T2I Cooepods (Cyclops blcusoldust Cyclops varlcans» Cyclops vernal Is, Fucvcloos agll Is.Macroc Macroeyclopa Fl State •nd Colleget BS» Hiss. 0.059 (91 percent KZI Orthoeyclops •o4stus) Conepods (Cyclops bleusnl ------- Coveeund Organise Field Field Study Location Toxiclty Experimental Active Variables, Ingredient, Controlled Ppa or Noted Pttovdrln •tiespnaeldon Ftiosphaaldon Cueyclops •gills, Haorocyelops 'albldus* Orthoeyelops •odestusI TubIfex tubIf ex Ft »nd BS" SelionI, Ml«. FI«h Inat ~ ~ specified) Labo rohlta 8SA — Ifrvt Hastoeeebolus BS« panealus Necrognethus BSA aculcatu* Nandus nandus BS» — 1.1 INTO greater than 1.0-11.1 IKI 137.7 1T7I Coaaents Reference IT7> .7 IT7) 5.7 \|T7I saee as above Approximate toxlcltles of numerous pesticides conaonly used In Britain were suaaarlzed. An excellent brief, general discussion of toxlctty tasting Is also present. Naovl, et at (19691, AN1C-5979 HaHdesley-Th oaas(1971) AHIC-1856 a«c,dtetf OOVP end Phooh»«ldon «ere shoiin Konar to be selective toxicants that can be 119691,•NIC- used for eradication of undesirable SS53 anloals fro* ponds without Injuring carp. OOVP seeaed superior since less UBS needed. It Mas not Influenced by turbidity, and It 'etrxlfled core rapidly than phosphaaldon. •»MP».la» >Hepael4on •ttosphaaldon •hesphaaidon Fh«ah*lden Labeo rohlta (flngerllna) Trlchogastar fasclatus Channa punctatus Ifryl Channa punctatus (f Ingerllngt Chitnna punctatus ledultl BSA — BSA ~ BSA — BSA ~ BSA — 177.0-215.? IT7I 30. Z IT7t 19.1 CT7) ?5.l ,AHIC- «HIC-5»53 Konar (1969).HIC- Koner « 19691, «HIC- Konar « 19691, •NIC- Konarll969>, ------- Phasenaaldon «»•» anaal don MiospMaaldon anosphaaldon Aaohlonou* BSA cuchla {younaj Aaphlpnous SSA cuchla tadultl Hrstus BSA vitatus PuntI us BSA sophor* 11. I ITTI ?.* ITTI ».e.d,».t 2.2 IT7I ate,d..f IT7I a.e.d.atf aM as abova saaa as abova San as above >••• as abov* Konar tl969) 51.53 Konar (l<)69»jHIC- 51.53 Konar 11969), »MIC-5«.5J Konar 119641. AHIC-5V53 •tiospnaaldon Inabas BSA tavtudlnau ITTJ atcdfa»r saa as abova Kcnar 119691 U) •tiosphaaldon PhvspnaaMon ftio«ona«lden PhMpnaalden Eateropnaoa- • BSA tea foaaills llryl H»t«ropa«ua- ' BSA tea roaailla BSA — danrlea lfr») Ovtlseus sp. BSA 66.8 IT7) ».c,d.«,« 66.1 ITT) a,Cid»«»r 178.2 (T7> a.e.d.atf 1.3 IT7I a,ctdtt» ••• as above sano as abovo sa« as abovo •an as abova Konar I1960).ANIC- 553 Konar (1969), Konar I1969),ANIC- 553 Konar I1Q69I .A1IC- 553 •»»«sphealdon Sohacredaaa BSA annulatua 2.6 IT7) a.Ctdta«f sano as abovo Konar <19M) 51.53 •1i«spha«l4on Ranatra BSA flllforal 2.9 IT7I a,Ctd.«>f SOB* as abovo Konar (1969), »MIC-5I,5J PhMpnaaldon Anl«oot«ra BSA Invaphs) 1.9 IT7t a«Ctd«a>f saw* as abovo Konar I1969).AHIC- 51.53 Crblstcr so. BSA — 2.3 IT7) saa* as abovo Konar I19S9), AMIC-5V53 •ttesphaaldon Napa BSA — 2.* IT7> sana as abovo Konar (1969). »HIC-553 Pnospnaaldon Bale«to«a BSA Indlea 6.3 (T7t •tcf saa as abovo Konar 11969) ------- Coepovnd Phospnaeldon Pneona«ldan •ttosahaaldon •hesphaaldon •nosBftaeldon •tiosphaaldon •nospnaeldon Phesphaeldon Phosptteeldon •tiesaneelden •es»na«ldan Field Field Organise Study Location Hydroohltus BSA — Volvox BS» — PanderIna BSA — Closterlua BSA — Bracnlonus BSA ~ Gastrotrlcha BSA ~ CyerIs BSA — Cyetoos BSA — NauDllus BSA — Oepnnla BSA — Cerlodapnnla BSA — Toxlcity. Cxoerleental Active Variables. Ingredient. Controlled Ppe or Noted Coeeents 9.S IT7I .• INTO 91 (NTEI It INTEI It INTO ?. (Kl ?.* IK) 2.5 IKI .• IKt atCtdtetf S.I (NTE) a.c.d.e.t e.c.d.etf (NTO a.c.d.e.f a«Ctde.f saite as above saee as above save as above saee as above «••• as above saae as above saae as above saae as above seae as above seae as above saae as above Reference NIC-tS3 Konar (1969), Konar (19691. Kon»r (1469), Koner (1969). iHIC-51.53 Kon»r 11069). Konsr (1969). Kanar (1969). »HIC-5«.S3 Konar (1969). »HIC-5«.53 Konar (1969). Koner (1969t, Konar (19691. ------- Phosphorus Paralabrax clathratu FH vn Phosphorus Phosphorus Phosphorus Phosphorus Phosphorus Phosphorus Phosphorus Phosphorus Paralabrax clathratus Paralabrax elathratu* Paralabrax clathratus Paralabrax clathratus Paralahrax elathratus Paralabrax clathratus (gravid females) Paralabrax elathratus Paralabrax clathratus FH FH FH FN FH FH FH Scattergood 6320 (dorsal Steaa) Plant, muscle Los Angeles, RrSIOUE) Cal. Catallna 7550 (dorsal Island* Cal. muscle raaldua) Seatterqood BfcliO (ventral Steaa Plant, muscle Los Angvlas, roaldua) Cal. Catalina Island, Cal. 6700 (ventral •use I a residua) Scatterqood Z3,6ZO (gonads Steam Plant, residue) Los Angeles, Cat. Catallna Island, Cal. ?3.920 loonads rest duel CatalInalsla 10.S50(gonads nd, Cal. residue) Scattergood 9600 (liver Steaa Plant, residue) Los Angeles, Cal. Catallna 7270 (liver Island, Cal. residua) Fish collected from an effluent Dlo* of a stean olant and from offshore waters of Catallna Island Mere analyzed for trace element content. Trace element content oT the effluent Hater was at le»t 1 times qreater than that of normal sea water for cadmium, copoer, nickel, zinc, and chromium. Livers of fish from the effluent Mere nearly tHlce the size of those from the ocean. Greatest differences In concentration occurred Nlth aluminum, cadmium, and nickel. Silver, barium, lithium, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on aarlne organises. same as above Staoleton (1968), AHIC-5980 same as above same as above same as above same as above same as above same as above saae as above Staoleton (19681. AHIC-5980 Staoleton AMIC-«98D Staoleton (1968), AMIC-59BO Staoleton AMIC-5980 Staoleton (19681, ANIC-^980 Staoleton (1968), AHIC-59BO Staoleton (1968), AMIC-S980 Stapleton (19681. ------- I Compound Phosphorus Phosphorus Phosphorus Phosphorus Phosphorus Phosphorus Phosto Organism Paralahrax clathrntus Paralabrax clathratus Paralabrax el nthrntus Paralahrax clathratus Paralabrax elathratus Paralabrax clathratus Crangon crangon Field Field Study Location FH Scattergood Steam Plant, Los Angeles, Cal. FH Catallna Island, Cat. FH Scattergood St»am PI iint, Los Angeles, Cal. FH Catallna Island, Cal. FH Scattergood Steam Plant, Los Angeles, Cal. FH Catallna Island, Cal. BSA — Toxlclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments ?53fl « same as above 1 Integument residue) 2520 -- same as above (Integuaent residue) 5800 (heart -- same as above residue) 5550 (heart -- saae as above residue) 7800 (eyeball — same as above residue! 10,d50 (eyeball -- same as above residue) greater than 10 a,»(oontln- one hundred-forty surface active ITZ) uous aer- agents, solvent emulslflers, pesticides, atlon, sea- polycMorlnated blohcnyls, pure Reference AHIC-5980 Staoleton (1968), AHIC-5980 Staoleton (1968), AHIC-5980 Staoleton (1968) , AHIC-5980 Staoleton (1968), AHIC-5980 Staoleton (1968), AHIC-5980 Staoleton AHIC-5980 Portnann, et al (1971), AHIC-7701 Pt»oto»1drln Ptiotoaldrln Anaeystls nldulans Agneneltue lloatw L — 1.0 (growth Inhibited) NTE water, and Inorganic, and organic chevlcals were daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms. a»,e»,r Hetabollc products ot Aldrln, SH Oleldrln, and Endrln can be as toxic as the parent compounds, as shown by 00 measurement. a»,c»,r saae as above SH Batterton, et al (1971), AHIC-1V71 Batterton, • t al 11971),AHIC- ------- Photodleldrln Photodleldrln Phygon igmenellum L ouadruolIcatu Anacystls nldulans Hereenarla •ercenarla f«99» L — 0.5-1.0 (growth a»,e»,r Inhibited) SH 0.9-1.0 (growth a'. Inhibited) SN 0.04 •hygon Phyqon Plcloraa (K salt) Mercenarla •ercenarla (larvae) Crassostrea vlrqlnlca l_ •• \| ^^ Grassestrea vlrglnlca I larvae) Rasbora BCF» heteronorpha and BSA 1.75 O.Olfc (T2I O.OI>1 (Til.) tl «TZ) hard (MM) orsof t (SH) synthetic dilution voter, or 1U71 Pattertoni et at Patterton. et al (1971) , sane as above sane as above The effect of 5? o»stleldes on Osvls, et al embryonic d«vcloo«ent of clams and oysters was reported. Synerqlstlc H969),AMIC- effects with solvents Here also reoorted. 5990 Most of the compounds affected develocment more than survival. Sonet however, drastically reduced larval growth. The authors point out the necessity of evaluating the effects of pesticides on all life staqes of an orqanlsa and note the oosslblllty of selecting chemicals for pest control that Mould not have serious affect on shellfish. same as above s»me as above same as above for soae species One hundred sixty-four pesticldeSf Netting agents, and miscellaneous Hater pollutants showed a xH« range of toxjclty scanning 1? orders of magnitude. Knowing the toxicity and percentage of all comoonents of a formulation did not result In easy predictability of the toxicity of a mixture of materials. Sometimes pesticides were most toxic In hard Hater Davis, «t al <1969>i««C- 5990 Oavis, et at <1969» 5990 Davis, et al (1969),AHIC- 5990 Alabaster (1969), AHIC-StZS ------- I Gonoound PMk Polycell product Po lye lens Polyclens Toxlclty, Experimental active Variables Field Field Ingredient. Controlled Organism Study Location Pp« or Noted Comments and sometimes the ooooslte Mas true. Testing the actual material as sold was found to be essential. Salmo L — 2.0 «S830) 8,e,f (1 Single exposures of fish to galrdnerl hr orianoercury compounds resulted In peak exoosure concentrations of mercury as follows dally for gills, f hri blood. 37 hri liver, 7 dat up to 11 Kl ------- renewal) elycl«ns Crangon er anger> 8SA — 10-33 (T2) ••(contin- uous aer- ation, sea- water, and dally solution renewal) •••• as above Porteann, «t 81 (19711, NIC-77ei •lclens PandaIus aontagul as* — a»(eontln- uo.ua aer- ation, aea- vater, and dally solution renewal) saaa as above Porteann, et al (i97i>,n-ic- 7701 Polycoaolax »-ll Steel head trout I finger line, I as* — i3.e mi rolyoojcplex A-U MlyeaeipIeK » Cobe aalaon B8A (flngerlinga) In •Ita Hood Canal, Hoodaport, Wash. Carctnus •aanas 8S» — 1.5 100-330 HIC-383<» ranking. Ranking was based on toxlclty and oil dispersal effectiveness. Corexlt 776t eppeared to have the least toxleltv Blth fair to good ell dlsoerslon caoabllltv. aano as aoova a(eontln- One hundred-forty surface active uous, a«r- agents, solvent eeulslflers, pesticides, atlon, soa'Polvchlorlnated blohenyls, pure water, and inorganic, and organic chemicals Mere dally evaluated against as aanv as ten aarlne solution organises. The authors noted that Best renewal) published data of this type deal nltn toxlclty of cnealcals to freshwater organises. a»(contln- saae as above uoua, aer- ation, aea- water, and dally solution ronawal) Tracy, et al (1969). AMIC-383U Portnann, et al (1971), »MIC-7701 Portaann, at al (197l>, •HIC-7701 ------- Compound Polycoaplex A Field Field Organise Study Location > • IJaanda BSA — llmanda Toxlclty, Active Inqredlent, Ppa 33-101 IT2) Experimental Variables. Control led or Noted Comments Reference renewal) ••(contln- saaa as above Portmann, et uou» aor- el (I97i>, aUon, aea- ANlc-7701 •mtar, and solution renewal) Roceus BSA saxatllls Polrotlc »ta> fetanlua chloride Nltzsehla 8S», linear Is L •otasslua chloride Physa BS», tteterastropha L •otasslua ehroaat* Lepoals BS», las Crl aacrocMrus L Pat ass I ua cttroaate NltzscMa BS« las Cr) llnearls L 1.337 (TSI 940 IT«) ITd) 7.8ITSI a>Ctd ------- Potess'lue; cyanide (•» cyanide) Carclnus BSA — greater than 5 ««(oontln- one hundred-forty surf»e* active IT?) uous. «ar- agents, solvent eaulslflers, pesticides, fctlon, aoa»oolychtorlnated blohenyls, our* water, and Inorganic, and organic chemicals were dally evaluated against as eany as ten aarlne solution organises. The authors noted that aost renewal) published data of this type deal tilth toxlclty of chealeals to freshwater organises. Potassluei Cyanide las cyanide) Crangon crangon BS* — greaterthan 29 a«(contin- uous, aer- ation, sea- water, and dally solution renewal) save as above Porteanrv, at at C1971>,»HIC- 7701 Portaann, at al 7701 •etasslu* cyanide (•• cyanldel Petasslua cyanide Pandelus aontagul Leblstes retleulatus (1 aot 1.1 cat BS« — U2) ecr — 0.26 IT2) liw cyanide Leblstes retleulatus II ao. 1.1 ea) BCF — IT1) a* (contin- uous aer- ation, sea- water, and dally solution renewal) a,c,d,e,f, n,q, phos- phates, carbon- ates, bl- earbon- ates, sul- fktas, and conduc- tance saae as above Portaann, et al (1 ------- Coajoound Field Field Organise* Study Location Toxlclty. active Ingredient, PC* Experimental Variables, Controlled or Noted Comments Reference carbon- ates, bi- earbon- ate», aul- ffttes, and conduc- tance Potassium* dlchroaate Leoomls BSA, fat Cr) macroehlrus L 113 mi Potassium dlehroaato Nltrsehla BS». las Cr) linearIs L Potassium) dlchroeate Ptwsa 85. (as Cr) heterostrettna L •otasslu dlchroaata Phoraldlua L (as Cr) aablquua 0.71 IT5) 17.3 O.S-10.0 (16 p«rcnt growth lanlbitad 14) a,a< and synthetic dilution •atar »«e» and srntnetlc dilution water »',», and synthetic dilution •ater This study Mas conducted to determine the relative toxlcltjes of 20 coon constituents of industrial wastes to a tlsh, an alqa» and an Invertebrate. The exoarlnents Here conducted over a ID-year period for varied purposes The authors reconend bloassays with at least three components of the food neb. saae as above Patrick, at al 11968), »MIC-57?J Patrick, at al C1968), saae as above Of 7<> chemicals evaluated as alqlcldes, only 9 Mere more toxic than CulOI.. Non« Inhibited gronfh of Bat-forming alqae for or* than 2 MeeHs* Cu'SOii formulated with certain wetting agents Mas more toxic than CuSOfc alone. Coeoer chloranlne was also found to be more toxic than Cu>0<>. No netting agents •ere found to be Inhibitory at the concentrations Investigated (0.05 and 0.005 ooml. Also reoorted are factors effecting groxth of al?ae In canals to determine whether there Mere leads to controlling aloae by environmental management. No practical environmental means Mere tound. Patrick, at al tl96«>,AHIC- 57?0 Otto ri?70>. 4HIC-892 •otasstua dIehrornate Brachydanlo BS» — 56-75 (SB) a,e. and Feeding behavior Mas affected by Cairns, at ------- p«rlo •otasslu* ventachloroohenate Oncorhynchus klsuteh (CSE 119 eabryo cells) L —• l.fl-120 (SB10) a* I U> •otatSlu* •ervanganate Trachlnotus carolInus (Juvenile) BS» — 1.6-2.9 «T> Potasslu permanganate •otasslu* »araan«anata BOCCUS saxatllls (fingerIinqs) BSA — Pnoraldlua aablguua 2.5 (TO 0.9-10.0 (16 percent groNth Inhlbltadi) synthetlcd zinc, cnroalue, and »flS In that mart tl«e al 119671• llutlen Has reaulred for consuming Measured AHIC-5707 ••tar aoeunts of food. rdlnq rcsoonse Mas •••so affected by aeration, feeding schedule, light Intensity, and Outside disturbances. The authors note that nuch •ore norfc Is needed to establish the reliability of this procedure. Growth of cultured coho salaon Hanes, et at enbrvo cells on Eanle's HEM was oartlally (1970), Inhibited at ".0 oon. stronqly Inhibited AMIC-3753 at 80 cow, and totally Inhibited at 210 , Dp. The SO percent Inhibitory dose »»s estimated to he 6ft DO". * linear relationship between dose and effect Mas noted, data on cell counts, population volune, dry Melaht, ash, nitrogen, orqanlc acids, and organic natter are renorted. •. None Inhibited growth of •at-fornlng alqie for nore than 2 Meeks. CuSOi. foreiulated xlth certain Netting aqents Mas more toxic than CuSO ------- Comoound "Organism Flald Flald Study Location Toilclty, Experimental Active Variables, Ingredient, Controlled Ppm or Noted Comments Reference •otasslum salt of flk-cnlorotolylt ony-N-metttaxy-acataa Ide Phormldlum aablguum L — •otasslum Mtt of Phormldlua J,3,5-trlctiloro--or amblguua rldlnol Precalne nydrochlorlde Neoeorlon brevlrostrls 11-3 !•«.» BS» — 8.5-10.0 (16 percent growth Inhibited 1%) l.f-lO.O(NTE) II (NTC 1 hr> a.c.e II Caaarus fasclatus m> Fish Inot soeclfledl Mesbors BCF heteroBoraha and BS« greater titan l«-lia IKI 10.1 IT?, hardnater) •,c.e ------- Pretia Rasbora BCFA heteromorpha and BSA l.t (TZ, softiiater) species »»,e.«f» hard (HWI or soft ISWI synthetic dilution Mater, or seaMBter tor some species Pro-Next Ish V/l Pro-Noxf Ish Pro-Noxf Ish PVP-lodlne, Oncorhynehus BSA tshaMytscha (fry) Oncorhvnchus BSA Klsutch • fry) Oncorhvnchus BSA Klsufch (eggs) 1.0 (SB) Mercenarla aercenarla (eggs» t — 0.135 (Tl) 1.7 (Tl» tT.l PVP-tetfln* Harcanarla arcnarla IIarwa«> 3».9 (Till ocstlcldcs H«re aost toxic In hard mt«r and so»etl»es the ooooslte Mas true. Tasting the actual material as sold Has found to be essential. sane as above Alabaster (19691. ANIC-5I.ZS Satmonld eqg embryos nay be able to survive rotenone treatment that kills fish. Toxlclty to the coho embryos was qreater at 53 f than at 39 and «6 F. Fgqs burled In gravel survived better than those at the gravel surface. Further field evaluations Mere reconmended. save as above same as above Garrison (1968), Garrison (1 ------- Compound •yramln Pyrlmithate Qulnaldlne Toxtclty, Experimental •Active Variables, Field Field Ingredient, Controlled 1 Orqanlsm Study Location Pom or Noted "asbora 8CFA — Z8 (T2I a.e,e,f. heteromorpha and bard BSA IHWtor soft (SHI synthetic dilution Mater, or seaMater tor SOB soeclos Fish (not — — • greater than specified) 10-10D (K) e Oasbora BCFA ~ t.l IT?) e.c,etf. heteromorpha and hard (HH) BSA or SOFTISHI synthetic dilution Mater, or seaMater for some species Neqaorlon BSA — a.? (SB 10 e.Cte brevlrostrls MINI (1-3 «q) Comments On hundred sixty-four pesticides* wettlnq aq«ntst and nlsc«1 laneeus nater DO! lutants shooed a old* rar>q* of toxlclty soannln; 1? orders of naqnltude. KnoMlnq the toxlclty and percent»o» of alt co»oon»nts ot a fornulation did not result In easy credlctaolllty of th« toxlclty of a •Ixture of oaterlals* So»»tl«s oestlcldes Mere mo<;t toxic In hard Mater and sonetlnes the ooooslte Mas true. Testing tht actual vaterlal as sold was found to be essential. Approximate toxlcltles of numerous DCS tic Ides commonly used In Britain Mere sunnarlze'l. An excellent brief, qeneral discussion of toxlclty testing Is also oresent. One hundred sixty-four pestlcldest wttlnq aq»nts> and •Iscel laneous Mater ool tutants showed a Mlde r»nqe of toxlclty scanning l? orders of laqnltude. KnoMinq the toxlcity and percentage of all conoonents of a fornul at ion did not result In easy predictability of the toxlcity of a •Ixture of materials. Sonetlnes pesticides Mere most toxic In hard Mater and sovetlnes the ooposlte Mas true. Testing the actual material as sold was found to be essential. Data from study of drug effects on youno, levon sharks Mere treated mathematically to demonstrate Reference Alabaster (14&9I, AMIC-91,2% MaMdesley- Tho«astl971) ANIC-10S6 Alabaster (19691, ANIC-SI.25 Paldrldqe 11969). ANIC-3t32 aoollcabl11ty of classical rate theory to the study of chemical sharK deterrents. Incaoacltatlon '(narcosis) Mas the orlnary parameter timed for effectiveness. This Mas usually quite rapid for the more effective druqs. ftaynap Sol B Cranqon BSA — 3.3-10 (T?) m»(eontln- One hundred-forty surface active Portminn, at ------- RD 1639 Rasbora heteromoroha 0.5» IT2t and BS. Region* Rasbora heteromoroha and BSA 37 (T2, softMater) Reglone Sa I no galrdnerl BCF. and AS* TO er soft (SW) synthetic dilution water, or seaMater for sea* tore Its a>,e,e,t, hard (HW)or soft (SM) synthetic dllutlon •ater, or seaxater for so** species aq«nts, solvent emutslflers, oestlcldes, a! (1971)f 'OOlychlorlnated blphenyls, our* AHIC-7701 Inorqanlo and orqanlc chemicals x«r* evaluated aqalnst as any as ten marine orqanisos. The authors noted that most published data of this type deal xith toxlclty of chenlcals to treshMater orqantsns One hundred sixty—four Alabaster, pesticides, xettlnq aqents. and (1969),»HIC- »lsc»l lancous Hater pollutants showed a 5<>?S Hide range of toxlcltv soannlnq 12 orders of naqnltude. Xnowlnq the toxlcltv and percentage of all conoonents of a formulation did not result In easy predictability of the toxlclty of a •Ixture of Materials. Sonetlnes pesticides were nost toxic in hard Mater and sovetlmes the ooooslte «as true. Testlno the actual naterinl as sold Mas found to b* essenfl). a,c,e,f, hard (HH) or soft (SMIsyntne tic dilution Mater, or seaxater for soe species a,c,e,f, hard (HW) or SOFT(SW) One hundred sixty-tour pesticides, itettlnq aqents, and •Iscellaneous oater pollutants shoMed a MMe range of toxlclty spanning 12 orders of magnitude. Knoxlnq the toxieity and percentage of alI comoonents of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Soaetlnes pesticides Mere «ost toxic in hard Mater and sometimes the opposite Mas true. Testing the actual «aferial as sold was found to be essential. same as above Alabaster (1969), Alabaster (1969), AMIC-5MS cane as above Alabaster (1969), AH.IC-5?? ------- Coapound Field ri«ld Organise Study Location Tonlelty, •Active Ingredient, Pp« Experimental Variables, Control lad or Noted Comments Reference KhDdaalne A Salao galrdnerl BS» Rhodaalne B Rhodaeln B RIdzlIK let Blur us punetatus 8S» Leooals BS« •acroehlrus Crangon cr angon BS« — $?6 ITU 379 IT»I 330-1000 (T?> synthetic dilution •ater, or seaxater tor so»e species The dyes Rhodamlne B and Harking Fluoresceln sodlu* Mere found to be Relatively non-toxic In ppe concentrations while antlaycln Has toxic at pob levels. The author states that neither dye at field us* concentrations should significantly Influence the activity of Antlnycin A against fish. Harking «1969), 1MIC-5TZS Harking (19f.9)t »HIC-57?g Portoann, et at (1971), »HIC-7701 Roccal Hercenaria •ercenarla 0.19 ITZ) sane as above as above ••(oontln- One hundred-forty surface active uous aer- agents, solvent enulslflrs, pesticides, atlon, sea-Polvchlorlneted blohenyis, pure water, and Inorganic, and organic chemicals were dally evaluated against as many as ten arlna solution organlsns. The authors noted that eost renewal) published data of this tvoe deal with toxlclty of cheelcals to freshwater organises. The effect of 9? pesticides on Oavls, et at enbryonlc developnont of clams and oysters «as reported. Synergistlc 11969),»MIC- eff»cts with solvents were also reported. 5990 nost of the compounds affected dev«loc»ent More than survival. So*, however, drastically reduced larval growth. The authors ooint out the necessity of evaluating the effects of pesticides on all life stages of an organise and note the possibility of selecting chealcals tor pest control that ------- Roccal Rola, OSO "ercenarli •ercenerli (larvae) Cranqon crangon I •• BSA ~ 0.1% UK 3.3-10 (TO HOuld not haw« serious effect on shellfish. same as above Rosin (ulna 01 acetate Phormldlum amblguum 0.5-10.0 (NTE) Rosin Ain 0 Crassostrea vlrglnlca lets than 0.25 Rosin Amlne 0 Crassostrea vlrglnlca L — less thanO.«?5 ITlM Davis, ct al (1969>,A1IC- 5990 »(contin- One hundred-forty surface active Portmann, et uous aer- agents, solvent emutslfiers, pesticides, at atlon, sea-P°l'chlorinated Mohenyls, cure (19^11 ,»HIC- water, and l"orq»nlc, and orqanlc ch»»lcals were 7701 dally evaluated aqalnst as •ony as ten »ar\|ne solution orqanlsns. T^« authors noted that Host renewal) published data of this tyo deal Kith toxlclty of chemicals to freshwater orqanisi»s. Of 71. chemicals evaluated as Otto (19701, alqlcldes, only 9 Here more toxic than AHIC-892 CuSOii. None Inhibited growth of rat-for»lnq aliae for more than 7 MeeHs. Cu^0>> formulated with certain Mettlnq a9ents »as «or« toxic than CuSQ<» alone. Coooer chlorairlne as also found to be •ore toxic than CuSOU. No wetting aqents were tourd to be Inhibitory at the concentrations Investigated (0.05 and 0.405 cpr). Also reoorted are factors effecting growth of alqae In canals to determine whether there Here leads to controlling atqae by environmental •anaqerent. No practical environmental means Here found. -- The effect of 5? oestlcldes on Oavls< etal embryonic development of clams and (1969), oysters Has reported. Synerqlstic AMIC-5990 effects with solvents were also reported. Host of the comoounds affected develocment more than survival. Some, however, drastically reduced larval qroxth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stages of an orqanlsm and note the possibility of selecting chemicals for pest control that Mould not have serious effect on shellfish. same s above Davis,et al (19691. ------- Compound Orients* Field FUld Study Location •Toxlclty, Active Ingredient, Pom Experimental Variables, Controlled or Noted Comments Bel erenee «otenon* It o tenon* o-n«et (larva) Sal no gelrdnerl Lepovls mecrochlrus Gamaarus fasclatus 8S* — 0.057 (TO (TO 2.6 IT) R-Wti Gamearus fasclatus 8SA ~ 15.0 (TO Salicylic acid (2-hydroxybniolc aeldl Phoraldlum aablguua 0.9-10.0 (NTE) — AMIC-5990 The pisclcldes Antlmyeln » and HoMland Rotenone nere found to b« co»oa»lbl» when I19ft<»>« alx«4 and furthermore aopeared to have an AHIC-5T2V additive effect in cbln»tlon. That Is both conpounds Here ore toxic In the presence of the other than alone. sane a« above Of the aquatic weed herbicides evaluated. Die Ion* Mas the nost toxic, Daohnla MBS oenerally the rost sensitive orqanlsn. Alt of the. Crustacea Mere affected by much lexer concentration levels of herhlcMes than Indicated by the TL sub 5Q values. All of the anlaats reoresent Imnortant food chain links. Of the aquatic weed herbicides evaluated, Dlclone Mas the nost toxic, Oaohrila xas qenerallv the most sensitive orqanlsn. All of the Crustacea Mere affected by nuch IOMCT concentration levels of herbicides than Indicated by the TL sub 90 values. All of the animals represent inoortant food chain links. Of 7 ------- means were found. Seas Deep SeesMeep S«foll Steel head trout (fIngerlInqs) Coho salmon BSA. IfIngerlIngs) In •Itu 20.2 CTO Hood Canal, Hood sport, Wash. Agonus cataohractus BS» — 1.5 W 1001-3300 CT2) Evaluation of 11 oil dlspersants Tracy, at al resulted In a ranking for each and a recommendation tor us* according to the (1969),AHIC- ranklng. Ranking Mas based on toxlclty •nd oil dlsoersal effectiveness. Corexlt 776fc acocared to have the least toxlclty xlth fair to good oil dispersion eaoablllty. Safe 11 Cranqon crangon BS» 1000-3301 ITt) •ana aa abora a«lcontln- one hundred-forty surface active uoua aor- agents, solvent eeulslflersi oestlcldes, atlon, aaa-oolvchlorInated blonenyls< pure water, and Inorganic, and organic cherlcals were dally evaluated against as «any as ten arlna solution organisns. The authors noted that lost renewal) oubllshed data of this tyoe deal with toxlclty of cheoleals to freshHater organises. a(eontln- saae as above uoua, aer- ation, sea- water, and dally solution renewal) et al Tracy, (1969). AKIC-363U Port»»nn, at al (1971), •MJC-7701 Porteann, at al (1971). ANIC-7701 Selenlua dioxide Caraislus auratus 12 «T7I Coregonus clupeaforals Hoose Lake, Can. 0.2 (relltlon to toxlclty data. Heir, at al conditioned avoidance resoonse xas (1970), studied at sublethal concentrations. The AHIC-739 lOHest concentration of netal resulting In significant Inealrnent Mast arsenic, 0.101 lead. 0.071 mercury, 0.003! and selenium, 0.25. Deleterious effects occurred at aetal concentrations aporoxlnately slallar to potable Mater standards. Concentrations of 13 toxic elements In dressed fish from heavily Industrialized and non-Industrialized areas Mere determined. Only mercury exceeded regulatory Halts, and concentrations of most elements were essentially the same in fish free both Uthe, etal (1971), •NIC-3S19 ------- 3 to Coaoound Selenlu* Selanlu* Selenlua Selenlua Selenlua Selenlua Sesaaex Sesanex Sesaaex Savin Organise. Coregonus cluoeaforels Esox tMclus Esox luclus Esox luclus Os«erus aordax Perca f lavescens Notenlaonus chrysoleucas Leooals eyanellus Leooals aeerochlrus Field Field Study Location FL Lake Ontario, Can. FL Moose Lake, Can. FL Lake St. Pierre. Can. FL Lake Erl. Can. FL Lake Erie. Can. FL Laic Erl, Can. L — L •"•• L — toxlclty. Active tnoredient. PM O.t (residue) O.t (residual • . (residue) » 0.2 (residue) B.Z (residue) 0.3 (residue) ? (NTE 1) t (NTE 1) ^ (NTE t) ExBerlaental Variables, Controlled or Noted Coaaents areas. — - saae as above saae as above saae as above — • saae as above saae as above — saae as above — Fish brain AChE activity MBS not affected by Sesanex alone but Has significantly Inhibited by oarathlon. Pretreataent with Sesaeex at 2 pan resulted In decreased Inhibition of AChe activity by oaratnlon. -- saae as above saae as above Reference Uthe, etal (19711. AHIC-3819 Uthe. et al (1971), AHIC- Uthe, et al (1971), AMIC- 3819 Uthe, et al (1971),A1IC- 3819 Uthe. et al (1971), AHIC- 3819 Uthe, et al 3819 Gibson, «t al (19711, AHI 3799 Gibson, et at <1<»711, A1IC-3799 Gibson, et 81(1971), AMIC-3799 Puntlus tlcto — 3.7 (TM a,c.d,e,f Of the pesticides Investigated, Bhatla the aost toxic MBS Ktofos tot toned In (19711, decreasing order by Sumlthlon, Halathion, AMIC-S".?J Foralthlon, Olaecron. Sevln. and BHC. The •uthor cites the. need for aore selective ------- S«vin asbora BCT» heteroorpha end BSA a,c,e,f, hard IHM) or soft ISM1 synthetic dilution Hater, or seanater tor SOM species Svvln •alae>on«tes kadlafcensts freslstant) ITU 0) Sovln S«»ln Palaeaonet* BSA — fcadlakmsls roalatant) Tublfex tub I fax Belzonl, HISS. 1.019 (Til l.M (NTCI — as pesticide* nontoxlc to fish or antagonistic agents for reducing fish tonlclty. Oo« hundred slxtr-»our 0stlcldSt wettlnq aqnts, »nd •lccl 1»noos KBter ool tutant? s^OMOd a Mlde ranoe ot toxlclty soannlnq 1? orders of "aqrliud. Knonlnq tn* toxlclty and prcent»q» of all cooeonvnts of a fornulatlon did not result In easy predictability of the toxlclty of a Mixture of «aterlsl. So«etl««s pesticides Here no^t toxic In hard Hater and voaetlaes the oooo^lte was true. Testing the actual Material as sold Has found to be essential. »lob«sto CUM). Naavl. at al Bloastays Here conducted with shrlap tron three areas of Intensive pesticide use and fro* an unexoased area. iMIC-5519 Previously exposed snrl«o Mere fro* t to ?•! tines »ore resistant than unexposed shrlvp. Both types of shrlap Here also exoosed In caqes to Maters ot the contaminated areas. Susceotlble shrlap suffered 6f> percent more norfality than did resistant shrimp. The toxlclty of the Insecticides ranked In descending order Mas as follOHsS Most toxic, Endrin, DOT, Methyl oarathlon, Parathlonl aedlue, toxlclty, Cuthlon, Llndane, Toxaohene, Strobanel lease toxic Chlordano, Savin, and Heptachlor. sa»e as above Naovl, (1970), •HIC-5S19 et al Th« response of pesticide-resistant aquatic organises to various pesticides Mas coloured to the response ot non-resistant species. Pesticide-resistant soecles Mere coflected at ftetzonl and non-resistant species at State Colleqe. Copeoods, elans, snails, and sludqe «ori.s fron Belzonl Her* considerably More tolerant to pesticides than the non-resistant organisms. The authors note that the affect of Increased tolerance In the erqanlsas Is an Increase In the aaount of pesticide residues available To anlaals of higher trophic levels. Haavl, et all1969), •NIC-5979 ------- Compound Sevln Field Field Organism Study Location Mercenarla L — •ercenaria (eggs) Toxlcity, Active Ingredient, PD» 3.« IT2) Experimental Variables, Control led or Noted Comments -- The effect ot embryonic development oysters Mas reported. ?? pesticides on of clans and Synerglstlc Reference Davis, et at t.l9&9>.«MIC- u> Sevln Sevln Sevln Serin Shamash R1885 Shaaasti R18S5 Mercensria mercenarla (I arvafO Crassostres vlrglnlca (eqqs) Crassostre* vlrglnlca (larvae! Wolffla papulifar* Crsngon cranqon greater than 8S* — 3 CTZI 3 ITHI 1000 (K) 3.3-10 It21 Panda I us •ontaqul BS» 1.0-3.1 (TZ) effects with solvents Mere also reoorted. S990 Host of the conoounds affected development more than survival. Sooet however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of oestlcldes on all life stages of an orqanls* and note the possibility of selecting chemicals for pest control that Mould not have serious effect on shellfish. same as above same as above same as above Davis, et al(19691. &HIC-5990 Davis, et al (19A9I. »MIC-599I> Davlsi et al (1969).»1IC- 5990 Hunter1 a .•nodlum diluted 1:5 «,»( contin- uous aer- ation, sea- water, and dally solution renewal) a«t( contin- uous, a or- ation, sea- water, and dally solution renewal) All compounds uere harraful to duckweed to nomo decree. Decreased populations woro noted at non-lethnl concentrations and some compound3 (Kalathlon and t-,^-I>) caused terotogenlc oTfocts at concentrations as low as 1 ppn. Worthley, et al (1971), AMIC-3233 One hundred-forty surface active Portmann, et agents, solvent emutslfiers. oestlcides, polychlorlnated biohenyls, pure inorganic, and organic chemicals Mere evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal Mlth toxlcity ot chemicals to freshwater organisms. sane as above it (1971), AMIC-7701 Portnann, et al (19711. »MIC-7701 ------- Shell 0-90 Sal no galrdnerl BCF» and BS» 105 (T21 a',e,,f, One hundred sixty-four Alabaster hard pesticides, wetting agents, and (1969). (HH)or miscellaneous water pollutants shotted a ANIC-525 soft (SHI "Me rang« of toxlclty scanning 12 orders synthetic of magnitude. Knowing the toxiclty and dilution percentage of at I comoonents of a Mater, or formulation did not result In easy seawater predictability of the toxlclty of » for some mixture of materials. Sometimes soecles pesticides were mast toxic In hard Hater and sometimes the ooooslte was true. Testing the actual material as sold was found to be essential. Silver •• thane-arsenate Phormldlu* amblguum 0.5-10.0 (16 percent growth lnhlblt«dl<>) vn SiIver Paralabrax clathratus F« Scattergood 0 (ventral Steao Plantt euscle Los Angeles, residue) Cat. Otto (1970>» AHIC-89? Of 71. chemicals evaluated as algiclties, only 9 Here more toxic than CuSOit. None Inhibited growth of mat-forming algae for more than 2 xeeks. CuSlit formulated with certain wetting agents was more toxic than CuSOfc alone. Coooer chloranlne was also found to be more toxic than CuSOi». No wetting agents were found to be Inhibitory at the concentrations investigated (0.05 and 0.005 com). «lso reoorted are factors affecting growth of algae in canals to determine whether there were leads to controlling algae by environmental Management. No practical envlronaentat •cans were found. Fish collected from an effluent Staoleton pioe of a steam olanf and from offshore (196(1! waters of Catallna Island were analyzed AMIC-598B for trace element content. Trace element content of the effluent water was at least 5 times oreater than that of normal sea water for cadmium, cooper, nickel. zinc, and chromium. Livers of fish fro* the effluent were nearly twice the size of those from the ocean. Greatest differences In concentration occurred with alurinum, cadmium, and nicKel. Silver, barium, lithium, and lead showed the least differences. The author concluded that trace element analysis of tissues could be used to determine the effect of pollutants on marine organises. ------- Coeoound Silver Stiver Silver Silver Silver SI Iver Stiver Silver Silver Sliver Orqanlsa Paral abrax clathratus Par»lat>r»« clathratus Paral brax clathratus Paral abrax clathratus Paral abrax cl athratus Paral abrax clathratus Paral abrax clathratus Par at abrax Clathratus (qravld te»alesl Paral abrax clathratus Paral abrax clathratus Field Study FM FH FH FN FM FM FN FM FM FH toxlelty. Experimental Active Variables, Field Ingredient, Controlled Location PO or Noted Comments Scatterqood 0.06 Iheart — saae as above Stea* Plant, residue) Los Anqeles, Cat. Catal Ina 0.16 — saoe as above Island. Cal. Iheart residue) Scatterqood 0.01 (eyeball — sane as above Staa Plant, residual Los Angeles, Cal. Catal tna O.OZ — saae as above Island, Cal. « eyeball res I duel Catal In» 0.04 (ventral ~ s»«e as above Island, Cal. auscle residue) Scatterqood 0 (qonad — saae as above Stean Plant, residue) Los Anqeles, Cat. Catal ins O.W? — s»»e as above Island, Cal. (oonad realdue) Catal ina O.lZaonad ~ saae as above Island, Cat. residue) Scatterqood 0 (liver — saae as above Steaa Plant, residue) Los Anqeles, Cal. Catal Ina 8.03 — saae as above Island, Cal (liver realdue) Reference Staoleton •196B), AMIC-59V) Staoleton (19S8), AMIC-S9SO Staol eton (1968), AMIC-S980 Staoleton (19681, AMIC-99BO Staoleton (1968), »MIC-5980 Staot eton (1968), AHIC-S980 Staoleton (1968), 1MIC-59SO Staolvton (1968), AMIC-S980 Staoleton (1968), AMIC-5980 Staoleton (1968), ANIC-5980 ------- Sliver Paratabrax FM Seatterqood O.ZZ clathratus Stea» Plant, (Intequnent Los Anqelcst residue) Cat. sane as above Staoteton (19fiB>, AMIC-5980 Silver Sllvex IBEEI I Sllvex (BEE) Sllvex IBEEI Sllvex IBEE) Sllvex (BEEI Sllvex (BEEI SI Ivex (BEEI Sllvex IPGBEI Sllvex IPCBEI Paralabrax FN CatalIna 0.1Z clathratus Island, Cat. (Intequnent residue) san« as above Staoleton Ganaarus faselatus BS» — 0.71, (TZ), O.ZS a» Paleonontes BS» kadlahenils 8S» brevicau'lus Orconectes BS* nals Oaphnla aaqna BS* CyprldoDSts BS* vldua Leoonls BSA •acroehlrus Gamnarus BS* fasclatus Paleonontes BS* kadlakensls 8.0 (TZ) ".0.0 (TZ) 60.t (T2> 2.1 (T2I .9 (TZI 70.0 (TZI 1.0 (TZ), 0.8 a* (TW) 3.Z ITZ) Of the aauatlc Heed herbicides evaluated, Oletone »»s the ost toxic, Oaohnia Mas generally the nost sensitive orqanisa. All ol the Crustacea were affected by auch loner concentration levels of herbicides than indicated by the TL sub SO values. All of the animals represent Inoortant food chain links. sane as above AMIC-S980 Sanders (1970), sane as above saae as above saee as above saae as above sane as above saae as above saae as above Sanders (1970), AMTC-fcSS Sanders (19701 , MIC-fcS3 Sanders (1970), AMTC-<.S3 Sanders (19701, MIC-<.53 Sanders (1970), ANIC-1.53 Sanders (1970), Sanders (1970) ,«MIC- 1.53 Sanders (1970), 4MIC-V53 ------- SI I vex (PG8E) Field Field Organism Study Location As11 us BSA — brevleaudus Orconectes BSA — nets •Toxlclty, Active Ingredient, Ppa o.s m> Experimental Variables, Control led or Noted Comments a* sane as above Reference Sanders (1970), qreater than 100.0 (T2! saae as above Sanders Sllvex (PG8E> Silvex (PGBE) Sllvex CPG8EI Silvex Sllvex Slnzlne Oaphnla aagna BSA Cyprldopsls BSA vldua leoonls BS» — •acroehirus Crassostrea L — vlrglnlca 0.16 IT2> 0.20 (T2) 16.6 (T2> $.9 (T2) Crassostrea L vlrglnlca (larvae) Fish (not specified! 0.7 (Tit) qreater than 10-100 IKI sa«e as above saae as above sane as above Senders (1970 Sanders (1970). Af1IC-«.S3 Sanders (1970), AHIC-493 The effect of 5? pesticides on Davis, et al embryonic develoonent of clans and (1969), oyst«r« was reported. Synerqlstlc AHIC-5990 effects with solvents Nere also reported. Most of the compounds affected develocment acre than survival. Some, honevert drastically reduced larval qroMth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that would not have serious effect on shellfish. same as above Approximate toxlcitles of numerous pesticides commonly used In Rrltalr Here summarized. An excellent brief, general discussion of toxlclty testing Is also present. Davis, et al (1969),ANIC- 5990 MantSesley- Th omas 119711, »«1IC- 1056 Slmazlne Sal mo 8CFA — 1.3 (T?) a'.c.e.f. One hundred sixty-four Alabaster ------- gairdnerl and BSft SlMazln* Sal MO galrdnerl BCF» •nd BS» (Til SlMazlne SlMazlne Roccus saxatllls (tInqerlinqs) BSA Carclnus Maenas BS» — 0.25 (TO qreater than 100 ITZI SlMazlne CardluM edule BSA — greater than 100 (TZ) hard (HMI or soft (SM) synthetic dilution Mater, or seaxater for soae species pesticides, wetflnq aqents, and (19691, Mlscel laneous Mater oollutants showed a (HIC-S<>?5 «Me rjnq« of toxlclfy scanning 12 orders of naanitude. Knonlnq the toxlcltv and percentage of all coxoonents of a formulation did not result in easy predictability of the toxlclty of a Mixture of Materials. Soaetlnes pesticides were most toxic In hard xater and sometimes the opposite Mas true. Testing the actual naterlal as sold Has found to ba essential. sa«e as above alabaster (1969», s'»c.ett, hard(HN) or soft (SMI synthetic dilution Mater, or seaMBter for soae species a,c,d,a,f Strloed bass f Inqerllnqs Mere Wellborn ,p and apoarently ouch More sensitive to (1969), iron theraoeutlc and herblcldat compounds than «MIC-5723 •any freshwater fish. »(contln- One hundred-forty surface active UOUs »«r- ,aqnts, solvent enuls1flers, pesticides, »tlon, sea-oo'vchlorlnated biohenyts, pure water, and inorganic, and organic chemicals Mere daily evaluated against as "any as ten Marine solution organisms. The authors noted that Most renewal) published data of this type deal with toxlcity of chemicals to freshwater organISMS no(contin- sMe as above uous, aer- ation, gea. water, and dally solution renewal) Portaann, et at (1971>, mc-rroi Portaann, at al (19711, ANIC-7701 SI mine Crangon BS» crangon qraatar than 100 (TZ) «»(contin- uous, aer- ation, sea. water, and dally solution renewal) s»Me as above PortMann, at al (1971), MIC-7701 ------- Coapound Orqanlsn Field Field Study Location Toxiclty. Active Ingredient, Pp. Expert nentat Variables. Control led or Noted Comments Reference SlMZlne Gannarus fasclatus BS* — qreater than 100.0 (TZ> SlMZlne > SiMZlne I SlMZlne SlMZlne SlMZlne SlMZlne SIlcKaone 1 Paleonontes BS* kadlaKensls Asellus BSA brevlcaudus Orconectes BSA nals Daehnla aaqna BSA Cyprldopsls BSA vldua Lepouls BSA •acroehlrus Carclnus Men as BSA — qreater than 180.0 (T2> qreater than 100.0 (T?) qreater than 100.0 IT?) 1.0 CT21 3.2 CT?> greater than 100.0 IT?) 33-100 «TZ> Of the aquatic Heed herbicides evaluated, Olclone «as the most toxic. Oaohnia Has generally the nest sensitive organism. All of the Crustacea were affected by much loner concentration levels of herbicides than indicated by the TL sub 50 values. All of the aniaals represent laoortant food chain links. saae as above Sanders (19701. ANIC-fcfS &»( contin- uous aer- ation, see- water, and dally solution renewal) sane as above sane as above sane as above sane as above sane as above One hundred-forty surface active aqentst solvent enutsiflers, pesticides. polvch lorinateef blohenyls. Dure Inorganic, and organic cherlcals Here evaluated aqalnst as nany as ten varlne organises. The authors noted that «ost published data of this type deal with toxlclty of chemicals to freshwater organises. Sanders (19701, AHIC- <>53 Sanders I1970),ANIC- <.SJ Sanders <>SJ Sanders (1970), AHIC-453 Sanders (1970», A1IC-ii53 Sanders (1970) , AHIC- ".53 Portnann, at al (1971), AMIC-7701 Sllckgon* 1 Cardlua edule BSA — 33 (Tz> a«(contln- saae as above Portaann, at ------- Sllcfcaon* l Crangon cranqon BSa 3.3-10 (T?» Sllckaone t Pan«aIus •ontaoul BS» 3.3-18 (T2I Sllchgone z Carclnus eaenas H-3S (T2I Sllekgone Cardlua «dul« BS» — J.S CT2I uous, aer- ation, aaa vater, and dally aolutlon renewal) *(contin- uous aer- ation, sea- water, and dally solution renewal) a(contin- uous aer- ation, sea. water, and daily solution renewal) a«(contin- uous, aer- ation, sea. water, and daily aolutlon renewal) a«( contin- uous aer- ation, sea- water, and daily solution renewal) »•• as above ••• as above aae as above saae as above »l (19711. HIC-7701 Portnann, «r »l CI^TD, MJC-7701 Porteann, et »i riqrn, •MIC-7701 Portnann, et al C19TH, »HIC-7701 PoPtuson, et af J197H, »MtC-7701 Sllekgone crangon 8S» 3.3-10 a»(contin- uous aer- ation, sea. water, and dally aolutlon renewal) seee as above Portnann, et »l (1971), »HIC-770t ------- Compound Field Field Organise Study Location Toxlctty, Active Ingredient, Ppa Experimental Variables, Control led or Noted Comments Reference Sllefcgone PandaI us BSA — aontaqut 3.3-10 ITZt renewal) «»(contin- uous aer- ation, sea- water, and. dally solution renewal) same as above Portmann. et al (19711. AHIC-7701 SI l> Rasbora BCFA. — heterovorpha and BSA 8.3 ITZI Carelnus •aenas BSA — 19 m> SIlK Cardlua edule BSA — 33 (T2I e,c»e.f, hard (HU)or soft (SH> synthetic dilution Mater, or seaiiater for son* species a«(eontin- uous aer- atlon, sea vater, and One hundred sixty-four pesticides, wetting aq«nts< and solution renewal) ton renewal) Alabaster 119691. «Isc»1 lanous Hater DOllutnnts shoHed a MIC-5«»?S Mld« range of toxlelty soannlnq I! orders of magnitude. KnoHlnq the toxlcity and Dercentaqe of all comoonents of a formulation did not result In easy or«rtlctabl 1 1 tv of the toxlcity of a nlxture of materials. Sometimes oestlcldrs Here most toxic In hard water •and sovet lines the ooposltr »ss true. Testlno the actual material as sold was found to be essential. One hundred-forty surface active Portaann, et aqents. solvent eaulslflers. pesticides, al (19711. Polyehlorlnated blonenyls. oure . AMIC-77B1 Inorqanlc. and orqanle chetlcals Mere evaluated against as aany as ten marine organisms* The authors noted that aost published data of this type deal with toxlcity of chemicals to freshwater organises* ae(contin- uous aer- ation, sea- watar, and dally solution .'renewal) same as above Portmann. et al (19711. AMIC-7701 SIlK Crangon crangon BS* — 100-330 (TZI a* (contin- uous, aer- ation, sea. water, and daily see* as above Portaann. et al (1971). AMIC-7701 ------- •olutlon ronaual) SI I* Os tree edulls BSA — 101 ITZI «( contin- uous, aer- ation, aea- wator, and dally •olutlon renewal) saae • above Porteann. at al 11971). AHIC-7701 Sill Randalus aontagul BSA 10-33 ITZ) U> Snowdrift SC90 Crangon crane; on BSA ~ 330-1100 IT) a(contin- saae a* above Portaann, at uoua,aer- al I197H. atlon, >0a> ntc-77ti vatar, and dally aolutlon renewal) a(eontin— One hundrcd-Torty surface active Port«»nn, «t UOUa aer- aq«nts> solvent eeulslflers, oestlcldest al 11971). atlon, B««.Dolych1orln»ted blohenyls, pure ANIC-7701 water, and Inorianlo and organic cheolcsls Mere dally evaluated against as many as ten aarlne •Olutlon orqanlsns. The authors noted that eost r«newil) published data of this type deal xlth toxlclty of ch«elcals to freshwater orqinlsas. Sodlua arsenate Carass1us auratus CT7» a.c In addition to toxlclty data. Weir, et al conditioned avoidance resoons* »as 119701,»HIC- studieo at sublethal concentrations. The 739 lOHest concentration of netal resulting In significant lapairoent was? arsenic, B.10I lead, 0.07t Mercury, fl.OIJt and selenium, 0.25. Deleterious effects occurred at aetal concentrations aoaroxlaately slallar to potable water standards. bicarbonate leooals •acrochlrus BSA. L 0.600 tT«) a.e, and synthetic dilution water This study Has conducted to deternine the relative toxlcltles of 79 coeeon constituents of Industrial wastes to a fish, an alga, and an Invertebrate, The experiments were conducted over a 10-year period for varied purposes. The authors recoeeend bloassays with at least Patrick, at al 119661. AHIC-S7ZO ------- Compound Organise Field Field Study Loot Ion Toxlclty. Active Ingredient, POM Experimental Variables, Control led or Noted Comments Reference Sodium bicarbonate Nltzschla BS», linear Is L Sodium carbonate lepomis BS», maerochlrus L Sodium carbonate Nltzschla BSA, linear is L Sodium cM orate Rasbora BCFA heteronorpha and as 650 (T5) 320 (TO 22 (T9) S600 Ul) Sodium chloride Leoomls BS1, •acrochlrus L t?,9«.6 mi Sodium chloride Nltzschla BSA, linearis L (T5> »',«, and synthetic dilution Mater a,e, and synthetic dilution • ater »•,«, and synthetic dilution •»t»r hard IHH) or soft (SMI synthetic dilution Mater, or seaMater for SODC soecles a,e, and synthetic dilution Mater a,e, and synthetic dilution water three eonoonents of th» food neb. sane as above sane as above sane as above Patrick, et al (19681, AMIC-S7?0 Patrick, et • I (1968), AMIC-S728 Patrick, et al (1968), AMIC-S7ZO One hundred sixty-four Alabaster o««tlcldes> netting aqrnts, and (1969), •Iscellaneous Hater pollutants showed a AHIC-9VZ9 MMe ranoe of toxlclty scanning 12 orders of magnitude. Knowing the toxlclty and Dercentaae of all conoonents of a formulation did not result In easy predictability of the toxlcity of a Mixture of materials. Sometimes pesticides Mere most toxic in hard Mater and sometlnes the ooooslte Mas true. Testing the actual Material as sold was found to be essential. This study Mas conducted to determine the relative toxlcltles of 20 common constituents of Industrial Hastes to a fish, an alga, and an invertebrate. The experiments Here conducted over a 10-year period for varied purposes. The authors recommend bloassays Mlth at least three components of the food web, same as above Patrick, et a I (196B), ANIC-5720 Patrick, «t al (1968), ANIC-S720 Sodium chloride Agonus BSA — ,000-33,DOO a(contln- One hundred-forty surface active Portmann.et ------- cataphractus «T2I Sodlwe chlorl«l« Carclnus aaenas BS» — Sodlua chloride Cardlua edule BS — 11,000-16,900 ITZJ 66,001 (TZ) VJI uoua aer— agents, solvent e>ulslflers, pesticides, atlon, aea-polychlorlnated blphenyls, our* water, and Inorganic, and organic chenicats Mere dally evaluated against as nany as ten Marine solution organises. The authors noted that aost renewal) published data of this type deal with toxlelty of chemicals to freshwater organises. a«(contin- sa»e as above uoua aer- ation, sea. water, and daily solution renewal) • a(contin- uous aer- ation, sea. water, and dally solution renewal) a I (19711, »MT.C-7701 saee as above Portaann, et el (1971), •NIC-7701 Portnann, et el I1471I. •HIC-7701 Sodlue chloride Crangon crangon BS» 16,900-33,000 (T2) a«(contin- uous aer- ation, sea. water, and dally solution renewal) sa»e as above Portnann, et at(197i), •NIC-7701 •Sodlue cyanide Negaprlon brevlrostrls (1-3 lull BS» — 6.6 (S810 aln) a.c.e Sodiu flueracetate Salao galrdnerl BCF» and as* 980 ITZ) a»,c,,f, hard (HH) or soft (SH) synthetic dilution Data (roe study of drug effects Baldrldge on young l«ion sharks Mere treated (1969), •athenatlcat ly to d««onstrate AHIC-3832 • pot Icabl 1 1 ty of classical rate theory to the study of cheolcal shark deterrents. Incaoacltatlon (narcosis) MBS the prlnary paraneter tlned for effectiveness. This •as usually quite raold for the aore effective drugs. One hundred sixty-four pesticides. Netting agents, and •Iscel laneous vater pollutants showed a Mlde range of toxlelty spanning 12 orders Of naqnltude. Knowing the toxlelty and percentage of all components of a Alabaster (1969). AMIC- •star, or foraulatlon did not result In easy ------- Field Field Corn-pound Organism Study Location Sodium fluoride Crangon BSA — cr angon Sodium hydroxide Agonus BSA cataohraetus Sodium hydroxide Cardlum edule RSA -- Sodlun hydroxide Crangon BSA — er angon Toxlclty, Cxoerimental Active Variables. Ingredient. Controlled Pom or Noted Comments seawater predictability of the toxlclty of a for so«e mixture of materials. Sometimes species oestlcides were most toxic In hard water and sometimes the oooosite was true. Testing the actual material as sold was found to be essential. greater than a»(contln- One hundred-forty surface active 300 (TZ) uous, eor- agents, solvent emulslflers. oestlcldes, atlon, sea. uolych lorlnated biphenyls, Dure uator, and inorganic, and organic chefricals were dally evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlclty of chemicals to freshwater organisms 33-100 (T?) a«(contln- same as above uous, aer- ation, sea- water, and dally solution renewal ) 330-1000 (T?) ao(eontln- same as above uous, aer- ation, sea- water, and dally solution renewal) 33-100 (TZI a»(contin- same as above uous aer- ation, sea- water, and dally solution renewal) Reference Portmann, etal (19711, AMIC-7701 Portmann, al (19711, AMIC-7701 Portmann, al (1971), AMIC-7701 Portmann, al (1971) , AMIC-7701 et et i et > Sedlun eolybdate Salmo qalrdnerl FL Castle Lake. 3.S Ib per A Cal. INTEI Molybdenum- fertilization resulted Cordon, et In greater standing crops of zooplankton al (1970). ------- Sodium molybdate Sodium nltrlt SalvelInus FL fontlnatis Rasbora BCFA heteromoroha and BSA Castle Laket 3»' "> Dtr A Cal. (NTE) 210 CT2I and bottom fauna and apparently In Increased yields of rainbOH and eastern brook trout. Mitigating factors nay have Influenced the results. A second experimental fertilization Has Initiated. same as above AHIC-5750 Cordon, et al (1970). AMIC-57SO Sodium N-methyldlthlo Phormldlum »«blguu« • ' ^— 0.5-10.0tNTE) Sodium pentachloroohenate Sal mo galrdnerl BCF» and BSA 9.19 (T3I atC<«tfi One hundred sixty-four Alabaster hard (HW1 pesticides! wetting agents, and (1969), or soft miscellaneous water pollutants showed a ANIC-5V2S CSH) wide range of toxlclty spanning 12 orders synthetic of waqnltude. Knowing the toxlclty and dilution percentage of all components of a water, or fornulat Ion did not result in easy seswater predictability of the toxlclty of a forsome mixture of materials. Sometimes species pesticides were most toxic In hard water and sometimes the ooooslte was true. Testlno the actual material as sold was found to be essential. Of 71, chemicals evaluated as Otto (1970)< alglcides* only 9 were more toxic than AMIC-892 Cu'tOU. None Inhibited growth of mat-formlnq algae for more than 2 weeks. CuSO", formulated with certain netting agents was more toxic than CuSO* alone. Copper chtoramlne was also found to be more toxic than CuSTt. No wetting agents were found to be Inhibitory »t the concentrations Investigated (0.05 and 0.00? oo wide range of toxlclty spanning 12 orders synthetic of magnitude. Knowing the toxlcity and dilution percentage of all components of a water, or formulation did not result In easy seawater predictability of the toxlclty of a for some mixture of materials. Sometimes species pesticides were most toxic In hard water and sometimes the opposite was true. ------- Compound Organise? Field Field Study Location ToxicIty, Active Ingredient* ppm ExperimentI Variables. Controlled or Noted Comments Reference Sodlue Phormldiu L — pentechlorophenate aablguua 0.5-10.0 INTEI — OQ Sodlua pyrldlne-N-oxide Sodium sulfate Phormldlua amblguum Lapoals aaeroehlrus a mm BS», L O.S-10.0 INTE) 13.900 a,e, and synthetic dilution •tater Sodlua sulfate Nltzsehla llnearls Sedlue thlocyenate Carclnus aaenas BSA, L BSA — 1,900 Also reported are factors affecting growth of alqae In canals to determine whether there Here leads to controlling algae by envlronaental management. No practical environmental •eans Here found. same as above Otto (19701. AMXC-892 Otto 11970). AMIC-69Z Patrick, at This study Has conducted to determine the relative toxlcltles of 20 al (14681. common constituents of Industrial Hastes 1HIC-97ZO to a fish, an alga, and an Invertebrate. The experiments Here conducted over a IB-year period for varied purposes. The authors recommend bioassays Kith at least three components of the food web. a.e. and synthetic dilution Hater a«{contin- uous, aer- ation, soa. water, and daily solution. ranowa.1) same as above One hundred-forty surface active agents, solvent emulslfiers, pesticides, polychlorlnated blPhenyls, pure Inorganic, and organic chemicals Here evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal nlth toxicIty of chealcats ta freshwater organisms. Patrick, at al (196M, •".IC-5720 Portmann, at a I (19711. ANIC-7701 ------- SodluM thloeyanate Cardlua edule BSA — Sodltm thlocyanata Crangon cranqon BSA — Sadlua thleeyanate Panda I us aontagul BSA Splll-X Steal head trout (finger)Ings) BSA — greater than SO* (T2I greater than SOI ITZI greater than 6.? (TZ) 35.5 IT) 3plll-X Spl 11 raaovar- Cobo salmon BSA Hood Canal, 1.5 (K) (finger-lings) In Hoodsport, situ Wash. Plaaphata proaI as 8S» — 5.ft mi Spill raaovar Spill raaov«r BS» — proaclai Blochealcal L — oxygen deeand IHSO 630,000 a«(contin- uous aer- ation, aea- water, and daily solution renewal) "a«(contin- uous, aer- ation, sea- water, and daily solution renov&l) a( contin- uous, aer- ation, sea. water, and daily solution renewal) saaa as above saae as above saae as above Portoann, at al (1971), ANIC-7701 Portaann.et a I (1971), •MIC-7701 Portaann, at al (1971), «C-7701 Evaluation of 11 oil dlsoersants Tracy, et al resulted In a ranking for each and a rcoi>mi>ndatlon tor use according to the t!969),»MIC- ranKlng. Ranking Has based on toxiclty 383* and oil dlsoersal effectiveness. Corexlt 776l> appeared to have the least toxiclty with fair to good oil dispersion capabllity. c,d,e,f c.d.e.f c,d,e,f same as above Toxlcltv of six oil spill dlsoersanfs was determined along with BOO values. Pond water Mas used as diluent and oil was Included In the experiment. Oil markedly reduced toxiclty of ell dlsoersants. Data are given as "aost probable** 96-hr TL sub a. saae as above sea* as above Tracy, et al (1969) ZllllCh (19691, AHIC-Z909 Zlllleh (19691,»HIC- 7909 Zlllleh (1969),HIC- ------- Compound Fiald Field Organise; Study Location Toxlcity, Active Ingredient, Ppm Experimental Variables. Controlled or Noted Streptomycin sultate llenodrllus I — SP Streptomycin sulfate Tublfex sp I — Streptomycin cut fate Peloseolex sp L — Streptomycin sulfate Phormldium L amblguum «.? (Til 0.5 (Tl) 0.9 IT1I O.S-1B.O (HTE) Strobane icpomls BS eyn«llux (Rtslstantt o.ta Tubiticid MOTHS Mere found to b« •ooroxliiately 300 tines nore sensitive than tf>elr oxn gut nicroflora. The authors recon»«nd that streptomycin should not be IndlscrInlnatelv applied In aquatic ecosystem. saae as above Col.r,., ,, «1968>, Coler, same as above 5S60 Coler. Of 7k chemicals evaluated as alqlcides. only 9 were more toxic than CuSOfc. None Inhibited growth of •at-fornlng alqae for nore than 2 weeks. CuSOd forpulated Kith certain Netting aqnts was more toxic than CuSOfc alone. Cooper chloraolne was also found to be nor* toxic than CuSO<<. No netting agents were found to be Inhibitory at the concentrations investigated (0.05 and 0.1105 cpm). lso reoorted are factors affecting growth of alqae In canals to determine whether there were leads to controlling aloae by environmental management. No practical environmental •cans nere found. Green sunflsh from Belzonl, Hiss. Minchen, et •ere resistant To Chlordane, HeDtachlor, al (1970), LIndanet and Strobane. but not to »MIc-5i,7i Parathion. Golden shiners fro the same location Here resistant to Llndane and Strobane, tolerant to Chlordane and MeotacMor, and susceptible to Parathion. lack of resistance to Parathion Indicated lack of agricultural usage of organophospnates in that area. Resistant ------- Strobane Lepomls cyan1I us (Susceptible) BSA — 0.05 (TZ) fish Mere coapared to susceptible ones collected at Starkvitte. same as above MlncheM, etal (19701. Strobane Strobane Noteiilqonus crysoleueas (Resistant) Notemioonus crysoleucas (Susceotlblel BSA — BSA — Z.2Z IT?) 0.06 (T2t save as above seme as above HlncheH, etal (1470). HlncheH, etal (1970) i »mc-5«i71 Strobane Strobane Strobane Palaeaonetes BSA had 1 aliens Is (resistant) O.OOSt-0.207 IT1I Palaeaonetes Hadlahensls (non- resistant) Cooeoods (Cvcloos blcusoIduSf Cycloos varicansf Cycloos vernal Is, Eucycloos aqllls. Kacrocyolops albldus, Orthocycloos •odestus) BSA FL State and College, BSA Hiss. 0.0393(11) 0.10 (KZ) Bloassays Mere conducted nlth Nagvl, et al shrlnp from three areas of Intensive (1970). pesticide use and from an unexoosed area. AHIC-S519 Previously exposed shrimp Mere from 1 to 25 times more resistant than unexposed shrimp. Both types of shrimp Mere also exposed In cages to Maters of the contaminated areas. Susceptible shrlvp suffered 6% percent more mortality than did resistant shrimp. The toxlcity of the insecticides ranked in descending order was as follows: most toxic. Endrln, DDT, Methyl parathlon, Parathlonl medium toxlclty, Cuthlon, Llndane, Toxaphene, Strobanes lease toxic Chlordane, Sevin, and Heptachlor. saae as above Naavi. et al (19701. AMIC-5519 The response of Nagvl, et al pesticide-resistant aquatic organisms to (1969). various pesticides Mas compared to the AtlIC-5979 response of non-resistant species. Pesticide-resistant soecles Here collected at Belzoni and non-resistant species at State College. Cooepods. clams, snails, and sludge norms from Belzonl Mere considerably more tolerant to pesticides than the non-resistant organisms. The authors note that the effect of Increased tolerance In the organisms Is an Increase In the amount of ------- Compound Organic Field Field Study Location Toxlelty, Active Ingredient, Ppa ExoerlHental Variables. Control led or Noted Comments Reference Strobane I Strobane Strontlu* CooepodS (Cyclops blcusDldus« Cyclops varlcans. Cycleos vernal Is. Eucyclops •9!IIs.laeroc Macrocyclops albldus. Or t hoc ye I oos aodestus) TubIfex tub Ifex FL •nd BSA Belzonl. Hiss a.to ------- Cal. Strontlua Sfrontlua Strontium Strontlw* Strontlua Strontlu* Strontlua Strontlu* Strontlua Strontlve) Strontlua Par•••bran clathratus Paratabrax clathratus Paratabrax clathratu* Paralabrax clathratus (qravld teaates) Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paral abrax elathratus FN FN FN FN FN FN FN Catallna 1.8 (ventral Island* Cal. auscle residue) Scattergood 2 (gonads Sta» Plant, rastducl Les Anqvtts, Cal. Catallna Island, call Catallna Island, Cal. 3.% Igonads residue) 3.2 (gonads. r«iidua) Seattcrgood 1.1 (liver Stesn Plant, residua) Los Angeles, Cal. Catallna 2.1 (liver Island, Cal. residua) Scattergood 5. (Intequaent Steam Plant, residue) Los Angeles, Cal. FN Catallna 10.1(Integuaent Island, Cal. residue) FN Scattergood 2.3 (heart Stean Plant, residua) Los Angeles, Cat. FN CatalIna 3.7 (heart Island, Cal. residue) FN Scattergood 92 (eyeball Stea* Plant, residue) Los Angeles, Cal. saaa as abova saae as abova saaa as above saaa as abova saaa as abova saaa as above saaa as abova saaa as above saaa as above saaa as above saae as above Staoleton 11968), AMTC-S980 Staoleton (1966), AMIC-9910 Staoleton (1968), ANIC-5<»»0 Staoleton (19681. IMIC-^980 Staoleton (1968), AMIC-5980 Staoleton (19681, AMIC-59SO Staoleton (1968), AMIC-99RO Staoleton (19681, AMIC-5980 5taoleton 11968), 1NIC-5980 Staoleton (1968). •MIC-5980 Staoleton (1968), ANIC-S9SO ------- Comoound Strontium Strychnine nitrate Sulf Isoxazote (Gantrlsln) Sulfurlc acid Sulf uric acid Toxlclty, Active Field Field Ingredient, Organism Study Location Pom ParalaH-ax FH Catallna 162 (eyeball clathratus Island, Cal. residue) Neqaorlon 8SA — 1.7 (SB 10 brevlrostrls MINI (1-3 Kg» Fundulus L — 0.96 (5830) hetereclltu* (3 in.) Agonus BSA — 80-90 (17) cataohractus Carclnus BS» — 79-SO (TZ» •aenas Experimental Variables, Controlled or Noted Comments e.c.e a.q a»( contin- uous aer- ation, sea. water, and dall7 aolutlon renewal) a«( contin- uous aer- ation, sea. water, and dally solution renewal) same as above Data from study of drug effects on young lemon sharks Here treated mathematically to demonstrate • ool Icahl 1 1 ty of classical rat theory to the stulv of chemical sharK deterrents. Incaoacl tat Ion (narcosis) Has the primary parameter timed for effectiveness. This Mas usually quite raold for the more effective drugs. The sutfa druq caused no significant difference In qronth rate. testes Height, Iodine uotaHe, or liver weight. Varylno degrees of adrenal Inactivity and adrenal deqranul at Ion occurred due to treatment. A significant Increase in hevatocrit Mas noted. As a result this chemical has become the sulf a drug of choice In the Rlngham Laboratory tor controlling sKln infection of hi 111 fish. One hundred-forty surface active agents, solvent emulslflers, pesticides. colychlorlnated blohenyts, cure inorganic, and organic chemicals were evaluated against as many as ten marine organisms. The authors noted that most published data of this type deal with toxielty of chemicals to freshwater organisms. same as above Reference Staoteton (1968) < AMIC-59SO Baldridge (1969), AMIC-383? CowmeadOH, et al (1969), AHIC-5736 Portmann, et al (1971), »HIC-7701 Portmann, at al (1971), AHIC-7701 Sulfwrlc acid Cardlurn edule 85* — 700-900 (T3) a«(eonttn- saoe as above Portmann, et ------- uous aer- ation, sea* water, and dally solution renewal) at (1971), 4HIC-7701 SulfurIc acid Cranqon crangon BSA — 70-so ITZI a»( contin- uous aer- ation, sea- water, and solution renewal) saae as above Port serin, et • I (1971). •HIC-7701 Sulfvrte acid PandaI us •ontaqul BS» — kt.S (TZt VJ1 »«(contin- uous aer- ation, sea- water, and (Jaily solution renewal) sae as above Portaenn, et al (1971), AHtC-7701 Sulfurlc acid Platlcthys fIesu BSA — 100-330 (T2) a»(contin- uous aer- ation, sea- water, and daily solution renewal) sane as above Porteann, et al (1971), •HIC-7701 Sulfur Suleet (tinted) Fish (not stwcltled) Hercenaria •ercvnarla L — 9reater than 1000 (K) greater than too m> Aoproxliiatc toxlcltles of HsHdestey- nuncrous pesticides co«only used In Thonas Brltiiln D«re summarized. In excellent (1971),MIC- brlef, general discussion of toxlclty 1096 testing Is also oresent. The effect of 5? pesticides on Davis, et al urbryonlc develooient of clams and (1969), oysters was reoorted. Synerqlstlc 4MIC-S990 effects with solvents were also reported. Host of the coxpounds affected develocient "or* than survival. Soae, hoiievcr, drastically reduced ------- Coaoound SulBet (tinted) Sulaet (untlnted) Sulf>et luntlnted) Sulaet luntlnted) SulBet (untlnted) SUB 1 till on Field Field Organise Study Location Hercenwla L — •ercenarla (larvae) lercenarls L ~ •erccnar la (eggs) Mercenarla L — •erccnarla (larva) Crassostrea L — vlrginlca (eggs) Crassostrea L — vlrglnlea (larvae) Puntlus tleto — ~ Toxiclty, Active Ingredient. fpm greaterthan 100 IT1Z) greaterthan 1000 m> greater than 1000 (TlZ) greaterthan 60R (TZI greater than 600 (Tli>) 0.0058 (TO Experimental Variables Control led or Noted Consents Reference selecting chemicals for oest control that Mould not have serious effect on shellfish. sa«e as above Oavlst et (1964). AMIC-5990 — sane as above Davls» et (1969), AMIC-5990 — saae as above Davis, et (1969), AMIC-5990 saae as above Davis, et (1969), AMIC-5990 -- sae as above Davis, et (1969). tMIC-5993 a.c.d.e.f Of the pesticides Investigated, Bhatla al al al al • 1 Sutan Ganaarus faselatus BSA — 10.0 the nost toxic Mas Ktofos follOMed In (1971), decreasing order by Sumithion, Malathlon, AMIC-5i>23 Fomtthlon, Olnecron, Sevln, and BHC. The author cites the need for more selective pesticides nontoxlc to fish or antagonistic agents for reducing fish toxlclty. Of the aquatic Meed herbicides Sanders evaluated, Dlclone xas the most toxic, (19701, Oaohnia was generally the most sensitive organism. All of the Crustacea Here affected by much loMer concentration levels of herbicides than indicated by the TL sub 50 values. til of the animals reoresent Important food chain links. S.O. 39ft? Hasbora heteroBoreha BCF» and 8S« greater than 1,000 (T?) a'.c.e.f, hard(HH) or soft ISM) synthetic dilution •ater. or seaMater for soae One hundred sixty-four pesticides. Netting agents, and •Iscel laneous Mater pollutants shoMed a Ml4e range of toxlclty scanning 1? orders of nagnltude. Knotting the toxlclty and percentage of all components of a f omul at ion did not result In easy predictability of the toxlclty of a Blxture of Materials. SoaetlBes Alabaster (1969>,AMIC- ------- S.O. 6211 Rasbora BCFA heteroaorpha and BSA 3.9 ITZ) S.O. S»7 > I Rasbora BCFA heteroBorpha and BSA U2I S.N. 5215 Rasbora BCFA heteronorpha and as* 23 IT2I species a,c,e.f • hard IHWI or SOFTCSMJ synthetic dilution water, or seawafer for some seecles a,c,e,f• hard IHH) or soft (SHI synthetic dllutloh water, or seftwater for soee soecles a,c,e,f» hard (HHI or SOFT(SW) synthetic dilution water, or seawater for SOB species TCC Mereenarla aercenarla • 0.032 IT2> pesticides «er« nost toxic In hard Hater and soaetines the opoeslt* was true. Testlnq The actual material as Sold Has found to be essential. save as above Alabaster sa> as abov* Alabaster One hundred sixty-tour Alabaster D»stlcldes, Mettlnq aqents, and (1969), •l^celleneous water oollutants showed a AHIC-SK2S • l<1e range of Toxlclty spannlnq l? orders of naqnltude. Knowlnq the toxlcitv and percentage of alt comoonents of a formulation did not result In easy predictability of the toxlcity of a •ixture of materials. Sooetlnes pesticides were nost toxic in hard water and soifetlnes the ooposite was true. Testlno the actual «aferial as sold was found to be essential* The effect of 52 pesticides on Davis, «t al ••bryonlc developvent of clans and oysters was reported. Synerqlstlc 11969)tAHIC- effeets with solvents were also reported. 9990 nost of the compounds affected development more than survival. Sone, hox»ver, drastically reduced larval growth. The authors point out the necessity of evaluating the effects of pesticides on all life stages or an organ Is* and note the possibility of ------- Compound Field Field Organism Study Location Toxlclty, Active Ingredient* Ppm Experimental Variables. Controlled or Noted Comment* Reference TCC TCP Hercenaria •ercenarla (larvae) Crassostrea vlrqlnlca 0.6 ITZI TCP TOE TOE Crassostrea vlrglnlca I larvae) Fish (not specified) White sucker FRL L ~ greater than 1.0 (TIM greater than 0.01-0.1 IK) Nlse. states 0.05-3.81 residue IS8> TOE TOE Vet ION oerch FRL Hlse. states 0.03-1.%7 residue (SSI Chain pickerel FRL Misc. states 0.09 residue (SB) selecting chemicals for oest control that would not have serious effect on shellfish. sane as above Davis, et al (ig69»,«HIC- 5990 The effect of 52 pesticides on Davis, et al embryonic development of dans and (1969), oysters was reoorted. Srnerglstlc 4HIC-5990 effects with solvents were also reoorted. Most of the compounds affected develocment more than survival. Some, however, drastically reduced larval orowth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stages of an organism and note the possibility of selecting chemicals for pest control that would not have serious effect on shellfish. sane as above Approximate toxlclties of numerous pesticides commonly used In Britain were summarized. An excellent brief, general discussion of toxlclty testing Is also present. The Bureau of Sport Fisheries continued its fish monitoring program by collecting I ------- TOE TOE TOE TOE TOE TOE TOE TOE TOE Mhltv catfish FRL Misc. White o«rch FRL Misc. Goldfish FRL Misc. Punpklnseed FRL NIsc. States 0.37-0.e as above saae as above saae as above save as above saae as above saae as above saae as above Henderson, et al (1971), Henderson, era! (19M)t Henderson* er al (1371), Henderson, et al ( Henderson, et al (197D, AMIC-l«i07 Her»lrson,et al (1971), »MIC-l«i07 Henderson, et al (19711 , »MIC-1"»07 Henderson, et al (1971), »MIC-l«t07 Henderson, et al (1971), TOE Gizzard shad FRL Misc. States 0.37-0.73 residue (SB) save as above Henderson, etal (1971), TOE TOE Snotted sucker FRL NIsc. Bluegllls FRL Misc. states 0.14-0.3? residue (SB) states 0.03-0.* residue (SB) sane as above sane as above Henderson, et al (1971), »MIC-1".07 Henderson, et al (1971), TOE Redbreast FRL sunfish NIsc. states 0.02 residue (sat saae as above Henderson, at al (1971). AMIC-U07 ------- Coaoound TOC TOC TOE TOC TOE TOE TOC TOC TOC TOC TOC TOC Field Field Study location ToKlelty, Active Ingredient, CxDerlaental Variables* Controlled or Notad Coaaents Strloed aullat Blue catfish RocH bass Freshttater •Ioatar lake •hlteflsh tali* trout FRL Hlse. states R.ZO-2.26 residua (SBI FRl HIsc. states 0.08 residue I SB) FRL HISC. States ».05-0.59 residua (SB) FL Nlse. states 0.20 residue I SBI FRL Hlse. states 0.15-9.71, residue ISBI FRL Hlse. states 0.12 residue ISB) FRL HIsc. states 0.02-0.15 residue (SBI White craDDie FRL Hlse. states 0.22-0.27 residue (SBI Blaaeuth FRL Hlse. states 0.17-0.60 buffalo residue (SBI $••11 couth FRL Hlse. states 0.1,6 residue buffalo «S«) Flathead FRL HIsc. states fl.SO residue eat fish ISBI Goldeve FRL HIsc. states 1.02-O.ZO residue ISB) se as above saae as above s«ae as above se as above ••• as above save as above saae as above sane as above sane as above saae as above saae as above saae as above Reference Henderson.et al (1971). »HIC-1<>07 Hendersont • t al (1471). Henderson, t »tll'37i1, AHIC-li.07 Men<1rson. et al (1971). »Mic-ii.or Henderson, et al (1971), •HIC-1V07 Henderson, et at (1971), AHIC-11,07 Henderson, et al (1971), AHIC-11,07 Hendrrson,et al (1971), »MIC-li,fl7 Henderson, at il (1971), • HIC-H07 Henderson.et al (1971), »HIC-107 Henderson, etal (1971), AMIC-H.07 Henderson, et al (1971), ------- AHIC-mO? roc roe TOE TOE Walleye FRL Hlsc. states fl.03-0.Z9 residue (SB) Sauqer FRL Hlse. t»t«s 0.10 residue (SB) Flannelmouth FRL Misc. sucker BlacH FRL Hlse. bullhead states O.ZB residue (SB) states fl.OZ-0.85 residue (SB) saae as above saae as above sane as above sane as above Henderson, et 11(1971), »MIC-1«.07 Henderson,et el (1971),»MIC- K.07 Henderson,et al (19711, »HIC-l«t07 Henderson,et »t (19711, HIC-li>!)7 > I TOE TOE TOE Unite bass FRL Misc. states 0.09'resldue (SB) Blaefc crapole FRL Misc. states Larqescaf FRL sueher residue (SB) Misc. states 0.06-0.29 residue (SB) saee as above saae as above saee as above Henderson, • t al (197H, MIC-1«.07 Henderson, et • I (19711, MIC-li»07 Henderson, et l (19711, 4HIC-H.07 TOE S»sllmouth FRL bass Misc. states 0.1<>-0.23 residue (SB) saae as above Henderson, et al TOE TOE Northern FRL Misc. Chlselmouth FRL Misc. states 0.03-0.".5 residue (SB) states 0.09-0.<>1 residua (SB) saae as above sae as above Henderson, et al (19711, Henderson, et al (1971), 4MIC-1I.07 TOE TOE Klaaath FRL sucker Misc. •alnbOH trout FRL Nlsc. states 0.01 residue (SB) states 0.03-8.16 residua (SB) saae as above saae as above Henderson, et al(1971), AMJC-H.07 Henderson,et al (1971), TOE Brldqello FRL Misc. states 0.30 residue saae as above Henderson, ------- Coaoound Field Field Organism- Study Location Toxlclty. Active Ingredient, »»a Experimental Variables, Controlled or Noted Coaaents Reference roe roc toe TOC sucker Arctic grayling Round •Mteflsh Longnose sucker Enqraulls •ordax CS8I FRL Misc. states FRL Nlse. states FRL Nlsc. states FN Pacific Northwest Coast, Grays Harbor, Hash. TOC roe ror TOC Cancer •eglster Cancer •eqliter Paroohrys vetulus Herlucclus productus FN FN FN FN 1.16 residue CSB) 1.32 residue (SB) 0.01-I.S? residue (SB) 0.07-8.?!. (reslduel seae as above saae as above s»»e as above et al «IC-Hi07 Henderson, et al(1971), AMIC-1<>07 Henderson, et al (19711, AHIC-U07 Henderson,et al (19711, HMIC-1V07 Pesticides front the Colunbll Stout Slver Into Puqet Sound aooarcntly (196A), contaminated fish constitutlna commercial AHIC-378 catches In Pacific Northwest waters. Residues In these earlne products Mere substantially lower than the FOA tolerance for beef (7 ponl. Fish froa locations near the aouth of the Columbia River had higher pesticide content than ones caught farther away. Pacific Northwest Coast, Destruction Island, Mash. Pacific Northnest Coast, Iliiaco. Hash. Pacific Northwest Coast, fttalne. Hash. Pacific Northwest Coast, Sarasota Passage. Hash. t.tl(rest duel — t.tZ (residue) — (.01-1.07 (residue) 0.13-0.05 treslduel saae as above saae as above seme as above same as above Stout (1968), AHIC-378W Stout (1966). AHIC-378% Stout (1966), AHIC-378V Stout (19681, ANIC-3784 ------- u> TOE TOE TOE TOE TOE- TOE TOE TOE TEP« Her luce I us FN productus Herlucclus FN produetus Nerlueclus FN productus (flshaeal) Sebastode* FN alutus Platlchthys FH stetlatus Gadus FN •acroceohalus Sebastodes FN flavidus Sebastode* FH flavidus Pocctlla BCM r«tlcu1«t« Pacific I.03-0.09 Northwest (rasldua) Coastt Fort Susant Hash. Pacific Northn«st Const. Capa Fou1w«»th«r, Ore. Pacific Northwest Const. •brrdeen. Hash. Pacific Northwest Coast. Hecate Strait, B.C. Pacific Northwest Coast * Rlalne, Mash. Pacific Northwest Const, Blalna, Mash. Pacific Northwest Coast, Hecate Strait, B.C. Pacific Northwest Coast* 11 Mace.Hash. t.arireslduet 0.03 (residue) Trace {residual 0.03(r«sldue1 0.01 Iresldue) — 0.01(residue) 0.02-0.09 (raslduel se»e as above saaa as above sa«a as above saae as above save as above saae as above saae as above saae as above Stout (1968), ANIC-378% Stout (to.6Bt . NIC-378«. Stout I196HI, NIC-378 hr each week over a 33 wk experlaental period to determine the (1969),«HIC- affaet of TEP* on reproduction and on the 9<»S7 vlablly, survival, and reproduction of ------- Compound ' Organism Field Field Studr Loot ion ToxlClty. •etlve Ingredient. PP» Experimental Variables, Controlled or Noted Connents Reference > TCP* TCPP Poecllla r«tlcul»ti Tublfex tublfex 8CH Ft •nd BSA Balzonit Hits. 190 IT«i» 8.00 INTO TCP1 Crassostrea vlrglnlca leggst L — greater than 10.0 m> StocH. et the unexposed Fl generation. Hat fertility xas adversely affect-d at concentration levels that did not influence resale reoroductlve caoablllty. Inhibited brood oroduction was associated Mlth atroohled and normal testes. The effect varied with concentration and exoosure frequency. Hale potency aooeared to recover Hhen exoofures Here discontinued. No aoparent effects Here observed In the Fl generation. TFTPA is a cheoosterl I ant used to Induce sterility In Insect pests. a«C(d • sane as above AMIC-51.57 The response of Novl> et pesticide-resistant aauatlc orqanlsms to al(19>9>t various pesticides was cooare ------- TCP Terramycln (concentrate) Crassostrea vlrglnjca (larvae) Moron* saxatllls IfIngerlIngs) L •— greater than 10.0 (TIM 165 would not have serious affect on shell fish. sane as above OavlSt et aldSKS), AMIC-5990 M«lI born (197H, ANIOSS71 Tetradlfon Cardlum edule BS» — k a,C,d,e,r, All compounds were Invest loafed p because of their probable usage In hatchery production of white bass. Compounds that can be used at recommended concentrations were Aauathol, Casaron, Llndanr, and Terramycln concentrate. Those that should not be used were Aerlftavlne, Baytuscide, Malachite green oxalate, and Malathion. greater than 10 a»(contln- One hundred-forty surface active Portmann, «t ITZ) UOU3, asp- agents, solvent emulslflers, pesticides, at (1971), ation, sea-Dolychlorlnated blphenyls, pure AMIC-7701 voter, and Inorganic, and organic chemicals were daily evaluated against as many as ten marine solution organisms. The authors noted that most renewal) published data of this type deal with toxlcity of chemicals to freshwater organisms. T«tradIfon Crangon crangon BS» greiter than 10 «(co.itin- uoxis, aer- ation, sea. water, and daily solution renewal) same as above Portmann, et al (1971), AW.IC-7701 Tetrshydrofurluryl alcohol Rasbora hetero«orph» OCFA and BSA 3,1,99 TFM Petroayzon •arlnus FLB Harauttte County, 3.8-9 (annual treataent. a,c,e,f. One hundred sixty-four Alabaster hardlHM) pesticides, wetting agents, and (1969),AMIC- or soft miscellaneous water ool lutants showed a 525 ISW) wMe range of toxlclty spanning 1? orders synthetic of magnitude. Knowing the toxlclty and dilution percentage of all comoonents of a water, or formulation did not result In easy seawater predictability of the toxlclty of a for some mixture of materials. Sometimes species pesticides were most toxic In hard water and sometimes the opposite was true. Testing the actual material as sold was found to be essential. a,f, TFN, a selective lamprey Man Ion conduo- larvlclde, w»s applied annually ever a (1969), ------- Compound Organ is Toxlclty, Active Field Field Ingredient, Studr Location Pom ExDri«ental Variables! » Control 1 ed or Noted Comments Refer« nee Michigan., 89-96 percent Garlic River peculation and SauxHead reduction) Lake Thailtun Crangon crangon BSA IB (Tit) ON Thlmet Rasbora BCFA heteromorpha and BSA less than 10 (ft) Thloglycolle acid Plmephales oroneIas BSA — 30.0 (UJ Thlolutln Phormldlum ambiguum • — a\| S.5-18.0 (100 percent growth tlvlty 3-year period to the Garlic River which AMIC-3T61 flows Into Saux Head LaHe. The final TFN treatment contained l oercent flayluselde as a syn»rglst and "bottom toxicant". The two compounds In combination were considerably "ore effective than TFN alone. The author believed total effectiveness Mas not achieved because lanoreys avoid lethal doses by moving to untreated water. a«(contln- One hundred-forty surface active Porteann. et uoua «er- aqcnts, solvent enulslflers, oestlcldeSt al (19711, at!or., aea'POlychlorlnated ntnhenyls, pur ANIC-7701 water, and Inorganic, and organic chemicals were dally evaluated against as many as ten marine solution organisms. The authors noted that most reneval) published data of this tyoe deal with toxlclty of chemicals to freshwater organisms. a,c,e,f. One hundred sixty-four Alabaster hard (HH) pesticides, Mettlnq agents, and (1969), or miscellaneous water oollutants showed a »HIC-S<.ZS SOFTtSH) wide range of toxlclty spanning It orders synthetic of magnitude. Knowing the toxlclty and dilution percentage of all components of a water, or formulation did not result In easy seawater oredlctabl11ty of the toxlclty of • for som mixture of materials. Sometimes species pesticides were most toxic In hard water and sometimes the ooooslte was true. Testing the actual material as sold was found to be essential. a,d,«,o, Halathion and Its hydrolysis Bender(19S9), •nd F« products were evaluated with the finding AHIC-37S7 that one such product (dlethyl fumarate) was lore toxic than Nalathlon to fathead minnows. Synergls" occurred between Halathion and two products of hydrolysis. Continuous exoosure resulted In Increased toxlclty. Of 71. chemicals evaluated as Otto 119701, alglcldes, only 9 were more toxic than AMIC-S92 ------- Inhibited Thluaet Rasbora BCFH — heteromorpha and BS» 1Z ITtl > I Thorlu Alosa psoudo- harengua Thorlua Thorlu* Coregonus artedll FL Coregomis FL clupeaformls a,c.e,f, hard (HH) or soft (SHI synthetic dilution Mater, or seawater lor some spec1es Great Lakes - Superior, Michigan, and ErU O.OOt(resldue) ~ Great Lakes - Superior. Michigan, •no Erie Great Lakes - Suoerlor, Nlchlgjn, and Erie O.OOJIresldue) ~ 0.00(residue) — CuSOU. None inhibited growth of •at-formlng aloae for more than ? NeeHs« CuSOii Tornulated Mlth certain wetting agents was nor* toxic than CuSOd alone* Coooer chloramlne Has also found to be •orp toxic than CuSOd* No wettina agents were found to be Inhibitory at th* concentrations Investigated (0.55 and 0.015 Dovl. Also reoorted are factors affecting qrowth of algae In canals to determine whether there were leads to controlling algae by environmental management. No practical environmental means were found. One hundred sixty-four Alabaster pesticides, wetting agents, and (1964), miscellaneous water pollutants showed a AHIC-St25 wll* range of toxlclty scanning 1? orders of magnitude. Knowing the toxlclty and percentage of all coioonents of a formulation did not result In easy predictability of the toxlelty of a mixture of materials. Sometimes pesticides were most toxic In hard water and sometimes the opooslte was true. Testing the actual material as sold was found to be essential. trace element content of fish Lucas, et from LrKes Sunerior, Michigan, and Erie (19701, was determined by activation analysis. AHIC-3778 Hhole body and IIver residues were determined. Concentrations varied with species and lake. Other elements found were! antimony - 5 to 100 Rpb, barium - 0.2 ppm, cesium - 3 ppb, lanthanum - 1 to 20 oob, mercury - 10 ppb, rhenium - 0.$ to S peb, rubldiu* - 0.06 to 6 ppa, scandium - ? ppb, selenlua - 0.1 to 2 ppb, silver - 0.001 PPb. same as above Lucas, et al (1970), al same as above Lucas, et (197Q), ANIC-37T« al ------- Compound Thorium Thorium thorium Thorium Thorium Thorium Thorium Thorium Thorium Organise COP eq onus hoyl Prosoolum eyl Indraceum Salvellnus namaycush Osmerus mordax Carassius auratus Notropls hudsonlus Percoosls omlsco*ycus Roecus chrysops Perce flave«c«n« Field Study Ft FL FL FL FL FL FL FL FL Field Location Great Lakes - Suoerlor, MIehlqan, and frle Great LaKes — Superlort Mlchlqan, and Erie Great LaKes - Superior, Mlchlqan, and Frle Great LaKes - Superior, Michigan, and Frle Great Lakes - Superior, Mlchlqan, •nd Erie Great LaKes - Superior, HIchlqvi, and Erie Great LaKes - Superior, Michigan, and Frle Great LaKes - Suoerlor, Michigan, and Trie Great LaKes - Superior, Nlchlqan, and Erie Toxlclty, Experimental Active Variables, Ingredient Controlled Pp» or Noted Consents O.BIZtCreslduet -- sane as above O.OtO(resldue) -- saae as above O.OOtlresldue) — saie as above ? (residue! — sane as above 93lresldue) — sane as above .O.OOS9(resldue> — saae as above V.flOZlif residue) — saoe as above t.003(resldue) — sa«e as above O.OOJfresIdue) — sa«e as above Reference Lucas, et al (1970) , »MIC-3778 Lucas, et al (1970) . •MIC-377S Lucas, et al (1970). AMIC-3778 Lucas, et al (1970). AMIC-3778 Lucas, et al (19701 . AMIC-3778 Lucas, et al 11970), AMIC-377 Lucas, et al (1970), AMIC-3778 Lucas, et at (1970). AMIC-3778 Lucas, et al (1970), AnTC-3778 Thorium Stlzostedlon FL Great Lakes 8.002(resldue> — saae as above Lucas, et al ------- vltreum vltrtun - Superior, Michigan, and Erla Thyroxlne Gadus morhua L ~ i.oooeii isati — Tlasan (ethyl Sal mo •ercury phosphate) galrdnerl L — (SB 1-ZI a,e,f (1 hr exposure daily for up to 11 days I Tin Coregonus FL clupeaforals Moosa Lake, 3.6 trasldual Can* Tin Tin Tin Coregonus FL etupemformls Esox luclu* Ft Esox luclus Lak* Ontarlot Can. Meosa Lakaf Can. O.S (residua) — (residua) ~ Lakt St. 0.7 (residua) Plarrat Can. (1970), •HIC-37TJ Line-caught Juvenile cod held In woodhead Snail tanks of seaxater rcsoonded to (1970) ,HIC- Thvroxln Injection by a 35 percent 3129 Increase In sulmnlnq speed. Large replication resulted In hlqhly slqnltlcant , Industrialized and non-industrial izad 11110-3819 areas were determined. Only mercury exceeded regulatory limits, and concentrations of most elements were assent laity the same In fish froa both areas* same as above saaa as above same as above Uthe, et ALM971), AMIC-3819 Uthe, et al <1971>,»HIC 3»19 Uthe, et al 11971), TIN Eax luclus FL Lake Erie, 0.5 (residue) — saae as above Uthe, at al ------- Coaoound Tin Tin TN Organise Osmerus •ordax Perc f lavescens Fundulus heterocl 1 tus Field Field Study Location Can. FL Laka Erie, Can. FL laka Erl«. Can. 8S» — Toxlclty, Active Ingredlenti Po» 1.2 Ires 1 due) 0.6 (residue! 0.000008-0.0001 9 CTO Experimental Variables, Controlled or Noted Comments •• seae as above -- sane as above a(c,e, 4 laboratory procedure based on »"d Standard Methods tor -hr toxlcity synthetic deter Ins t Ions of crurte oil and Reference 11971), •MIC-3819 Uthe, et al U971),»HIC- 381-3 Uthe, et al (1971) .AMIC- 3819 LaRoehe, et 81 (1470), AHIC-I.1,5 TN TOR Nereis vlrens 8S* Gei«arus fasciatus BS» — 0.00006-0.00033 a>,c.e. and synthetic seaHater e.3o seanater oll-dlsp«rsant mixtures was described. The dlsoersants varied considerably in toxlcity, ranging from 0.01 to 7.1 ml/I, TL50 for 96 hr. These did not differ slinl f Icsntl y from 2i«0 hr values. The dlsoersants were designated as CX, DO. Cl, 00, AO, PC, MM, TN, BP, and MA Hith no further descrlotloft of their chemical nature or source. Only a fen bloassays were conducted Hith shrino. MollusHs and echlnoderns xere suggested as suitable test animals. The authors stated that the method could be used to test any product for toxlcity In seaxater. sa»e as above leBoche.et al (19701, »nJC-«ii.5 Tordon C Rasbora heteroeorpha BCFR and 8S IT2J a» Ot the aouatlc weed herbicides Sanders Devaluated, Olclone «as the most toxic, (1970), 'Oaohnle was generally the most sensitive »HIC-<>53 organism. All of the Crustacea Here affected by much lower concentration levels of herbicides than Indicated by the TL sub <>0 values. All of the animals reoresent Important food chain links. a,c,e,t. One hundred sixty-four hard (HH) pesticides, wetting agents, and or soT miscellaneous water pollutants showed a (SHI wMe range of toxlcity spanning 12 orders synthetic of magnitude. Knowing the toxlcity and dilution percentage ot all comoonents of a water, or formulation did not result In easy seawater predictability of the toxlcity of a for some mixture of materials. Sometimes species pesticides Mere most toxic in hard Hater Alabaster (1969), ------- Tordon N Rasbora 8CF* heteromorpha and 8S» IBS IT2) Toxephene Ictalurus punctatus BSA — 0.013 «Tfcl Toiaphene Toxaphene Toxaphene Toxaphene Toxaphene Toxaphene Ictalurn ••las Carasslus auratus Cyprlnus carplo Plmeohales pr oii BSA — BSA BSA — BS» Leoomls BSA •acrochlrus leoouls 8S» micro!oohus Hlcrppterus 8S» sal no Idas O.OD5 (Tli) 0.014 (TM 0.004 IT4) 0.01% 0.01» (Ti.) 0.013 (T4I 0.002 IT) and sonetIves the opposira Mas true. Testing the actual Material as sold Has found to b essential. aSCit,f, saaa as above Alabaster hard ------- CoMtound Field Field Organise Study Location Texlelty. active Ingredient, Experimental Variables, Controlled or Noted Cements Reference Telephone Texopttene Texapheno Texephene Texaphene Seleo BSA — galrdnerl Salao trutta BSA ~ Oncorhynchus BSA ~ nlsutch •erea BS* flevescens Palaeeonetes BS» — kadlakensls (resistant! •.111 ITM ».D«3 IT) I.lit (TM 1.112 IT»I ITU test water e. synthetic test nater syntnetlc test Hater a< synthetic test Hater a, synthetic testoater Toxephene Tovapnene Palaeeonete BS* — fcedlekensls reslatant) Cooepods FL State (Cyclops and Col 1090* bleusoldus, BSI Miss. Cyclops v Orleans, Cycloos !.•?•• a* percent K8) save as above saae as above saae as above saee as above Hacek, etal I1WO). AHIC-SS10 et al(1470). Hac«k,et at (19701, at (19/0), Bloassays Here conducted with Naovl, et al shrleo fron threr areas of Intensive (19701, pesticide use and froe an unexoosed area. ANIC-5519 Previously eitoosed shrlep Mere from 1 to 25 tlaes "ore resistant than unexposed shrlep. Both tyoes of shrlep nere also exposed In cages to Maters of the contaminated areas. Susceotlble shrlep suffered 66 oercent aore aortal Ity than. did resistant shrleo. The toxlclty of the Insecticides ranked In descending order «as as folIOMS* eost toxic, fndrln, DOT, Methyl oarathlon, Parathlonl •edlue toxlclty> Guthlon, Llndane, Toxaphene, Strobanel lease toxic Chi ordene, Sevln, and Heptachlor. saoe as above The response of pesticide-resistant aquatic organises to various pesticides Mas coooared to the response of non-resistant species. Pesticide-resistant species Mere collected at Belzonl and non-resistant Naovl, et al (19701, AN.IC-5519 Maovl. et al (1969). •HIC-5979 ------- Telephone > Jr Tmaphene Toiaohene Toirophene T«apnene Telephone Te«»pn«ne v«rnalIt, Eucycloos agllls.Maeroc Hterocyelops •ibldus, Orthocyeloos •odestust Cooeoods (Cyclops blcusoldus. Cycloes varl cans, Cyeloos vernal Is, Eucyctoos C9l lls, ------- CoBoound Organls Field Study Location Toxlclty, Active Ingredient, Po» Experimental Variables. Controlled or Noted Cooments Reference Toxaphene Toxlon Nercenarla •ercenarlo (larvae! Care I nut I — USA — ToBlon Cerdlue edule SS* — Toilen Crengon crengon 8S» — TexIen PandaIus •ontagul SS* — less than t.Z5 IT12) 1S3 CTZ) ?7.% (Til «.6 IT2) (.9* ITZ) -- ••(contin- uous, aer- ation, aaa water, and daily solution renewal) a( contin- uous, aer- ation, sea. wator, and daily solution renewal) a«( contin- uous, aer- ation, gea> water, and daily solution renewal) a« (contin- uous, aer- ation, saa. water, and dally. solution renewal) necessity of evaluating the effects of pesticides on all life stages of an organise and note the possibility of selecting cheelcals for pest control that would not have serious effect on shellfish. saae as above se«e as above OavlSt et al(1969>, HMIC-5990 Portnann. et al 119711. •HIC-7701 One hundred-forty surface active Portmann, et solvent enulsMlers> prstlcldest al (1971), polychlorlnated blohenyls. pure AMIC-7701 InorqarlCt and orqanlc cheilcals Mere evaluated against as nany as ten aarine organls». The authors noted that aost published data of this type deal »lth toxlclty of chenlcals to fresh«ater organlsa«« sa«e •* above Portaann. et al 119711, nIC-7711 sae as above Portaann, et al 11971), AHIC-7701 ------- Trace organic* «CCC» Rainbow trout BSA •«- 36 IT1) I U> \n Trace organic* ICCE) Rainbow trout BSCH — Trace organic* Rainbow trout BSCH ICCEI Tract organic* ICCE) Gotdan shiner BSA Trace organic* Blue-green BS» ICCE) ionfish Trace organic* (CCE Rainbow trout BS» and C»E) Traca organic* ICCE Rainbow trout BSCH and CIE) Trace organic* (CCE Rainbow trout BSCH and CE) IB ------- > t- Compound Trace organic (CCE •nd CAE» Trace organic* (CCE •nd CAEI Trace; organic* (CCC •nd Cr> Trace organlcs (CCE •nd CAE> Trac organlcs (CCE •nd CEI Trace organlcs ICCC •nd CAE) Traflan C.C. Trail an E.C. Flatd Field Organise Study Location Olue-green BSA — sun fish Red shiner BS» — Red shiner BSCH — Red shiner BSCH — Col den shiner BSA — Hosaultoflsh BSA Rasbora BCFA « heteromorpha and BSA Rasbora BCFA — - heteroaorpha and BSA Toxlcltr. Active Ingredient Po» 137-166IT1I 195 IT1) ?«. (T ZO-301 S.6 . MIC-993 Smith, et al (1970), AHIC-993 Smith, et l doro), AMIC-993 Smith, et al (1970), &HIC-993 Smith, et al (1970), AMIC-993 Alabaster (1969) < AMIC-S1.85 Alabaster (1969), AHIC-S1.Z5 ------- spec Us Trlbutyl tin chloride Phormldlum amblguu* 0.5-10.0 percent growth inhibited Hi) (100 Trlbutyl tin oxide Sal ao qalrdner I BCF» and BS« 0.027 (Tl) Trlbutyl tin oxide Sal no galrdnerl BCFm and BS» 0.0?0 (T2> a«c,e.f. hard (HH) or SOFTISW) synthetic dilution itater, or seawater for some soeeles a,c,e.f, hard (HtO or soft (SMI synthetic dilution Mater, or seawater for some species Triealne •ethanesul tonate (lingual) SalvetInus fontlnalls 100 CNTEI Of 7(» chemicals evaluated as Otto (1970), alqlcldes, only 9 Here more toxic than ANIC-S92 CuSOi.. None Inhibited growth ot niat-forning algae for wore than t weeks. CuSOt* formulated with certain Mettlnq aqent« was more toxic than CuSOfc alone. Coooer chlorawlne Mas also found to be • ore toxic than CuSO<>. No Mettlnq aqents •ere found to be Inhibitory at the concentrations Investtoated (0.05 and 0.905 DDK). Also r«oorted are factors affecting growth of alqae In canals to determine whether there were leads to controlling alqae by environmental • aig>ient. No practical environmental •cans were found. One hundred sixty-four Alabaster oestlcldesi wetting agents, and (1969), • Isce I laneous water oollutants showed a NIC-5<»25 wide range of toxlclty scanning 1? orders of nagnltude. Knowing the toxlclty and percentage of all co»oonents of a formulation did not result In easy predictability of the toxleity of a • Ixture of Materials* Sometimes pesticides were most toxic In hard water and sometimes the ooooslte was true. Testing the actual material as sold Mas found to be essential. sane as above Alabaster (19691, »NTC-5«5 Anesthetization of brook trout resulted In alterations of hemoglobin, tissue and Plasma water content, electrolytes, aortic pressure, and ventllatory rate and amplitude. Flnguel apparently exerted depressive Influence on central autonoalc functions. Handling alone resulted In changes In plasas Houston, et al 11971), •MIC-38Z3 ------- Compound Organise Field Ft ft TrlcMorobenzane Hercenarla •arcenarla (•qqs) • ^^ greater thanlO.O tTZI TrIchIorobenzene Tr leM orobenzene Trlfturalin Merc en aria mercenarla (larvae) Crassostrea vlrqtnlca (eqqs) •set I us brevlcaudus BS» — greater Than 10.0 (T1ZI 3.13 ITZ) ?.0 ITZt Trlfluralin Oreonacta* nal« 50.0 (TZI glucose and lactate content, and In a number of electrolytes. Study of the effects of Houston, at anesthesia, handling, and experimental at (19T1), oreoaratlon of brook trout resulted In AMIC-382? alterations In henatoloqlcal characteristics* hyoerqlycemla, changes In oI asms, tissue, cellular Ion concentrations, and e-Jul I Ibrlun conditions. Short-term (?-•> hr) effects correlated with clearances of the anesthetic while oerslstent effects Here believed to be associated with generalized enoocrlne resoonse to trauaa. The effect of 52 pesticides on Davis, et at embryonic devetooment of clans and (1969), oysters was reported. Synerglstlc »HIC-?990 effects with solvents were also reported. Host of the compounds affected develocnent more than survival. Soe, however, drastically reduced larval growth. The authors oolnt out the necessity of evaluating the effects of pesticides on all life stages of an orqanls and note the possibility of selecting chemicals for pest control that would not have serious effect on shall fish. saae as above saae as abova Davis, et at (19691, »MIC-5990 DavlS* at al(1969), AMIC-5990 Of the aouMlc weed herbicides Sanders evaluated, Olclone was the irost toxic, (14701, Oaohnla was generally the most sensitive »MIC-<>5* orqanlsm. »ll of the Crustacea were affected by much lower concentration levels of herbicides than Indicated by the TL sub SO values. AM of the animals renresent Important food chain links. same as above Sanders (19701. AHIC-f.53 ------- Trtflur«Un Trlfturalln Trlfluratln Trl Mural In Banhnla naqna BSA — Cyorldoosls vlitua Lepovls aacrochlrus Caaaarus faselatus BSA — BSA — BS» — 8.56 IT21 «.2« »T2> •••19 CT2I 1.8 IT2t saae as abova sane as abova saae as abova saaa as abova Sanders Sanders(1971>. Sanders (19701. AHIC-t3 Sanders(19731. Trlfluralln Trloxon Paleoaonta* kadi aliens Is Salao 9«lrdn«rl BSA — BCF» and •S* i.i mi !• ITZI Sanders (19701. Trlnabon Rasbora heterooorpna BCF» and BS* (TZ) ••,o,a,, bard (HW) or soft (SW) •ynthatle dilution water or aoa.ua tar for some spacloa a>,e,a>tt hard (HNI or SOFT(SM) synthetic dilution •ater, or saawatar for soaa soecles saae as above One hundred sixty-four Alabaster pesticides. MCttlnq agents, and 119691. miscellaneous Mater pollutants shotted a ANIC-5fc25 • Me range of toxlcity spanning 12 orders of eignltude. Knotting the toxlelty and percentage of all components of a foraulaflon did not result In easy predictability of the toxlelty of a alxture of Materials. Soaetlaes pesticides Mere aost toxic in hard water and soaetlaes the opposite Mas true. Testing ttie actual aaterlal as sold Mas found to be essential. saae as abova Alabaster (19691. ANIC-M2S TubatOK Rasbora •CM — •.27 IT2I ••tC,a»f* One hundred sixty-four Alabaster ------- Compound Organise heteroaorpha Field Field Study Location •nd BS* Toxlclty* Active Ingredient, Pp. Experimental Variables, Controlled or Noted Comments Reference Uranlu* A lose paeudo- harangua FL Uranium Urenlua Uranlua Uranium Percoosls omlscomaycus Roccus chrysocs Perca Haves eens Stlzostedlon vltrtum vltreua FL FL hard (HH) or SOFT(SH) synthetic dilution water, or seawater for some species Great Lakes 0.9026 - Superlort (residue! Michigan, •nd Erie Great Lakes t.OOta(residue) • Superior, Michigan, and Erie Great Lakes O.OOZ(resldue) - Superior, Ulchlg»n,and Erie Great Lakes - Superior, Michigan, •nd Erie Great Lakes - Superior, Michigan, and Erie 0.0009(resldue» — 0.001 (residue) pesticides, netting agents, and (1969), miscellaneous water pollutants showed a AMI •Ide range of toxlclty spanning 12 orders of magnitude. Knowing the toxiclty and percentage of all components of a formulation did not result In easy predictability of the toxlclty of a mixture of Materials. Sometimes pesticides Mere most toxic In hard water and sometimes the opposite Has true. Testing the actual material as sold was found to be essential. Trace element content of fish Lucas, et al from Lakes Suoerlor, Michigan, and Erie (19701, was determined by activation analysis. AMIC—3778 Whole body and liver residues were determined. Concentrations varied with species and lake. Other elements found •erel antimony - 5 to 100 ppb, barium - 0.? ppm, ceslu* - 3 ppb, lanthanum - 1 to 70 pob, mercury - 10 ppb, rhenium - 0.5 to 5 ppb. rubidium - 0.06 to 6 ppm, scandlua - 2 ppb, selenium - 0.1 to t ppb, silver - 0.001 ppb. same as above Lucas, et (19701, AMIC-3/78 • I same as above sane as above same as above Lucas, et at (1970), AMIC-377S Lucas, et al (1970), •MIC-3778 Lucas, et at (1970), •HIC-J77S ------- Uranlua Uranlua Uranlue uranlue Uranlua Uranlua) Uranlua Urenlua Coreqonus Fl artedll Ceregonus Ft cluveaforals Cereqonu* FL hey I Prosoolue Ft eyllndraeeua SalvetInu* Ft Osaerus FL •ordax Carasslu* FL euratus Motrools FL hud«onlu* FL cluoastoral* Great Lakts - Suotrlor, Rlchlqan, •nd frl« Great Lakes - SuoerloPt Michigan, and Frle Great Lake* - Sooerlor, Michigan, •nd Erie Great Lake* • Suoerior, NIeMaant and Erie Great Lakes - uoerlor« g.H2(re«lduel — l.flltfretlduel l.ltVSIretlduel ~ I.OZ(resldue> — and trie Great Lakes - Suoerlort Hlchlqan.and Erie Great Lakes - Suotrlor, MIcMeant •nd Frla Great Lakes • Suoerlort Hlchlaan. and Erla Hoose Lake. Can. I.••{(residue! I.0fl9(reslduel I. lift(residue) — S (residue! — Uranlua Coreaonus cluoeefarals Fl lake Ontario. Can. f (residual — save as above ••• as above saae as above saae as above sane as above cane as above saae as above sane as above Concentrations of 13 toxic elements In dressed fish fro heavily Industrialized and non-Industrialized areas Mere determined. Only ercury exceeded regulatory Malts, and concentrations of Host eleaents Here essentially the saae In fish froa both areas. saae as above Lucas, at al (197BI, •MIC-JTT8 Lucas, et at C19TO), •HIC-377H Lucas, et al •19701, »NIC-3778 Lucas, et al (19701, ANIC-377C Lucas, et al (19701, »MIC-S778 Luces, et al (19701, •HIC-37T8 Lucas, et al (1970), »HIC-J778 Lucas, et al (19701, AHIC-3778 Uthe, et »L<1971I, INIC-3819 Uthe, et »L«1971I, •HIC-3S19 ------- Conoound Uranlun Uranlun Uranlun Uranlua Uranlun Uraabor Vaaldothlon Toxlclty, Experimental Active Variables, Field Field Ingredient, Controlled Organism Study Location Ppn or Noted Comments Esox luclus Fl Moos Ush«, 3 (residue) Can. Esox luclus Fl Lake St. f (residue) Plerret Can. Esox luclus FL Lake Erlet 1 (residue) Can. Osmerus FL Lake Erie* 2 (residue) -- aordax Can. Perce FL Lake Erie, 1 (residue) flaveseeis Can. Sel«o BCF* — 925 (T2I »»,c,e.t. galrdnerl and hard ,Hw) BS» or SOFT(SH) synthetic dilution •ater, or seawater for some species Rasbora BCF» ~ «60 (T2I a»,c,,f. heteroaoroha and hard (HW) BSI or SOFT(SH) synthetic dilution xater, or seaxater for soae soecles saae as above sane as above sane as above sane as above sane as above One hundred sixty-tour pesticides, wetting agents, and nlscel lancous Hater pollutants shoned a Hide ranqe ot toxlclty spanning 12 orders of magnitude. Knonlnq, the toxlclty and oe^c^ntaQ ot alt eomoonents ot a formulation did not result In easy Dredlctabll 1 ty of the toxlclty of a Mixture of materials. Sot"* tines pesticides Here most toxic in hard nater and sonetlnes the opposite Has true. Testing the actual naterlal as sold Has found to be essential. saae as above Reference Uthe, et al 119711, AHIC- JB19 Uthe, et al J197U,»MIC- 3819 Uthe, et al (19TH,»»1IC' J819 Uthe, et al tl97H,»MlC J«19 Uthe. et al (1971), »1IC- 3819 Alabaster (1969) . MIC-5<.25 Alabaster (1969), AHIC-S«25 ------- Vanadium Paralabrax clathratus FM U) Vanadium Vanadium Vanadium Vanadium: Paratahrax clathratus Paralabrax elathratut Paralabrax elathratut Paralabrax clathratus FH Scatterqood 3.3 (dorsal Steam Plant, museI• Los Angelas? r«sldua» Cal. Catallna 1.9 (dorsal Island, Cal. auscl residue* Fish collected from an effluent ploe of a steam plant and from offshore Maters of Catallna Island oere analyzed for trace element content. Trace element content of the effluent water was at least 5 times greater than that of normal sea Miter for cadmium, copoer, nickel, zinc, and chromium. Livers of fish from the effluent Here nearly twice the size of those from the ocean. Greatest differences In concentration occurred •1th aluminum, cadmium, and nlcKel. Silver, barium, lltnluit, and lead showed the least differences. The author concluded that trace element analysts of tissues could be used to determine the •fleet of oollutants on marine organises. same as above FH Scatterqood 3.2 (ventral Steam Plant, muscle Los Anqeles, residue) Cal. FH Catallna 1.7 (ventral Island, Cal. muscle residual FH Scatterqood 5.7 (gonads Steam Plant, reslduel Los Anqeles, Cal. same as above Same as above saee as above Staoleton (19681, 1MIC-5980 S t ao I f t on IHIC-5980 Staoleton (1968). Staoleton (1968) , »HIC-':980 Staoleton (19681, 4MIC-59BO Vanadium Paralahrax clafnratus FH Catal Ina .2 (qonads Island, Cal. residual same as above Staoleton 119681 , 1MIC-S980 Vanadium Vanadium Vanadium Paralabrix elathratus (qravld females) Paralabrax elathratus Paralabrax clathratus FH FH FH Catallna Island, Cal. Iqonads residua) Seetterqood Z.K (liver Steaip Plant, residue) Los tnqeles, Cal. Catallna Island, Cal< 3.1 (liver rasldual same as above same as abova same as abova Staoleton (196(11. »MIC-S980 Staoleton (19681. »HIC-5980 Staoleton (1968), ------- Compound Vanadlua Vanadlua Venedluii Vanadium Vanadlua Vanadlwa VIM Velslcol •« 516 l»7.e percent olus 9 percent E»eol H-1%6. Field Field Organise Study Location Paralabrax FN elathratus Paralabrax FN elathratus Paralabrax FN clathratus Paralabrax FN clafhratus Paralabrax FH elathratus Paralabrax FN clathratus Raxbora BCFA heteroKorpha and 8S* Pasboro BCF» heteroaorpha and BSA Scatter good Steam Plant, Los Angeles. Cat. Catal Ina Island. Cat. Scatterqood Steam Plant. Los Angeles. Cat. Catal Ina Island, Cal. Scatter good Steaa Plant. Los Angelas. Cal. Catallna Island. Cal. _ M. Toxlclty, Experimental Active Variables. Ingredient. Controlled Pp» or Noted Comments 2.9 lln tegument ~ resldue) ?.9 (Integuaent -- residue) 3.Z Iheart residue) 3.2 Iheart residue) 9 (eyeball residue! r.t, (eyeball residue) I.1S IT?) a'.c.e.f. hard(HH) or soft (SW> synthetic dilution Hater, or seawater tor seme species r.t Oil a,c.e.f. hard (NH)OT saae as above saae as above saae as above saae as above saae as above same as above One hundred sixty-four pesticides. Netting agents, and miscellaneous water pollutants showed a Hide range of toxlclty scanning 12 orders of magnitude. Knowing the toxlclty and percentage of all components of a formulation did not result In easy prellctabll 1 ty of the toxlclty of a •Ixture ot materials. Sometimes pesticides Here most toxic In hard Hater and sovetlaes the opposite Has true. Testing the actual material as sold was tound to be essential. One hundred sixty— four pesticides, netting agents, and miscellaneous water pollutants showed a Reference Stapl»ton I i9f»M , AHIC-5988 Staoleton (196M. Staoleton (19661, ANIC-S910 Staoleton (19601, ANIC-S980 Staoleton (196M , AHIC-598H StaDleton (1961 , AMIC-S980 Alabaster (19691. ANIC-5«Zf Alabaster ( 19691, AHIC- S25 ------- t pereentCmeol H-SOOX, l.Zoercent Eplchlorhydrln) Vctslcol A« 506 189 percent plus 9 percent Emcol H-ll>6f 8 percent Emcol H-5IOXI ftasbora heferoaorpha BCF» •nd BSA 9.2 (TZJ > V/l Venzar Rasbora BCF« heteromorpha and 85 51 (TZ> sort tswi synthetic. dilution Mater, or seawater forsome species a»,c,e,f, hard (HH> or so It CSH) synthetic dilution Hater, or seawater for some soeel«s a,c,e,f, hard IHUIor soft (SH) synthetic dilution Mater, or seawater for soae species Ver9en«ter tlallne Sal no verqlclde •••dklller galrdnerl •I BCF •nd BSA «TZ» a>,e,e,f, hard IHW) or soft (SHI synthetic dilution Hater, or seaMater for soae species Vernol ate Caxvarus fasciatut BS» ?0.8 \|T2>t 13.1 a* mt ranqe of toxlclty soannlnq 12 orders of maqnltude. KnoMlnq the toxlclty and percentage of all coooonents of a femulation did not result In easy predictability of the toxlclty of a •Ixture of materials. Sometimes pesticides Mere most toxic In hard Mater and soeetlmes the opposite Has true. Testlne. the actual material as sold Has found to be essential. same as above tlabaster 119691., One hundred sixty-four Alabaster pesticides, xeftlnq agents, and (19691* miscellaneous water pollutants showed a INIC-SfcH Hide range of toxlclty soannlnq 12 orders of magnitude. Knowing the toxlclty and percentaoe of all comoonents of a formulation did not result In easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides Here most toxic In hard water and sometimes the opposite Mas true. Testing the actual material as sold Mas found to be essential. same as above alabaster (1969), •HIC-ftZS Of the aouatlc Heed herbicides Sanders evaluated, Olclone Has the most toxic. (1970).4HIC- Oaphnla Mas generally the eost sensitive 5J organism. All of the Crustacea Mere affected by much loner concentration ------- Conoound Field FUld Organism Study location Toxic!ty, Active Ingredient, Ppn Experimental Variables, Controlled or Noted Convents Reference Vernolate Verne)ate Pateonontes BS» kadlakensls Asellus BSA brevlcaudus 1.9 IT2I 5.6 CT2» levels of herbicides than Indicated by the Ti sub SO values. All of the anlnals represent laoortant food chain links. sane as above Sanders same as above Sanders 119701, VernotBte Vernolate Vernolate Vernolate Vinyl acetate Oreonectes BS» nals Daphnla magna BSA CvnrldoDsls BSA vldua •acrocMrus Asterlas rubens BSA BSA — 71.. B U2» 1.1 (T7» O.Zi (TZI 9.2 (TZ) 330-1000 ITZ) Vinyl acetate Cranqon crangon BSA 10-100 IT2t a»(contin- uous «ar- atlon, sea. water, and dally solution renewal) ao(contin- uous aer- ation, sea. water, and dally solution renewal) sane as above sane es above same as above sane as above One hundred-forty surface active aaents, solvent eulslflers, pesticides oolych lorlnated blphenyls, pure Inorqanlc, and organic chenlcats Mere evaluated against as eany as ten narlne organises. The authors noted that aost published data of this type deal with toxlcity of ehenlcals to freshwater orqanlsos. sane as above Sanders (19701, Sanders 119701, Sanders(1970t, AHIC-W53 Sanders 11970) , AHIC-SSS Portnann, et al (1971), AHIC-7701 Portnann, et al (1971), AKIC-7701 ------- Vinyl acetate Platlcthys ftesus BS» ~ greater than 100 «TZ» ml contin- uous aer- ation, sea- water, and daily solution renewal) saee as above Porteann, at el (1971. AHIC-7701 Meedazot T-L Crane, on crangon BS» — 1000-3001 (TZI »«•( contin- uous aer- ation, sea- water, and dally solution renewal) saee as »bov« Portmann, et • I 119711, »nIC-77fll Meedazol Rasbora BCF« heteromoroha and BS 90 (TZ) m. Rasbora BCF heferoaerpha and 8S» (T?> *,Cf«,f, herd (MM)OP SOft (SHI synthetic dilution «at«p, or seanttep lor son soeetes h»p ------- Compound Ye 1 1 OH phosphorus Organism Gammarus oeeanlcus Field Fltld Study Location BCF» — Toxlcity, »ctlv« Ingredient, Pom S-* CHI! Experimental Varl ablest Control led or Noted Comments •tCtf sane as above Reference Tell OH phosphorus Salvellnus BCFA — tontlnalls 0.0009 IT 200 hrl Ye11OH phosphorus Ye 11 OH phosphorus Ye 11 OH phosphorus Ye11 OH phosphorus Young" OafIV Salvellnus fontlnalis Osmerus mordax Oseerus •ordax Clup«a harengus BCF» — BCF» BCF» ~ BCF» — Rasbora BCFA heteroaorpha and BS» 1.2 IT f.T hr) O.OOOS (T 190 hrl 1.0 (T 12 hrl 0.1 IT 3.6 hr) .s mi ZltKo, et al (1970),AMIC- 3S17 the data were presented at LT sub Fletcher, et 50 (tire to 50 percent lethality). The al <1970>, approximate TL sub m data cited were AHIC-8J9 Interpolated from plotted TL sub 50 values. Redness, henolvsls, and reduced heiiatocrlts correlated directly with toxlclty to brook trout. No redness or hemolysls occurred In smelt although reduced henatocrlts occurred. Herring also turned red with hemolysls and redness around head and fins. In time phosphorus Has toxic at concentrations as I OH as 0.5 micron/1. same a* above Fletcher, et al(1970), »MIC-»J9 Fletcher, et al(t970>. »MIC-S39 Fletcher, et at (1970), AMIC-839 Fletcher, et al(1970), AHIC-839 Alabaster, (19691,ANIC- sane as above sane as above sane as above Zectran Ictalurus punctatus BS» ~ 11.»0 (T»l a,c,e,f. One hundred sixty-four hard pesticides, wetting agents, and (Hw)or miscellaneous Hater pollutants showed a soft (SM) Hld» range of toxlclty spanning 12 orders synthetic of magnitude. Knowing the toxlclty and dilution percentage of all components of a Hater, or formulation did not result in easy seanater predictability of the toxlcity of a for some mixture of materials. Sometimes species pesticides Here most toxic in hard Hater and sometimes the opposite Has true. Testing the actual material as sold Has found to be essential. •t Organochtorine Insecticides Here Hacek,et ml synthetic the most toxic compounds, (19701, test nater organoohosphates intermediate, carbamatas AHIC-5510 the least toxic. Brown trout Has the ------- lectren loctran Zectran 7eetran Zectran Zectrafl Zee t ran Zeetran Zeetren Zectren Zectr«n Zinc chloride tes tlncl Ictalurus ••las Carass 1us auratus Cyorlnus carolo Pleephales or ore I s Leoeeils •acroeMrus leoeuls elcroloehus Mlcropterus sal noI das Sal BO <a Irdner I BS> ~ B3» — BS BS» 8S» — BS* — BS» — Saleo trutta B5» — Oocorhynchus BS« klsuteh 16.TO IT) 19.1 IT»» 13.1.0	, •MIC-5910 Macek, etal (1970)t »«IC-551Q Macek, et a)I1970)t •MIC-S510 Hacek.et al (19701, AHIC-SSIO Meeek, etal •HIC-5510 Macek, etal 11970)t •HIC-5510 Macek, etal (1970), •HIC-SSIO Hacek, et •t(1970)t et •1(1970), »HIC-5510 HaceKt etal (197Q), Br«chyd«nle BSI rerle J.7-».7 (SB) a,e, and Feedlnq behavior Has affected by synthetic zinc, chroulu, and aftS In that eore tlae dilution Has rtoulred for consunlnq eeasured water amounts of food. Feeding response Has Macek, et al(1970)t 4HIC-5510 Calrnst et al (1967),»M,IC- 9707 ------- Compound Field ri«td Organise: Study Location Toxlclty, ctlve Ingredient t Pp« Experimental Variables. Control led or Noted Comments Reference Zinc chloride (a Znl Leoomls •acrochlrus BS. L 3.3 (T%» > Zinc chloride (as Nltzsehia BS», Znl linear Is L .3 ITS) ae,«> and synthetic dilution water a»,e, and synthetic dilution water also affected by aeration, feedinq schedule, llqht Intensity, and outsld* disturbances. The authors note that much •ore work is needed to establish the reliability o1 this procedure. This study was conducted to Patrick, et determine th« relative toxlcltles ol 20 al (19S8), common constituents of Industrial Hastes AMIC-5770 to a fish, an alga, and an Invertebrate. The experiments Here conducted over a 10-year period for varied purposes. The authors recommend bloassavs with at least three components of the food »eb» sane as above Patrick, et al (H68), 4MIC-57ZO Zinc chloride (as Znl Physa BSft, heterostropna L 0.9S a,a, and synthetic dilution Water sane as above Patrick, et a I (19681, Zinc chloride Leblstes BCF retleulatus (1 mo, 1.1 cm! Zinc chloride Leblstes retleulatus (1 BO. 1.1 ee) BCF — 0.56 CTM a,C,d.e,f, Toxlclty thresholds and a n,q, ph03- dilution mixture threshold Here phates, calculated from fish bloassav data for carbon- zinc chloride and ootassiun cyanide. •tea, bi- Threshold concentrations for rlnc and Carbon- cyanide Mere found to be 0.33 and 0.736 fttes, sill- mo/I, resoectlvety. A orocedure for fates, and determining toxlclty threshold conduc- concentrations for mixtures of chemicals tanoe »as also presented. A zinc-cyanide dilution ratio for toxlcltv threshold (THn9) Has found to be a linear function of the concentration of the tno Ions taken separately, and therefore: THDR eouals 1 .?f>-0. 86CN-1.'2Zn. Based on a multlcoponent equation, mixtures ot zinc •nd cyanide exhibit an antagonistic •ffeet. This appears to be a significant advance In an approach to estimating safe concentrations for Hater pollutants. 1.0 (T 1.51 a,c,d,e,f, same as above Chen.et al (19691, »HIC-3»3i a,c,d,e,f, n»q» phos- phates, carbon- ates, bl- Chen, et al (19691, ANTC-3631 ------- carbon- ates, sul- fates, and conduc- tance Zinc Phormldlum amblguum 1.5-lO.t (NTEI — > M Zinc hyoT«Kyoulnon« Rasbora 8CFA hateromorpha and SS« 0.10 (TZ» a,C.e,f• hard (HWIor •oft (SHI synthetic dilution water, or seawater for some species Of 7V chemicals evaluated as •Iglcldest only 9 were more toxic than CuSOV. None Inhibited growth of mat-forming algae for more than 2 weeks. CuSOV formulated with certain wetting agents Mas more toxic than CuSO«AHIC" Zinc sodium citrate (as Znl Watersloora cueullata I larva) 33 IT t hrl ••Cflt and This study Mas conducted to salinity determine sovcles of marine larvae suitable for use in test screening antlfoullng chemicals. A. sallna (brine shrimnt appeared to have the best potential for this purpose. A. sallna larvae sensitivity Mas greatest starting at mge 20-ao hr, and tolerated relatively IOM pH (5.01. wisely, et at (1«6», Zinc sodlua citrate (as Zn) SPlrorbM lamellose (larvnel ••• IT Z hrl •tCtli and salinity same as above Mlsely al AMIC-5708 et ------- Compound Orqanls* Field Flald Study Location Toxlclty. »etl»e Ingredient, »»• Fxperlmental Variables, Control led or Noted Comments Reference vn ro Cine sodium citrate Buqula los Znl nerltlne (1erv»«l line ulfate(as Znl Acroneurla BSA Zinc suit ate (as Cphemerella BSA Znl Zinc «ulf>to let Hydroosyche BS Znl IT Z hrl a,c,I, and ••Unity son* e* above MIsely, et • I (19671. Zinc suit ate laveIs BSCF •aeroehlrus SZ (Tit) 16 (T10I 32 (Tilt 2.55 ISBI »«TC-S767 a,c,d,e,f Cphemerella (mayfly) Mas the most Marnich, at sensitive aquatic Insect of those studied, and copper the most broadly tonic metal. The authors suggest that aquatic Insects nay not be as sensitive to heavy metals as fish. a,e,d,e,f same as above Warnlefc, et al I19S9),»«IC- J767 MarnlcK, et .1(1969), »HIC-3767 a,c,d.e,f sae as above Zinc sol fate Zinc sulfate Sal ao Salao qalrdnerl BCF ~ BCF — 0.0056 (avoidance) a,c,d,a,f, Results of nonltorlnq fish Cairns, et r»»t brssthlnq frequency were orlnarlly al (19711, reoortml. The Indicated 7n concentration AMIC-3232 •as the lowest detectable. Reproduction and qroMth of blueallls Mere aooarently not Affected by 0.079 and 0.07? nq/l. «t a concentration of 0.?5 mq/l spawning HIS Inhibited and neMlyhatchrd fry Here killed. The authors suggest ways of lnorovlng this technique and suqqest simultaneous use xlth fish movement change (See Cairns and Waller, 1971). The threshold avoidance llHlt Mas Sprsgue essentially the same at 4.5 and 17.0 C. (196B), The value noted Is 0.01 of the lethal ANIC-3760 threshold concentration, according to the author. Improvements In the test procedure are described. ,c,f 0.56 (threshold a»,c,f toxlcltyl saaa as above Sorague (196S). AMIC-3760 Zinc sulfafe Plmephales BCFCM — 0.1$ (SBI a,c,d,a,t, Hatching was unaffected at the Brungs ------- preaeles II. 3-1.* 0) Zinc suitate > t line sulfate Zinc sulfate Xll •aculatus Ml Plaephales preaelas 1* MalnbOM trout I tftTC-2 eenad cell BS« — K.I ITI lc«d,e** f»a Zinc faiws copper, nickelI Salao I.9-1.I ITtl e,c,e save as above Tissue culture study using the Eagles MEM eedluH resulted In 71 percent reluct Ion In eltotlc Index and eytotoxtc cn«no.«s In cell «oro»»oloqY. Concentrations at I to 19.0 pp* tine had no significant effect. The trout cells were less sensitive than cultured cells of fathead alnnon. Rainbow trout were exposed to Brown, of al concentrations of fluctuating levels of 1199), aeeonla, phenol, and zinc and to constant ANIC-S993 •Ixtures of the three. Tests with fluctuating levels of toxicants showed that ICSO values were stellar to those for constant concentrations es lone es the periodicity of the fluctuation did not exceed the resistance tlee for the poison. Except when zinc oredonlnated In the •Ivtures, the fractional toxlcltles could be sueeed to give the toxlclty of the •Ixture. Rainbow trout were exposed to Brown.et al cooper, phenol, zinc, or nickel solution 11971), to determine M-hour ICSI values for AHIC-S99* •Ixtures of copper and phenoli copper, tine* and phenol I end cooper, sine, and nickel* It Mas concluded that acute lethal toxlcltles of the •Ixture* could ------- Field Field Compound 'Organism Study t»catlen Toxlclty, Active Ingredient, Ppm Experimental Variables. Controlled or Noted Consents Reference line (plus copper, phenol I tine Salmo galrdnerl BS« 0.&-?.«.« (T2t a.cte be adeouately described bv summations of the fractional toxlcltles. sane as above Broun,et al (1970), Coregonus FL Great Lakes 38(resldue) artedll - Superior, Michigan, and Erie line Zinc Zinc Zinc Zinc Coregonus FL elupeaforais Coregonus FL hoyl Prosoolua FL cyllndraceuei Salve!Inus FL naaaycush Caress1us FL auratux Great Lakes - Superior, Michigan, and Erie Great LaKes - Superior, Mlehloan, and Erie Great LaKes - Superior, Hlchlqan, and Erie Great Lakes - Superior, Hlchlqan, •nd Frle Great Lakes - Superior, Michigan, •nd Erie ?3lres!due> th(residue) 11(residue) ta(residue) 36lresldue) ~ Trace eleeent content of fish fro* Lakos Suoerlor, Michigan, and Erie Mas determined by activation analysis. Whole body and liver residues Here determined. Concentrations varied with species and lake. Other elements found • ere! antimony - 5 to 100 ppt>, barium - O.Z ppm, cesluit - 3 ppb, lanthanum - 1 to ?0 ppb, mercury - 10 aob, rhenium - O.f to 5 PCb. rubidium - 0.06 to 6 ppm, scandium - 2 ppb, selenium — 01 To 2 pob, silver - 0.001 ppb. same as above Lucas, (1970), »nic-s77» et al same as above same as above same as above saae as above Lucas, et al (19701, •MIC-3779 Lucas, at 11970). tMIC-3778 • I Lucas, et al 11970). AMIC-3778 Lucas, et al (19701, •MIC-3778 Lucas, et al (1970). •NXC-3778 Zlne Roecus FL Great Lakes 28(residue) saee as above Lucas at al ------- Zinc chrysoDS Coregenus FL clupeatormls VJ1 vn Zinc Zinc Zinc Zinc Zinc Zinc Zinc Coregonus FL elupeaformls Esox luclus FL Esau luelus FL Eox luclu FL Osaerus FL •ordax Peres FL flaveseens Parel abrax FN elathratus - Superior, Michigan, and frit Moos* Lake, i* (residue) Can. Lake Ontario* Can. Moos* Lake, Can. Lake St. Pierre, Can. 12 (residue) 19 (residue) 14 (residue) — Lake Frle, Can. Lake Erie, Can; Lake Erie, Can. Scattergood Steaa Plant, Los Angelas, Cat. 11 (residue! it (residue) 17 (residue) Z6 (dorsal auscla residue) Concentrations of 13 toxic eleoents In dressed fish fro* heavily industrialized and non-IndustrialIzed areas Here determined. Only aercury exceeded regulatory Halts, and concentrations of aost elements Her* essentially the saae In fish Iron both areas. saae as above sane as above saae as above saae as above saae as above saae as above Fish collected fro* an effluent Dloe of a steaa plant and froa offshore waters of Catnllna Island Mere analyzed for trace element content. Trace eleaent cottent of the ffluent xater Mas at least > tlaes greater than that of normal sea Mater for cadalum, copoer, nickel, zinc, and chroalua. Livers of fish froaj the effluent Here nearly t«lc« the size of those froa the ocean. Greatest differences In concentration occurred •Ith aluminum, cadmium, and nickel. Silver, barium, lithium, and lead showed the least differences. The author concluded that trace eleaent analysis of (1970), •H!C-37r« Othe, at •L11971), •MIC-3S14 Othe, et M.U971), •NIC-SSI? Uthe, et al (1971). «1IC- 3819 et al Uthe, C1971 3819 Uthe, at al 11971). MUC- 3819 Uthe, et al (19711, MIC- 3819 Uthe. et al (19M),»HIC- 3S19 Staolaton (1968). 4HIC-598B ------- Compound Zinc Zinc Zinc Zinc Zinc Zinc Zinc Zinc Zinc Zinc Organise; Paralabrax clathratus Paralabrax elathrafus Paralabrax clathratus Paralabrax clathratus Paralabrax clathratus Paralabrix clathratus (gravid feaates) Paral abrax clathratus Paral abrax clathratus Paralabrax elathratus Paral abrax clathratus Field Study FN FN FN FN FN FH FN FN FH FH Field location Catallna Island, Cal. Seattergood Steaa Plant, Los Angeles, Catal ina Island, Cal. Seattergood Steaa Plant, Los Angeles, Cal. Catallna Island, Cal. Catallna Island, Cal. Seattergood Sttaa Plant, Los Angeles, Cal. Catallna Island, Cal. Seattergood Steam Plant, Los Angeles, Cal. Cafallna Island. Cal. Toxielty. Active Ingredient. Pee 10 (dorsal •uscle residue) 1? (ventral •use 1 • residue) 9 (ventral •usele residue) 172 Igonads residue) 119 (gonads residua) Igonads residue) • 61 (liver residue) 100 (liver residue) Z?J (Integument residue) 190 1 Integument residue) Experimental Variables, Controlled or Noted CoMents tissues could be used to determine the effect of pollutants on Marine organism. — saee as above — same es above same as above saee as above — same es above — same es above ~ same as above ~ same as above — same es above same) as above Reference Stvolete* (1968), AHIC-5980 Staoleton ANIC-5980 Staoleton 11968), AHIC-S980 Staoleton 11968), AKTC-S980 Steoleton (1968), ANIC-S980 St»oleton (19681, ANIC-S980 Staoleton (1968), AHIC-5980 Staoleton (19681. AHIC-5988 Staoleton 11968), ANIC-S980 Staoleton ------- •MIC-59SO > Zinc Zinc Zinc Zinc Zinc Par a I abrax elathratu* Paratabrax et athratu* Paralabrax clsthratus Par at abrax clathratus Salao galrdnerl FN FN FH FH Scatterqood »? (heart Stcaa Plant* residua) Los Angeles, Cat. Cataltna Island* Cal< 98 (heart r as I dual Scatterqood 701 (eyeball Steae Plant• resIduel Los Angeles, Cat. Catatlna 6«« (eyeball IsIandt Cat. residual saae as above sane as above save as above saae as above Stapleton (1968), Staoleton (1968). »NIC-S9«0 Staoleton (198). ANIC-9990 Stapleton (1968), »HIC-59«0 •Sft — 1.99-9.19 (fluctuating cone, T !3%0-!96I Bin) a,c,d.e. Ralnbon trout were exposed to Brown, et al concentrations ot fluctuating levels of (1969), aaaonlHi phenol, and zinc and to constant AHIC-S99J alxtur«s of the three. Tests with fluctuating levels of toxicants showed that LC50 values were slallar to those for constant concentrations as lonq as the periodicity of the fluctuation did not exceed the resistance tlae for the poison. Except «hen 2lne predominated In the alxturesf the fractional toxlcltles could be sunned to 9lve the toxlelty of the alxture. Zinc Zinc Salvo oalrdnerl Salao qalrdner! 8S« — 3.9 IT a In) a,c»,d,a, t.a save as above BroMn, at al 119691, •NIC-9993 ITZI ZnSO* . t 01 US I THZt (as Zn Lepoals aaerochlrus and CF a,Cte PalnbOH trout were exposed to Brown, at at cooper, phenol, zinc, or nickel solutions (19701. to determine da-hour LC90 values for AHIC-999* alxturei of coooer and phenol I cooper, zinc, and phenolt and eoooer, zinc, and nickel. It Mas concluded that acute lethal toxlcltles of the Mixtures could be adequately descrlb« ------- Compound Organism Field Field Study Location Toxlclty, Active Ingredient* Pp« Exotrl»«ntl Variables. Controlled or Noted Comments Reference ZnSOt . 7H20 2 plus) las Zn vn OO ZnSOt . 7HZO (as Zn ? olus) Zn, Ml Cr, CH, Cu, and Zn Notemlgonus crysoleueas Carasslus auratus Catostonus commersonl 8S» — BSA 7.5 Igan BSACF Grand River betiieen IHL» at 1.25-3.75 Mypalng.Hlch percent IT3» Igan a,c,d,e,t, r,t a,c,d,e,r, r,t lOHest detectable concentration causing significant movement changes. Values for qolden shiners and goldfish nere obtained In preliminary studies. At 1/10 the Indicated concentration, gronth end reoroduetlon of bluet) 11 Is Here Significantly affected but not at 1/100 dilution. Considerable discussion and additional data are presented. same as above saae as above Cairns, et el 11971. a,c,a, con- A mobile bloassay unit Mas ductlvity, utilized to conduct this study of Hl,Cu,Cr, municipal MasteHater containing the CH, and Zn Indicated toxicants. River Hater •• used as diluent. The conclusion Mas reached that synerglstlc or additive toxic vffects occurred since toxlcltv Mas greater than that e» any ol the Ions singly. Cairns, et 119711, ANIC-3231 Zllllch (19691 , AHIC-?906 a.c.s, con- ductivity, Hi.Cu.Cr, CH, and Zn sane as above al Zllllch (19691, AHIC-Z906 l,l--methylenedl-2- Ptyehochellus USA ~ napbthol oregonensls 171 ••) 0.8B6-0.815 IK 6-31 hrt The chemical studied Mas found to MacPhee, et and be selectively lethal to soua«flsh at conduo- concentrations 3 to 100 times more toxic tlvity to th»se species than to salmonids. Potency varied positively Hlth concentration and temperature. Concentrations cited are for 10-U C. A sheep and ducks showed no ill effects over a 7-day period Mhen forced to drink. Mater containing in ppm of the naphthol. A field application In a small lagoon containing several species of fish resulted only in kill of P. oregonensls. This chemical appears to be an effect Iva Ptsclclde that Is selective tor squanfish. al «19691,AHIC- 551 ------- vn nephthol 1. l"-»«thy lenedl-?- naphthol ltl"-«ethylenedl-?- naphthol l,l"-e>ethylenedl-2- naphthol l,l"-athylenedI-Z- naphthol 1,2 dleMoroprooane Ptychochellus 8S« IMDQliae 158 mi) Salvellnus BS« fontlnalls 191 ••) Oncerhynchus BS» tshawvtseha 18* ••) Oncorhynchus BS» klsutch M) Salao qcl M) Crsngon crsngon (66 BSI 8.01-0.03IK 6-ZO hr) 0.3 (SB> (.1 ISBd) 8.6-t.JISB»> 0.6-1.3 ISBkl BSA ~ than 180 (TZ> a'.c.d.l, and conduc- tivity a.c(d«rt and conduc- tivity and conduc- tivity •••e«dtf • and conduc- tivity atc«dt ft and conduc- tivity a«( contin- uous aer- ation, sea- water, and dally solution renewal) sane as above sea as above ••• as above seae as above saae as above heet et al ll<6«>« »HIC-5I.50 HacPhee, at al tl<>6«>. •HIC-5«,50 HacPhee. t al f 19691. »HIC-5«.50 at al I1969I,»HIC- 550 NacPheet et al (1969), »HIC-5<,50 t — 0.9-10.0 IMTF) — ro-l,-••than anblguua t.»t»»t»a-tatrahydro -5,e-naohth«Qulnoo« One hundred-forty surface active solvent emulilflers, pestleldest polychlorlnated blphenyls, oure Inorqtnlc, and organic chemicals Mere evaluated against as many as ten marina organises. The authors noted that »ost published data of this tyoe deal with toxlclty of chealcals to freshwater organisms. Of 71, chemicals evaluated as alglcldes, only 9 were more toxic than CuSTt. None Inhibited growth of •at-foralnq algae for more than ? weeks. CuSOU formulated with certain wetting agents was more toxic than CuSOfc alone. Coooer chlorarln* was also found to be more toxic than CuSOt. No wetting agents were found to be Inhibitory at the concentrations Investigated (0.05 and 0.005 com). Also reoorted are factors affecting growth of algae In canals to determine whether there were leads to controlling algae by envlronaental manegement. No practical envlronaental aeans were found. Porteann, al (1971) •NIC-7701 et Otto 11978), »HIC-»9Z ------- Compound Organise) Field Field Study location Toxlclty. Active Ingredient, Exoerlmental Variables, Controlled or Noted Cements Reference Z-a«lno-3-eMoro-l,* Phoraldlua -nephtheouInane eablguu* 0.-iO.OI16oer cent growth Inhibited 1M t-ehloro-.i-bls lethyl««lne> S-trlazlne •normldlua •eblouuti 1.5-10.0 tNTE) <-dlmethyt-aalno-l, Pnoraldlua -naohtheoulnone •ablauu* 0.9-10.OU&oer cent growth Inhibited Ul Dt 71, chemicals evaluated as Otto (1970)* •lalcldest only 9 Here nore toxic than AHIC-89Z CuSOd. Non« Inhibited qronth of •at-formlng algae lor more than ? weeks. CuSOt formula ted with certain Netting aqents Mas more toxic than Cu50t alone. Cooper chloramlne Mas also found to be •ore toxic than CuSOfc. No wettlnq aqents Mere found to be Inhibitory at the concentrations Investigated (0.05 and O.OQ* DOM). Also reoorted are factors allotting growth of algae In canals to determine whether there Mere leads to controlling alcne by environmental •antqerent. No practical environmental •evns Here found. Of T<» chemicals evaluated as Otto (1970), •tqlcldes, only 9 Here nore toxic than ANXC-842 CuSOt. None Inhibited growth of •at-forInq algae for more than 2 Meeks. CuSOJ. formulated nlth certain xettlnq aqents Mas «or« toxic than CuSOU alone. Coooer chloravlne Has also found to be •ore toxic than CuSO<«. No Netting agents Mere found to be Inhibitory at the concentrations Investigated (II. OS and 0.00$ DP), llso reoorted are factors affecting growth of algae In canals to determine Mhether there Mere leads to controlling algae by environmental •anagevent. No practical environmental means Mere found* Of 71. chemicals evaluated as Otto alqlcldest only 9 Mere more toxic than »HIC-89? CuSOt. None Inhibited qroHth of mat-foraing algae for more than ? meeks. CuSO* formulated Mlth certain netting agents Mas more toxic than CuSO* alone. Coooer chtoranlne Mas also found to be •ore toxic th»n CuSO<>. NO wetting agent* •ere found to be Inhibitory at the concentrations investigated tO.05 and O.tlS »o»). Also reoorted ere factors ------- t-Hereaotedlethyl succlnato Plveohales proa* In 35. • (Ul g-oreeenai faereleln) Phormldlu* aablguum L — 1.9-10.8 166 percent gromth Inhibited !«.» ?-preo«n«-l-ol tallyl alcoholl PhormldlUB •mblguum r-tert-butylamlno ffiorvidlue) ^-ethyl-amlno amblguum t-methyl S-trlazlne I — • _,.^ 0.5-10.8 116 oereent growth Inhibited 114.) V.5-10.0 «** percent growth Inhibited 1» affecting growth ot algae In canal to determine whether thr «»r« leads to controlling alga* by environmental aanaqeacnt. No oractical environmental •eans Her* tound. a* chemicals evaluated as alqlclOeSt only 9 MT more toxic than CuSOt. None Inhibited growth of aat-foralnq algae tor More than f HOCKS. CuSO". foreulated with certain wetting aqents was nore toxic than CuSOt alon. Coooer chloraelne Has also found to be •or toxic than CuSOt. No netting agents •ere found to be Inhibitory at the concentrations Investigated 11.05 and 0.005 noiil. »lso reported are factors aftectlno growth of alga* in canals to deternine whether there Here leads To controlling algae by environmental aanaqeaent. No practical environmental •eans were found. — same as above Bender (19641, •HIC-3707 Otto (19701. •HXC-vtt Otto (14701, •NIC-09Z Of Tfc chemicals evaluated as alglcldes, only 9 Here more toxic than CuSOi.. None Inhibited growth of aat-forming algae for more than Z Heeds. CulO* formulated with certain netting agents Has more toxic than CuVJt alone. Coooer cMor»«\|n« Mas also found to be •ore toxic than CuSOfc. No wetting agents Here tound to be Inhibitory at the concentrations Investigated (0.05 and 0.405 opmt. Also reported are factors affecting growth of algae In canals to determine whether there Here leads to controlling algae by environmental •anagement. No .practical environmental Otto (1970), ANIC-89Z ------- Ceewound Organise Field Field Study Location Toxlclty, Active Ingredient, Ppa Experimental Variables, Control led or Noted Comments Reference Z.3-dtcMoro-l,» Phoraidlua L — Mphthftq"""! amblguu* 0.5-10.0 (NTE> -- i •cans Here found. Of 7i» chemicals evaluated as algtcldes, only 9 were more toxic than CuSO".. None Inhibited growth of •at-formlng algae for more than Z weeks. CuSOd formulated with certain wettlnq agents was more toxic than CuSO* alone. Cooo«r cMorawlne was also found to be nore toxic than CuSOii. No wetting agents •ere found to be Inhibitory at the concentrations Investigated 10.OS and 0.005 DDF). Also reported are factors affecting growth of algae in canals to determine whether there were leads to controlling algae by environmental •anagerent. No practical environmental weans Here found. Otto (19701. AHIC-B9? Xt-0 (acid) Gaanarus feselatus BS — 3.7 IT?) ft»-0 facldl <«%-O (add) >t%-0 IBEEJ Oaphnla «a Of the aquatic weed herbicides Sanders evaluatedt Die I one Mas the vest toxic, (19781, Oaohnla DCS generally the ost sensitive »HIC-SS orqanlsas. All of the Crustacea Here affected by much lower concentration levels of herbicides than Indicated by, the TL sub 50 values. All of the anlaals represent Important food chain links. sane as above saae as above saae as above Sanders 119701. AHIC- •.53 Sanders 11970). AHIC-WJ Sanders (19701, A1IC- (BECI Paleonontas BS* HadlaHensls Asellus BS* br««leudu« IT2) IT2I saae as above saae as above Sanders (19701. ANIC-4.5J Sanders (19701, ------- ?,»-0 IBEEI Orconectes BSA nail greater than 100.0 JTII as abov AMIC-tS] Sanders IBEEI «t%-0 IBEEI Z»-0 IBEEI t,-0 ftasbor* Ibutoxyethylester) heteromorpha and BSA Oaohnla maqna BS» — Cvorldopsls BSA vldua lepomls BSA aacrochlrus 9.6 1.1 t.t ITZ1 lei ay bascdl Kasbora BCM httaroaerorta and BS» ITII hard (HH) or soft ISM) synthetic dilution ••tor, or se»H»ter for sone toecles ••tCte.f . hsrd(HHt or soft synthetic dilution ••ter, or seMter for so«e •DOC I a* ttk-D ldla«thvlaatn« Cra««str«a L •altI vlrglnlea IT2I Sanders I19»«1. INIC-VS3 Sanders 119701. HIC-»5J Sanders 11901, saa as abov* <••• as above «••• as abov* One hundred sixty-four Alabaster pesticides, netting agents* and 119691. •Iscet lereous neter pollutants shewed a AHtC—9%K nlde range of toxlclty spanning li orders of magnitude. KnoHlng the toxlclty and Percentage of all components of a formulation did not result In easy Predictability of the toxlelty of a mixture of materials. Sometimes pesticides nere aost tonic In hard natar •nd sonatinas the opposite Mas true. Testing the actual aaterlal as sold »as found to be essential. save as above Alabaster I1969I.AHIC- The effect of 52 pesticides on embryonic development of clans and oysters Mas reported. Synerglstlc effects with solvents Here also reported. Host of the compounds affected development more than survival. Some. however, drastically reduced larval qronth. The authors point out the necessity of evaluating the affects of Oavls. etal 119691. AHIC-S990 ------- Coaoound Organise Field FUld Study Location Toxlclty, Active Ingredient. POB Exoerlaental Variables. Controlled or Noted Convents Rotoronce (dlaethyl*lne Cr»ssostrea L ••Itl vlrglnlca flervaet Z.fc-0 (dleethrlaalne Caevaru •altt feiclatus BSA — 6».S ITU) greater thanllt.O (T2I pesticides on all life stages of an organ Is* and note the possibility of selecting chealcats for oest control that Mould not have serious effect on Shellfish. saae as above Oevls. et al 114691. ANIC-9990 Of the aquatic need herbicides Sanders evefuatedf Olelone M»S the aost toxic. 119701. Oeohnlt nas generally the east sensitive »HJC-53 organism. All of the Crustacea were affected by uch loner concentration levels of herbicides than Indicated by the TL sub SO values. All of the anlaals reoresent Important food chain links. ,»-D (dlaethylealne Paleoaontes US seltl MdlaHensls Z.V-0 Idlwathylanlne Astllus BS» salt I ' brevlcaudus »,»-0 Idlaethylaalne Orconectes BS» saltl nals greaterthan 101.• tTtl greater than greater than lit.I ITZ) saae as above saee a* above saae as above Senders (11TO), Senders (19701. Senders (19701, Z.-0 ••Itl Z,»-0 ••Ml Idlaethylaalne Daohnla aagna 8S» — fdleethylaalne CyorldoosU BS» vldua ••.0 •.0 IT2I saae as above saae as above Senders (14701. AHIC-W1 Sanders 119701 ,»1IC- fdl«ethyl»«lie lapoals BS« aacrochlrus ••Itl Z,%-0 (ester! Crassostraa L vlrglnlea leoesl greater than 110.I IT2I t.O IT2I saae as above saaa as above Sanders 119701. AMIC-1,53 Davis, et al (1969t,AMIC- ------- 8,»-0 fester) Crassostrea L vlrolnlca tlervael 2t-0 INa salt ftasbora 8CF» heteroeorpha and es* i.r* IMVI 1.11 (Til t,»-D (PGDC) Gaaaaru fesclatus 8S* — ».« ITZtt 2.S ITM 5999 saae as above Davis, et al (1969>.»MIC- 5990 e«c ------- 0\ Toxlclty, Cxoerlmental Active Variables, Field Field Ingredient, Controlled Comoound Organism Study Location pom or Noted Comments ?,»-0 fresln basedl Rasbora BCFA — heteromoroha and BSA Z,t-0 fresln based) Sal mo BCFA — galrdnerl and BSA Z,,-0 Fish «not « — specif led) 2,lt-D Wolffla L papullfera 2««tO (T2) a,c,e,f. hard(HH) or soft (SHI synthetic dilution nater, or seaxater for same soecies 1,920 IT2) a'.e.e.f. hard (HW)or soft (SW) synthetic dilution Hater, or seaxater for some species greater than — 0.1-1.0 (K) 1000 (K) Hunter's- raediun diluted 1:5 One hundred sixty-four oestlcldes, xettlnq qqents, and miscellaneous Hater pollutants shoxed a Hide range of toxiclty spanning IZ orders of mqnltude. Knonlnq the toxlclty and percentaqe of all components of a formulation did not result in easy predictability of the toxlclty of a mixture of materials. Sometimes pesticides Here most toxic In hard Hater and sometimes the opposite Has true. Testing the actual material as sold Has found to be essential. same as above Approximate toxlcltles of numerous pesticides commonly used In Britain Here summarized. An excellent brief, general discussion of toxlclty testing Is also present. All compounds were harmful to duckweed to some degree. Decreased populations were, noted at non-lethal concentrations nnd some compounds (Malathlon and 2,k->) caused teratogenlc effects at concentrations as low as 1 pp», Reference AHIC-I.S3 Alabaster •19691, ANIC- 525 Alabaster (1969), AMIC-5%2S Haxdesley- Thomas (19711.AHIC- 1056 Worthier, at al (1971). AKIC-3233 t dlnlfroohenol Neqaorion BSA brevirostrls 10 (NTE 3 nrl a.c.e «t»,5-T Ibutoxyethylesterl Rasbora 8CFA heteroeorpha and •SA 1.0 (TZ» a,c.e,f, hard (HH) •r left Data fro study of druq effects Baldrldq* on young Ienon'sharks Here treated (19691, Mathematically to demonstrate AMIC-3832 aoDllcablllty of classical rate theory To the study of chemical shark deterrents. Incaoacltatlon (narcosis) Has the or!aery parameter timed for effectiveness. This Has usually quite rapid for the aore effective drugs. One hundred sixty-four alabaster pesticides* netting agents, and (19691t Miscellaneous na.ter pollutants shoved • ANIC-54Z* ------- Fish (not specified) Z'-broao-l-nltrosall Salao eylanltlde galrdnarl BS» — greater than 8.1-1.1 IK» 1.8 IK I hrl 8"-bro»o-3-n I trosa 11 Carass tin cylanlllde auratus Z"-»ro»io-3-nltrosall Cvorlnus cylanlllde carolo ?"-bro>o-3-nltre«ell Plmephales cylanlllde proaelas Z'-broao-S-nltrosall Ictalurus cylanlllde Betas Z~-bro«o-3-nltrosell leooals cylanlllde eyenellvs BS» — as — BS» as* — as* ?"-bro»o-3-nltrosaII Leooals BSA cylanlllde aacroehlrus Z"-broao-3-nltrosall Perca 8SA cylanlllde flavescens - Salao BSA — oelrdnerl 3-nitro»«llcyl- anillde 10 (Kit 1.8 IKt) 1.0 IK S Iwl t.O IK1I 10 IK 3 hrl 10 IK 3hr) 1.0 IK1) 1.0 IK 3 hrl ISUt wld* pang* of toxlclty ioannlnq 12 orders synthetic of «aqnltud«. Knowing the toxlclty and dilution ore<«nt»q« of all co«Don«nts of a ••tp, or fopulatlon did not result In easy seaiiater predictability of the toxlclty of a for soa Mixture of materials. Sonetlnes species pesticides Mere »ost toxic In hard Hater and soaetlnes the ooooslt* Has true. Testing the actual Material as sold was found to be essential. — Approximate toxlclties of W»wdeiley- numePous pesticides eoaaonly used In Thoas Britain were summarized. An excellent H9ri»,»«IC- bPlef, general discussion of toxlclty 1056 testlnq Is also present. •• Twenty-nine nltrosal Icylant I Ides Markinq,t and related coaoounds Here evaluated for at 11970)* their relative toxic effect to selected ANTC-63tl fish. Potency varied with type and position of substitutions. Several compounds were selectively toxic to yellow perch. Goldfish Her* the aost resistant to the sallcy tanllldes. a* «••• as above Narhlnq, •tal 114701 • •HIC-6391 •farhlnq.at al (1470). AHIC-6341 Herkinq.et al 119701. AM.IC-6391 Narklnq, •tal 119701* •HIC-6391 Narhlnq.et al 119701* AHIC-6391 Harfclnq.et • I 119701* •HIC-6341 a» saae as above saae as above saae as above saae as above saae as above saae as above saae as above • fat 119701. AHIC-6391 Narhlnq. et • I (19701, ANIC-a391 ------- Compound Toxlclty, experimental ctlve Variables, Field Field Ingredient Controlled Study Location Ppa or Noted Convents Reference ?"-eMoro-i>"-»«thyl- Carasslus BS* — 3-nltrosallcyl- , auratus anlllde ?"-ehloro-«i"-»ethyl- Cyprlnus BS* — 3-nltrosallcyl- carpio anllide Z"-cMoro-~-»tnyl- Plnephales BS* — 3-nltroaalierl- prowela* anllide f~-cnloro-~-«ethyl- Ictalurus BS — 3-nltrostllcyl- •»I as •nillde ?"-ehloro-"-««thyl- Lepoalc 8S» — 3-nltro»«llcyl- cyan I l\is anlllda "-ehlor»-»"-»«thyl- Lapoals BS» — 3-nltrosallerl- ••croehlrus •nllida ?"-chloro-«i"-»«thyl- Perca BS — 3-nltroMlleyl- tlavescan* •nlllda "-ehloro-«»"-nltro-3 Salao BS» —• -nllrosalleylanlllde qalrdnarl «"-ehloro-»"-nltro-J Carassl«n BS -nltrosalIcylanllld» auratus J"-ehloro-"-t»ltro-3 Cvorlnus BSA -nltrosallcylantlId carpio J--chloro-"-nltro-S Plaepltalas BSA ~ -nltrosalleylanlllde croaalas 1.0 (K 3 hrl 1.9 IK1I 1.0 IK1I 1.0 IK1I t.O IKtl 1.0 (Kit 1.0 fKll 1.0 IK 3 lw> 1.0 IK1I 1.0 1.0 fKll sea as above saae as above sae as above saae as above saae as above sane as above saae as above saae as above save a above saae as above aae as above Harking, t al 114701. •NIC-6391 Marking, at al (11791. Harking, t al (1970), •HIC-6391 Harking, at al (19701, ANIC-6391 Harking, at al 119701 , •HIC-6391 Harklnq, t al (19701, Harking, et al (19701, AHIC-6391 Harking, et al (19701, kHIC-6391 Harking, et al (1970). •NIC-6391 Narking, et al (1970). AHTC-6391 Narking, at al 11970). NIC-63«1 Ictalurw BS* ~ 1.0 CR 3 hr\| saae as above Narking, at ------- -nltrosallcylanllId* a* I as F-eh>lero-»-nltro-3 lepoals -nltrentlcvlanllld* cyan* 11 us l--ehloro-»"-nItro-3 Lcooals -nltrosalleylanllld* •aerochlrus •"-€hloro-»~-nltro-3 P«re» •nltracalleylantlIda (lav*cns f"-ehlor-S-nltro •tliejrUaiilde 8"-ehIoro--nlfro «"-•»! OPO-«-l»ltP« •alleylanllid J"-cMoro-5-nitro •alloylwtllld* r-chlr»-»-i»ltr« Mllejrlanlllde 8"-eh1ore-»-nitre aallcjlanlllda ?"-eM ore-5-oI fro 8"-ehlor«-»-nlfro •Blleylmnlllda r-.lodo-3-nltra Sclao aalrdnr\| Car»«slu« auratux earole Pt«Dhals preaf»* Ictaturu* Ivpoals cyahellus Lcpoal* •acrechlrus Prea flav«en« Salae qalrdnrl •s* — BS» ~ BS* — as* BS» — BS» BSA — BS« — BS« — (K2I l.t (Kit i.n 1.1 IK 3 hr» a» 10 IKtl 10 IK 3 hrl a* 10 IK 3 hr) a* 1.0 (KZI 10 IK 3 hrl • 10 IK 3 hr) »• 10 IK 3 hr) a l.OIK 3 hr) a* sa«* as abov* <•• as abov ••• as abov saw* as abov* San* as ataov* ••a* as abov* saa* as abov* aa as abov* ••• as abova saa as abov* saa* as abov* saa* as abov* •I 11970). 4MIC-6391 Marking. t • I 11970). AMIC-6391 Harklnq. t • I (1970). IHIC-6391 Marking, t • I (19701, AHIO6391 Marking. t • I (19/0). »NIC-J9l Carklng. t • I (1970). IHIC-6391 Harking. t • I (1970). «NIC>6391 Narking, at al (1970), AHIC-6391 Marking. t al 11970), Harking, at al (1970). »HTC-6391 Marking, t al (1970), (HIC-6391 Narking, t al (1970), ANIC-6391 Harking, t al (1970). ANIC-6391 f-lade-3-nltr CarassIus BSA — 10 IK1) saa* as abov* Narking, ------- Field Field Coaoound Organise Study Location Mllcylinillde auratus l"-ldo-3-nltrosallc Cyorlnus BS» — ylanlllde carplo t"-lodo-3-nltrosalle Plnephates BS» — ylanlllde proe1as f-lodo-3-nItrosallc Ictalurus BS» — ylanlllde metes Jr- Z--lodo-3-nltrosallc Leoonls BS» ~ —4 vlanlllde cyanellus O Z"-lodo-3-nltrosalIc Leponls BS. — ylanlllde nacroehlrus Z"-Iodo-3-nltrosallc Perca BS» — ylanlllde flavescans l"-aethOKy-~-«ltro- Salao SS» — 3-nltrosaJ.lcyl- galrdnrrl •nUlde Z"-netbo»y-l»"-nltro- Carasslus BS» — 3-nltroaalicyl- auratus anlllde ?"-aathoxy-li"-nltro- Cyorlnus OS* — 3-nltrosalloTl- earplo oaUlde Z"-«ethoxy-»"-nItro- Plneohales BS« ~ 3-nltroaalicyl- prone las anlllde 2"-»«thoxy-"-nltro- Ictalurus BS» — 3-nltro»«llcyl- nelas anil Ida Toxlelty, Expcrlaental Active Variables, Ingredient, Controlled Poa or Noted 1.0 tKll •• 1.0 IK1I a> 10 (Kl) a 10 (K 3 hr) a* 10 IK 3 hrl a* 1.0 IK1I a* 10 IK 3 hr) a* 10 (Kl) a* 10 (Kl) a* 10 (Kll a* 10 (Kl) a* Conaents sane as above save as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above sane as above saae as above Reference «ral (1970), Marking, et al (1970), »MIC-6391 Marking, et al (1970), »HIC-6391 Marking, etal (1970). MIC-639t MarHInq,et al (1970), MTC-6391 Marking, et al (1970), Marking, et al (1970), »HIC-»>391 Marking, et al (1970), Marking, et al (1970), 4MIC-6391 Marking, et al (1970), AMIC-6391 Marking, et al (1970), »MIC-639l Marking, et al (1970). AMIC-6391 ------- 8"-«athoiiv-"-nltro- 3-nlirosftllcyl- crane ttus aollide es» — 3-altroMllcrl- anllide Leooals BS •aeroehlrus "-««thoiev-"-r«ltre>- P«rc» 3-nltrosallcyl- flaveseam* anlllda - Sala« nltroaalicylanlllde qalrdncrl f-.»"-dl«etnyl-3- Carasslira nltrosaJ.leylanU.lde auratus r.~-dl»«thvi-s- Cvorinus carol o , nltro»«lloyl«Jilll ------- CoMound t-tV-dlbr oo-3- nitroaaliejaanllida ~,--dIbr oo-3- nltroaallorlanillde J-.V-dlbr oao-3- al troaal loylanU. Ide e",S"-dlbr oo-S- nltroaaaicylenllld 8", V-dl or oo-l- nltroaalleylanllid «-,S--dlbr oo-S- nitroaallcylanilld ",S"-dlethoxv-»"- ohloro-3-nltrosa- l-,5"-dl«thox»-"- obloro-3-ni troaa- llcylanillda ofiloro-3-nl troaa- chloro-3-4U.trosa- lloyluillld* chlOTO-3-Altroaa- llvflanliid* Z-,5--dl*thox»-»-- cerelo P^:.?:," tetelurus •alas Leoovls crenel I us Lepoats •acrochlrus Perca flevescens Sal no Carasslus auratus Cvorlnus carpi o proa las Ictalurus ••fas Leooais Toxlclty, •ctlve Field Field Ingredient. Study Location Pe* as* — i.o i«t as* — 1.1 IKII as* — 1.1 tKii as* — i.o IKII as* — 10IK 3 hrl BS» — 1.0 IK S hrl BS* — 1.0 IK 3 hrl as* — i.t iKti BS* — 1.0 IK2I as* — i.o IKII as* — i.o IKII as* — i.o IK;I Experimental Controlled or Noted Comments a* so** as above a* seme as above a* seme as above • seme as above a same as above a* saae •» above a* saae as ebove a* saae as above a* saae as above a* same as above »• same as above a* seme- as above Reference Narklnq.et al (1970), •MIC-6391 Nerklnq. et al (19701, •H1C-6391 Narklnq, et al (19?OI, AHIC-6391 al 119701, Harking, et al (1970). AMIC-6391 Nerklnq, et al <1«70). »HIC-6391 Harking, et el (1970), AHIC-6391 Harking, et al (1970), •MIC-6391 Harking, et al (197D), AHIC-6391 Harklnq, et al (1970). «HIC-6391 Harking, et al (1970), AHIC-6391 Narking, et ------- •blaro-3-altvoM- cywwllu* aioylamllldo Z",S~-dI»othoxy-V- Loo«Is • c6loro-3-nltro«B>- ••crecMru • I f-,--dlB»thoicr-»-- P«re» eUaro-3-altroM- flavaseon f«,»"-dlothyl-l,S-dl Saleio nltrobanzanllld* salrdnerl 'f",«,"-dl>th»l-3.»-dl Carasslws nltrobnzanllld* auratus f,«"- it INTCI INTCt It INTE) it INTCI It INTCI It INTEI tt INTO It nl tr«b«nxan\| 1 1 d« f I •««sc.«n« h«rd(HM) or soft (SHI synthetic dilution •otor. or ««M»t«r for •«•• »»« • bev ••• •« »bov« »bov« •* «bov« •* •be«« •* bow« • »bov« •••• •* cbov* cbev* abev* On* hundred sixty-four pesticides, wetting agents, and •Iscellaneous »at«r oollutants sho«od • Hid* range of toxlclty scanning H orders of •aqrltud. Knotting the toxlclty and percentage of all coaoonents of a formulation did not result In easy predictability of the toxlclty of a •Ixture of aaterlals. Sonetlaes pesticides nor aost toxic In hard natr •nd «o»tla«s th* opposlta was true. (••rklnq. «t • I (19781, Marking, »t • I C1970), »HIC-%391 Nark I no, «t • I (19701. AMIC-6391 H«rklnq. «t • I (197ttt •HTC-6391 . «t • I (19701. NtC-6391 N.rklng. t • I (19701. Marking, t al (1970). ANIC-6391 Narking, t •I 11970). •NTC-6391 Marking, t al (19781, mc-639i Marking, et • I (1970). AH1C-6391 Alabaster (1969>.A«tC- »»2» ------- Compound 3 1 p-ch 1 oropheny 1 1 Organism Phormldlum Field Field Study Location L Toxlclty, Active Inqredlentt 0.5-10.0 INTO Experimental Variables, Controlled or Noted species Comments R«f >r«nc« Of 7 it chemical* evaluated as Otto (197< -J fr 3,»-dlchlorobenzyl •ethyl carbamate Phormldlum ambiguua 3»-dIhydroxybenzolc Phormldlum acid (protocatechulc amhlguum acldl 3t«5-trlhydroxy benzole acid (gallic ftcld) Phormldlue amblguum L — 0.5-11.0(16 percent growth Inhibited !"•) 0.5-10.0(50 percent growth Inhibited 1) 0.9-10.0 IMTEt — 3t5-dlbreno--hy Phoreldlu* ••bIquue t — 0.5-lO.i INTE) ~ CuSOl,. None Inhibited growth of mat-forming aloae for more than ? weeks. CuSOt* formulated with certain wetting agents was more toxic than CuSOi* alone. Coooer cMoraiMne was also found to be more toxic than CuS1. None inhibited growth of •at-formlno algae for more than 2 weeks. CuSO<> formulated with certain wetting agents was more toxic than CuSOi, alone. Cooo»r chloraolne was also found to be nore toxic than Cu50it. No wetting agents were found to be Inhibitory at the concentrations Investigated (O.OS and 0.005 ppn). Also reoorted are factors affecting growth of alqae In canals to determine whether there were leads to controlling algae by environmental •anaqevent. No practical environmental •cans were found. Of 7«, chemicals evaluated as Otto (1970), alglcldest only 9 Here aore toxic than ANIC-892 ------- J,5-dllodo--hydroxy Phormldlum droxybansonitrlls amblguu 3,5-«fImethyltetrahyd Phormldlum hydro 1,35,2- amblguum 3.9,7-trfaza-l-azonl Phormldlum; Mania •jdaiaantane amMguum 3™-bromo-3-nltrosall Sal no cylanlllde galrdnerl 3"-bPomo-3-nltrosall Carasslus eylanltide auratus L — BS« — BS» 0.5-10.0 «NTEI — n.5-tn.o (16pPCnt Inhibited 11 0.9-10.0 (NTEI -- 1.0 IK 3 hr> a» 10 IX 3 hr» CuSOt. None Inhibited gpOMth of mat-forming al<;ae IOP mart than 2 Hecks. CuSO(» formulated Mlth ceptaln Mettlnq aqcnts was morr toxic than CuSOfc alone. Cooo«r chlopanlne Has also found to be •ore toxic than Cu^flfc. No netting agents wep found to be Inhibitory at the concentrations Investigated (0.05 and 0.105 com). Also reoopted ape factors affecting growth of alqae In cranats to detepmlne whether there Here leads to controlling algae by environmental management. No practical environmental •cans Her* found. same as above same as above same as above Otto (1970), •MIC-89Z Otto (1970). AHIC-89? Otto (1970). THenty-nlne nltrosalIcylanllldes HarKlng.et and related compounds Here evaluated for al (1470). their relative toxic effect to selected AHIC-6391 fish. Potency varied with type and position of substitutions. Several compounds Here selecttvely toxic to yelloH perch. Goldfish Here the most resistant to the s»IIcylanllldes. same as above Mark\|i-iq,et al <1970), •NIC-4391 3"-bromo-J-nitros»ll Cyprlnus cytanltld* carol a S"-bromo-3-nlfrosal\| evlanllld* cylanilld* Ictalurus ««las 3--bPO«o-J-nltPO«ll L«DOls eylanllld eyancllu* 3"-broeo-3-nltrosall tepomls cylanlllde maeroehlrus BS» — BS» — BS« ~ BS» — 1.0 IK1) 1.0 IK 3 hp) 1.0 IK 3 hrt 10 IK 3 hP> 1.0 IKlt same as above same as above same as above same as above same as above Harking, etal (1970). • MIC-6J ------- Ceajoound 3"-bro«o-3-nttrosal 1 cylanl lid* 3"-enlore-S-nltreben zanlllde 3"-ch 1 or o-S-n I trobtn zanlllde 3"-cMoro-3-nItroben zanllltfe 3"-chloro-3-nltroben zanllld* 3"-ch 1 oro- 3-n 1 t r oben zenlllde 3"-eh t oro- 3-n 1 troben zenltlde 3"-cM or o-3-nl troben zanitlde 3"-chloro-5-nltro 3"-eM oro-5-nI fro sallcylanllldo 3"-cn 1 oro-5-nl tro •alieylanllldo Field Field Organise) Study Location Perca BS* — flavescens Carasslus BSA — - auratu* Cyprlnus BS* — - carplo Plaephates BS* — Ictalurus BS* — aelas leooals BS* — cyanellus lepoals BS* ~ aaerochlrus Perca BS* — f laveseens Sal 0)0 BS* — gelrdnerl Carasslus BS* ~ auratus Cyorlnus BS* carplo Toxiclty, Exoerlaental Active Variables. Ingredient, Controlled Ppa or Noted t.O IK 3 nr) a* 10 IK 3 hr) a* 10 IK 3 hr) a* 10 IK 3 nr-) a» 10 IK1) a* 10 IK S hr) a* 10 IK1I a« 10 IK 3 hr) a* 1.0 IK,) a> 10 IK1) a 10 IK 3 hr) a* Consents saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saae as above saa* as above Reference AHIC-6391 Harking, et al (19701, AHIC-5391 Marklno. et al (1970), Harking, et al (1970), AHIC-6391 Harking, et al (1970), AMIC-6391 Harking, et al (1970), Harking, et al (1970). Harking, et al (1970), AHIC-6391 Marking, et al (1970), AHIC-6391 Harking, et al (1970), AHIC-6391 Harking, et al (1970), AHIC-6391 Marking, et al 11970), AHIC-6391 ------- 3"-ehloro-5-nltr» saj.lcyl«nlllde S"-chloro--nlfro •aaicylantlldo 3"-ch I oro--f» 1 tr o a»licyl«nil5d« 3"-ehlaro-f-nltro aallcylanlllda Ictaturus aelas Lepoels cyanI I us aacrocMros Pare a f I avcscn* 3"-lodo-3-nltro«alIc Carasslus vlanlllde auratus 3~-la«lo-S-nltrosalle Cyprlnus ytanil Id* carplo 3"-lodo-J-nltrosalle ylanillde proaeias 3"-Iodo-3-n! trosal le tetalurws ylanillde aelas 3-lodo-S-nl»resallc lepoals ylanillde cyanellus 3"-lodo-J-nltrosatIc Lepoels y I anil Id aacrochlrm 3"-lodo-3-nltPOsallc Prea y I anil Id llavascns 3"-lo«lo-3-nltrosal le Salao yI anil Id galrdnerl Satao BSft — BS« — 8S» BS» — BS» BS* BS« BS« ~ BS* as* BS* ~ BS* — 16 IK 3 hr» IB fK 3 II fK 3 hr» 1.1 (K2I ia IKII IB IK 3 hr> l.a (Kit IB IK 3 nrl l.a (Kll i.a IKII l.a IK 3 hr) ia IK 3 hrl l.B IK 3 saac as abov* saa* as abava saa* as abava saa* as abov* saa* as abov* saa* as abov* saa* as abava saa* as abova saa* as abava saa* as abov* saa* as abova saa* as abova Twenty-nine nltrosallcylanlllds and rlatd coapound «r evaluated for thalr ralatlv* toxic ttct to stctd fl«h. Potency varied tilth typ and al (1970) t NIC-639t , et al (19701. •MIC-6391 Marking, et al 11470), 1NIC-6391 Harking, et al 11978), AHIC-6391 Marking, •tal (19701, 41IC-6J")! Marking, at al(1970), •MIC-6391 Marking, et al (1970), AHIC-6391 Mark I no., etal (19701. • MIC-639-1 Marking, «t al (1970), AMIC-6391 Marking, et al (1970), AMIC-6391 Marking, et al 11970), AMIC-6391 Marking, et al (1970). AHIC-6391 Marking, at al (1970), AMIC-6391 ------- Coaoound Organise Field Field Study Location Toxlclty, active Ingredient, Pom Experimental Variables, Controlled or Noted Comments Reference i 3","-dIchloro-3- Carasslus 8Sa. —- nitroaalicylanllldo auratus 3-.--dlchloro-3- Cyprlnus BS» — nltroaallcylanlllde carpi« 3~»"-dlehloro-3- Plmeohales 8S» — nltroaallcylanlllde promelas S",li~-dlchloro-3- Ictalurus nitroaallcylanllide eel as 3",l.--dlchloro-3- Leoomls BSA — nitroaa.llc>lanllldo cyanellus 3",i."-dIch I oro-3- Leoomls 8S» — nltroaallcylanlllda macrochlrus 3",^--dlchloro-3- Perca 8S» nltrosalIcylanllide flavescens -cyaoo-?« -dllodophenyl-N- nethyl carbamate PhoraldiuB amblguua i.aiKii 1.0 IKlt 0.1 CK2I 0.1 IKlt •• 1.0IK1I 0.1 IKdt 0.1 IK«> 0.9-10.0 (NTEI — position of substitutions. Several compounds Mere selectively toxic to yelloH perch. Goldfish mere the most resistant to the salicylanltIdes. same as above same as above same as above same as above same as above same as above same as above Of 7i» chemicals evaluated as alqicldeSt only 9 H<re more toxic than CuSOit. None inhibited qroxth or mat-formlnq al^ae for more than ? weeks. CuSO<> formulated »lth certain wettlnq aoents «as more toxic than Cu50<» alone. Coooer chloravlne was also found to be more toxic than CuSOfc. No xettlnq agents Mere found to be Inhibitory at the concentrations Investigated (0.05 and 0.105 op«t. Also resorted are factors affecting growth of algae In canals to determine whether there Here leads to Marfcino. et al 114701. 4MIC-6391 Marking, et al (19/0), MIC-fj39l Marking, et al 119701, Marking, et al (1970), »HIC-fiS91 Harking, et al (1970), »«IC-6391 Harking, et al (1970), • HIC-S391 Harking, et al (1970), WC-6391 Otto (19701, mC-892 ------- controlling algae by environmental •anaqemtnt. No oractlcal environmental Here found. I V-aiophenyl-3-nltro Salve sellcylanlllde galrdncrl BS» — t.l IK1I "-8»ophenyl-3-nltrp Caresslus sallcyfan!tide auratus ~-azophenyl-3-nltro Cyprlnus set Icy I anil Id* carole %~-azophenyl-3-nltro Plm«phales •allcylanlllde proeelas --azopher»yl-3-nltro Ictalurus •allcyfanlllda aela --az»phenyl-3-n!tro Lepoals sellcylanlllde eyanellus •/•-azophenyl-3-nltro lepoal sallcylanlllde aacrochlro* V-azophenyl-S-nltrp Ptrea sallcylanllld* fla»€e«n» V"-bro«o-?-««thyl-3- Salvo nltro«allcylanllld« g»lr ------- Coa/pound Organise "-broi«o-7-athvl-3- Pleephates nltrosal Icvlanl lid provetas »"-broao-2-e>thyl-3- Ictalurus nltrosal Icvlanl 1 Id velas "-broao-?-athyl-3- Lpo>ls nltrosal Icy 1 anil Id* c vane II us V-broao-Z-«thyl-S- lepoais nltrosal Icvlanl lid* aacrechlrus »"-bro»o-Z-»thyl-3- Prca nltrosalleylanlllda tlavescans "-broBo-3-nl trosall Salao Cylanllld galrdnerl "-broao-3-nl trosall Carasslus Cylanltld auratus V-broo-3-nl trosall Cyprlnus cylanllld* carplo a "-broeo-3-nl trosall Pla»phals cylanllld pro»las eylanllld alas cylanllld cyanellus Toxlclty, Exoerlaental Active Variables, Field Field Ingredient, Controlled Study Location Ppa or Noted BSA — 1.0 (Xl> a» BSA — 1.0 (K 3 hrl a* BSA — 1.0 (K 3 hrl a* BSA ~ 1.0 (Kll a* BSA — O.KKZI a* BSA — 1.0 (K 3 nrt a* BSA — 1.0 (Kl) a« BSA — o.l IK 3 hrl a» BSA — 1.0 (K 3 hrl a* BSA — 1.0 IK 3 ttrt a* Coneents saae as above saae as above saa* as abov* saae as above saae as above saae as above saae as above saae as above saae as above saae as above Reterenc* (, Marking, et al (1970), MHC-6391 Marklng,et al (19701. AMIC-6391 al (1970). Harking, • tat (1970), AHIC-S391 Marking, «t al (1970), AHIC-6391 al (1970), AHIC-6391 Marking, et al (1970), AHIC-6391 "-bro«o-3-nItrosall lapoals BSA — 1.0 (Kl) saa as above Harking, t ------- cylenltld aaeroehlrus V-broao-3-nltrosall Cere* cytanlllda ftaveseens ja-3- Salao nttrosallcylanlltd* aatrdnarl »"-bro«o-«.-bro«o-3- Car ass 1 us nltresat leylanlllde auratus nltrosalIcylanlllda carpio V-bro>o-9-broMO-3- Plavohalas nifrasaltevlanlllda pronalas V-braao-9-bromo-S- Ictalurus nltraxllcylanllid •»!•* %"-bro«o--bro«o-3- l- Plm«phal«s nltrosalIcylanlltda proavla %--ehlor-r<-a«thyl- letalurus n\|tro«alleylanlUd« a»ia« nllrosalleylanllld eyanclius <-»athyl- lao«al« 8S» — ss» — BS» BS* — nltrosallcylanlllda %"-bro»o-5-br oo-3- Lapoals 8SA nltrosal Icylanlllda aaeroeMrus 8S« — BS« BS« — as (.1 1.0 IK 3 hrl 1.0 IK1) 1.0 IK1I a* «••* as above as abov* sa>c as abav* saa« as abova «••• as abova saa* as above saaa as abova saaa as abova »•• as abova san as abova saaa as abova saaa as abova saaa as abova al 11970). AHIC-6391 M«rKlngtet al (1970), AHIC-&391 M»pKlng,«t at (1970), ANIC-6391 al (1970). ANIC-6391 H«rKlnq, etal (1970) ( AHIC-6I91 al (1970), AI1IC-S391 N»rKlntj,«t at (1970), AMIC-S391 al (19701, AMTC-6391 M»Phlng,«t al (1970), ANIC-6391 Harking, et al (19701, ANIC-1J91 Marking, «t al (19701, ANIC-6391 HarHInq, «t at (1970), ANIC-6391 Harfcln?, «t at (1970), AHIC-6391 Marking, at ------- Coaoound nltrosal Icylanlllde %--chloro-?"-«afhyl- nltrosal lev lanl llde V-cMoro-2"-«ethyl- nltrosal ley lanl tide V-ehloro-Z"-nethyl- nitrosal Icylanlllde %"-chl oro-2"-aethy 1- nltrosal Icylanlllde %"-chl oro-3-nl trosal Icylanlllde V-ehloro-3-nltrosal Icylanlllde V-ch 1 oro-3-nl trosal Icylanlllde "-chl oro-3-nl trosal ley lanl llde V-ehloro-3-nltrosal Icylanlllde V-chl oro-3-nl trosal Icylanlllde V-ehloro-3-nl trosal Icylanlllde Field Field Orqanlsa Study Location •acrocMrus Perca BSA — f lavescens Sal«o BSA — galrdnerl Car ass 1 us BSA ~ auratus Cvorlnus ASA — earolo Salao BSA — 9alrdnerl Carasslus BSA auratus Cyorlnus BSA — earolo Placonalas BSA — Ictalurus BSA ••las Leooals BSA cyanellus Leooals BSA — aaereMrus ToKlcitv. Exoerlaental Active Variables. Ingredient. Controlled Poa or Noted 1.0 IK 3 hrl a* 1.0 IK 3 hr) a* 1.0 (Kll a* 1.0 (Kll a> 1.0 (Kll a* 1.0 (Kll a* 1.0 (Kll a* l.t (K3 hrl a* 1.0 (K 3 hrl a> 1.0 (Kll a* 1.0 IK1) a* Conaents saaa as above saae as above saae as above saae as above saae as above saoe as above saaa as above seae as above saae as above saae as above saaa as above Reference al (1970). AMIC-6391 Harking, et al (1970), Harking, et al (1970), AMTC-6391 Harking, et al 11970), AMIC-6391 Harking, et al (1970), AHIC-6391 Harking, et al (1970). »HIC-6391 Harking, et al (1970), AMTC-6391 Harking, et al (1970), AMIC-6391 Harking, et (I (1970). Harking, et «( (1970), AMIC-6391 Marking, «t al 11970). AMIC-6391 Marking, «t at (1970). ANIC-639X ------- fe 00 <--ehlore-5-nltrosal Parea 8S« — Icylanllld* flavaseans V-ehloro-5-bro«o-nl Salao 8S« ~ trosalleylanlllde valrdnerl V-€h)oro-5-bro»o-nl Carasslus BS» — trosal ley I anil Ida awatus V-cnloro-5-brono-nl Cyprlnus BS» — trosalleylanlllda carolo %»-cnloro-9-bro«o-nl Pla«ohl« 8S» — tr«s«llcylmllld« pren«fn Ictclurus 8S* ~ loml« 8S cy»o«1lus L«DOKl« BSI ••erochlrtM P«re» BS» fl»v«se«ns Salao BS* qatrdncri Carasslus BS* auratus Cyorlnu* BS» carolo Plaaphalas BSt proaalas tre«»llcylnlllda tro«»lleyl»nllld« tro«»lleyl»nllld« "-chloPc-5-nltrosal Icy Ian! I Id* «'-chlore-t-nltrsal lerlanlllda »"-ehloro-5-nltro»al leylanlllda V-cMoro--nltrosal leylanlllda 1.0 CK1I 1.1 CK1I 1.0 (Kl) 0.1 IKZI O.i IKZ) 1.0 IK 3 tori 0.1 IK%> 0.1 (K2I 0.1 IK1I 1.0 (Kl) 10 IK2I 10 (Kfct l.OIKlt ••• «s abova saaa as abova saaa as abeva saaa as abova saa* as abava •aaa as abova sane as abova saaa as abova saaa as abova saaa as abova saaa as abova saaa as abova saaa as abowa Marking, «t al (1970). HarKing< at al (1970). HarKlnat at at (1970) t AHTC-6391 , at al 119701. • NI06391 Marklnq, at al (1970). Harking, at al (1470). AHIC-S391 Harking, at al (1970). AHIC-S391 Harking, at al (1970). ANIC-S391 Harking, at al (1970). •HIC-6391 Harking, at at (1970). 41IC-6391 Harking, at al 11970). 4HIC-6391 Harking, at al 11970). AHIC-6391 Harking, at al (1970), AHXC-6391 ------- Compound »"-ehloro-5-nltro sallcylanlllde "-chloro-5-nltro sallcylanlllde V-ehloro-5-nItro sallcylanlllde »"-chl oro-5-nI tro sallcylanlllde »"-lodo-3-nl tro sallcylanlllde Field Field "Organise Study Locaflor let slur us BSA •el as leoomls BSA cyanel lus teoomls BSA macroehlrus Perca BSA f 1 avescens Ictalurus I nebulosus (Z.5-6.01n.t Toxlcltyi Experimental Active Variables, Ingredient, Controlled t Ppn or Noted Comments Reference 1.0 CK1I a same as above Marking, et al (1170), AMIC-6391 1.0 (Kit a* same as above Marking, et al (19701, AHIC-6391 1.0 (Kit a* same as above Marking, et al (1970), AMIC-6391 1.0 (Kl) a* same as above Marking, et al (1970), AMIC-6391 5.0 (Kl a,c«9 Broun bullheads were subletted to Loeb, et al solutions of V-lodo-ni frosal Icyl anl 1 ld« (1966), In laboratory Jars some of which AMIC-6199 »"-Jodo-3-nltro sallcylanlllde "-lodo-3-nltro salleylanlllde Ic,talurus nebulosus (Z. -5-6.0 IN.I Salmo galrdnerl -lodo-3-nltro sallcylanlllde %~-Iodo-3-nltro sallcylanlllde BSA — Kl (partial 0.1 IK2) Carasslus auratus Cyorlnus carple 8SA BSA — 1.0 IK 3 hr) 0.1 (Kl) contained bottom sediments of different deaths up to Z Inches. Upon exposure to the toxicant, some of the bullheads burled themselves In the sediments thereby surviving the chemical treatment 1 to 16 days. The phenomenon of burying appeared to be temperature dependent. a,c,g same as above Twenty-nine nltrosalIcylanlI ides and related comoounds were evaluated for their relative toxic effect to selected fish. Potency varied with type and position of substitutions. Several comoounds Here selectively toxic to yet Ion perch. Goldfish were the most resistant to the sal icytanlI Ides. same as above same as above Loeb, et al (1966), AMIC-6199 Marking, et al (1970), AMIC-6391 Marking,et al (1970), AMIC-6391 Marking, etal (1970), AMIC-6391 V-lodo-3-nltro PImephales BSA — 0.1 (Kl) same as above Marking,et ------- lallcylanillde pronelas al (1970), fe \n 4"-lodo-3-nItrosallc r I en tilde "-lodo-3-n\|trosallc ylanlllde "-lo<»o-3-nltrosaUe ylantllde %"-Iodo-3-nItrosallc ylanlllde %"-lo 1.0 IK?) 1.0 IK2) 1.0 (Kl) a saae as above sa»e as above sane as above sane as above saae as stove sane as above sane as above saae as above Harking, efal (19701, HMIC-6391 Marking. et al (19701, •KIC-6391 Marking, et al (1970), »NIC-6391 Marking, «t al (1970). AMI06J91 MerKlng, et at (1970), AHIC-6391 Harking, etal (1970), ftMIC-6391 Marking, et al 11970). AMIC-%391 Marking, et al %"-lodo-5-nltPOsal Ic riant tide S"-lod»-S-nltrosalle y I ant tide %--Iodo-5-nItrosellc ytanllld* tctalurus me I as Leponls cyanetlus Leponls aaeroehlru* BSA BS4 BSft 1.0 IK1> l.D IK2I 1.0 IK1I sane as above sane as above saae as above Marking, et 81(1970, 4MIC-S391 Marking, et al (1970), AHIC-6391 Harking, et 81(1970), ANIC-6391 ------- Conoound »~-lodo-5-nl trosal le ytanillde "-a«f hoxy-2~-nl tpo- 3-nltrosallcyl- anlllde Field Field Organism Study location Peres BSA — f 1 sveseens Sal no BS galrdnerl Toxlclty, Active Ingredlentt Pom 1.0 1.0 (Kit Experimental Variables. Control led or Noted Contents a* a» sane as above THenty-nlne nltrosal Icy lanl 1 1des their relative toxic effect to selected fish. Potency varied tilth type and position of substitutions. Several compounds Here selectively toxic to yellow perch. Goldfish were the »ost resistant to the sallcytanl 1 ides. Reference Marking, et al (1970). »MTC-63 10 IK 3 nrl 10 (K 3 hr) 1.0 IK1I 10 (Kll 1.0 (Kll 1.0 (Kll 1.0 (K 3 hr) a» save as above sane as above saae as above sane as above sane as above sane as above sane as above MarKInq, et al (1970), »MTC-S3 ------- 5-brono-J-nltrosal Ic Carasslus rile acid auratus S-browo-3-nltrosalIc Cyprlnus rile acid carplo 5-bro«o-3-nltrosallc Plmeohales rile acid promelas 5-bro»o-J-nitrosal Ic Ictalurus yllc acid »elas 5-brono-3-nltrosallc Leoouls rile acid cyanellus S-brono-J-nltrosallc leponls BS» — 8S« BS* BS* BS« 8S» rile acid •acrochlrus 9-bro«o-3-nltrosalIc Perea rile acid flavescens -bro«o-3-«ac-butrl- Phormldlum 6-»«thyluraclI amblquun L — 1.0 (Kl) 1.0 IK1I 1.0 (Kl) 1.0 IK1I 1.0 (Kl) 1.0 (Kl) 0.1 (Kl) 0.5-10.0 (NTE) — eenoounds were selectively toxic to yalIOM perch. Goldfish were the «ost resistant to the sal ley I anil Ides. sae as above sane as above same as above sane as above sane as above sane as above same as above Of 7ii cheilcals evaluated as alqleldes, only 9 Here more toxic than CuSCNt. None Inhibited growth of •at-fornlng algae for more than 7 weeks. CuSO<> formulated with certain wettinq agents was more toxic than CuSOW alone. Cooper chtpraiKlne was also found to be more toxic than CuSOU. No wettinq agents were found to be Inhibitory at the concentrations investigated (0.09 and 0.005 ppn). Also reported are factors affecting growth of algae In canals to determine whether there were leads to controlling algae by environmental •anageoent. No practical environmental •cans were found. Marking, at al 11470). 4MIC-6391 MarKlnq, et al (1470). MsrKinq, et al (1970), 4HIC-6J91 MarKlnq, et al (1070), ONIC-6391 Harklnq, et al (1970), AMIC-6391 Marking, et al (1970), •MIC-6391 Marking, et al (1970). •MIC-6391 Otto (1970), »MIC-B« - Rasbora 8CF» (l.mathyl-n-heptyl) hetarenorDha and -U,6-dlnltrophenyl- BS» 0.92 (TZ) atC«e«f« One hundred sixty-four hard (HM) pesticide, wetting agents, and or soft mlscal laneou* water pollutants showed a Alabaster 11969). ------- Organise Field Study Location ToxicltVt Active Ingredient* Experiment) Variables, Controlled or Noted Comments Reference thlel carbon»»e S,8-dlhydroxyl-l,Z,3 Phormldlum •».9t9-hexachloro-lt amblguum t-methano-l.b-rtlhy dronaphthaiana 0.5-10.0 (33 percent growth Inhibited li "-chloro-2"-metho»v Salmo -3-nltrosallcyl galrdnerl anlllde as —• 1.0 IK 3 hr> iSw) Hide range of toxlclty spanning 1? orders synthetic of magnitude. Knowing the toxlclty and dilution percentage of all components of a water, or formulation did not result In easy seawater predictability of the toxlclty of a for some Mixture of material!. Sometimes species pesticides Mere aost toxic In hard water and sometimes the opposite was true. Testing the actual material as sold Has found to be essential. Of 7, their relative toxic effect to selected ANIC-6391 fish. Potency varied with type and position of substitutions. Several compounds Mere selectively toxic to yellow perch. Goldfish Mere the most resistant to the sallcylanllldes. »"-chloro-?"-m»thoxy Carassius 8S» — -3-nltrosalleyl euratus •nltlde 5"-ehloro-?"-methoxy Cyprlnus BS» — -3-nltrosallcyl carplo anlllde 5"-ehloro-?~-metho«y PImephales 8S» — -3-nItros»IIcyl promelas anlllde II 1.1 IK1I 1.0 IK1) same as above same as above same as above HarKlnq, et at 11970). •HIC-6391 Marhlng, et • I (1970), 1HIC-6391 MarKIng, et al (1970), »MIC-%391 ------- 5~-eMoro-Z~-««»hony Ictaturus 8S» — -3-nltr»salleyt .•: act as •nil Id* S~-chloro-?"-«ethoxy l«Donls BS« — -'S-nltrosalleyl cyan11us •nit Ida 5"-ehloro-?"-aethoy LCDoIs BS» — -3-nltrosalleyl •acroehlrus anil Id »"-eM •ro-r-«thoy Pert a BSA — -3-nttr»s«>fIcyl tlavsc«ns 1.1 IK1I 1.9 (Kll t.O IK1I 1.1 IK1I a* »bov« ••• as above sane as above saa as above Marhlnq, «t •I (1970). Marking, «t al (1 ------- APPENDIX B SPECIES INDEX ^ccipiter cooperii - A -159, 360 Acroneuria - A-5U, 76, 82, 92, 2U?, 280, 306, 330, U52 Acroneuria lycorias - A -269 Aechmophorus occidental! s - A-115, 130, 157 Agmenellum quadruplicatum - A-7, 199, 23^, 278, 376, 377 Agonus cataphractus - A-23, 2U, 26, 28, 19, 50, 53, 75, 80, 8l, 103, 206, 221, 232, 301, 311, 33^, 393, ^k, U06, inU Alewife - A-17U, 206 Algae - A-1^9 Alosa pseudoharengus - A-29, 55, 76, 82, 96, 117, 131, 166, U27, M» Ambassis safgha - A-308, 369 Ambloplites rupestris - A -117, 119, 131, 133, 166, 176 Ameirus nebvdosus - A-118, 132, 176 American smelt - A-17^, 206 Amia calva - A«l8 Amphidinium carter! - A-105, 335 Amphipnous cuchla - A-l8o, 263., 373 Anabaena - A -9 Anabas testudineus - A -178, 26j» 373 Anacystls nidulans - A-7, 199, 233, 278, 376, 377 Anas cyanoptera - A -158, 360 Anguilla rostrata - A-113, 121, lUl, 266, 355 Anlsoptera - A-178, 26^, 373 Anisotremls davidsoni - A-1U9, 351 Aplodlnotus grunniens - A -19 Aquatic plants - A-1U9 Aquila chrysaetos - A-159, 202, 360 Archoplites interruptus - A-115, 116 Arctic grayling - A-U6, 12U, lU6, 197, 35^, ^22 Artemia salina - A -307 Artemia spp. - A-1U8 Asellus brevicaudus - A-lU, l8U, 190, 191, 217, 2U6, 320, 397, 398, ItOl, ^38, V6, U62, »«6U, U65 Asplanchnopus - A -112, 121, 136, 313 Asterias forbesi - A -68 Asterias rubens - A-10, 65, 75, 302, 331, Backswimmers - Belostoma indica . A-180, 26^, 373 Benthic insects - A -177 Betta splendens - A-U8, 2kk Bigmouth buffalo - A-U5, 123, iWt, 196, 352, U20 Birds - A. 150 Black bullhead - AJ+5, 123, 1^5, 197, 353, ^21 Black crappie - A-U5, 12U, 1^5, 197, 353, U21 Bloater - A-UU, 123, l1^, 17^, 195, 207, 352, U20 B-l ------- Blue catfish - A-M, 71, 122, llU, 26l, 352, 120 Bluegills - A-ll, 122, 1U6, 195, 3^6, 351, 119 Blue-green sunfish - A-l+35, 1+36 BOD - A-22, 66, 100, 2?6, 292, 109 Bottom Invertebrates - A-168 Boyeria vinosa - A-269 Brachionus . A -179, 265, 371* Brachycentrus americanus - A-269 Brachydanlo rerio - A-2, 7, 62, 211, 250, 370. 382, 119 Bridgelip sucker - A-U6, 124, 1U6, 197, 35^, &21 Brevoortia patronus - A-27 Brook trout - A-269 Brown bullhead - A-13, 71, 125, 1^7, 175, 195, 207, 260, 351, 119 Bucephala clangula - A-115 Bugula neritina - A-89, 306, 152 Callibaetis sp. - A-185, 186, 218 Callinectes sapidus - A-27, 28 Cambarus bartoni - A-150 Campeloma decisum - A-9^, 95 Campeloma sp. - A-119, 133, 176 Cancer magister - A-127, ^22 Carassius auratus - A-l8, 30, Ul, 52, 55, 61, 97, 11*, 128, 15!, 155, 16U, 235, 217, 2U8, 258, 277, 279, 2&0, 28U, 298, 308, 309, 317, 365, 391, 103, ^28, 131, 111, 119, l5U, 158, 167, 168, U69, 170, 171, 172, 173, ^75, 176, 177, 178, 179, Wo, 181, 182, 183, 181, 185 186 187 188 Carcinus maenas -A-3, 33, 31, 17, W, 68, 79, 86, 87, 90, 103, 170, 205, 213, 22U, 227, 2U2, 252, 25, 270, 279, 307, 329, 33^, 337, 310, 368, 378, 379, 381. 399, 100, 101, 102, 105, 108, UlU, 131. Cardium edule - A-10, 22, 2U, 26, 28, 29, 32, 33, 31, 17, !9, 50, 54, 65, 67, 75, 79, 80, 81, 85, 86, 91, 101, loU, 110, 170, l8l, 206, 213, 221, 221, 225, 227, 232, 2U2, 2U5, 250, 253, 25U, 278, 279, 291, 301, 302, 207, 311, 323, 329, 331, 337, 3M, 3»6, 3»9, 369, 378, 379, 399, *00, 401, 102, 105, 106, 1+09. ^l1, 25, 13U Carp - A-l3, 71, 122, H7, 175, 195, 260, 351, ^19 Carpiodes cyprinus - A-20 Carpiodes sp. - A-198 Catostomus coramersoni - A-20, 82, 105, 108, U7, n8, 131, 133, 165, 176, 277, 297, 337, !58 Ceriodaphnla - A-179, 265, 376 Cerorhinca monocerata - A-161, 362 Chaetoceros sp. - A-105, 335 Chain pickerel - A-13, 125, ll6, 19!, 350, 119 Channa punctatus - A-7, 177, ISO, 181, 863, 372 Channel catfish - A-to, 13, 71, 122, ll7, 175, 195, 207, 26o, 31?, 351, U19 Chara sp. - A-315 Chironoraus sp. - A-7, 129, 130, 131, 135 Chironomus tentans - A-313 Chiselmouth - AJ6, 12U, ll5, 197, 353, 21 arcuata - A-8, 203 B-2 ------- Chrosomus eos - A-18 Closterium - A-179, 265, 376 Clupea harengus - A-113, 121, lUl, 266, 355, ^7, UU8 Coho salmon - A-6, 69, 101, 175, 207, 2U6, 253, 268, 276, 365, 379, 393, U09 Coleps - A-112, 120, 136, 313 Copepods - A-72, 73, 203, 20U, 238, 239, 267, 285, 286, 299, 300, 371, Ull, U12, U32 Coregonus artedii - A-29, 55, 82, 96, U27, Mn, U5U Coregonus clupeaformis - A-17, 29, 30, 31, 51, 55, 56, 77, 82, 96, 97, 280, 281, 302, 310, 331, 393, 39U, U27, U29, UUl, k5k, 1+55 Coregonus hoyi - A.29, 51, 55, 83, 96, U28, UUl, hjk Coscinodiscus - A-112, 120, 137, 313 Cottus bairdi - A-llU, 126, 138, 151, 200 Crangon crangon - A-2, 3, 5, 10, 22, 23, 2U, 26, 28, 29, 32, 33, 31, 36, 38, 17, U9, 50, 5U, 66, 67, 79, 80, 8l. 86, 87, 91, 101, 102, 103, 10U, 107, 110, 182, 206, 213, 2lU, 221, 22U, 225, 227, 231, 232, 2U2, 2U3, 2U5, 2U8, 250, 251, 251, 255, 256, 257, 268, 270, 277, 286, 287, 289, 301, 302, 307, 3H, 319, 323, 328, 329, 337, 338, 3U1, 3U6, 3^9, 363, 36U, 369, 370, 371, 376, 378, 379, 381, 386, 388, 389, 391, 39U, 399, Uoi, U02, 1+03, U05, Uo6, U09, 1+15, 1+25, 426, 1+31+, kk6, UU7, U59 Crangon septemspinosa - A.67 Crassostrea conmercialls - A-307 Crassostrea virglnica - A-U, 13, lU. 26, 103, 169, 181, 20«, 205, 217, 220, 223, 230, 231, 233, 2Uo, 260, 28U, 300, 301, 305, 326, 3^0, 3^3, 36U, 367, 377, 389, 39^, 398, Ul6, In8, U2U, U25, »38, W3, Mk, U65 Crepldostomum farionls - A-222 Culex plpiens - A-112, 120, 133, 13^, 136, 312 Cybister ap. - A-178, 26U, 373 Cyclops - A-179, 265, 371* Cyclops bicuspidatus - A-72, 73, 168, 203, 20U, 238, 239, 285, 286, 299, 300, 371, Ull, U12, U32, U33 Cyclops varicans - A-72, 73, 168, 203, 20U, 238, 239, 285, 286, 299, 300, 371, Ull, M2, U32, U33 Cyclops vernalis - A-72, 73, 168, 203, 20U, 238, 239, 285, 286, 299, 300, 371, Ull, U12, U32, U33 Cyclotella nana - A-105, 335 Cynosclon nebulosus - A-27 Cypridopsis vldua - A-lU. 185, 191, 217, 2U6, 320, 397, 298, UOO, U39, UU6, U63, U6U, U65 Cyprinodon varlegatus - A-68, 176, 2Ul Cyprinus carplo - A-9, 19, Ul, 6U, U7, 118, 131, 132, 16U, 166, 176, 198, 258, 277, 28U, 296, 298, 299, 317, U31, UU9, U67, U68, U69, U70, U71, U72, U75, U76, U77, U78, U79, U8o, U8l, U82, U83, U8U, U85, U86, U87, U88 Cyprls - A-279, «65, 37U Daphnla - A J.79, 26U, 267, 37U Daphnla mgna - A-6, 7, lU, 69, 112. nU, 115, 120, 128, 129, 133, 13U, 136, 18U, Ml, 217, 2^, 312, 320, 397, 398, UOO, UU6, 1+62, i»63, U6U, U65, U66 B-3 ------- Diaptoraus - A-180, 264 Diatomella - A -112, 120, 137, 313 Diatoms - A -112, 120, 137, 313 Diploneis - A-112, 120, 137, 313 Dragonflies - A-40 Dunaliella tertiolecta - A -105, 335 Dytiscus sp. - A-178, 264, 334, 373 Elanus leucurus - A-159, 360 Emerald shimer - A -174 Enallagma sp. - A -189, 190, 218 Endomychura craveri - A-155, 201, 231, 357 Engraulis mordax - A -126, 422 Ephemerella - A -54, 76, 82, 92, 248, ;>80, 306, 330, 452 Ephemerella subvaria - A -269 Esomus danrica - A-178, 263, 373 Esox lucius - A -17, 18, 31, 56, 77, 97, 98, 119, 133, 176, 198, 199, 270, 271, 277, 281, 303, 310, 315, 331, 391, 29, 442, ^55 Esox niger - A-113, 117, 121, 131, l4l, 166, 266, 297, 355 Estigmene acrea - A -111, 119, 135, 312 Eucalia inconstans - A -20 Euclanis - A-112, 121, 136, 313 Eucyclops agilis - A-72, 73, 168, 203- 204, 238, 239, 283, 284, 299, 300, 371, 411, 412, 432, 433 Euglena - A -9 Eupera singleyi - A-239, Falco columbarius - A-159, 36l Falco peregrimis - A-162, 201, 202, 2tl, 356 Falco sparverius - A-159, 160, 36! Fathead minnow - A-74 Fish (not specified) - A-7, 13, 34, 62, 88, 109, 1^3, 150, l8l, 193, 212, 216, 221, 223, 225, 231, 233, 277, 28l, 286, 295, 301, 305, 365, 371, 372, 386, 388, 398, 415, 4l8, 466, 467 Flannelmouth sucker - A-45, 123, 1^5, 196, 353, ^21 Flathead catfish - A-45, 123, 144, 196, 352, 420 Fregata magnificens . A -158, 359 Freshwater drum - A-44, 122, 144, 170, 196, 206, 352, 420 Freshwater mussels - A-150 Fulmanus glacialis - A -157, 358 Fundulus diaphanus - A -132, 167 Fundulus heteroclitus - A -23, 51, 54, 68, 79. 108, 117, 131, 166, 227, 228, 319, 327, 3»H, 3te, 363, UlU, 430 Fundulus ma Jails - A -68 Gadus macrocephalus - A -127. 153, Gadus morhua - A -121, 355, 429 Galeolaria caespitosa - A-89, 306 Gambusia affinis - A-112, 120, 136, l4l, 142, 147, 169, 205, 236, 237, 238, 286, 312, 368, 390 Gammarus fasciatus - A-13, 35, 4l, 129, 133, 131, 184, 190, 191, 215, 217, 222, 242, 246, 271, 273, 319, 338, 363, 384, 397, 400, 4l6, ^30, 439, ^5, ^2, 464, 465 B-4 ------- Qammarus oceanlcus - A-2U, 25, 101, 102, 448 Gamraarus pseudolimnaeus - A-69, 95, 271 Gamraarus sp. - A-llU, 126, 138, 151, 200, 235 Gastrotricha - A.179, 26U, 376 Gerris - A.267 Gizzard shad - A-44, 71, 122, lU3, 171, 195, 208, 261, 351, 419 Golden shiner - A-435, 436 Goldeye - A-U5, 145, 196, 351, 352, ^20 Goldfish - A-43, 123, 125, 1^6, 170, 19^, 419 Green sunfish - A-3U6 Haliotus corrugata - A-ll+9, 355 Haliotis rufescens - A-149, 35U Halocyptena microsoma - A-163, 357 Heteropneustes fossilis - A-178, 263, 33S 373 Hexagenia bilineata - A-7, 129, 133, 135 • Hinnites multirugosis - A-149, 35^ Hippoglossoides platessoides - A-121, 356 Homarus americanus - A.M7 Hyallela azteca - A-189, 219 Hydrophilus sp. - A-179, 265, 374 Hydroprogne caspia - A-l6o, 362 Hydropsyche - A-54, 76, 82, 92, 248, 280, 306, 330, 452 Hydropsyche betteni - A-269 Ictalurus catus - A-20, 116, 165 Ictalvirus melas - A-20, 4l, 63, 164, 199, 258, 277, 28U, 298, 317, 431, 449, ^67, ^68, 469, ^70, 471, 472, 473, ^75, ^76, 477, ^79, U80, 481, 482, 483, ^8U, 485, 486, 487, 489 Ictalurus nebulosus - A-21, 117. 131, 166, 350, 48U Ictalurus punctatus - A-7, 20. 40, 59, 63, 163, 198, 2^9, 258, 277, 283, 298, 315, 316, 390,- 431, 448 Ictiobus cyprinellus - A-20, 198 Invertebrates - A-150 Ischnura verticalis - A-129, 134, 135 Isochrysis galbana - A-105, 335 Isogenus frontalis - A-270 Kelletia kelletii - A-1^9, 355 Kiyi - A-171, 208 IO,amath sucker - A-124, 145, 353, 421 Kuklia sandvicensis - A-169, 205, 287, 368 Labeo rohita - A-177, 266, 333, 372 Lagodon rhomboides - A-25, 27, 28 Lake herring - A.171, 208 Lake trout - A-44, 123, iWt, 171, 196, 208, 352, 420 Lake whitefish - A-4U, 123, l^1, 171, 196, 209, 352, 420 Largemouth bass - A-43, 71, 125, 147, 195, 351, 419 Largescale sucker - A-46, 124, 145, 197, 353, 421 Larus delawarensis - A-115, 130 B-5 ------- Larus heermani - A-156, 357 Larus occidentalls - A-160, 36l Larus spp. - A-115, 130 Lavlnia exilicauda - A-116 Lebistes reticulatus - A-169, 205, 267, 287, 368, 381, 450 Leiostoraus xanthurus - A-25 Lepdotius floridanus - A-199 Lepisosteus platostomus - A-17 Lepomis auritus - A-118, 132, 167 Lepomis cyanenus - A-20. 72, 116, 201, 238, 262, 277, 283, 316, 347, 348, 394, 410, 4li, 467, 468, 169, 470, 471, 472, 173, 475, 476, 477, ^78, 479, 480, 48l, 482, 483, 484, 485, 486, 487, 489 Lepomis gibbosus - A-19, 116, 131, 165 Lepomis macrochirus - A-2, 3, 4, 14, 16, 19, 21, 41, 58, 59, 64, 87, 93, 108, 117, 131, 156, 164, 166, 168, 185, 186, 191, 192, 199, 217, 239, 240, 241, 246, 249, 258, 277, 284, 295, 298, 315, 317, 320, 323, 327, 344, 347, 358, 367, 380, 382, 388, 390, 394, 397, 398, 4oo, 403, 4o4, 4o8, 431, 439, 446, 449, 450, 452, 457, 462, 463, 464, 465, 467, 468, 469, 470, 471, 472, 473, 475, 476, 477, 478, 479, 480, 481, 482, 483, 484, 485, 486, 487, 489 Lepomis microlophus - A-19, 4l, 64, 164, 240, 258, 271, 284, 298, 431, 453 Libellula sp. - A-129, 130, 134, 135, 187, 219, 228 Llmanda limanda - A-34, 49, 101, 382 Lepomis megalotis - A-19 Limnephilus rhombicus - A-113, 125, 137, 150, 199, 235 Llmnephllus sp. - A-187, 188, 219 Limnodrilus sp. - A-410 Longnose sucker - A-46, 124, 146, 197, 354, 422 Loomelania melanla - A-163, 357 Lophodytes cucullatus - A-150 Lymnaea stagnalls - A-17 Macrocyclops albidus - A.72, 73, 168, 203, 204, 238, 239, 285, 286, 299, 300, 371, 411, 412, 432, 433 Macrognathus aculeatum - A-l8o, 372 Mastocembelus pancalus - A-l80, 372 Megaceryle alcyon - A-150 Mercenaria mercenarla - A-4, 8, 9, 10, 69, 70, 102, 103, 181> 185, 221, 222, 223, 225, 226, 233, 247, 257, 260, 286, 323, 325, 326, 327, 328, 336, 340, 342, 343, 367, 377, 385, 388, 389, 394, 415, 416, 417, 4l8, 433, 434, 438 Mergus merganser - A-115, 150 Merlucclus productus - A-123, 128, 152, 153, 422, 423 Microcystis - A-9 Micropogon undulatus - A-27 Micropterus dolomieul - A-19, 117, 131, 166 Micropterus salmoldes - A-19, 4l, 64, 116, 130, 164, 188, 259, 284, 299, 316, 317, 431, 449 Mlnytrema melanops - A-20 Monochrysls lutherl - A-106, 335 B-6 ------- Morone saxatilis - A-5, 22, 39, 67, 102, 285, 295, 299, Mosquitofish - A-U36 Muds - A-150, 3^5 %a arenaria - A-68, 220 Myriophyllum spicatum - A-221 hfystus vitatus - A-180, 2651 373 Mytilus edulis - A-68, 121, 307, 355 tfytilus edulis planvilatus - A-89 Nandus nandus - A-180, 265, 372 Nannochloris occulata - A-106, 335 Nassarius obsoletus - A-69 Nauplius - A.179, 26U, 37^ Navicula - A-112, 120, 137, 313 Negaprion brevirostris - A-69, l8l, 2U2, 267, 323, 333, 365, 381, 386, 105, UlU, 166 Nepa sp. - A-179, 265, 375 Nereis virens - A-23, 51, 69, 79, 108, 228, 319, 327, 3^2, 363, Nine-spined stickleback - A-172, 209 Nitzschia closterium - A-106, 335 Nitzschia linearis - A-2, 3, U, 16, 59, 60, 87, 327, 367, 380, 382, kok, 108, 450 Northern squawfish - A-l6, 12*, 1U5, 197, 353, ^23 Notendgonus crysoleucas - A-72, 117, 131, 166, 262, 283, 297, 316, 3^7, 3W, 3^9, 391, Ml, ^58 Notomatta - A-112, 121, 136, 313 Notonecta sp. - A-178, 265 Notropis analostanus - A-132, 167 Notropis hudsonius - A-30, 5U, 76, 82, 97, 1^28, bkl Notropis cornutus - A-117, 132, 166 Nuclearia - A-112, 120, 136, 313 Nycticorax nycticorax - A-l6o, 361 Oceanodroma homochroa - A-157, 359 Oedogonium cardiacxm - A-112, 120, 136, 312 Olisthodiscus luteus - A-106, 335 Oncorhynchus kisutch - A-35, Ul, 63. 6k, 1U8. 152. 16U, 235, 252, 259, 28U, 296, 299, 317, 336, 383, 385, U32, &1+9, ^59 Oncorhynchxis nerka - A-337 Oncorhynchus tshawytscha - A-9U, 336, 387, U59 Ophiogomphus rubinsulensis - A-269 Orconectes nais - A-lU, Uo, 133, 13^, 18U, 190, 191, 217, 2U6, 320, 397, 398, too, UUo, UU8, W3, U6U, U65 Orconectes rusticus - A-9U Orthocyclops roodestus - A-72, 73, 168, 169, 203, 20U, 238, 239, 285, 286, 299, 300, 371, Ull, U12, 132, 133 Orthodon microlepidotus - A-115 Oscillatoria - A-9 Osmerus mordax - A-17, 30. 31, 55, 57, 77, 83, 96, 98, 281, 303, 310, 331, 391, te8, U30, Wll. UU2, UU8, 155 Ostrea edulis - A-U9, 91, 2U3, 255, 307, 329, U03 B-7 ------- Pacific oyster - A-6, 101 Pagurus longicarpus - A-68 Palaemonetes kadiakensls - A-13, 72, 110, 111, 115, 129, 133, 134, 165, 184, 170, 191, 217, 228, 237, 246, 259, 262, 263, 285, 317, 318, 320, 348, 393, 397, 4oo, 4ll, 132, 439, 446, 462, 464, 465 Palaemonetes vulgaris - A-68, 342 Pandalus montagui - A-379, 381, 394, 401, 402, 403, 409, 4l5, 434 Pandion haliaetus - A-159, 236, 361 Pandorina - A-179, 26k, 37k Pandulus montagui - A-32, 35, 49, 80, 91, 182, 213, 224. 225, 227, 243, 247, 253, 254, 256, 279, 280, 307, 329, 337, 34l, 369 Panopenus herbstii - A-199 Panulirua interruptus - A-149, 355 Paralabrax clathratus - A-ll, 12, 13, 37, 38, 57, 58, 60, 61, 77, 78, 79, 83, 84, 85, 98, 99, 100, 274, 275, 281, 282, 283, 289, 290, 292, 293, 303, 304, 305, 320, 321, 322, 331, 332, 333, 375, 376, 395, 396, 397, 412, 113, klk, 443, 444, 455, 456, 457 Paralabrax nebulifer - A-149, 354 Paralichthys sp. - A-26 Paramecium - A-112, 120, 136 Parophrys vetulus - A-127, 152, 422 Pelecanus occidentalis - A-158, 202, 236, 259 Peloscolex sp. - A-UlO Penaeus duorarum - A-25, 27, 28 Penaeus setiferus - A-27 Perca flavescens - A-17, 19, 30, 31, M, 56, 57, 6k, 77, 83, 97, 98, 116, 118, 130, 132, 164, 165, 176, 259, 281, 285, 297, 299, 303, 310, 317, 331, 39^, ^28, 430, 432, kkQ, kk2, kk$, 155, U67, 468, 469, 470, 471, 472, 473, 476, 477, 478, 479, 480, 481, 482, 483, 484, 485, 486, 487, 489 Percopsls omiscoraaycus - A-30, 56, 77, 83, 97, 428, 440 Petromyzon marinus - A-425 Phalacrocorax pelagicus - A-158, 360 Phalacrocorax peniciliatus - A-158, 359 Phalaropus fulicarus - A-160, 362 Phormidium amblgutan - A-4, 9, 10, 15, 47, 48, 59, 70, 76, 85, 87, 88, 89, 90, 92, 107, 109, 183, 215, 222, 223, 266, 271. 273, 313, 322, 328, 330, 339, 382, 383, 384, 389, 390, 395, 407, 408, 410, 426, 437, 451, 459, 460, 461, 462, 473, 474, 475, 478, 487, 488, 489 Physa gyrina - A-204, 239, 433 Physa heterostropha - A-2, 17, 109, 327, 367, 380, 382, 450 Physa Integra - A-95 Physa spp. - A-lll, 119, 136, 312 Pilodictus olivaris - A-20 Pimelometopon pulchrum - A-149, 354 Pimephales proraelas - A-20. 22, 4l, 47, 64, 66, 69, 73, 8l, 93, 100, 105, 108, 140, 153, 164, 211, 214, 215, 235, 237, 245, 258, 272, 276, 278, 284, 287, 291, 292, 297, 298, 301, 317, 337, 346, 347, 409, 426, 431, 449, 452, 453, 458, 461, 467, 468, 469, 470, 471, 472, 473, ^75, 476, 477, ^78, 479, ^80, 481, 482, 483, 484, 485, 486, 487, B-8 ------- Pisidium sp. - A-119, 133 Pizonyx viversi - A-163, 357 Plankton - A -115 Plants - A-1U9 Platessa vulgaris - A -250 Platichtbys flexus - A-91, 110, 225, 251, 308, 3Ul, 369, M5, Platichthys stenatus - A -127, 153, ^23 Platymonas subcordiformls - A-105, 335 Pleuronectes platessa - A-10U, 170, 3^9 Podiceps caspicus - A-163 Poecilia latipinna - A -193, 194- Poecilia reticulata - A-U23, b2h Pomoxis annularis - A -156, 198, 358 Pomoxis nigromaculatus - A -19, 115, 118, 132, 156, 16?, 198, 358 Porphyridium cruentum - A -105, 335 Procambarus simulans - A-^0 Prosopium cyllndraceum - A -29, 51, 55, 83, 96, 128, kbl, Protozoa - A -112, 120, 136, 313 Pseudopleuronectes americanus - A -92, 93 Pteronarcys dorsata - A -270 Ptychocheilus oregonensis - A-U58 Ptychocheilus umpquae - A-l-59 Ptychoraraphus aleuticua - A-l6l, 362 Puffinus creatopus - A -157, 358 Puffinus griseus - A -157, 359 Puffinus tenulrostris - A-157, 359 Pumpkinseed - A-^3, 125, 1^7, 19^, 351, Ul9 Puntius sophore - A-8, 177, 180, 265, 33^, 373 Puntius ticto - A -46, 212, 252, 278, 297, 39^, Pygoscelis adeliae - A -156, 358 Rainbow trout - AJt6, 12k, 1^5, 197, 3^5, 353, ^21, U35, Rana teraporaria - A -128, 15 U Ranatra fillformls - A -178, 265, 33^, 373 Rasbora heteromorpha - A-3, 5, 6, 11, 15, 16, 21, 23, 31, 32, 33, 31, 35, 36, 38, 39, Ul, U2, 51, 52, 53, 6l, 65, 66, 67, 73, lh, 75, 87, 102, loU, 106, 109, 110, 137, 139, lUl, 1U2, 1^3, 182, 183, 18^, 185, 192, 193, 211, 212, 216, 226, 229, 230, 232, 2Ul, 2U^, 2U5, 2U6, 2U8, 2U9, 252, 255, 256, 257, 261, 267, 273, 275, 276, 288, 391, 293, 29^, 297, 305, 306, 310, 318, 319, 32U, 325, 326, 327, 338, 339, 3^, 3^5, 366, 367, 370, 371, 377, 38^, 385, 386, 387, 393, U02, UoU, U07, ^16, Ul?, U25, te6, U27, ^30, U31, ^36, ^39, M2, W, W5, U7, W8, ^51, ^63, U65, ^66, U73, ^87 Redbreast sunfish - A-122, lU6, 295, 351, U21 Redhorse sucker - AJtf, 71, 122, 1^3, 195, 351, 14-19 Red shiner - A-U36 Rhinichthys atratulus - A-llU, 118, 126, 132, 138, 139, 151, 167, 200, 201 Rita rita - A-1&0 Roccus americanus - A-118, 132, 166 Roccus chrysops - A-30, 52. 56, 83, 97, 199, ^28, 14-10, 1+5^ Roccus saxatilis - A-Uo, 9^, 220, 229, 252, 256, 277, 380, 383, 399 Rock bass - A-UU, 122, lU4, 171, 195, 209, 352, U20 B-9 ------- Rotifers - A-112, 120, 136. 313 Round whitefish - A-46, 124, 146, 171, 197, 209, 354, 422 Salmo aquabonita - A-223 Salmo clarki - A-21, 62, 63, 148, 234, 296 Saline gairdneri - A-14, 15, 18. 21, 35, 41, 48, 63, 64, 70, 73, 91, 95, 100, 106, 148, 154, 164, 191, 192, 213, 217, 226, 229, 234, 249, 250, 251, 259, 267, 272, 276, 284, 294, 296, 299, 315, 317, 322, 324, 325, 330, 333, 336, 343, 366, 368, 370, 378, 387, 388, 390, 395, 398, 399, 405, 406, 407, 429, 432, 437, 439, 442, 445, 449, 452, 453, 454, 457, 459, 466, 467, 468, 469, 470, 471, 472, 473, 475, 476, 477, 479, 4&0, 481, 482, 483, 48U, 485, 486, 488 Saljno salar - A-23, 24, 101, 113, 121, 141, 155, 266, 355, 447 Salmo trutta - A-l8, 4l, 64, 142, 143, 164, 251, 259, 284, 299, 315, 317, 432, 449 Salvelinus fontinalis - A-18, 62, 98. 107, 114, 126, 137, 138, 147, 150, 151, 152, 155, 167, 200, 234, 295, 296, 315, 407, 437, 438, 441, 448, 459 Salvelinus namaycush - A-l8, 30, 51, 55, 83, 96, 309, 310, 314, 315, 428, 454 Sauger - A-45, 123, 145, 196, 353, 421 Scardium - A-112, 121, 136, 313 Scomber scombrus - A-113, 121, l4l, 266, 355 Sea lamprey - A-172, 209 Sebastodes alutus.- A-128, 153, 423 Sebastodes flavidus - A-127, 153, 423 Sebastodes marinus - A-121. 355 Sebastodes sp. - A-149, 354 Semotilus atromaculatus - A-114, 117, 126, 131, 138, 150, 151, 166, 200 Semotilus corporal!s - A-117, 131, 166 Slalis ep. - A-114, 126, 138, 151, 200, 235 Simulium venustum - A-168 Siphlonurus sp. - A-13U, 135 Skeletonema costaturn - A.105 Slimy sculpin - A-172, 209 SmallBouth bass - A-46, 124, 145, 197, 353, 421 Smallmouth buffalo - A-U5, 123, 144, 196, 261, 352, 420 Sorghum halpense - A-lll, 119, 311 Sphaerodema annulatum - A-178, 265, 373 Spirogyra sp. - A-9, 345 Spirorbis lamellosa - A-89, 306, 451 Spottail shiner - A-172 Spotted sucker - A-44, 122, 143, 195, 351, 419 Steelhead trout - A-6, 69, 100, 245, 253, 268, 276, 365, 379, 391, 409 Stenonema candidum - A-313 Stenonema rubrum - A-269 Sterna forsteri - A-160, 361 Stizostedion vitreum - A-19, 30, 52, 56, 83, 97, 198, 314, 428, 440 Stolephorus purpurea - A-169, 205, 287, 368 Stonecat - A-172 B-10 ------- Striped mullet - A-UU, 71, 122, lM, 195, 351, 120 Strongylocentrotus franciscanus - A-1U9, 35^ Sturnella neglecta - A-l6l, 363 Sula leucogaster - A-158, 202, 236, 359 Synthliboraraphus antiquum - A-l6l, 362 Taeniopteryx nlvalis - A-313 Taenlopteryx maura - A-269 Tendipedidae - A-220 Thalasseus elegana - A-156, 357 Tilapia mossamblca - A-169, 205, 287, 368 Trachinotus carolinus - A-5, 93, 252, 383 Trichogaster fasciatus - A-177, 265, 372 Triturus cristatus - A.128, 15^ Trout perch - A-173 Tubifex sp. - A-U12 Tubifex tubifex - A-8, 73, 169, 20U, 215, 228, 239, 2UU, 259, 277, 286, 300, 318, 3^9, 36U, 372, 393, M2, U2U, U33 Tubificids - A-267 Tyto alba - A-161, 363 Ulothrix sp. - A-8, 203 Uria aalge - A-161, 362 Urophycis tenuia - A-121, 355 Urosalpinx cineria - A.68 Volvox - A-179, 26U, 37U Vorticella - A-112, 120, 136, 313 Walleye - AJ5, 71, 123, 1^5, 173, 196, 210, 353, Watersipora cucullata . A -306, »-51 Whirligig beetles - A-Uo White bass - AJ5 , 123, 1^5, 173, 197, 210, 353, White catfish - A-U3, 125, 1&6, 19U, 350, Ul9 White crappie - A-U5, 123, iW;, 196, 352, U20 White perch - A-U3, 71, 125, l1^, 173, 191, 210, 350, Ul8 White sucker - A-U2, 71, 125, 1^3, 173, 191, 210, 350, Ul Wolffia papiilifera - A-105, 1^7, 18^, 211, 272, 301, 391, Xiphophorus maculatus - A-U53 Yellow perch - A-U2, 125, 1^6, 173, 191, 2U, 350 Zenaidura macroura - A-l6l, 363 B-n ------- APPENDIX C IDENTIFICATION OF COMMERCIAL CHEMICALS (Note: Many of the names Included In this list are tradenames and should be treated as such.) Chemical Name ABS Acrlflavlne Acrolein Actusol Aflatoxin Bl Agridip Amitrole Amltrol-T Amphenone B Antimycin A Aphitox AQ Aquaclene Aquaclene 100 Aqualin Aquathol Aroclor 1221 Aroclor 12U2 Aroclor 12U8 Aroclor 1251 Aroclor 1260 Aroclor 1262 Asuntol (Sheep dip) Asulum Atlas 1901 Atlavar Composition Alkyl benzene sulfonate Mixtures of 2,8-diamino-10- methylacridinium chloride and 2,l-diaminoacridine see Aqualin No information available C17H1206 No information available 3-Amino-l,2,U-triazole 3^Amino-l, 2, U-triazole-ammonium thiocyanate mixture 3,3-Bis [p-aminophenyl]-2-butanone- 2-dihydrochloride C28HUON209 Fluoroacetamide and Ilssapol No information available No information available No information available 2-Propenal Disodium salt of endothal (19.2 percent-H-Pennsalt) Commercial PCB with 21 percent chlorine Commercial PCB with U2 percent chlorine Commercial PCB with k& percent chlorine Commercial PCB with 5U percent chlorine Commercial PCB with 60 percent chlorine Commercial PCB with 62 percent chlorine see Coumaphos Methyl-U-aminobenzene sulfonyl- carbamate No information available Sodium chlorate, 2,luJ), Monuron mixture C-l ------- Chemical Name Composition Atrazine Avadex Avadex BW Azinphosmethyl Balan Banner DG01 Banner DG02 Banner DG03 Banner DGOU Banvel Barban Basol AD6 Basol 99 Bayer 3900? •Bayluscide Baytex Baywood k3 Benazolin Bensulide Betasan BHC Borasceu BP BP 1002 BP 1100 BP 1100X Brakontrole Bromophos Bromoxynil Busan 90 Busan 88l Canal Bank Weedkiller Captan Carbaryl Carbophenothion Carbyne Caeol Casoron Casoron G Casoron 133 Chem-floe Chevron NI-0 2-Chloro-U-ethylamine-6-isopropyl- amino-s-triazine S-2,3-Dichloroallyl diisopropylthio- carbamate S-2,3,3-Trichloroallyl-diisopropyl thiolcarbamate see Guthion see Benefin No information available No information available No information available No information available 3,6-Dichloro-o-anisic acid h-Chloro-2-butynyl-m«<;hlorocarbanilate No information available No information available N-methyl 2 isoprqpoxyphenyl carbamate 2',5J>ichloro J1-nitrosalicylanilide ethanolamine see Fenthion Maleic hydrazide, 2,Uj) as triethanol, amine salt, vetting agent, water No information available see Betasan S-(0,0-Diisopropyl phosphorodithioate) ester of N-(2-mercaptoethyl) benzene sulfonamlde Benzene hexachloride No information available No information available No information available No information available No information available U-CPA see QMS-658 3,5-Dibrono-k-hydroxybenzonitrile No information available Organosulfur formulation No information available cis -N-( (trichloromethyl)thio)- 4-cyclohexene-l,2-dicarboxlmide 1-Naphthyl methylcarbamate see Trithion see Barban No information available see Dlchlobenil see Dlchlobenil see Dichlobenil Isopropyl N-phenylcarbamate No information available C-2 ------- Chemical Name Chloramphenicol Chloral hydrate Chlorainine Chlorax Chlordane Chlorea Chlorfenvinfos Chloroflurazole Chloropropylate Chlorthiamid CI Cleanosol Clophen A30 Clophen AUO Clophen A50 Clophen A60 Compass Cooper's Fly Dip Co-Ral Corexit ?66U Corexit 8666 Coumaphos Craine QBE Crossguard Crotothane Crow Solvent M Cunilate RQ 2k Cuprinol CX Dalaclde Dalapon D.B. Granular DBF DDD DDE DDT DDVP Decamethdnium dibromlde De De Tane Delrad Composition (Chlororaycetin) D-(-)-threo-2- dichloroacetamido-1-p-nitrophenyl- 1* 3-propanediol 2,2,2-Trichloro-l,1-ethanediol (N^hloro-p-toluenesulfonamido) sodium No information available Mixture of 60 percent octachloro-li.,7- methanotetrahydroindane and Uo percent related compounds see Monuron 2,U -Dichlorophenyl-1-chloroethylene diethyl phosphate No information available No Information available No information available No information available No information available No information available No information available Commercial mixture of PCS No information available No information available see Chlorfenvinfos 0,0-Diethyl 0-3-chloro-U-aethyl-2- oxo-2H-l-benzopyran-7-yl- phosphorothioate No information available No information available see Co-Ral No information available No information available see Karathane No information available Oxine copper No information available No information available DalaponJfa, Sodium 2,2,3trichloro- propionate 2,2 Dichloropropionlc acid No Information available U, U' -J)lchlorobenzophenone see TDE l,l-Cichloro-2,2-bis (p-chlorophenyl) ethylene 1,1,l-Trichloro-2,2-bis(p-chlorophenyl) ethane 0,0-dimethyl-0-( 2, a^Llchlorovlnyl) phosphate No Information available see DDT Dehydroabiethylamine acetate C-3 ------- Chemical Name Composition Delrad 70 Demeton methyl Dermol Diazinon Dicamba Dicapthon Dichlobenil Dichlone Dichlorofenthion Dichlorophen Dichlorvos Dicofol Dieldrln Dlfolatan Dimanin Dimecron Dimethoate Dimite Dinocap Dinoseb Diphenamid Dipterex Diquat Dispersol SD Disulfoton Di-Syston Diuron DNOC Dobs .JN Dobs 055 Dowicide A Dowicide G Dowpon Doxide (C 102) DSS DTMC Dursban Dylox E-31U EC-90 Technical grade of dehydroabietylamine see Meta-Systox No information available 0,0-Diethyl 0-( 2-isopropyl-6-methyl- U-pyrimidinyl) phosphorothioate see Banvel 0-(2-Chloro-U-nitrophenyl)0,0- dimethyl phosphorothioate 2,6J)ichlorobenzonltrile 2,3-Eichloro-l,U-naphthoquinohe see VC-13 2,2'-Methylenebis [4-chlorophenol] see DDVP 1,l-bis(p-Chlorophenyl)-2,2,2- trichloroethanol Not less than 85 percent of 1,2,3,^, 10,10-hexachloro-6,7-epoxy-l,U,Ua, 5,6,7,8,8a-octahydro-l,U-endo-exo- 5,8-dimethanonaphthanlene cis-N-[(l,l,2,2-Tetrachloroethyl)thio]- U-cyclohexene-1,2-dicarboximide Alkyldlmethylbenzyl ammonium chloride plus urea see Phosphamidon 0,OJ)imethyl S-(N-methylcarbamyl- methyl) phosphorodithioate 1,l-bis(p-Chlorophenyl)ethanol see Karathane 2-( sec-Butyl) -14-,6-dinitrophenol N,N J)imethyl-2,2-diphenylacetamid see Dylox 6,7-Dehydrodipyrido [l,2a:2',l'c] pyrazinedium salts No information available 0,0 J)iethyl-S-[2-(ethylthio)-ethyl] phosphorodithioate see Disulfoton 3-( 3, k J)ichlorophenyl) -1.1-dimethylurea 2-Methyl-U,6-dinitrophenol sodium salt No information available No information available 0-phenylphenol, sodium salt Sodium pehtachlorophenate see Dalapon No information available see Dioctyl sodium sulfosuccinate see Dicofol 0,0-Diethyl 0-3,5,6-trichloro-2- pyridyl phosphoro thioate 0,0-dimethyl (2.2,2-trichloro-l- hydroxyethyl) phosphonate No information available No information available C-U ------- Chemical Name Composition Econal 13086 Emcol H-ll6 Emcol 702 EMID Emkem Spill Wash Empilan Emulsifier .Blend 350 Endosulfan Endothal Endothall Endrin Epichlorohydrin Eptam Eserine sulfate ESSO Solvent FG-155 Essolvene Ethanediol Ethion Ethomeen S-25 Ethyl Parathion EVIK Fenac Fenoprop Fenthion Fentin acetate Fenuron Finasol ESK Finasol OSR2 Finasol SC Flock O.P. Fly Dip Florescein sodivun Fluorokill F.O. 300B Foilzoil Folpet Formothion Furfural Gamlen CW Gamlem D Gamlen OSR 2,U,5-T (as butoxy ethyl ester) No information available No information available 2,U-Dichlorophenoxy-acetamide No information available No information available No information available 6,7,8,9,10,10-Hexachloro-l,5,5a,6,9, 9a-hexahydro-6,9-methano-2,kt3- benzodioxathiepin-3-oxide see Endothall 7-Oxabicylo(2.2.1)heptane-2,3- dicarboxylic acid 1,2,3t b,10,10-Hexachloro-6,7-epoxy- l,4,l^a,5,6,7,8,8a-octahydro-l,U-endo« endo-5> 8-dimethanonaphthalene l-Chloro-2,3-epoxypropane S-Ethyl dipropylthiocarbamate No information available No information available No information available No information available 0,0,0',0'-Tetraethyl S,S'-methylene biophosphorodithioate No information available see Parathion 2-(Ethylamino)-U-(isopropylamino)s 6-(methylthio)-s-triazine 2,3»6-Trlchlorophenylacetic acid or sodium salt No information available 0,0 J)imethyl-0-[ U] (methylthio) -m- tolyl]-phosphorothioate No information available 3 Phenyl-1,1-dimethylurea No information available No information available No information available see Dichlorofenthion 9-(0-carboxyphenyl) «^-hydroxy-3- isoxanthenone Fluoroacetamide No information available No information available N-(Trichloromethylthio)-phthalimide Phosphorodithioic acid 0,0-dimethyl ester S-ester with N-formyl-2- mercapto-N-methylacetamide 2-Furaldehyde No information available No information available No information available C-5 ------- Chemical Name Composition Gamlen FBX Gamlen WBX Gamma BHC Gesapax Globe Terramycin Pet Tabs Gloquat C Gramoxone W Griseofulvin Gulf Agent 1009 Guthion Heptachlor Heptachlor epoxide Herbane Hillvale Fly Dip Histamine phosphate Hobstone OSD Hoc SC 1780 Holl-Chem 622 Houghtosolve Hydrothol 191 IAA laline Brushweed Killer laline grass growth regulator (Regulox) laline Vergicide Weedkiller D laline Vergicide Weedkiller I.C.I. Sunnier Sheep Dip loxynil loxynil Na IPC Jansolv-60 Juglone Karathane Karmex Kelthane Ketoendrin KLofos LAS Lenacil Lindane No information available No information available see Lindane see EVIK Oxytetracycline hydrochloride No information available see Paraquat 7-Chloro-2f,U,6-trimethoxy-6'p-methyl- spiro-[benzofuran-2(3H),l' [2] cyclohexene]-3,^'-dione No information available 0JOJ)iethyl-s-[U-oxo-l,2,3-benzotriazin. 3(to)-ylmethyl]-phosphorodithioate Jk percent l,U,5,6,7,8.8a-Heptachloro- 3a,U,7a-tetrahydro-U,7-methanoindene Photoisomer of Heptachlor 3-(Hexahydro-4,7-methanoinden-5-yl)-1, a-dimethylurea Dichlorofenthion No information available No information available No information available No information available No information available Mono (N,N-dimethylalkylamine) salt of endothall Indole-3-acetic acid No information available see Maleic hydrazide No information available see Vergemaster see Pyrimithate 3,5-Diodo-luhydroxybenzonitrile No information available see Chem Hoe No information available 5-Hydroxy -1, k- naphthoquir.one 2-(1-Methylheptyl)-^,6-dinitrophenyl crotonate see Diuron see Dicofol No information available No information available Linear alkylate stilf onate 3-Cyclohexyl-6,7-dihydro-lH- cyclopentapyrimidine-2, (3H, 5H) - dione 1,2,3,k,5,6-Hexachlorocyclohexane containing at least 99 percent gamma isomer C-6 ------- Chemical Name Composition Linuron Lirostanol Lissapol IPA Llssapol NM Lissapol NX Lubrol APNS Lubrol L Magic Power Malathion Maleic hydrazide Manazon Mancozeb Maneb Manoxol MCPA Mecarbam Mecoprop Menazon Meta-Systox Methoxychlor Methyl parathion Methylpentynol Mevinfos (Mevinphos) Milbex MM Moaspill Mobilsol Molinate Monoxone Monuron Morphothion MS-222 Mystox LSC-P Mystox LSE-L Mystox LSE-P Mystox LSL Mystox LSL-L Mystox LSL-P N-3^52 3-( 3* ^ J)ichlorophenyl) -1-methoxy-l- methylurea Fentin acetate Mixture of the sodium salts of sulfated fatty alcohols Mixture of the sodium salts of sulfated fatty alcohols Mixture of the sodium salts of sulfated fatty alcohols No information available No information available No information available 0,0-Dimethyl phosphorodithioate of diethy1 mercaptosuccinate 1,2-Dihydro-3,6-pyridazinedione No information available No information available Manganous ethylene blsdlthiocarbamate No Information available 2-Methyl-U-chlorophenoxyacetic acid No information available No Information available S-(k,6-Diamino-s-triazin-2-ylmethyl) 0,0-dlmethyl phosphorodithioate Isomeric mixture of 0-[2-(ethylthio) ethyl]0,0-dimethyl phosphorothioate 2,2-bis(p-Methoxyphenyl)-1,1,1- trichloroethane 0,OJ)imethyl 0-p-nitrophenyl phosphorothioate No information available 2-Carbomethoxy-1-methy Ivinyl dimethyl phosphate, evisomer No Information available No Information available No information available No Information available see Crdram No Information available 3-(p-Chlorophenyl)-1,1-dimethylurea No information available Tricaine methanesulfonate No Information available No information available No Information available No information available No Information available No information available Alkyl(C8-Ci8)dimethyl benzyl ammonium chloride C-7 ------- Chemical Name Composition NA Nabam Nalco 201 Nalco 2UO Nalco 2U3 Neburon Nemagon Mew BP 1100 Nitrofurazone Nitrofen Norea Norseman NPH 1253 NFH 1313 Nucidol Diazlnon Sheep Dip Nystatin OD Oil Herder Ordram Omazene (Omazine) OMS-658 Paraquat Parathion PC PCB Pebulate Penetone X Perolin No. Perthane Petrolite W-ll39 Phenkapton (Phencapton) Phenobarbital Phenoxylene Phenoxytol (Phenoxetol) Phorate Phordene Phosalone Phosdrin 2-Chloro-l-nitropropane No information available Disodium ethylenebisdithiocarbamate Chlorinated phenol formulation Organobromine formulation Organosulfur formulation l-n-Butyl-3-(3,ludichlorophenyl)- 1-methylurea 1,2-Dibromo-3-chloropropane No information available 5-Nitro-2-furaldehyde semicarbazone 2,U-Dichlorophenyl p-Nitrophenyl ether see Herban No information available see loxynil see Mecoprop see Diazinon No information available No information available No information available S-Ethyl hexahydro-lH-azepine-1- carbothioate Cupric dihydrazinium sulfate 0-( l4~Bromo-2,5-dichlorophenyl) 0,0-dimethyl phosphorothioate 1,1' -Dimethyl-U,k'-bipyridinium dichloride or 1,1 ^Dinethyl-U,!1- b ipyridiniumb i s [ methylsulfate] 0,0-Diethyl-O-p-nitrophenyl phosphorothioate see Phosphocreatine Polychlorinated biphenyl see Tillam No information available No information available 1,l-Dichloro-2,2-bis(p-ethylphenyl) ethane (88 percent) plus related compounds, 12 percent No information available 0,0-Diethyl-S-(2,5-dichlorophenyl- thioraethyl) phosphorodithioate 5-Ethyl-5-phenylbarbituric acid No information available 2-Phenoxyethanol 0,0-Diethyl S-(ethylthio)-methyl phosphorodithioate No information available see Zolone see Mevinfos C-8 ------- Chemical Name Composition Phosphamidon Phosphocreatine Phostox Photoaldrin Photodieldrin Phygon Picloram PMA Polycell Product Polyclens Polycomplex A Polycomplex A-ll Polyotic Polyram Praparat Alfol WV 1019 Princep Procaine hydrochloride Pro-Noxfish Propanil Propham Protim PVP-Iodine Pyramln Pyrazon Pyrimithate Quinaldine R-1910 Raynap Sol B RD 11639 Reglone Rhodamlne B Ridzlik Roccal Rola OSD Ro-Neet 2-Chloro-N,N-diethyl-3-( dimethoxy- phosphinyloxy)crotonamide N-(Phosphonoamidino)sarcosine No information available Photoisomer of Aldrin Photoisomer of Dieldrin see Dichlone U-Amino-3,5,6-trichloropicolinic acid Pyrldylmercuric acetate Sodium carboxymethyl cellulose No information available No information available No information available Tetracycline hydrochloride Mixture of 5.2 parts by weight (83.9 percent) of ammoniates of [ethylene- bis-(dithiocarbamate)] zinc with 1 part by weight (16.1 percent) ethylene bis[dithiocarbamtic acid], bimolecular and trimolecular cyclic anhydrosulfides and disulfides Hexadecanol 2-Chloro-U, 6-bis( ethylamino) -s-triazine p-Aminobenzoyldiethylaminoethanol hydrochloride Rotenone 3, ^-Dichloropropionanilide see Chera Hoe Copper pentachlorophenate plus chloronaphthalene and dieldrin l-Vinyl-2-pyrrolidinone polymers, iodine complex 5-Amlno-U-chloro-2 phenyl-3 (2H). pyridazinone see Pyramin Phosphorothioic acid 0-[2-dimethylamino)- 6-methyl-U-pyrimidinyl] 0,0-diethyl ester 2-Methylquinoline Ethyl-N,N-diisobutyl thiolcarbamate No information available N-methyl carbamate derivative Diquat-dibromide [ o/.( O-carbcoyphenyl) -6-diethylamino) = 3H-xanthene-3-ylidene]diethylammonium chloride No information available Benzalkonium chloride No Information available S-Ethyl N-ethyl-N-cyclohexylthio. carbamate C-9 ------- Chemical Name Composition Rosin Amine D S.D. 3562 (Bidrin) S.D. 8211 S.D. 8UU? Seasweep Sefoil Sesamex Sevin Shamash R1885 Shell D-50 Silvex Simazine Slickgone 1 Sllckgone 2 Slix S.N. 5215 Snowdrift SC98 Spill Remover Spin-X Streptomycin Sulfate Strobane Sulfisoxazole Sulmet Sumithlon Sutan TCC TCP TDE TEPA' TEPP Tetradifon TFN (Lamprecid) Thimet Thiolutin Thiumet Thyroxine Tinam Tlmsan TN see Delrad 70 Phosphoric acid dimethyl ester, ester with cis-3-hydroxy-N,N-dimethylcrotan. amide Phosphoric acid, 2-chloro-l-(2,5- dichlorophenyl)vinyl dimethyl ester 2-Chloro-l-(2, U, 5-trichlorophenyl) vinyl dimethyl phosphate No information available No information available No information available see Carbaryl No information available 2,^,0 amine (triethanolamine salt) 2-(2,^,5-Trichlorophenoxy)-propionic acid see Princep No information available No information available No information available No information available No Information available No information available No information available 2 C21 H3oN70ip.3HoS(\ Terpene poiycnlorinates Nl-(3,U-Dimethyl-5-isoxazolyl) sulfanilamide (Sodium sulfamethazine) sodium (U,6- dimethyl-2-sulfanilamidopyramldlne) 0,OJ>imethyl O-(U-nltro-m-tolyl)- phosphorothioate S-Ethyl diisobutylthiocarbamate 3,M'-Tricnlorocarbanilide Tritolyl phosphate (CgiHpiC^P) 1,l-Dichloro-2,2-bis(p-chlorophenyl) ethane tris-(l-Aziridlnyl)phosphine oxide Tetraethyl pyrophosphate U'-Chlorophenyl 2,U,5-trichlorophenyl sulfone S^Trlflucromethyl-Ji-nltrophenol, sodium salt see Phorate No information available see Polyram No information available S-Propyl butylethylthiocarbamate 6.25 Percent ethyl mercury phosphate No information available C-10 ------- Chemical Name Composition TOK Tordon C Tordon M Toxaphene Toxion Treflan E.C. Trifluralin Trioxone Trithion Trixabon Tubotox Ureabor Vamidothion Vapam VC-13 Velaicol AR 50G Venzar Vergemaster Vernam Vernolate Weedazol Weedazol T-L WL U205 Young's Defly Zectran Zolone see Nitrofen Picloram (potassium salt) plus mecoprop Picloram (potassium salt) plus MCPA Chlorinated camphene with 67-69 percent chlorine No information available see Triflurolin o/t oft a-Trifluoro-2,6-dinitro-N,N-dipropyl- dipropyl-p-toluidine No information available S-[[p-Chlorophenyl)thio]methyl] o,o-diethyl phosphorodithioate loxynil plus Dimexan, cycluron, BIPC, emulsifier, methyl alcohol, propionic acid, and solvent naphtha see Dinoseb No information available No information available Sodium N-methyl-dithiocarbamate 0-2,l»-Dichlorophenyl 0,0-diethyl phosphorothioate No information available see Lenacil No information available S-Propyl dipropylthiocarbamate see Vernam see Amitrole No information available A triazine see Trithion luDimethylamino 3»5-JCylyl methyl- carbamate 0,0-Diethyl S[(6-chloro-2- oxobenzoxazolin-3-yl)methyl] phosphorodithioate 2,U-Dichlorophenoxyacetic acid 2,U,5-Trichlorophenoxyacetic acid C-U ------- SELECTED WATER RESOURCES ABSTRACTS INPUT TRANSACTION FORM W 4 Title WATER QUALITY CRITERIA DATA BOOK - VOL. 5 - EFFECTS OF CHEMICALS ON AQUATIC LIFE 7. Author(s) Kemp, H. T.\| Little, R. L.) Holcman. V. L.\| Darby, R. L. S. Report T>ate "6. " • $, Performim; Organization Report No, Battalia Manorial Institute, Columbus, Ohio Columbus Laboratories 18050 HLJt . 13»> Tsse of Report and * Covered 15. Supplementary Notes Environmental Protection Agency report number, 18050HLA09/73 16. Abstract Ibis report is an extensive compilation of data on the effects of chemicals on aquatic life which were extracted from literature published during the period 1968.1972. It is an update of an earlier report entitled "Water Quality Criteria Data Book, Volume III, Effects of Chemicals on Aquatic Life" (Kemp, et al., 1971). The data are arranged alphabetically by chemical and are concisely represented in a columnar format which Includes organism names, typo of study, chtmlr^i effect, controlled parameters, significant comments on the test, and source of the data. The data were compiled using a program prepared as part of the work. (Llttle-Battelle) i?a. Descriptors Toxicity, Water pollution effects, Industrial wastes. Pesticides, Aquatic plants, Aquatic animals, Absorption, Reviews, Marine fish, Freshwater fish, Chlorinated hydrocarbon pesticides, Carbamate pesticides. Phosphothioate pesticides. Organic acids, Antibiotics (pesticides), Heavy metals, Metals. Inorganic pesticides, Biochemical oxygen demand, Thiocarbamate pesticides, Triazine pesticides, Organophosphorus pesticides, Polychiorinated biphenyl Organic pesticides, Zoop Chlorophyta, Pyrrophyta, Aquatic Insects, Benthic fauna, „ , . Marine animals, Newts, Toxins, Phenolic pesticides, Dyes, Chemicals, Nutrients. Urea pesticides. Organic cc ankton. Aquatic algae, Marine algae, Wat ophyta, Crustaceans, Mollusks, Annelids, ., Invertebrates, Diatoms, Euglenophyta, Frogs, 17b. Identifiers Anesthetics, Oil dlspersants, Eehlnoderms, Macrolnvertebrates I7c. COWRR Field i Group OJC, OJB, 18. Availability Send To: WATCH MKSOUMCKS KIKNTIflC INFORMATION CENTER UJ. DEPARTMENT Of THE INTERIOR WASHINQTON. OX. *Ot4O Abstractor Robert L. Little iBatfeeUe's Columbus Laboratories, Columbus, Ohio WRSIC 102 (REV. JUNF 1971) U. S. GOVERNMENT PRINTING OFFICE : 1974 720-125/511 -------


'tf
 \
 o WATER POLLUTION CONTROL RESEARCH SERIES 18O50HLA O9/73
 WATER QUALITY CRITERIA  DATA BOOK
              VOLUME 5
EFFECTS OF CHEMICALS ON AQUATIC LIFE
   U.S. ENVIRONMENTAL PROTECTION AGENCY

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        WATER QUALITY CRITERIA DATA BOOK - VOL. 5
           EFFECTS OF CHEMICALS ON AQUATIC LIFE
    (Compilation From the Literature Dated 1968-1972)
                    Homer T.  Kemp
                   Robert L.  Little
                   Verna L. Holoman
                         and
                    Ralph L.  Darby
                Grant Number R-8009^2
               Project Number 18050 HLA
                     Project Officer

                     Robert Andrew
          U.S. Environmental Protection Agency
            National Water Quality Laboratory
               Duluth,  Minnesota  55&OU
                        for the

          OFFICE OF  RESEARCH AND DEVELOPMENT
         U.S. Environmental Protection Agency
               Washington, D.C.  20U60
                    September 1973
For ttte by the Superintendent of Document*. U.S. Government Printing Office, Washington, D.C. 20402

-------
                       EPA REVIEW NOTICE
This report has been reviewed by the Office of Research and
Development, EPA, and approved for publication.  Approval does
not signify that the contents necessarily reflect the views and
policies of the Environmental Protection Agency, nor does
mention of trade names or commercial products constitute
endorsement or recommendation for use.
                               ii

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                             ABSTRACT
This report is an extensive compilation of data on the effects of
chemicals on aquatic life which were extracted from literature published
during the period 1968-1972.  It is an update of an earlier report
entitled "Water Quality Criteria Data Book, Volume III, Effects of
Chemicals on Aquatic Life" (Kemp, et al., 1971).  The data are arranged
alphabetically by chemical and are concisely presented in a columnar
format which includes organism names, type of study, chemical effect,
controlled parameters, significant comments on the test, and source of
the data.  The data were compiled using a program prepared as part of
the work.
                                 iii

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                             CONTENTS
Section                                                       Page
   I    Recommendations                                         1

  II    Introduction                                            3

 III    Procedure                                               5

  IV    Acknowledgements                                        9

   V    References
                                                               11

  VI    Appendices

          A,   Chemical Names                                   A-l
          B.   Species Index                                    B-l
          C.   Chemical Index                                   C-l
                                iv

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                            SECTION I
                          RECOMMENDATIONS
In a prior report (Water Quality Criteria Data Book, Volume III.
Effects of Chemicals on Aquatic Life,  Kemp, H. T., Abrams, J. P.,
Overbeck, R. C., EPA Contract No. 68-01-0007, Project No. 18050 GWV,
1971, 528 pp), several recommendations were presented.  These are
restated as follows with any appropriate comments.

(l)  Establishment of a Chemical Pollution Effect Information Analysis
     Center.The Analytical Methodology Information Center (AMIC)
     sponsored by EPA at Battelle's Columbus Laboratories fills this
     need.

(2)  Preparation of Listings of Chemical Constituents in Effluents by
     Cooperative Input From Industry".   To the authors' knowledge this
     has not been done nor is there a  current attempt to do so.

(3)  Development of a Standard Pattern of Laboratory Evaluations for
     Estimating More Accurately the Effect of Chemicals on Aquatic
     Life.To the authors' knowledge  no standard pattern of laboratory
     evaluations is widely accepted.  Considerable progress has been
     made recently, however, in particular at the National Water Quality
     Laboratory (Duluth, Minnesota) and Virginia Polytechnic Institute.
     Significant efforts to compile bioassay information are in
     progress by Drs. Seba, Stephans,  Tarzwell,  and Weber, respectively,
     located at EPA establishments at  Denver (Colo.), Duluth (Minn.),
     West Kingston (R.I.), and Cincinnati (Ohio).  The classic report
     by McKee and Wolf (1963) is reportedly now  being updated.

(U)  Development of In Situ Field Bipassay Procedures for More Realistic
     Results Than Those Obtained in Laboratory Bioassays.Although
     increased publication of these types of data are apparent, there
     appears to be no large-scale trend in the published literature
     toward this approach.

(5)  Improved Reporting Would Greatly  Enhance the Utility of Chemical
     Effects Data and Allow More Precise Development of Multiyariate"
     Analysis and Mathematical Modeling.There  is a large volume of
     literature on mathematical modeling, a significant amount of which
     is concerned with environmental pollution problems.  For the most
     part, these models are not refined enough for practical utility in
     water pollution problems.  Improved, more detailed data would assist
     greatly in verifying these models and enhancing their practical
     utility.  The next few years will be crucial in this development.

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                            SECTION II
                           INTRODUCTION
This report was prepared to update the document,  "Water Quality Criteria
Book, Volume 3", published in May, 1971 (Kemp,  et al.,  1971).   This
updated version primarily contains extracted information from original
published data, but does not critically review bioassay procedures,
factors affecting chemical toxicity, and other subject  areas important
in the study of water pollution by chemicals.

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                           SECTION III
                            PROCEDURE
The literature search technique primarily involved acquisition of docu-
ments cited in selected sections of annual reviews published in the
Journal of the Water Pollution Control Federation, for the years 1968-1972.
These listings were quite comprehensive,  but were supplemented by addi-
tional documents identified in routine screening activities  of the
Analytical Methodology Information Center (AMIC), Battelle's Columbus
Laboratories.

The data were prepared on punched paper tape so that the  compilation
could be prepared by computer.  In addition, the format of the data  is
such that they can be loaded in the Analytical Methodology Information
Center data base.  Since index terms were added to each line of data,
they can be remotely searched on an on-line real-time computer system
located at Battelle's Columbus Laboratories.  Persons interested in
having access to this system should contact the AMIC Project Officer:

                  Mr. Luther E. Garrett
                  Data & Information Research Division
                  Office of Research & Development
                  Environmental Protection Agency
                  UoU M Street, S.W.
                  Washington, D.C.  2002^

As in the earlier document, extracted data are alphabetically arranged
by chemical name (Appendix A).  In all cases, chemical names and names
(common or scientific) of organisms designated by the authors were used
in this report.  Nomenclature was not changed or corrected in any
manner, that is, when the common name of a fish or a chemical was cited
by an author, this and this alone was used.  Therefore, in using these
data compilations, care should be exercised by the reader to search
chemical and biological synonomy.  For example, in Appendix  B,  Species
Index, data searches on bluegills (Page B-2) should include  the scienti-
fic name, Lepomis macrochirus (page B-6)  for completeness.   Likewise
trade names such as Sevin and Carbaryl should be searched for all data
on this insecticide.

In the authors' Judgment, the most significant toxicity levels in the
aquatic studies are those for fish specifically designated 96-hr TLjQ.
These were usually selected but other values were included when these
were not available.  96-hr TLm is designated as TU to abbreviate this
notation.  T2 was used for U8-hr TLm, and so on.  When £050, LC5Q, and
LD50 were Judged to be essentially equivalent to TLjn or TL5Q» then the
designation T was used to improve the consistency of data presentation.
The authors acknowledge that this is not standard practice and that
there may be important differences in these designations.

-------
Experimental conditions noted by authors in column six are denoted in
lower case letters (see page A-l) with asterisks to indicate when condi-
tions vere controlled.  In some cases, authors briefly referred to previ-
ous publications as a simple means of describing experimental conditions.
No asterisks were included in these instances although some conditions
were probably controlled.  The letters in footnote k were augmented so
that additional conditions could be indicated.  These were light (q)
(r) and (s).

Comments in general are brief, and it is recommended that interested
readers consult the original document for more complete information.

The chemical nature of most industrial effluents is very complex and
difficult to characterize.  Although increased numbers of publications
on this type of pollution problem are being published, there is no
highly satisfactory technique to include these data in the tabular format
used here.  For these reasons, this document must be described as
primarily containing data on the effect of single chemicals or simple
mixtures of chemicals on aquatic life.

There was no attempt to extract data from the various reviews available
since these rarely contained descriptive information concerning experi-
mental conditions.  Furthermore, only selective data are usually
discussed.  In the earlier report, more than 83 review papers were
cited.  To these can be added:

   Becker, C. D., Thatcher, T. 0., "Toxicity of Power Plant Chemicals
   to Aquatic Life",  Battelle Memorial Institute,  Pacific Northwest
   Laboratories. Richland, Washington, Report Nos. WASH-1214-9, UC-11,
   June 1973, 2k& pp.  AMIC-9135.

   Boccardy, J.  A.,  Spaulding, W.  M.,  Jr.,  "Effects of Surface
   Mining on Fish and Wildlife in Appalachia",  Bureau of Sport Fisheries
   and Wildlife, Publication No. 65,  1968.   AMIC-6389.

   Hunt,  E. G.,  Keith, J. 0., "Pesticide Analysis in Fish and Wildlife",
   Analytical Methods for Pesticides,  Plant Growth Regulators, and Food
   Additives, Vol. 5. 1907, p 147.AMIC-5758.

   Johnson, D. W., "Pesticides and Fishes - a Review of Selected
   Literature",  Transactions of the American Fisheries Society, Vol. 97*
   1968,  pp 398*52T;AMIC-5^63.

   Jones,  A.  N.,  Howells,  W.  R., "Recovery  of the River Rheidol",
   Effluent Water Treatment Journal, Vol. 9,  1969, pp 605-610.
   AMIC-5752.

   Seagran, H. L., "Mercury in Great Lakes  Fish",  Limnos,  Vol. 3*  No.  2,
   Summer 1970,  pp 3-10.   AMIC-153.

   Sprague, J. B., "Measurement of Pollutant Toxicity to Fish.
   I.   Bioassay  Methods for Acute  Toxicity",  Water Research,  Vol.  3,
   1969,  PP 793-821.   AMIC-137.

-------
    Sprague,  J. B.,  "Measurement of Pollutant Toxicity to Fish.
    II.  Utilizing and Applying Bioassay Results", Water Research,
    Vol. k, 1970,  pp 3-32.  AMIC-358.

    Swabey, Y. H.,  "The Autopsy of Fish Collected in Fish Kills",
    The Ontario Water Resources Commission, Canada, Publication No.
    11. 1966, 19 PP.

Not reviewed in this report are bioassay procedures, field assessment
techniques,  and related topics.  A number of recent documents would be
useful for this purpose, including:

    Bell, M.  C., "Fisheries Handbook of Engineering Requirements
    and Biological Criteria", Fisheries-Engineering Research Program,
    Corps of  Engineers, North Pacific Div., Portland, Oregon, Contract
    No. DACW57-68-C-0086, 1973, 508 pp.

    Cairns, J., Dickson, K. L., "Biological Methods for the Assessment
    of Water  Quality", ASTM Special Technical Publication No. 528,
    1973, 262 pp.

    Dills, G. G., Rogers, D. T., "Aquatic Community Structure as an
    Indicator of Pollution", Geological Survey of Alabama, Circular 80,
    1972, 25  pp.

    Smith, L. S., Saddler, J. B., Cardwell, R. C., et al., "Responses of
    Teleost Fish to Environmental Stress", University of Washington,
    Fisheries Research Institute, Seattle, Washington, EPA Grant No.
    18050EBK, 1971, 11^ pp.

One report by McPhee and Ruelle (1969) was received too late to include
in  this compilation.  In it are summarized toxicity data for 1888
chemicals against five fish species in a piscicide screening program.

It  was previously suggested that ecological investigators be encouraged
to  include in their  reports:

     •  Positive identity of chemicals under test
     •  Precise description of test organisms
     •  Use of standard test or field methods, where applicable,
          or of procedures if standard methods are not used
     •  Closer definition and control of test conditions

Although papers have generally improved in these regards, not all
investigators include all desirable details of their experimentation.

A species index is included as Appendix B.  Appendix C is a list of
commercial chemicals cited in the data section (Appendix A) and includes,
when available,  the chemical nature of the compound.

-------
                            SECTION IV


                         ACKNOWLEDGEMENTS
The authors wish to express their appreciation to the  Project Officer,
Mr. Robert Andrew,  for his assistance and concern for  this work.
                                             Homer T.  Kemp
                                             Robert L. Little
                                             Verna L.  Holoman
                                             Ralph L.  Darby

-------
                             REFERENCES
Abedi, Z. H., McKinley, W. P.
"ZEBRA FISH EGGS AND LARVAE AS AFLATOXIN BIOASSAY TEST ORGANISMS",  Journal
of the Association of Official Analytical Chemists,  Vol.  51,  No.  U, 1968,
pp 902-905.  AMIC-3712.

Abedi, Z. H., Turton, D. E.
"NOTE ON THE RESPONSE OF ZEBRA FISH LARVAE TO FOLPET AND DIFOLATAN",
Journal of the Association of Official Analytical Chemists, Vol.  51, No.  5,
1968, pp 1105-1109.  AMIC-3717.

Adelman, I. R., Smith, L. L., Jr.
"EFFECT OF HYDROGEN SULFIDE ON NORTHERN PIKE EGGS AND SAC FRY",
Transactions of the American Fisheries Society, Vol. 99,  No.  3,  1970,
pp 501-509.AMIC-5516.

Alabaster, J. S.
"SURVIVAL OF FISH IN l6U HERBICIDES, INSECTICIDES, FUNGICIDES, WETTING
AGENTS AND MISCELLANEOUS SUBSTANCES", International Pest Control, torch/
April 1969, PP 29-35.  AMIC-5U25.

Anderson, J. M.
"EFFECT OF SUBLETHAL DDT ON THE LATERAL LINE OF BROOK TROUT,  SALVELINUS
FONTINALIS", Journal of the Fisheries Research Board of Canada,  Vol. 25,
No. 12, 1968, pp 2677-2652.  AMIC-37651.

Anderson, J. M., Peterson, M. R.
"DDT:  SUBLETHAL EFFECTS ON BROOK TROUT NERVOUS SYSTEM",  Science, Vol. 16U,
April 25, 1969, PP UUo-UUl.  AMIC-3838.

Anderson, J. M., Prins, H. B.
"EFFECTS OF SUBLETHAL DDT ON A SIMPLE REFLEX IN BROOK TROUT", Journal of
the Fisheries Research Board of Canada, Vol. 27, No. 2, 1970, pp 331-331*.
AMIC-3782."""""

Arthur, J. W., Leonard, E. N.
"EFFECTS OF COPPER ON GAMMARUS PSEUDOLIMNAEUS, PHYSA INTEGRA, AND
CAMPELOMA DECISUM IN SOFT WATER", Journal of the Fisheries Research Board
of Canada, Vol. 27, No. 7, July 1970, pp 1277-12«3.AMIC-B67.

Ashley, L. M.
"ACTION OF IRON SALTS IN SOLUTION ON GOLDFISH", The Progressive  Fish-
Culturist, Vol. 32, April 1970, p 109.  AMIC-5^3^

Aubin, A. E., Johansen, P. H.
"THE EFFECTS OF AN ACUTE DDT EXPOSURE ON THE SPONTANEOUS ELECTRICAL
ACTIVITY OF GOLDFISH CEREBELLUM", Canadian Journal of Zoology. Vol. kj,
No. 2, March 1969, PP 163-166.  AMIC-3B35.
                               11

-------
Bache, C. A., Gutenmann, W. H., Lisk, D. J.
 "RESIDUES OF TOTAL MERCURY AND METHYLMERCURIC SALTS IN LAKE TROUT AS A
FUNCTION OF AGE", Science, Vol. 172, May 28, 1971, PP 951-952.  AMIC-3818.

Bahr, T. G., Ball, R. C.
 "ACTION OF DDT ON EVOKED AND SPONTANEOUS ACTIVITY FROM THE RAINBOW TROUT
LATERAL LINE NERVE", Comp, Biochem. Physiol., Vol. 3&A, 1971, PP 279-284,
AMIC-3&08.

Baker, J. T. P.
 "HISTOLOGICAL AND ELECTRON MICROSCOPICAL OBSERVATIONS ON COPPER
POISONING IN THE WINTER FLOUNDER ( PSEUDOPLEURONECTES AMERICANUS) ", Journal
of the Fisheries Research Board of Canada, Vol. 26, No. 11, 1969,
pp 2785-2793.  AMIC-3763.

Baldridge, H. D., Jr.
 "KINETICS OF ONSET OF RESPONSES BY SHARKS TO WATERBORNE DRUGS", Bulletin
of Marine Science, Vol. 19, No. U, 1969, PP 88U-892.  AMIC-3832.

Ballard, J. A., Oliff, W. D.
 "A RAPID METHOD FOR MEASURING THE ACUTE TOXIC ITY OF DISSOLVED MATERIALS
TO MARINE FISHES", Water Research, Vol. 3, 1969, pp 313-333.  AMIC-300.

Batterton, J. C., Boush, G. M. , Matsuraura, F.
 "GROWTH RESPONSE OF BLUE -GREEN ALGAE TO ALDRIN, DIELDRIN, ENDRIN AND
THEIR METABOLITES", Bulletin of Environmental Contamination and
Toxicology, Vol. 6, No. 6, November/December 1971, PP 589-594.  AMIC-lU?l.

Bell, H. L., Nebeker, A. V.
 "PRELIMINARY STUDIES ON THE TOLERANCE AQUATIC INSECTS TO LOW pH", Journal
of the Kansas Entomological Society, Vol. 42, No. 2, April 1969, pp 230-
Bender, M. E.
 "THE TOXICITY OF THE HYDROLYSIS AND BREAKDOWN PRODUCTS OF MALATHION TO THE
FATHEAD MINNOW (PIMEPHALES PROMELAS, RAFINESQUE ) ", Water Research, Vol. 3,
1969, PP 571-582.  AMIC-3787.

Bender, M. E.
"UPTAKE AND RETENTION OF MALATHION BY THE CARP", The Progressive Fish.
Culturist. Vol. 31, July 1969, PP 155-159.  AMIC-5731.

Bender, M. E., Eisele, P.
"LONG TERM EFFECTS OF PESTICIDES ON STREAM INVERTEBRATES", University of
Michigan, Department of Environmental and Industrial Health, Ann Arbor,
Michigan, Project Completion Report, December 1971, 28 pp, PB-206 692.
AMIC-3279.

Bennett, H. J., Day, J. W., Jr.
"ABSORPTION OF ENDRIN BY THE BLUEGILL SUNFISH, LEPOMIS MACROCHIRUS ",
Pesticides Monitoring Journal, Vol. 3, No. U, March 1970, pp 201-203.
AMIC-195.


                                12

-------
Berger, B. L., Lennon, R. E., Hogan, J. W.
"LABORATORY STUDIES ON ANTIMYCIN A AS A FISH TOXICANT",  U.  S. Bureau of
Sport Fisheries and Wildlife, Fish Control Laboratory, La Crosse,
Wisconsin, Investigations in Fish Control No. 26,  February  1969, 21 pp.
AMIC-5^95.

Bhatia, H. L.
"TOXICITY OF SOME PESTICIDES TO PUNTIUS TICTO (HAMILTON)",  Science and
Culture, Vol. 37, No. 3, March 1971, pp 160-161.  AMIC-5^23.

Birdsong, C. L., Avault, J. W., Jr.
"TOXICITY OF CERTAIN CHEMICALS TO JUVENILE POMPANO", The Progressive Fish-
Culturist, Vol. 33, No. 2, April 1971, PP 76-80.  AMIC-5570.

Boer, H. H., Lever, J.
"THE EFFECT OF AMPHENONE B ON THE EGG PRODUCTION OF LYMNAEA STAGNALIS",
Malacologia, Vol. 5, No. 3, 1967, PP U31-UUU.  AMIC-5^5.

Brown, V. M., Dalton, R. A.
"THE ACUTE LETHAL TOXICITY TO RAINBOW TROUT OF MIXTURES  OF  COPPER, PHENOL,
ZINC, AND NICKEL", Journal of Fish Biology, Vol. 2, 1970, pp 211-216.
AMIC-5991*.

Brown, V. M., Jordan, D. H. M., Tiller, B. A.
"THE ACUTE TOXICITY TO RAINBOW TROUT OF FLUCTUATING CONCENTRATIONS AND
MIXTURES OF AMMONIA, PHENOL, AND ZINC", Journal of Fish  Biology, Vol. 1,
1969, pp 1-9.  AMIC-5993.

Brungs, W. A.
"CHRONIC TOXICITY OF ZINC TO THE FATHEAD MINNOW, PIMEPHALES PROMELAS
RAFINESQUE", Transactions of the American Fisheries Society,  Vol.  98,
1969, pp 272-2791AMIC-5458.

Buhler, D. R., Shanks, W. E.
"INFLUENCE OF BODY WEIGHT ON CHRONIC ORAL DDT TOXICITY IN COHO SALMON",
Journal of the Fisheries Research Board of Canada, Vol.  27, No. 2, 1970,
PP 3^7-358.  AMIC-3701.

Burton, D. T.
"LACTIC AND FYRUVIC ACID CHANGES IN BLUEGILL SUNFISH (LEPOMIS MACROCHIRUS
RAFINESQUE) DURING GRADUAL HYPOXIA AT TWO ACCLIMATION TEMPERATURES. (5 AND
20 C)", The ASB Bulletin, Vol. 17, No. 2, April 1970, p  35.  AMIC-6385.

Butler, G. W., Ferguson, D. E., Sadler, C. R.
"EFFECTS OF SUBLETHAL PARATHION EXPOSURE ON THE BLOOD OF GOLDEN SHINERS,
NOTEMIGONUS CRYSOLEUCAS", Journal of the Mississippi Academy of Science,
Vol. 15, 1969, PP 33-36.  AMIC-5977.

Cairns, J., Jr., Sparks, R. E.
"THE USE OF BLUEGILL BREATHING TO DETECT ZINC", Virginia Polytechnic
Institute and State University, Center for Environmental Studies,  Blacksburg,
Virginia, Water Pollution Control Research Series 18050  EDQ 12/71, December
1971, fc5 PP.  AMIC-3232.


                                   13

-------
Cairns, J., Jr., Waller, W. T.
 "THE USE OF FISH MOVEMENT PATTERNS TO MONITOR ZINC", Virginia Polytechnic
 Institute and State University, Center for Environmental Studies, Blacksburg,
Virginia, Water Pollution Control Research Series 18050 EDP 12/71,
December 1971, 55 pp.  AMIC-323L

Cairns, J., Loos, J. J.
 "CHANGED FEEDING RATE OF BRACHYDANIO RERIO (HAMILTON-BUCHANAN) RESULTING
FROM EXPOSURE TO SUBLETHAL CONCENTRATIONS OF ZINC, POTASSIUM BICHROMATE,
AND ALKYL BENZENE SULFONATE", Pennsylvania Academy of Science, 1967,
pp U7-52.  AMIC-5707.

Chen, C. W., Selleck, R. E.
 "A KINETIC MODEL OF FISH TOXICITY THRESHOLD", Journal Water Pollution
Control Federation. Vol. Ul, 1969, PP R29^-R30^.  AMIC-3831.

Coler, R. A., Gunner, H. B., Zuckerman, B. M.
 "TUBIFICID SENSITIVITY TO STREPTOMYCIN", Transactions of the American
Fisheries Society. Vol. 97, 1968, pp 502-503.  AMIC-5^60.

Cooke, A. S.
 "SELECTIVE PREDATION BY NEWTS ON FROG TADPOLES TREATED WITH DDT", Nature,
Vol. 229, January 22, 1971, pp 275-276.  AMIC-381^.

Cordone, A. J., Nicola, S. J.
 "INFLUENCE OF MOLYBDENUM ON THE TROUT AND TROUT FISHING OF CASTLE LAKE",
California Fish and Game, Vol. 56, No. 2, 1970, pp 96-108.  AMIC-5750.

Cowmeadow, M. M., Steege, P. T., Pang, P. K. T., Grant, F. B.
 "A STUDY OF THE PHYSIOLOGICAL EFFECTS OF SULFISOXAZOLE ON THE KILLIFISH",
The Progressive Fish-Culturist, Vol. 31, October 1969, PP 226-228.
AMIC-5736.

Davis, H. C., Hindu, H.
"EFFECTS OF PESTICIDES ON EMBRYONIC DEVELOPMENT OF CLAMS AND OYSTERS AND
ON SURVIVAL AND GROWTH OF THE LARVAE", U.S. Fish and Wildlife Service
Fishery Bulletin, Vol. 67, No. 2, 1969, pp 393-^04.  AMIC-5990.

Dimond, J. B., Getchell, A. S., Blease, J. A.
"ACCUMULATION AND PERSISTENCE OF DDT IN A LOTIC ECOSYSTEM", Journal of the
Fisheries Research Board of Canada, Vol. 28, No. 12, December 197!,
pp 1877-1882.  AMIC-3291.

Duke,  T. W., Lowe, J. I., Wilson, A. J., Jr.
"A POLYCHLORINATED BIPHENYL (AROCLOR 125 *0 IN THE WATER, SEDIMENT, AND
BIOTA OF ESCAMBIA BAY, FLORIDA", Bulletin of Environmental Contamination
and Toxicology, Vol. 5, No. 2, March/April 1970, pp 171-180.  AMIC-720.

Earnest, R. D.
"THE EFFECT OF PARAQUAT ON FISH IN A COLORADO FARM POND", The Progressive
Fish-Culturist, Vol. 33, No. 1, January 1971, PP 27-31.

-------
Eaton, J. G.
"CHRONIC MALATHION TOXICITY TO THE BLUEGILL (LEPOMIS MACROCHIRUS
RAFINESQUE)", Water Research, Vol. k, October 1970,  pp 673-6$f.  AMIC-1312.

Ebel, W. J.
"SUPERSATURATION OF NITROGEN IN THE COLUMBIA RIVER AND ITS EFFECT  ON
SALMON AND STEELHEAD TROUT", Fishery Bulletin, Vol.  68, No. 1,  1969,
pp 1-9.  AMIC-6198.

Eisler, R.
"CADMIUM POISONING IN FUNDULUS HETEROCLITUS (PISCES:  CYPRINODONTIDAE)
AND OTHER MARINE ORGANISMS", Journal of the Fisheries Research  Board of
Canada, Vol. 28, No. 9, September 1971, pp 1225-123^.AMIC-1621.

Eller, L. L.
"PATHOLOGY IN REDEAR SUNFISH EXPOSED TO HYDROTHOL 191", Transactions of
the American Fisheries Society, Vol. 98, 1969, PP 52-59.  AMIC-5^59.

Epifanio, C. E.
"EFFECTS OF DIELDRIN IN SEAWATER ON THE DEVELOPMENT OF TWO SPECIES OF CRAB
LARVAE, LEPTODIUS FLORIDANUS AND PANOPEUS HERBSTII", Marine Biology, Vol.  11,
No. k, December 1971, PP 356-362.  AMIC-2653.

Erickson, S. J., Lackie, N., Maloney, T. E.
"A SCREENING TECHNIQUE FOR ESTIMATING COPPER TOXICITY TO ESTUARINE
PHYTOPLANKTON", Journal Water Pollution Control Federation, Vol. U2, No. 8,
Part 2, August 1970, pp R270-R278.  AMIC-W?.

Ferguson, D. E., Ludke, J. L., Finley, M. T., Murphy, G. G.
"INSECTICIDE^RESISTANT FISHES:  A POTENTIAL HAZARD TO CONSUMERS",
Mississippi Academy of Science Journal, Vol. 13, 1967, PP 138-1^0.
AMIC-5970.

Fletcher, G. L., Hoyle, R. J., Home, D. A.
"YELLOW PHOSPHORUS POLLUTION:  ITS TOXICITY TO SEAWATER-MAINTAINED BROOK
TROUT (SALVELINUS FONTINALIS) AND SMELT (OSMERUS MORDAX)", Journal of the
Fisheries Research Board of Canada, Vol. 27, No. 8,  August 1970,
pp 1379-13W.  AMIC-839.

Fredeen, F. J. H., Duffy, J. R.
"INSECTICIDE RESIDUES IN SOME COMPONENTS OF THE ST.  LAWRENCE RIVER
ECOSYSTEM", Pesticides Monitoring Journal, Vol. 3, No. U, March 1970,
pp 219-226.  AMIC-53^.

Gardner, G. R., Yevich, P. P.
"HISTOLOGICAL AND HEMATOLCGICAL RESPONSES OF AN ESTUARINE TELCOST TO
CADMIUM", Journal of the Fisheries Research Board of Canada, Vol.  27,
No. 12, 1970, pp 210-5-2193.  AMIC-3«27.

Garrison, R. L.
"THE TOXICITY OF PRO-NOXFISH TO SALMONID EGGS AND FRY", The Progressive
Fish-Culturist, Vol. 30, January 1968, pp 35-38.  AMIC-573TK


                                  15

-------
Gibson, J. R., Ludke, J. L., Ferguson, D. E.
"SOUBCES OF ERROR IN THE USE OF FISH-BRAIN ACEIYLCHOLINESTERASE ACTIVITY
AS A MONITOR FOR POLLUTION", Bulletin of Environmental Contamination and
Toxicology, Vol. U, No. 1, 1969, pp 17-23.  AMIC-3783.

Gibson, J. R., Ludke, J. L.
 "EFFECT OF SESAMEX ON BRAIN ACETTLCHOLINESTERASE INHIBITION BY
PARATHION IN FISHES", Bulletin of Environmental Contamination and
Toxicology. Vol. 6, No. 2, 1971, PP 97-99.  AMIC-3799.

Grant, B. F., Mehrle, P. M.
 "CHRONIC ENDRIN POISONING IN GOLDFISH, CARASSIUS AURATUS", Journal of the
Fisheries Research Board of Canada. Vol. 27, No. 12, 1970, pp 2225-223^.
AMIC-3t42b.

Grosch, D. S.
 "POISONING WITH DDT:  SECOND- AND THIRD-YEAR REPRODUCTIVE PERFORMANCE
OF ARTEMIA",  Pollution  - Foundations for Today. Vol. 2, 1971, pp 8U-85.
AKLC-2090.                           '

Guthrie, J. E., Acres,  0. E.
 "TOXICITY TO  FISH OF TWO ORGANIC REACTOR COOLANTS", BvT»0tin of
Environmental CpntaMnatipn and Toxicology. Vol. 5, No. 2, March/
April 1970, pp W-5-151.AMIC-721.

 Hones, D., Krueger, H., Pilcher, K. S.
 "PENTACHLOROPHENOL AND  CULTURES OF EMBRYONIC CELLS FROM ONCORHYNCHUS
 KISUTCH",  Proceedings of the Western Pharmacological Society, Vol. 13*
 1970* PP 62-68.  AMIC-5753.

 Hansen,  D.J., Parrish,  P.R., Lowe, J.I., Wilson, A.J.,  Jr., Wilson, P.D.
 "CHRONIC TOXICITY, UPTAKE, AND RETENTION OF AROCLOR 125^ IN TWO ESTUARINE
 FISHES", Bulletin  of Environmental Contamination and Toxicology, Vol. 6,
 No.  2, March/April 1971, pp 113-119.  AMIC-1811.

 Hatfield,  C,  T.
 "EFFECTS OF DDT  LARVICIDING ON AQUATIC FAUNA OF BOBBY'S BROOK,
 LABRADOR", Canadian Fish Culturist. Vol. Uo, 1969, pp 61-72.  AMIC-5770.

 Haven, D.  S.
 "LEVELS  OF THE HERBICIDE DIQUAT IN TWO ESTUARINE MOLLUSCS AND IN THE
 WATER AND MUD",  Journal of Science. Vol. 20, 1969, pp 51-53.  AMIC-5978.

 Hazel, C.  R., Meith, S. J.
 "BIOASSAY OF  KING  SALMON EGGS AND SAC FRY  IN COPPER SOLUTIONS", California
 Fish and Game. Vol.  56, No. 2,  1970, pp  121-12U.  AMIC-5572.

 Henderson, C.,  Inglis,  A., Johnson, W. L.
 "RESIDUES IN FISH, WILDLIFE, AND ESTUARIES. ORGANOCHLORINE INSECTICIDE
 RESIDUES IN FISH - FALL 1969 NATIONAL PESTICIDE MONITORING PROGRAM",
 Pesticides Monitoring Journal.  Vol.  5, No.  1,  June 1971, PP 1-11.
 AMIC-1W7.
                                   16

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Hiltilaran, R. C.
"A PROPOSED BIOCHEMICAL MECHANISM OF THE TOXIC ACTION OF DDT", Trans-
actions of the Illinois Academy of Science, Vol. 6k t No. 1, 197!,
PP U6-5^.  AMIC-5975.

Hogan, R. L. , Roeloes, E. W.
"CONCENTRATIONS OF DIELDRIN IN THE BLOOD AND BRAIN OF THE GREEN
SUNFISH, LEPOMIS CYANELLUS, AT DEATH", Journal of the Fisheries Research
Board of Canada. Vol. 28, No. k, 1971, pp 610-612.
Holland, H. T., Coppage, D. L.
"SENSITIVITY TO PESTICIDES IN THREE GENERATIONS OF SHEEPSHEAD MINNOWS",
Bulletin of Environmental Contamination and Toxicology, Vol. 5, No. U,
July /August 1970, pp 3o2-367.  AMIC-726.

Houston, A. H., Madden, J. A., Woods, R. J., Miles, H. M.
'VARIATIONS IN THE BLOOD AND TISSUE CHEMISTRY OF BROOK TROUT, SALVELINUS
FONTINALIS, SUBSEQUENT TO HANDLING, ANESTHESIA, AND SURGERY", Journal of
the Fisheries Research Board of Canada, Vol. 28, No. 5, 1971,
PP 035-642.  AMIC-3B22.

Houston, A. H., Madden, J. A., Woods, R. J., Miles, H. M.
"SOME PHYSIOLOGICAL EFFECTS OF HANDLING AND TRICAINE METHANE -SULPHONATE
ANESTHETIZATION UPON THE BROOK TROUT, SALVELINUS FONTINALIS", Journal of
the Fisheries Research Board of Canada, Vol. 28, No. 5, May 1971,
PP 025.533.  AMIC-3B23.

Rowland, R. M.
"INTERACTION OF ANTIMYCIN A AND ROTENONE IN FISH BIOASSAYS", The
Progressive Flsh-Culturist. Vol. 31, January 1969, pp 33-31*. "AMIC-5725.

Hubschman, J. H.
"EFFECTS OF COPPER ON THE CRAYFISH ORCONECTES RUSTICUS (GIRARD)
I.  ACUTE TOXICITY", Crustaceana, Vol. 12, 1967, PP 33-^2.  AMIC-5985.

Huner, J. V., Dovden, B. F., Bennett, H. J.
"THE EFFECTS OF ENDRIN ON THE OXYGEN CONSUMPTION OF THE BLUEGILL SUNFISH
LEPOMIS MACROCHIRUS", Louisiana Academy of Sciences. Vol. 30, 19^7,
PP 80-86.  AMIC-5981.

Jackson, D. A., Anderson, J. M., Gardner, D. R.
"FURTHER INVESTIGATIONS OF THE EFFECT OF DDT ON LEARNING IN FISH",
Canadian Journal of Zoology, Vol. ^8, 1970, pp 577-580.  AMIC-3837.

Johnson, B. T., Saunders, C. R., Sanders, H. 0.
"BIOLOGICAL MAGNIFICATION AND DEGRADATION OF DDT AND ALDRIN BY FRESHWATER
INVERTEBRATES", Journal of the Fisheries Research Board of Canada,  Vol.
28, No. 5, 1971, pp 705-709.  AMIC-3«20.

Kawatski, J. A., Schmulbach, J. C.
"ACCUMULATION OF INSECTICIDE IN FRESHWATER OSTRACODS EXPOSED
CONTINUOUSLY TO SUBLETHAL CONCENTRATIONS OF ALDRIN OR DIELDRIN",  Trans-
actions of the American Fisheries Society, Vol. 100, No. 3, 1971,
PP ^5-567.  AMIC-5506.


                                   17

-------
Kihlstrom, J. E., Lundberg, C., Hulth, L.
 "NUMBER OF EGGS AND YOUNG PRODUCED BY ZEBRAFISHES (BRACHYDANIO RERIO,
HAM. .BUCK. )  SPAWNING IN WATER CONTAINING SMALL AMOUNTS OF PHENYLMERCURIC
ACETATE", Environmental Research, Vol. k, No. U, October 1971,
PP 355-359.  AMIC-2707.

Konar,  S. K.
 "TOXIC ITY OF HEPTACHLOR TO AQUATIC LIFE", Journal Water Pollution Control
Federation.  Vol. te, No. 8, Part 2, August 1970, pp R299-B303.
 Konar, S. K.
 "EFFECTS OF HEPTACHLOR AND NICOTINE ON THE BARBELS OF A CATFISH
 (HETEROPNEUSTES FOSSILIS)", The Progressive Fish-Culturist. Vol. 31,
 1969, pp 62-63.  AMIC-5726.

 Konar, S. K.
 "NICOTINE AS A FISH POISON", The Progressive Fish-Culturist. Vol. 32,
 April 1970, pp 103-10U.  AMIC-5^35.

 Konar, S. K.
 "LABORATORY STUDIES ON TWO ORGANOPHOSPHORUS INSECTICIDES, DDVP AND
 PHOSPHAMIDON, AS SELECTIVE TOXICANTS", Transactions of the American
 Fisheries Society. Vol. 98, No.  3, 1969, PP ^30-^37.  AMIC-5^53.

 Konar, S. K.
 "LETHAL EFFECTS OF THE INSECTICIDE DDVP ON THE EGGS AND HATCHLINGS OF THE
 SNAKE -HEAD, CHANNA PUNCTATUS (Bl) (OPHICCEPHALIFORMES:  OPHIOCEPHA1IDAE)",
 Japanese Journal of Ichthyology, Vol. 15, No. 3, February 15, 1969,
 PP 130-133.  AMic-6388.

 Lane, C. E., Scura, E. D.
 "EFFECTS OF DIELDRIN ON GLUTAMIC OXALOACETIC TRANSAMINASE IN POECILIA
 LATIPINNA", Journal of the Fisheries Research Board of Canada, Vol. 27,
 No. 10, October 1970, pp 1869-1871.  AMIC-1283.

 LaRoche, G., Eialer, R., Tarzwen, C. M.
 "BIOASSAY PROCEDURES FOR OIL AND OIL DISPERSANT TOXICITY EVALUATION",
 Journal Water Pollution Control Federation, Vol. ^2, No. 11, November
 1970, pp 1982-1989.  AMIC-445.

Lincer, J. L., Solon, J, M., Nair, J. H., Ill
 'DDT AND ENDRIN FISH TOXICITY UNDER STATIC VERSUS DYNAMIC BIOASSAY
CONDITIONS", Transactions of the American Fisheries Society. Vol. 99,
No. 1, 1970, pp 13-19.  AMIC-5509.

Linn, J. D., Stanley, R. L.
 "TDE RESIDUES IN CLEAR LAKE ANIMALS", California Fish and Game, Vol. 55,
No. 3, 1969, PP 16U-178.  AMIC-5521.
                                   18

-------
Lloyd, R., White, W. R.
"EFFECT OF HIGH CONCENTRATION OF CARBON DIOXIDE ON THE IONIC COMPOSITION
OF RAINBOW TROUT BLOOD", Nature, Vol. 216, December 30, 19^7, PP 13^
AMIC-3721.

Loeb, H. A., Starkey, R. J.
"SURVIVAL OF BURIED BULLHEADS SUBJECTED TO U'-IODO-3JfITROSALICYLANILIDE",
New York Fish and Game Journal, Vol. 13, No. 2, July 1966, pp 196-205.
AMIC-6199.

Lucas, H. F., Jr., Edgington, D. N.
"CONCENTRATIONS OF TRACE ELEMENTS IN GREAT LAKES FISHES", Journal of the
Fisheries Research Board of Canada, Vol. 27, No. k, 1970, pp 677-6W.
AMIC-3778.

Lyraan, L. D., Tompkins, W. A., McCann, J. A.
"RESIDUES IN FISH, WILDLIFE, AND ESTUARIES", Pesticides Monitoring Journal,
Vol. 2, No. 3, December 1968, pp 109-122.  AMIC-3b39.

Macek, K. J.
"REPRODUCTION IN BROOK TROUT (SALVELINUS FONTINALIS) FED SUBLETHAL
CONCENTRATIONS OF DDT", Journal of the Fisheries Research Board of
Canada, Vol. 25, No. 9, 1968, pp 1707-1796.AMIC-3716.

Macek, K. J., Korn, S.
"SIGNIFICANCE OF THE FOOD CHAIN IN DDT ACCUMULATION BY FISH", Journal of
the Fisheries Research Board of Canada, Vol. 27, No. 8, August 1970,
pp 1496-11*98.AMIC-tm.

Macek, K. J., McAllister, W. A.
"INSECTICIDE SUSCEPTIBILITY OF SOME COMMON FISH FAMILY REPRESENTATIVES",
Transactions of the American Fisheries Society, No. 1, 1970, pp 20-27.
AMIC-5510."~

MacPhee, C., Ruelle, R.
"A CHEMICAL SELECTIVELY LETHAL TO SQUAWFISH (PTYCHOCHEILUS OREGONENSIS
AND P. UMPQUAE)", Transactions of the American Fisheries Society, Vol.  98,
1969, pp 676-68^.  AMIC-5^50.

Manion, P. J.
"EVALUATION OF LAMPREY IARVICIDES IN THE BIG GARLIC RIVER AND SAUX HEAD
LAKE", Journal of the Fisheries Research Board of Canada, Vol. 26, No.  11,
1969, PP 3077-3002.  AMIC-3761.

Mann, H.
"BIOLOGICAL EFFECTS OF FATTY ALCOHOLS ON FRESHWATER ANIMALS", Internationale
Revue der Gesamten Hydrobiologie, Vol. 56, No. U, 1971, PP 599-607,
AMIC-3079.
                                  19

-------
Marking, L. L.
"TOXICm OF METHYLPENTYNOL TO SELECTED FISHES", U. S. Bureau of Sport
Fisheries and Wildlife, Fish Control Laboratory, La Crosse, Wisconsin,
Investigations in Fish Control No. 30, February 1969, 7 pp.  AMIC-5^77.

Marking, L. L.
"JUGLONE (5-HYDROXY-l,U-NAPHTHOQUINONE) AS A FISH TOXICANT", Transactions
of the American Fisheries Society, Vol. 99, No. 3, 1970, pp 510-514*.
AMIC-5517.

Marking, L. L.
"TOXICITY OF RHODAMINE B AND FLUORESCEIN SODIUM TO FISH AND THEIR
COMPATIBILITY WITH ANTIMTCIN A", The Progressive Fish-Culturist, Vol. 31,
July 1969, pp 139-lte.  AMIC-5729.

Mathur, D. S.
"TOXICITY OF ALDRIN TO CERTAIN FISH", Science and Culture, Vol. 35, No. 8,
August 1969, pp 418-^19.  AMIC-5^22.

Mawdesley-Thomas, L. E.
"TOXIC CHEMICALS - THE RISK TO FISH", New Scientist, Vol. k?t No. 73^,
January Ik, 1971, pp 7^-75.  AMIC-10561

Mclngvale, C. R., Ludke, L., Ferguson, D. E.
"OXYGEN CONSUMPTION OF ENDRIN-SUSCEPTIBLE AND ENDRIN-RESISTANT GAMBUSIA
DURING SUBLETHAL AND ACUTE ENDRIN EXPOSURE", Journal of the Mississippi
Academy of Science, Vol. lU, 1968, pp 116-1211AMIC-5V75.

McKim, J. M., Christensen, G. M., Hunt, E. P.
"CHANGES IN THE BLOOD OF BROOK TROUT (SALVELINUS FONTINALIS) AFTER SHORT-
TERM AND LONG-TERM EXPOSURE TO COPPER", Journal of the Fisheries Research
Board of Canada, Vol. 27, No. 10, 1970, pp Ibb13-1889.AMIC-382B.

McKim, J. M., Benoit, D. A.
"EFFECTS OF LONG-TERM EXPOSURES TO COPPER ON SURVIVAL, GROWTH, AND
REPRODUCTION OF BROOK TROUT (SALVELINUS FONTINALIS)", Journal of the
Fisheries Research Board of Canada. Vol. 28, No. 5, 1971, PP 655-662.
AMIC-3821.

McKone, C. E., Young, R. G., Bache, C. A., Lisk, D. J.
"RAPID UPTAKE OF MERCURIC ION BY GOLDFISH", Analytical Chemistry, Vol. 5,
No. 11, November 1971, PP 1138-1139.  AMIC-15957

McReynolds, H. E.
"PRACTICALITY OF ENDRIN AS A FISH TOXICANT", Indiana Academy of Science
Proceedings. Vol. 79, 1969, pp 1U8-161.  AMIC-lOtJ.

Metcalf, R. L., Sangha, G. K., Kapoor, I. P.
"MODEL ECOSYSTEM FOR THE EVALUATION OF PESTICIDE BIODEGRADABILITY AND
ECOLOGICAL MAGNIFICATION", Environmental Science and Technology. Vol. 5,
No. 8, August 1971, pp 709-713.  AMIC-1495.


                                  20

-------
Minchew, C. D., Ferguson, D. E.
"TOXICITIES OF SIX INSECTICIDES TO RESISTANT AND SUSCEPTIBLE GREEN
SUNFISH AND GOLDEN SHINERS IN STATIC BIOASSAYS", Journal of the
Mississippi Academy of Science. Vol. 15, 1970,  pp 29-32.   AMIC-5U71.

Mitchum, D. L., Moore, T. D.
"EFFICACY OF DI-N-BUTYL-TIN OXIDE ON AN INTESTINAL FLUKE, CREPIDOSTOMUM
FARIONIS, IN GOLDEN TROUT", The Progressive Fish-Culturist, Vol.  31,
July 1969, PP 1U3-1W.  AMIC-5730.

Morris, R. L., Johnson, L. G.
"DIEIDRIN LEVELS IN FISH FROM IOWA STREAMS", Pesticides Monitoring
Journal, Vol. 5, No. 1, June 1971, PP 12-16. AMIC-1452.

Moubry, R. J., Helm, J. M., Myrdal, G. R.
"CHLORINATED PESTICIDE RESIDUES IN AN AQUATIC ENVIRONMENT LOCATED
ADJACENT TO A COMMERCIAL ORCHARD", Pesticides Monitoring Journal, Vol.
1, No. U, March 1968, pp 27-29.  AMIC-3753.

Mount, D. I., Boyle, H. W.
"PARATHION - USE OF BLOOD CONCENTRATION TO DIAGNOSE MORTALITY OF FISH",
Environmental Science and Technology, Vol. 3, No. 11, November 1969,
pp 1103-1105.  AMIC-11.

Mount, D. I., Stephan, C. E.
"CHRONIC TOXICITY OF COPPER TO THE FATHEAD MINNOW (PIMEPHALES PROMELAS)
IN SOFT WATER", Journal of the Fisheries Research Board of Canada, Vol.
26, No. 9, 1969, pp 2U49-2457.  AMIC-3765.

Munson, T. 0.
"CHLORINATED HYDROCARBON RESIDUES IN MARINE ANIMALS OF SOUTHERN
CALIFORNIA", Bulletin of Environmental Contamination and Toxicology,
Vol. lf No. 1*, April 1972, pp 223-220.  AMIC-3096.

Murphy, P. G.
"THE EFFECT OF SIZE ON THE UPTAKE OF DDT FROM WATER BY FISH", Bulletin of
Environmental Contamination and Toxicology, Vol. 6, No. 1, January/
February 1971, PP 20-23.AMIC-1005.

Murphy, P. G., Murphy, J. V.
"CORRELATIONS BETWEEN RESPIRATION AND DIRECT UPTAKE OF DDT IN THE MOSQUITO
FISH GAMBUSIA AFFINIS", Bulletin of Environmental Contamination and
Toxicology, Vol. 6, No. 6, November/December 1971, PP 501-500.  AMIC-1U70.

Naqyi, S. M., Ferguson, D. E.
"LEVELS OF INSECTICIDE RESISTANCE IN FRESHWATER SHRIMP,  PALAEMONETES
KADIAKENSIS", Transactions of the American Fisheries Society, No. U,
1970, pp 696-699.  AMIC-5519.
                                   21

-------
 Naqvi, S. M., Ferguson, D. E.
 "PESTICIDE TOLERANCES OF SELECTED FRESHWATER INVERTEBRATES",  Journal of
 the Mississippi Academy of Science,  Vol. lU, 1969,  pp 121-1271   AMIC-5979.

 Nimmo, D. R., Blackman, R. R.,  Wilson, A.  J.,  Forester,  J.
 "TOXICITY AND DISTRIBUTION OF AROCLOR 125U IN THE PINK SHRIMP PENAEUS
 DUORARUM", Marine Biology, Vol. 11,  No. 3, November 1971, pp  191-197.
 AMIC-26U5.

 Nunogawa, J. H., Burbank,  N.  C.,  Jr.,  Young, R.  H.  F., Lau, L. S.
 "RELATIVE TOXIC HIES OF SELECTED CHEMICALS TO SEVERAL SPECIES OF
 TROPICAL FISH", University of Hawaii,  Water Resources Research Center,
 Honolulu, Hawaii, Technical Report No. Uo, August 1970,  38 pp,
 PB-196-312.  AMIC-6567.

 Otto, N. E.
 "ALGAECIDAL EVALUATION AND ENVIRONMENTAL STUDY OF MAT PRODUCTING BLUE.
 GREEN ALGAE", Bureau of Reclamation, Office of Chief Engineer, Denver,
 Colorado, Report No. REC-OCE-70-25,  July 1970, 31 pp, PB-19^  808.
 AMIC-892.

 O'Hara, J.
 "ALTERATIONS IN OXYGEN CONSUMPTION BY  BLUEGILLS  EXPOSED  TO SUBLETHAL
 TREATMENT WITH COPPER", Water Research, Vol. 5,  1971, pp 321-327.
 AMIC-3793.

 Pal,  R. N., Gopalakrishnan, V.
 "PRELIMINARY TRIALS  ON THE TOXICITY OF 'ALGISTAT' TO FISH AND ALGAE",
 Fishery Technology,  Vol. 5, No. 2, July 1968, pp 101-103.  AMIC-575U.

 Patrick, R., Cairns, J., Jr., Scheier,  A.
 "THE  RELATIVE SENSITIVITY  OF  DIATOMS,  SNAILS, AND FISH TO TWENTY COMMON
 CONSTITUENTS OF INDUSTRIAL WASTES", The Progressive  Flsh-Culturist.  Vol.
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 Pickering, Q. H., Thatcher, T.  0.
 "THE CHRONIC TOXICITY OF LINEAR ALKYLATE SULFONATE ( LAS) TO PIMEPHAIES
 PROMELAS, RAFINESQUE ", Journal  Water Pollution Control Federation. Vol.
 1*2, No. 2, Part 1, February 1970, pp 2^3-254-.  AMIC-65.

 Portmann, J. E., Wilson, K. W.
 "THE TOXICITY OF lUo SUBSTANCES TO THE BROWN SHRIMP AND OTHER MARINE
ANIMALS", Ministry of Agriculture, Fisheries and Food, Fisheries Laboratory,
Burnham-on-Crouch, Essex, England, Shellfish Information Leaflet No. 22,
December 1971, 12 pp.  AMIC-7701.

Post, G., Schroeder, T. R.
 "THE TOXICITY OF FOUR INSECTICIDES TO FOUR SALMONID SPECIES", Bulletin
of Environmental Contamination  and Toxicology, Vol. 6, No. 2, March/
April 1971, PP 1^-155.  AMIC-1812.
                                  22

-------
Rabe, F. W., Wissmar, R. C.
"SOME EFFECTS OF ANTIMJfCIN IN AN OLIGOTROFHIC LAKE", The Progressive Fish.
Culturist, Vol. 31, July 1969, P 163.  AMIC-5732.

Rachlin, J. W., Perlmutter, A.
"RESPONSE OF AN INBRED STRAIN OF FIATYFISH AND THE FATHEAD MINNOW TO ZINC",
The Progressive Fish-Culturist, Vol. 30, October 1968, pp 103-207.
AMIC-5722.

Rachlin, J. W., Perlrautter, A.
"RESPONSE OF RAINBOW TROUT CELLS IN CULTURE TO SELECTED CONCENTRATIONS OF
ZINC SULFATE", The Progressive Flsh-CulturistJ Vol. 31, April 1969,
pp 9^-98.  AMIC-5728.

Ragab, M. T. H.
'ttAS CHOMATOGRAPHIC ANALYSIS OF MALATHION IN WATER AND IN FlSH",
Bulletin of Environmental Contamination and Toxicology, Vol. 3* No. 3,
1968, pp 155-163.  AMIC-3728.

Raynes, A. E., Ryback, R. S.
"EFFECT OF ALCOHOL AND CONGENERS ON AGGRESSIVE RESPONSE IN BETTA
SPLENDENS", Boston City Hospital, Alcohol Study Unit, Boston,
Massachusetts.  AMIC-5712.

Ray, J., Stevens, V.
"USING BAYTEX TO CONTROL CRAYFISH IN PONDS", The Progressive Fish-
Culturist, Vol. 32, January 1970, pp 58-60.  AMIC-54§3.

Reinert, R. E.
"PESTICIDE CONCENTRATIONS IN GREAT LAKES", Pesticides Monitoring Journal,
Vol. 3, No. U, March 1970, pp 233-2^0.
Risebrough, R. W., Rieche, P., Peakall, D. B., Herman, S. G., Kirven, M. N.
"POLYCHLORINATED BIPHENYLS IN THE GLOBAL ECOSYSTEM", Nature, Vol. 220,
December 1^, 1968, pp 1098-1102.  AMIC-38UU.

Rucker, R. R., Amend, D. F.
"ABSORPTION AND RETENTION OF ORGANIC MERCURIALS BY RAINBOW TROUT AND
CHINOOK AND SOCKEYE SALMON", The Progressive Fish-Culturist, Vol. 31,
October 1969, PP 197-201.  AMIC -57337

Sanders, H. 0.
"TOXICITIES OF SOME HERBICIDES TO SIX SPECIES OF FRESHWATER CRUSTACEANS",
Journal Water Pollution Control Federation, Vol. U2, No. 8, Part 1, August
1970, pp 15^-1550,  AMIC-453.

Savitz, J.
"EFFECT OF M.S. 222 ON NITROGEN EXCRETION OF THE BLUEGILL (LEPOMIS
mCROCHIRUS)". Journal of the Eli sha Mitchell Scientific Society.
Vol. 85, No. 4, 1909, pp 150-151.  AMIC -583».
                                23

-------
 Shaw,  T.  L.,  Brown, V. M.
 "HEAVY METALS AMD  THE FERTILIZATION OF RAINBOW TROUT EGGS", Nature, Vol.
 230, No.  5291, torch 26, 1971, P 251.  AMIC-1444.

 Smith,  J. W., Grigoropoulos, S. G.
 "TOXIC EFFECTS OF  TRACE ORGANICS ON FISH", Journal American Water Works
 Association,  Vol.  62, No. 8, August 1970, pp 499-506.AMIC-993.

 Solon,  J. M., Lincer, J. L., Nair, J. H., Ill
 "THE EFFECT OF SUBLETHAL CONCENTRATION OF LAS ON THE ACUTE TOXICITY OF
 VARIOUS INSECTICIDES TO THE FATHEAD MINNOW (PIMEPHALES PROMEIAS
 RAFINESQUE)", Water Research, Vol. 3, 1969, PP 767-775.  AMIC-3785.

 Sonstelie,  L. C.
 "THE EFFECTS  OF DDT ON THE INSECT POPULATION OF TROUT CREEK", University
 of Utah,  Salt Lake City, Utah, Dissertation Abstracts No. 70-3796, 1969,
 136 pp.   AMIC-964.

 Sparks, R.  E., Cairns, J., Jr., Cross, F. B.
 "SOME  EFFECTS OF A NEUTRAL MIXTURE OF CALCIUM OXIDE AND SULFURIC ACID ON
 CHANNEL CATFISH ICTALURUS PUNCTATUS (RAFINESQUE)", Transactions of the
 Kansas Academy of  Science, Vol. 72, No. 1, Spring 1969, pp 1-15.
 AMIC-5902.

 Sprague,  J. B.
 "AVOIDANCE  REACTIONS OF RAINBOW TROUT TO ZINC SULPHATE SOLUTIONS", Water
 Research, Vol. 2,  1968, pp 367-372.  AMIC-3760.

 Stapleton,  R. P.
 "TRACE ELEMENTS IN TISSUES OF THE CALICO BASS PARALABRAX CLATHRATUS
 (GIRARD)",  Bulletin of the Southern California Academy of Sciences, Vol.
 67, No. 1,  1968, pp 49-58.AMIC-59BO.

 Stock,  J. N., Cope, 0. B.
 "SOME EFFECTS OF TEPA, AN INSECT CHEMOSTERILANT, ON THE GUPPY, POECILIA
 RETICULATA", Transactions of the American Fisheries Society, Vol. 98,
 1969, PP 280-28TAMIC-5457.
Stout, V. F.
"PESTICIDE LEVELS IN FISH OF THE NORTHEAST PACIFIC", Bulletin of Environ-
mental Contamination and Toxicology, Vol. 3, No. 4, 1968, pp 240-245.
AMIC-3784.

Tracy, H. B., Lee, R. A., Woelke, C. E., Sariborn, G.
"RELATIVE TOXICITIES AND DISPERSING^EVALUATIONS OF ELEVEN OIL-DISPERSING
PRODUCTS", Journal Water Pollution Control Federation, Vol. 41, No. 12,
December 1959, PP 2062-2069.  AMIC-3B34.

Uthe, J. F., Bligh, E. G.
"PRELIMINARY SURVEY OF HEAVY METAL CONTAMINATION OF CANADIAN FRESHWATER
FISH", Journal of the Fisheries Research Board of Canada, Vol. 28, No. 5,
1971, pp 786-780-.  AMIC-3819.
                                   24

-------
Vaala, S. S., Mitchell, R. B., Anthony, A.
"CYTOPHOTOMETRIC STUDIES OF DNA IN CIRCULATING ERYTHROCYTES OF BROOK TROUT
EXPOSED TO ACID pH", Proceedings of the Pennsylvania Academy of Science.
Vol. 1*3, 1969, PP 191-19^.  AKTC-5709.

Wamlck, S. L., Bell, H. L.
"THE ACUTE TOXICITY OF SOME HEAVY METALS TO DIFFERENT SPECIES OF
AQUATIC INSECTS", Journal Water Pollution Control Federation! Vol. Ul,  No.
2, Part 1, February 1959, PP 200-204.  AMIC-37&7.

Wedemeyer, G.
"THE STRESS OF FORMALIN TREATMENTS IN RAINBOW TROUT (SALMO GAIRDNERI) AND
COHO SALMON (ONCORHYNCHUS KISUTCH)", Journal of the Fisheries Research
Board of Canada, Vol. 28, No. 12, December 1971, PP 1899-1904.AMIC-328?.

Wedemeyer, G., Ross, A. J., Smith, L.
"SOME METABOLIC EFFECTS OF BACTERIAL ENDOTOXINS IN SALMONID FISHES",
Journal of the Fisheries Research Board of Canada, Vol. 26, No. 1, 1969,
pp 115-122.AMIC-377^.

Weir, P. A., Hine, C. H.
"EFFECTS OF VARIOUS METALS ON BEHAVIOR OF CONDITIONED GOLDFISH", Archives
of Environmental Health, Vol. 20, January 1970, pp U5-51.  AMIC-739.

Wellborn, T. L., Jr.
"TOXICITY OF SOME COMPOUNDS TO STRIPED BASS FINGERLINGS", The Progressive
Fish-Culturist, Vol. 33, No. 1, January 1971, pp 32-36.  AMIC-5571.

Wellborn, T. L., Jr.
"THE TOXICITY OF NINE THERAPEUTIC AND HERBICIDAL COMPOUNDS TO STRIPED BASS",
The Progressive Fish-Culturist. Vol. 31, January 1969, PP 27-32.  AMIC-5723.

Wildish, D. J.
"THE TOXITY OF POLYCHLORINATED BIPHENYLS (PCB) IN SEA WATER TO GAMMARUS
OCEANICUS", Bulletin of Environmental Contamination and Toxicology.
Vol. 5, No. 3, 1970, pp 202-204.  AMIC-69.

Wilson, D. C., Bond, C. E.
"THE EFFECTS OF THE HERBICIDES DIQUAT AND DICHLOBENIL (CASORON) ON POND
INVERTEBRATES.  PART I.  ACUTE TOXICITY", Transactions of the American
Fisheries Society, Vol. 98, 1969, PP ^38-^3-  AMIC-5^52.

Wisely, B., Blick, R. A. P.
"MORTALITY OF MARINE INVERTEBRATE LARVAE IN MERCURY, COPPER, AND ZINC
SOLUTIONS", Australian Journal of Marine and Freshwater Research, Vol.  18,
1967, pp 63-72.  AMIC-570B.

Woodhead, P. M. J.
"AN EFFECT OF THYROXDJE UPON THE SWIMMING OF COD", Journal of the
Fisheries Research Board of Canada, Vol. 27, No. 12, 1970, pp 2337-2338.
AMIC-3825.
                                 25

-------
Worthley, E. 0., Schott, C. D.
 "THE COMPARATIVE EFFECTS OF CS AND VARIOUS POLLUTANTS ON FRESH WATER
PHYTOPLANKTON COLONIES OF WOLFFIA PAPULIFERA THOMPSON", U.S. Department
of  the Army, Biomedical Laboratory, Edgewood Arsenal, Maryland,
Technical Report EATR 1*595, December 1971, P 12.  AMIC-3233.

Young, R. G., St. John, L., Lisk, D. J.
 "DEGRADATION OF DDT BY GOLDFISH", Bulletin of Environmental Contamination
and Toxicology, Vol. 6, No. U, 1971, PP 351-35^.  AMIC-3796.

Zillich, J., Wuerthele, M.
 "THE TOXIC EFFECTS OF THE LANSING WASTEWATER TREATMENT PLANT EFFLUENT
TO  THE FATHEAD MINNOW, PIMEPHALES PROMELAS", Michigan Department of
Natural Resources, Water Resources Commission, Lansing, Michigan, paper,
January 19-20, 1970, k pp.  AMIC-2899.

Zillich, J., Wuerthele, M.
 "THE TOXIC EFFECTS OF THE GRANDVILLE WASTEWATER TREATMENT PLANT EFFLUENT
TO  THE FATHEAD MINNOW, PIMEPHALES PROMELAS", Michigan Department of
Natural Resources, Water Resources Commission, Lansing, Michigan,
Report, November 17-21, 1969, 10 pp.  AMIC-2898.

Zillich, J.
 "THE TOXICITY OF THE WYOMING WASTEWATER TREATMENT PLANT EFFLUENT TO THE
FATHEAD MINNOW AND THE WHITE SUCKER - JULY 28 - AUGUST 1, 1969", Michigan
Department of Natural Resources, Water Resources Commission, Lansing,
Michigan, Paper, 1969, 7 pp.  AMIC-2906.

Zillich, J.
"A  BIOLOGICAL EVALUATION OF SIX CHEMICALS USED TO DISPERSE OIL SPILLS",
Michigan Department of Natural Resources, Water Resources Commission,
Lansing, Michigan, Paper, April 1969, 12 pp.  AMIC-2909.

Zitko, V., Aiken, D. E., Tibbo, S. N., Besch, K. W. T., Anderson, J. M.
"TOXICITY OF YELLOW PHOSPHORUS TO HERRING (CLUPEA HARENGUS), ATLANTIC
SALMON (SALMO SALAR), LOBSTER (HOMARUS AMERICANUS), AND BEACH FLEA
(GAMMARUS OCEANICUS)", Journal of the Fisheries Research Board of
Canada, Vol. 27, No. 1, 1970, pp 21-29.AMIC-3817.

Zitko, V.
"POLYCHLORINATED BIPHENYLS (PCB) SOLUBILIZED IN WATER BY NONIONIC
SURFACTANTS FOR STUDIES OF TOXICITY TO AQUATIC ANIMALS", Bulletin of
Environmental Contamination and Toxicology,  Vol. 5, No. 3, 1970,
pp 279-205.  AMIC-23.

Zitko, V.
"POLYCHLORINATED BIPHENYLS AND ORGANOCHLORINE PESTICIDES IN SOME
FRESHWATER AND MARINE FISHES", Bulletin of Environmental Contamination
and Toxicology, Vol. 6, No. 5, 1971, PP 464-470.  AMIC-3715.
                                  26

-------
SECTION VI






APPENDICES

-------
                     Abbreviations for  Appendix A
 Note;  Names of chemicals and organisms are as given by the various
        authors.  Readers should search for alternate, common,  and/or
        scientific names of both chemical and aquatic species.

 (1)  Letters represent:
          B • bioassay, used in combination with S = static,
              CF m continuous flow, A = acute, and CH = chronic.
          L " laboratory bioassay.
        BOD « biochemical oxygen demand.
          F • field study, used in combination with R - river,  stream,
              creek, etc., L = pond,  M - marine, E = estuarine, and
              0 • other (port facility, flooded area, etc.).
 (2)  Field location is indicated by abbreviation of the state  or  county.
 (3)  The number indicates ppm (mg/1),  unless otherwise indicated  by
      appropriate designations.  The  letters within parentheses following
      indicate T - TI^, K = kill, SB  » sublethal effects, NTE - no toxic
      effect.   The number following these indicates the time in days
      (unless  otherwise noted) at which observations were made.  ECjg,
      LCjQ, and similar designations  for 50 percent lethality were all
      considered as TLn and designated  as such.   The numbers within
      parentheses following these designations indicate the  time in  days
      when the effect was observed.
 (4)  The following indicate (when  followed by an asterisk the variable
      was controlled):
          a •  water temperature
          b -  ambient air temperature
          c -  pH
          d -  alkalinity (total,  phenolphthalein or caustic)
          e •  dissolved oxygen
          f -  hardness  (total,  carbonate, Mg,  or CaO)
          g -  turbidity
          h m  oxidation-reduction potential
          i «  chloride  as  Cl
          j -  BOD,  5  day;  (J)  - BOD, short-term
          k -  COD
          1 -  nitrogen  (as  N02  or N03)
          m -  ammonia nitrogen  as NH3
          n •  phosphate (total, ortho-,  or poly)
          o -  solids  (total,  fixed, volatile,  or suspended)
          p •  C02
          q -  light
          r -  flow rate
          s «  sound
 (5)   Other miscellaneous  abbreviations  are:
         SM -  sterilized media
       SSM -  synthetic  seawater medium
       NSW •  natural seawater
       MSC • maximum safe  concentration

The AMlC-xxxx number following each reference is the accession number
which was  assigned by  the Analytical Methodology Information Center  to
facilitate  location of original documents.
                                A-l

-------
  Cowound
•BS
»BS
*BS
•as
•cataldehyde
*cet aldehyde
•cataldehyde
Toxicltyt Experimental
Active Variables,
Field Field Ingredient, Controlled
Or9anls» Study Location Pp» or Noted Comments
Br achy dan lo BSt —
rerlo






Lepoals BSt. ~
•acrochlrus L






Nltzsehlaj as*. —
linear!* L


Phvsa BS*, —
heferostrooha L


Leoomls BSA, —
•eerochlrus L






Nltzsehla BSk. ~
II near is L


Crangon BS* —
crangon
32 (SB*) a,e, and
synthetic
tt 1 1 ii # 1 nn
o 1 1 u • i on
Hater





17.* (Tfc) a»,e, and
synthetic
dilution
•ater




10 (T5I a«,e, and
synthetic
dilution
water
31.. 2 IT*) a*,e, and
synthetic
dilution
Mater
53 IT*) a»,e, and
synthetic
d 1 1 ut 1 on
Mater




236.6 ITS) ,..., ,„„
synthetic
dilution
Mater
greater than A«(contin-
100 IT2) uoua, aor-
Feedlnq behavior «as affected by
zinc, chromluir, and Aq<; in that more tl«e
amounts of food. Feeding resoonse Mas
alto affrctft'l by aeration, feeding
schedule, light Intensity, and outside
disturbances. The authors note that «uch
•ore MorK is needed to establish the
reliability of this procedure.
This study Mas conducted to
determine the relative toxieities of ?0
common constituents of Industrial wastes
to a fish, an atqi, and *n invertebrate.
The experiments Mere conducted over a
ID-year period for varied purposes. The
authors recoaoend hloassays Mith at least
three conoonents of the food Neb.
same as above



sa*e as above



This study Mas conducted to
determine the relative toxlcltles of 20
coiinon constituents of industrial Hastes
to a fish, an alga, an-) an invertebrate.
The experiments Mere conducted over a
10-year period for varied purposes. The
authors recommend bloassays Mith at least
three components of the food web.
same as above



same as above

ation, soa-
Reference
Cairns, et
al (19.67> ,
*MIC— 5707






Patrick, et
al (I960).
*NIC-«7?0





Patrick, et
al M,
»MIC-57?8

Patrick, et
al 111691.
»*IIC-5720

Patrick, et
al (196M.
«NIC-5720





Patrick, «t
at (196S).
• MIC-57Z!)

Porteann, at
81(1971),
4MIC-7701

-------
                                                                               water, and
                                                                               daily
                                                                               solution
                                                                               renewal)
         Acetic acid
                              Leooals
                              aaerechlrus
                                   BSA,
                                   I
                                                               75  (T*>
>

U>
         Acetic ecld
Acetic acid
                              Nltrschla
                              Uncarts
                     Carclnus
                     eaenas
                                   BSA,
                                   L
                                   BSA
                                                               7* (T5»
                                                      180 (TZl
         Aeatle acid
                              Crangon
                              cranqon
                                            BS*   —
                                                      greater  than
                                                      100 (TZl
 a»,e,  and
 synthetic
 dilution
 water
a*, a, and
synthetic
dilution
water
«»(contin-
uous aer-
ation, sea.
water, and
daily
solution
renewal)
         This  study  was conducted  to
 determine the relatlve' toxlclties of  ?fl
 contort constituents of Industrial  wastes
 to a fish,  an alqa, and an Invertebrate.
 The experiments  Here conducted  over a
 10-year  period for  varied  purposes.   The
 authors  reconnend bloftssays  with  at least
 three  components of the food xeb.

       sane as above
Patrick, at
at  (1968),
a«( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
         One  hundred-forty  surface active
 aq»nts,  solvent  enulslflers,  pesticides,
,polychlorlnate
-------
           Compound
         Ice tone
>
I
         •cetene
         acetone
Toxlclty, Experimental
Active Variables.
Field Field Ingredient, Controlled
Organise Study Location Ppm or Noted Comments

Lepomls BSA, —
macrochlrus L






Nltzschla BSA, —
linear Is L


Hercenarla L
•ercenarla
(eggs)

8,3011 

found to be essential.
This study was conducted to
determine the relative toxlcltles of ?0
common constituents of industrial wastes
to a fish, an alga, and an invertebrate.
The experiments were conducted over a
10-vear period for varied purposes. The
authors recommend bioassays with at least
three components of the food web.
same as above


The effect of 5? pesticides on
embryonic development of clais and
oysters was reported. Synerqlstlc
Reference

Patrick,
al (1968)
AMIC-5770





Patrick,
al (196$)
ANIC-S7?0



et
*






et
•


Davis, et
al (19691.
AHIC-^990

I
          •eaten*
         •cetene
         Acetone
Hercenarl a
•ercenarla
(larvae!

Crassostrea
virqlnlca
                              Phormidium
                              ••blauuB
                                            L     —
                                            L

                                                                qreater  than
                                                                100.0  (T13)
                                                                qreater  than
                                                                100.0  (TZ)
                                                                0.5-10.0  (NTE)   —
                                                                                           effects  with  solvents  Here  also  reported.
                                                                                            Host  of  the  compounds affected
                                                                                           develoc«ent more  than  survival.  Some.
                                                                                           however,  drastically reduced  larval
                                                                                           growth.   The  authors point  out the
                                                                                           necessity of  evaluating the effects  of
                                                                                           pesticides on all  life stages of an
                                                                                           organism and  note  the  possibility of
                                                                                           selecting chemicals  for pest control  that
                                                                                           Mould  not have serious effect on
                                                                                           shellfish.

                                                                                                 same as above
                                                                                                  same  as  above
                                                                    Of 7i> chemicals evaluated as
                                                            algieides. only 9 were more toxic than
                                                            CuSOnts Has more toxic tnan CuS04 alone.
Davis, eta!
(19591 ,
»MIC-5990

Oavls, et
at (19691,
AMIC-S990
otto
  AHIC-892
-------
          »erlflavin*
          (neutral)
Moron*
saxatllis
(finger!ings)
                                             BS»
                                                                16.*
>
vn
          tcrlftavine
TraeMnotus
carollnu»
(Juvenile)
                                             BSk
                                                                llV-llt  (Ti>)
          AeroI•In
Rasbora       8CFA
heteromorphe  and
              BSA
          Acrrlonltril*
Crangon
crangon
                                             BS*   ~
                           Coooer ehiorairlne Mas also found to be
                           more toxic thar CuSO2$
                           wHe range of toxlclty spanning 12 orders
                           of magnitude.  Knowing the toxlcity and
                           percentage of all co«oonents of a
                           formulation did not result In easy
                           predictability of the toxlclty of a
                           mixture oT materials.  Somot lines
                           pesticides were most toxic In hard water
                           and sometimes the opposite was true.
                           Testing the actual material as soM was
                           found to be essential.

10-3J (Til       a«(contln-         One hundred-forty surface active  Portmann, et
                uoua aer-  agents, solvent emulslfiers, pesticides,  al (1971),
                aticn,  sea- potychlorlnated blohenyls, pure           AHIC-7701
                water,  and Inorganic, and organic chemicals Hera
                dally      evaluated against as many as ten marine
                                                                0.06  IT2)
 a,c,e,f,1,
 and
 sulfate,
 sodium,
 calcium,
 potassium,
 magnesium,
 carbonate,
 bicarbon-
 ate,
 ••Unity

a»,c,o,f,
hard IBWJ
or soft
(SW) syn-
thetic
dilution
water, or
seawater
for some
species
-------
  Compound
                       Orqanlsn
                                   Field  Field
                                   Study Location
                                 Toxic! ty,
                                 Active
                                 Ingredient,
                                   Ppm
                                   Experimental
                                   Variables,
                                   Control led
                                   or Noted
                                                                                                 Comments
                                                     Reference
                                                                      solution
                                                                      renewal)
Ac tu*o I
                     Steelh»ad
                     trout
                     (IIngerlIngs)
                                   BSA
Actusol
Actusal
• Matoxln ai
•gridID
                     Coho salmon   BSA
                     (fInqerllnqs) In
                                   lltu
                    Hood Canal,
                    Hoodsportt
                    Nash.
Pacific
oyster
(larvae)

Br achydanto
rerlo (eggs)
Rasbora
heteromorpha
                                   BS»   —
BCF*  ~
and
BSA
                                                      ".0.0 IK)
                                                      ?«. 0-1.0.0 CS)
                                                      1.0 (X)
                                                      1.9 
synthetic
dilution
Mater, or
seawatfir
for some
species
Aldrln IC-1«
labelled)
Oaphnia aaqna BCF
(adult)
                                                          (residue)
                                                            orqanlsms.  The authors noted that most
                                                            published data of this type deal with
                                                            toxlclty of ehenlcals to freshwater
                                                            organisms.

                                                                    Evaluation of 11 oil dlspersants
                                                            resulted In a ranklnq for each and a
                                                            recommendation for use according to the
                                                            ranking.  Ranking was based on toxlclty
                                                            and oil dispersal effectiveness.  Corexlt
                                                            TT&H acoeared to have the least toxlclty
                                                            with fair to good oil dispersion
                                                            caoablllty.

                                                                   same as above
                                                                                        sane as above
                                                      This fungal toxin was acutely
                                              toxic to Rrachydanlo rerlo embryos and
                                              larvae, especially the latter.  The
                                              authors suggest this response as an
                                              easily performed assay for aflatoxln.

                                                     same as above
                                                                                        Tracy, «*
                                                                                        al I
                                                      Magnification of DOT and Aldrln
                                              taqo«rt with R-tu occurred rapidly.
                                              Bloloqlcal magnification factors of 2900
                                              to llfc.100 denendlnq on the species were
                                              found for DDT, and Z?,AOQ to Ul.OOO for
                                              Aldrln.  Harked deqradatlon of DOT as
                                              determined by analysis for DOT
                                              metabolites occurred.  The authors
                                              conclude that aquatic Invertebrates
                                              Influence Duality and quantity of
                                              Insecticide residue passed via the fish
                                                                                        Tracev* *'
                                                                                        al (1969>«
                                                                                        Tracy, *r
                                                                                        a I (19691*
                                                     Abedl,«t
                                                     (1968),
Alabaster
(1969)
5«5
                                                     Johnson,et
                                                     at  11971' •
                                                     AMlC-38?»
-------
Aldrln IC-1*
I•belled)
Aldrln (C-l*
labelled)
Hexaqctnla
blllneata
(nyaoh)

Chi ranonus
so. (larval
                                   BCF   —
                                   BCF
                                                      0.7 (residue)   a*
                                                       0.5  (residue)   a*
                                                                                 food chain.

                                                                                        sane as above
                                                                                         same as above
                                                     Johnsoni et
                                                     al (l"»7il,
                                                     AHIC-38ZO

                                                     Johnson,et
                                                     al (197D,
                                                     AHIC-3878
Aldrln (C-l*
labelled!
Oaohnla naqna BCF
(adult)
                                                       0.0001  (SB3)    a*
                                                                                         same  as above
                                                     Johnson,et
                                                     al (1971),
                                                     A1IC-3S79
• Idrln  (C-l*
labelled)
Aldrln  CC-1*
labelled)
Hexagenla
blllneata
(nyoph)

Ch Iron-onus
so. (larva)
                                   BCF
                                   8CF    —
                                                       0.0001  (SB3)    a*
                                                       0.0001(383)      a*
                                                                                         sane  as above
                                                                                         same  as above
                                                     Johnson., et
                                                     al (1971),
                                                     Johnson, et
                                                     al (19711,
                                                     AMIC-3«?0
• Idrln
• Idrln
Aldrln
                     Fish  (not
                     specifled)
                     Tctalurus
                     punetatus
Woima
papullfera
                                    FRLO   Tana
                                 greater  Than
                                 0.001-0.91  
                                  0.91
                                  (accumulation,
                                  SB)
                                          Ha«deslev-
                                          Thomas
                                          H<*71) , AMIC-
                                                      1000 (X)
~                 Approximate toxlcltles of
           nuovrous ce«tlcin>s commonly us»d In
           nrltaln *rre summarized. An excellent
           brief, grnvral discussion of toxlcity
           testinq is also present.

—                 Edible flesh of fish collected    Horrls, et
           fro* rivers, lakes, ponds, and reservoirs al(1971),
           was analyzed.  Fish taKen In areas        AMIC-H5?
           receiving agricultural runoff shOHed
           highest accumulation,  especial Iv In
           bottoa feeding fish.
Hunter1*            All compounds wore harmful to    Worthier, at
medium     duckweed to  some degree.  Decreased       al (1971),
diluted    populations wore noted at non-1 a thai      AMIC-3233
1:5        concentrations and  sone comrounO.3
           (Hnlathlan and 2,!|-D) caused teratocenlc
           effects at concentrations as low as 1 ?p».
• Idrln
•Idrln
Aldrln
•Idrln
Anacvstls
nldulans
Aqaenellua
quadrup-
lloatun
                     Channa
                     punctata
                     Channa
                     punctata

                                    BSA
                                    BSA
                                                       NTE
                                                       NTE
a»,c*,r
SM
a»»e»,r
SH
                                  0.000166  (K Z   a*,C
                                  hr)
                                  0.000333  (K 30  a*,c
                                  • in)
        Hetabollc products of Aldrln,     Batterton,
Oleldrln, and Endrin can be as toxic as   et al (1971),
the parent compounds, as sho»n by  00     AMZC-1471
measurement.

       s»«e as above                      Ratterton,
                                          et al
                                          (197l),AHIC-
                                          1*71

        Aldrin Has shown to be more toxic Katbur (1969),
than DOT, BHC, dieIdrln, and llndane.     AM1C-5U22
Behavioral responses prior'to death Her*?
recorded In some detail.
                                                                                         same  as above
                                                     Hathur
                                                     (19691.»MIC-
-------
Compound

Ifdrln
Afdrln

Organism

Puntlus
sophore
Puntlus
soohore
arcuate
Field Field
Study Location

BSA
BSA
BSCH -•
and
A
Toxiclty,
Active
Ingredient,
Ppn

O.OOD166 (K 1.5
hr)
0.000133 (K 30
•tin)
1130-1700
ppbresldue 6i»
HK)
Experimental
Variables.
Control led
or Noted

a»,c
a»,c
0.01
neeKs
each
Comments

same as above
same as above
and 0.1 cpb of the toxicants Tor ?5
after Hhich time the amounts added
Reference
51.3?
Hathur
(1969), AHIC-
51.22
Mathur
(1969>,AHIC-
51.22
al (1971),
AMIC-5506
                                                                                  the  Initial amounts.  Ulothrlx occurred
                                                                                  spontaneously In the  test  tanks.  The
                                                                                  results shoH  that chronic  accumulations
                                                                                  In Chlamydotheca exceeded  levels which
                                                                                  Here  toxic  In acute tests.  Residues  In
                                                                                  Chlaroydotheca ranqed  fro1"  12.000 to
                                                                                  260,300 times Greater than the
                                                                                  theoretical Concentrations In the water!
                                                                                  those  In Ulothrlx Here 235-3,000 tines
                                                                                  exposure levels.
Aldrln
Aldrin
                     Chlamydotheca BSCH
                     arcuata       and
                                   A
                     Ulothrlx SD.  BSCH  —
                                                      0.0015 (Tl)
                                                      0.00001-0.001
                                                      <120-1700 opb
                                                      residue 33-<>8
                                                                                        same as above
                                                                                        same as above
                                                                                        Kaxatskl, et
                                                                                        al
                                                                                        (197H ,A1IC-
                                                                                        5506

                                                                                                  et
                                                                                        al  (1971),
                                                                                        AMIC-5506
Aldrln
                     Tubltex
                     tub If ex
FL
and
BSA
Belzonli
Miss.
                                                      3.0 (NTE)
        The response of
pesticide-resistant aauatlc organisms to
various pesticides Has coloured to the
response of non-resistant species.
Pesticide-resistant soecles Here
collected at Belzonl and non-resistant
soeeles at State Colleqe.  Cooeoods.
clans, snails,, and sludqe norms from
Belzonl were considerably more tolerant
to pesticides than the non-resistant
organisms.  The authors note that the
effect of Increased tolerance In the
organisms is an Increase In the amount of
pesticide residues available to animals
of higher trophic levels.
Naqvi, et al

(1969),AHIC-
5979
-------
                     Hercan aria
                     awcenarla
                      (ego.0
                                          1ha*>
                                  11.0 (T2)
 • Idrln
 •lelstat
 •Iqlstat
 • lolstat
 Alglstat
Alglatat
Algletat
• Ikyl dlaethyl
benzy I aeaienl ua
chloride
                      Mercenarla
                      aercenarla
                      I larvae)
                      Cyprlnus
                      car pie
 Splroqyra
                                    L     —
                                    t     —

                      OscillatorI*  L     —
 Anabaena
Hierocratla
Buglena
Phoraldiua   L
•abiautn

 O.»l IT 1Z)      ~




 8.66 (Kl        —





 •.8 flO



 0.66 (Kl



 0.66 (K>



0.66 (K)



1.0 (1TB)
 0.5-10.0
 I33p«rc*nt
 qrewth
 inhibited Ul
                                    Tt>» atliiet ol  5? pesticides on    Davli. at al
                            ••bryonlc d«v*loo*«nt  of cfavs and        (19691 <
                            oysters was reported.   Synerqlstle        *HIC-5998
                            eftaets with solvents  were also reported.
                             Host of the compounds affected
                            dcveloraent a ore than  survival.  Soaat
                            however t drastically reduced larval
                            aronth.  The authors point out the
                            necessity of evaluating the effects of
                            pesticides on all  life stages of an
                            orqanisa and note the possibility of
                            selecting chealcals for pest control that
                            would not have serious effect on
                            shellfish.
                                                                    saae as above
        The results are described as
preliminary and  the authors state that
further testing  should be conducted
before Aigistat  Is used In hatcheries and
rearing ponds.

       saae as above
                                                                                                       Davis* at a I

                                                                                                       I 19691. *HIC-
                                                                                                       599«

                                                                                                       Pal, et al
                                                                                                       (1968)f
                                                                                                                            Pat,  et al
                                                                                                                            (196S).
                                                                                         saaa as above
                                                                                         saae as above
                                                                   sama as
       aaM ai above
Pal, et al
(1968),»KIC-
575*

Pal, et al
(196«>,
*NIC-57S*

Pal. et al
(1963).
AMXC-57A

Pal, et al
U9&8).
        Of 7it chemicals evaluated as
alqlcldesi only 9 were more toxic than
CuSOd.  None Inhibited growth of
mat-forming alqae for more than 2 weeks.
CuSOi> formulated with certain wetting
aqents was more toxic than CuSCH alone.
Cooper chlorarlne was also found to be
more toxic than CuSOU.  No Netting agents
were found to be Inhibitory at the
concentrations investigated (0.09 and
0.005 ppal.  Also reported are factors
affecting growth of algae In canals to
Otto (19701,
  AHIC-S9Z
-------
   Compound
                        Organism
                                    Field  Field
                                    Study Location
                                   Toxlclty,
                                   Active
                                   Ingredient,
                                    Ppa
                  Experimental
                  Variables i
                  Control led
                  or Noted
                                                                                                  Comments
                                                                                                                            Reference
 Allldene dlacetate   Phormldlum
                      amblguum
 • Myl  alcohol
                      Hertenart a
                      •ercenarla
                                  0.5-10.0  (NTEJ  —
                                                       1.03 ITZ)
•llrl alcohol
Ally I alcohol
Mercenarla
•ercenarla
(larvaa)

Asterlas
rubens

                                   BSA
                                                      less than fl.?5  —
                                                      (T1Z)
                                                      10-33 CTZ)
Ally I  alcohol
                     Cardlua edule USA
                                 greater  than
                                 100 ITZ»
                                                                      a*(contin-
                                                                      uous aer-
                                                                      ation, aea.
                                                                      water, and
                                                                      daily
                                                                      solution
                                                                      renewal)
                                                                      a* (contin-
                                                                      uous aer-
                                                                      ation,  sea-
                                                                      water,  and
                                                                      duUy
                                                                      solution
                                                                      ranawel)
                                                              determine whether there were  leads to
                                                              controlling algae by environmental
                                                              •anaqevent.  No practical environmental
                                                              means Mere found.

                                                                    same as above
                                                                                                                            Ottoll970),
                                                                                                       Davis, «t al
                                                                     The effect of ?2 pesticides on
                                                             embryonic devetooment of clams and
                                                             oysters was reported.  Synerqlstlc        (1969),AMIC-
                                                             effects Nith solvents were also reoorted. 5990
                                                              Host of the eonoounds affected
                                                             development more than survival.  Some,
                                                             however, drastically reduced larval
                                                             qrpwth.  The authors colnt out the
                                                             necessity of evatuatinq the effects  of
                                                             Pesticides on all  life stages of  an
                                                             orqinlsm and note  the possibility of
                                                             selecting chemicals  for nest control  that
                                                             would not  have serious effect on
                                                             shell fish.
                                                                                        same as above
                                    One hundred-forty  surface  active
                            agents,  solvent  emulslfiers,  pesticides,
                            polychlorinated  blohenyls,  pure
                            Inorganic,  and organic chemicals were
                            evaluated against  as many as  ten marine
                            organisms*   The  authors noted that most
                            published data of  this type deal with
                            toxlclty of  chemicals to freshwater
                            organisms.
                                  same as above
                                                     Davis,et al
                                                     ei96<>>,
                                                     AHIC-5990

                                                     Portmann, et
                                                     al (I97l>,
                                                                     Portmann, et
                                                                     al (19711.
                                                                     ANIC-7701
Ally! alcohol
Crangon
                                   BSA    —
qraater than
»»(contin-
                                                                                       sane as above
                                                                                                                          Portaann, et
-------
dlehlorobenzal-
doxine HOI
                     crangon
                     Rasbora
                     heteroBorpha
BCFA
and
BSA
                                                      100  (T?)
                                                      190 (T2)
aloha-aBlno-2,6      Rasbora
dleniorobenzaldoxlne Ftttaroaoroha
BCF*  —
and
BSA
                                                          (T?)
Alualnua
                     Paratabrax
                     clathratus
                                   FN
      Scattergood  25  (dorsal
      Steaa Plantf nusclc
      Los          reaid.ua)
      Angeles,Cal.
 Aluainua
                      Paralabrax
                      clathratus
                                    FH
       Catallna     a  (dorsal
       Islandi Cat. muscle
                   residue)
uous aer-
ation, sea-
water, and
dally
solution
renewal)

«o,c,e,r,
bard I Hit;
or soft
ISO syn-
thetic
dilution
water, or
seawater
for aor.e
species
        One hundred sixty-four
DestlcldeSt netting aqentSt and
miscellaneous Hater pollutants showed a
xlde rungr of toxlclty soainlnq 12 orders
of magnitude.  Knowing the toxlclty and
percentage of 81 I  components of a
formulation did not result In easy
predictability of  the toxlclty of a
mixture of materials.  Sometimes
pesticides were most toxic In hard water
and sometimes the  oooosite was true.
Testing the actual material as sold was
found to be essential.

       sa*e as above
                                                                      hard (HHt
                                                                      or soft
                                                                      ISM)
                                                                      synthetic
                                                                      dilution
                                                                      Hater, or
                                                                      seaMater
                                                                      for son*
                                                                      species
                                                                                        al  (14711,
                                                                                        AHIC-7701
Alabaster
(19691,
ANIC-51.35
                                          Alabaster
                                          (19691.
                                          AHTC-S4.2S
        Fish collected  from an effluent
 ploe  of a  steam  olant and  from offshore
 waters of  Catalina  Island  were analyzed
 for trace  element content.  Trace element
 content of  the effluent  water was at
 least 5 times greater than that  of  normal
 se? water  for cadmium,  coooer, nickel,
 zinc, and  chromium.  Livers of fish from
 the effluent were nearly twice the  size
 of  those  from the ocean.  Greatest
 differences In concentration  occurred
 with  aluirinum, cadmium,  and nickel.
 Silver, barium,  lithium, and  lead showed
 the least  differences.   The author
 concluded  that trace element  analysis of
 tissues could be used to determine  the
 effect of  pollutants on marine organisms.

       sane as above
Staoleton
(19681.AHIC-
5980
                                          Staoleton
                                           (1968).
-------
Compound

Alualnua
*'-Im-
Alualnua
Alualnua
Alualnua
Alualnua
Alualnua
Alualnua
Alualnu*
Alualrtww
Organls*

Paral abrax
cl athratus
Paralabrax
el athratus
Paralabrax
el athratus
Paral »br ax
cl athratus
Paralabrax
clathretus
(gravid
leaales)
Paralabrax
el athratus
Paral abrax
cl athratus
Paral abrax
el athratus
Paral abrax
cl athratus
Paralabrax
el athratus
Toxlclty, Experlaental
Active Variables.
Field Field Ingredient, Controlled
Study Location Poa or Noted Coeaents

FH Scatterqood 2? (ventral — saae as above
Steaa Plant, nuscle
Los raaidue)
Angeles, Cal.
FH Catallna 8 (ventral — saae as above
Island, Cal. auscl*
residue)
FH Scatterqood 28 (gonads — sane as above
Steaa Plant, residue)
Los
Angeles, Cal.
FH Catal Ina 38 — saae as above
Island, Cal. (gonads
residua)
FH Catallna 22 (gonads — saae as above
Island, Cal. residue)
FH Scattergood 28 (liver — saae as above
Steaa Plant, residue)
Los
Angeles, Cat .
FH Catal Ina ?« — saae as above
Island, Cal. (liver
raaidua)
FH Scattergood 69 (Intequaent — saae as above
Steaa Plant, residue)
Los
Angeles, Cal.
FH Catal Ina 23 — saae as above
Island, Cal. (Intequaent
residue)
FH Seattergood 1* (heart — saae as above
Steaa Plant, residua)
Los
Reference
AHIC-S980
Stapl eton
(I960),
4HIC-5980
Staoleton
(L1IC-5980
Staoleton
(1968),
Staoleton
(1968).
AMIC-S980
Staol eton
(1968) .
AMIC-S980
Staol eton
AHIC-5980
Staol eton
(1968),
AHTC-S980
Staoleton
(1968),
Staoleton
(1968),
AHIC-5980
Staoleton
(19681,
AHIC-S988
-------
                                         Angeles,Cal.
Aluminum
Aluminum
Alualnum
Aalnotrlazole
••|trol-T
                     Parafabrax    FH
                     clathratus
                     Paralahrax    FH
                     clathratus
                     Paralabrax    FN
                     clathratus
                     Fish (not
                     specif l««ll
                     Crassostrea   L
                     vlrglnlca
                     (eggs)
                    Cat* Una      k
                    Island. Cal.  (heart
                                 r*«idu«)

                    Scattergood   33  (eyeball
                    Steam Plant,  residua)
                    Los
                    Angeles,Cat.

                    CatalIna      3*
                    Island, cat.  (eyeball
                                 raaidue)

                    —            greater than
                                 1000  (Kl
                                greater than 10
                                IT2)
 •altrol-T
 Aaltrol-T
Crussostrea
vlrginlea
(larvae)

Catiaarus
fasciatus
                                   a     ^^
                                   as*   —
                                                      greater than
                                                      10IT1I.)
                                                      greater than
                                                      100.0 CT2)
                                                                                        saae as above
                                                                                        sane as above
                                                                                        same as above
        Aporoxlmate toxlcltles of
nuoerous o«stlcldes cownonly used In
Britain Here summarized. An excellent
brief, qen«ral discussion of toxlclty
testing is also present.

        The effect of ^2 oesflcldes on
enbryonlc d*veloc*ent of clans and
oysters was r»oorf*rt.  Syn»rql*tlc
effects nith solvents Here also reoorted.
 Host of the coioounds affecfed
develocnent more than survival.  Some,
however, drastically reduced larval
growth.  The authors oolnt out the
necessity of evaluating the effects of
pesticides on all life stages of an
organlsr and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
shall fish.

       same as above
                                          Staoleton
                                          (19681,
                                          AMIC-^BO

                                          Staoleton
                                          (19681,
                                          ANIC-5980
Staoleton
(1943).
»MIC-?98D

Nandesley-
Iho'aas
(19/1),»NIC-
1056
Davis, et
• 1(1969),
»MIC-S990
 Aaltrol-T
                      Paleoaontes
                      kadiaKens Is
                                    BS»    ~
                                 greater than
                                 100.0 
-------
t
Compound
Amltrol-T

Amltrol-T


Amltrol-T


Amltrol-T


Amltrol-T

Amltrol












Amltrol



Field Field
Organism Study Location
Asell us BSA —
brevlcaudus
Orconectes BSA —
nals

Daphnla maqna BSA —


Cyprtdoosls BSA —
vldua

Leoouls BSA
macrochlrus
Crassostrea L --
vlrqlnlea
(eqqs)










Crassostrea L
vlrglnlca
(larvae)

Toxlclty,
Active
Inqredlentt
Ppm
greater than
100.0 (T?)
greater than
100.0 (T2)

30.0 (TZ)


3Z.O (TZ)


qr eater than
100.0 (T2)
733.7 (T2>












255. fc (Til.)



Experimental
Variables,
Controlled
or Noted Comments
a* sane as above

a* sane as above


a* sane as above


a* sane as above


a* sane as above

~ The effect of 5Z pesticides on
eobryonlc development of clans and
oysters was reoortel. Svnerglstle
effects with solvents were also reported.
Host of the compounds at fected
* *
growth. The authors oolnt out the
necessity of evnluatlnq the effects of
pesticides on all life stages of an
organism and note the possibility of
selecting chenlcals for pest control that
would not have serious effect on
shell fish.
— sane as above



Reference
Sanders
(1970I.AHIC-
Sanders

453
Sanders
(1970),
A1IC-W53
Sanders
(1970).
AMIC-1.53
Sanders
(1970). «MIC-
Oavls, et al

(1969) .*1IO-
5990









Oavls. et al

•1969), AMIC-
5990
        Aanonla (plus ohenol Sal no         BSA
        and zinc)            galrdnerl
                                                              0.5-2.5". «T?I
a.c*,d,e*.         Rainbow trout Mere exposed to     Brown, et al
f,n        concentrations of fluctuating levels of   (1969),
           aniionla, phenol, and zinc and to constant AHIC-5993
           •Ixtures of the three.  Tests with
           fluctuating levels of toxicants showed
           that LC50 values were slillar to those
           for constant concentrations as tonq as
           the periodicity of the fluctuation did
           not exceed the resistance tine for the
           poison.  Except when zinc predominated In
           the mixtures,  the fractional  toxlclties
           could be summed to qlve  the toxtclty of
           the mixture.
-------
Amaonla
•••enla
Salao
qalrdnerl
                     Salno
                     galrdnerl
                                   BSA
                                    BSA
Anoonlun carbonate   Phorraidium
plus Copper sulfato  arabiguum
 Aaaonlm chloride    Pbormldium
 plus Copper aulfate  ambiguum
 (1.-2J
22.5-67.5       a,c*,d,e*,
(fluctuating    f,m
Cone, T 370-
greaterthan 700
mln)

V5.0 IT greater a,c*,d,e*.
than 700 Bin)   f,m
                                 0.5-10.0  (100
                                 percent growth
                                 Inhibited Id)
                                  0.5-10.0 (100
                                  percent growth
                                  Inhibited ll|)
                                                                                        same as above
                                                                                         sane  as  above
                                                                                                                           Bronn. et at
                                                                                                                            (1969)i
                                   Of 7i> chemicals evaluated as
                           alglcldes, only 9 were more toxic than
                           CuSO
-------
Field Field
Comoound Organism Study Location
heteronorpha and
USA







Ammonium sultanate Rasbora BCFA — •
heferomorpha and
BSA







Ammonium sulfamate Rasbora BCF* ~
heteromorpha and
BSA







Ammonium Irs NH3I leoomls BSA, —
macroettlrus L






Ammonium (as NM3) Nitzschla BSA, —
11 near Is L


Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppot or Noted Conaents
5.7) hard (HM)
or soft
(SM)
synthetic
dilution
water, or
seaxater
lor sone
soecles
610 (Tl, DH a'.c.p.f.
7.1> hard (HM)
or soft
1SW)
synthetic
<11 1 u t i on
Mater, or
seaHater
•or some
soecies
55 (Tl.pH S.OI a*,c.e,f.
hard (HM)
or soft
(SH)
synthetic
dilution
water, or
aeawater
for aorao
species
>.<> (T4I a«,e, and
synthetic
dilution
water




1.20 (SB5) a»,e, and
synthetic
dilution
water









saae as above









sane as above









This study Has conducted to
determine the relative toxlclties of 20
common constituents of Industrial Hastes
to a fish, an alga, and an Invertebrate.
The experiments Here conducted over a
10-year period for varied purposes. The
authors recoanend bloassays with at least
three components of the food web.
same as above



Reference
(1969),
ANIC-5ii25







Alabaster
(1969).
AhIC-5«S







Alabaster
(1969).
AMIC-S«?S







Patrick, et
al (1968),
AMIC-5720





Patrick, et
al (1968),
ANIC-5730

-------
                 la*
        Amphenon* B
        Antimony
>
        Antimony
        Antimony
        •ntlneny
        Antimony
        AntIaony
        Antimony
        Antlmyeln  A
                             Physm         BSA,
                             heterostroona L
                             Lymnaea
                             staqnalIs
                             (adults)
             90.0 mi
             10.0 ISB71
                «»,e,. and
                synthetic
                dilution
                water

                a»»o
                                               same as above
                                                                                  Patrick, et
                                                                                  at (196*1.
                                                                                  AMIC-5720
                             Coregonus     FL    Moose Lake,  0.002
                             cluoeaformis        Can.         (residue)
                             Coregonus     FL
                             clupeaformls
                             Esox luclus   FL
                             Esox tuclus   FL
                             Esox luclus   FL
                             Osier us
                             aordax
                             Peree
                             flavescens
                                           FL
                                           FL
Lake
Ontario.
Can.

Moose Luke.
Can.
                                                 Lake St.
                                                 Pierre* Can.
                                                 Lake Erie,
                                                 Can.
Lake Erie,
Can.
Lake Erie,
Can.
                             Leplsosteus   BS»,
                             piatostoaus   FO
0.003
(residue)
                                                              0.003
                                                              (residue)
             0.001.
             (residue)
             O.OOd
             (residue)
0.00".
(residue)
0.003
(residue)
             0.000,
                                          AMIC-J819

                                          Uthe, et al
                                          (19711,AHIC-
                                          3B19

                                          Uthe, et al
                                          (1971),ANIC-
                                          3819

                                          Uthe, et
                                          ALU971).
                                          AMIC-3819

                                          B«rg«r, et
                                          al  (1969).
                                                                                                same as above
                                                                                                same as above
                                                                                                same as above
                                                                                                same as above
                                                                                                same as above
                                   Liquid and sand formulations of
                           antlmycin A Here tested as a  fish
                           toxicant In lab Maters of various
                           temperature, hardness, PH. and turbidity
                           aqalnst 31 species of freshMater fish of
                           various sizes and life stages.  Each
                           formulation of toxicant MBS lethal under
                           all Mater conditions to fish eggs, fry,
                           finger IInqs, and adult fish.  Trout Mere
                           the most sensitive and cat fishes the
                           least sensitive.  Of the 31 species. ?<•
-------
Coaoound

Antlaycln A
Antl.ycln A
Antlnyeln A
Antlaycln A
Antlaycin A
Antlaycln A
Antlaycln A
Organise

Aala ealva
Sal no
galrdnerl
Salao trutta
Sal vel Inus
fontlnal Is
Sal vel Inus
naaaycush
Esox luclus
Carasslus
auratus
Field Field
Study Location

BSA, --
FO
BSA, —
FO
BSA, —
FO
BSA, —
FO
BS», —
FO
BSA, —
FO
BSA, —
FO
Toxlclty,
Active
Ingredient,
Pp*

0.015 (60
percent K*>
0.00003-0. DODOS
0.009 (K3>
0.00003-0.00006
0.00007 (TU)
0.00011-0.00059
0.00070-0.001
Experimental
Variables,
Control led
or Noted Comments

deionized
water
a,c,e,f,e,
deionized
water
a.c.e.f »q,
deionized
Hater
a»c,e,f,s,
deionized
water
deionized
nater
deionized
Hater
a,c,e,f,g,
deionized
water
succunbed to 0.009 opm or less of the
toxicant! only certain catflshes survived
0.025 CPU.
saae as above
sane as above
saae as above
saae as above
saae as above
saae as above
saae as above
Reference

Berger, et
al (1969),
AHIC-5I.9S
Berqer, et
al (1969).
ANIC-5U95
Berqer, et al
(1969).
Berqer, et
al (1969).
• MIC-51.95
Berq»r, et
al (1969),
Berqer, et
al (19691,
Berger, et
al (1969),
ANIC-9«»95
Antlaycln A
                     Cnrosoaus eos BSA,  —
                                                      0.00009-0.00052 a,C,e,f,q,
                                                                                        saae as above
                                                                                                                          Berger,  et
-------
                     LeDOBlS
                     glbbosus
              BS»,
              FO
O.OOOOS-O.OOOZ* a,c,e,f,E,
IT*)            deionized
                water
                                                                                        sane as above
                                                     Berg*Pt *t
                                                     a I (1969),
                                                     4HIC-5I.9S
AntlBycln *
              BS*«
•acrochlrus   FO
0.00006-0.ODDS
mt
                                                                      deionlzed
                                                                      water
                                                                                        sane as above
                                                     Berger, «t
                                                     a I  (19691 •
                                                     • WIC-Si.9*
••ttleycln
•ntlaycln »
Anttaycln
Lvoouls
••galotit
                                   BS«,
                                   FO
                     Lepouls       BS«,
                     •IcreloDhus   FO
                     Hlcrooterus   BS»,
                     deloaleul     FO
                                                      D.OOD08  (TV)
                                                      0.00009
                                                                      d«lonlz«d
                                                                      •at*r
                                                                      delonlzed
                                                                      Hat«r
                                 O.OOOOV-O.OOOOt a.e.e.f.g,
                                 IT*)            dilution
                                                 ua tor
                                                                                        save as above
                                                                                        *••• as above
                                                                                        saae as above
                                                                     6erqerf »t
                                                                     al  (1969) i
                                                                     »MIC-5V95

                                                                     Berqer, et
                                                                     al  (1969).
                                                                     •HIC-5V9S

                                                                     B«ro»r, et
                                                                     al  (1969).
tnttvycln
                     ••(•oldes
                                   FO
                                 0.00009-O.OOflllf »,c,e,f,s,
                                                 deionlzed
                                                 water
                                                                                        cane as above
                                                                     B*rq«r, *t
                                                                     a I  (1969)t
                                                                     •HIC-SV9S
•ntlarcln «
         >     BS»,
nigro-        FO
•aoulatua
0.001  (V3
percent K)
a,c,e,f,s,
daionized
water
                                                                                        sane as above
Berqer, *t
al (1969).
tntlaycln A
Perce         BS»,
flavescens    FO
0.00003-0.00012 «,e,e,f,E,
IT*)            deionized
                water
                                                                                        s«*e as above
                                                                                                                           al (196<>»,
•ntl«rcln *
                     Stlzostedlon  BS»,
                     vltreu*       FO
                                 0.00002-0.OOOOd »,c,e,f,g,
                                                 dilution
                                                 water
                                                                                        sa«e as above
                                                                     fterqer, et
                                                                     al  (1969).
•ntlavcln *
•plodlnotus   BS».
orunnlens     FO
0.00002-0.0001* a,e,e,f,c.
IT*I            deionizad
                water
                                                                                        sane as above
                                                     Rerger, et
                                                     al (1969).
                                                     *HIC-S*95
                     Cyorlnus
                     carolo
              BSA,
              FO
0.00012-0.000*3 a,c,e,f,g,
(T*)            deionlzed
                water
                                                                                        saae as above
                                                    Berqcr, et
                                                    al  (1969).
-------
Compound
Antlaycln A
Antlaycln A
Antlmycln A

Antlaycln A
Antlmycln A

Antlaycln A
Antlaycln A
Antlmycln A
Antlmycln A
Antlmycln A
Antlmycln A
Orqsnlsm
•iaephales
promelas
Car pio
0. 021-0. 08S
0.0052-0.0105
m>
0.2 CK*>
0.0000
-------
                                   FO
                                                      IT*)
                                                                      delonieed
                                                                      Ma tar
                                                                                                                          • I  (196911
AntUycIn A
•ntlaycln •
Antlaycln *
Saleo
galrdnerl

                     Leooals       L     —
                     aacrochlru*
                                 0.00003 m>
                                                      0.00016 ITU     a*
Salao elarkl  Ft    Copper Lake. 0.005 (K)
                    Idaho
                                                                      a.c.d.e
Antlaycin *
                     Sal BO         BS*
                     galrdnerl
                                                      0.00009  (TV)
Antlaycln A
AntlayeIn A
Aphltex
                     Ictalurus     8SA
                     punctatus
lepoels       BS*
eacrochlrus
                     Rasbora       BCFA
                     heteroaorpha  and
                                   BSA
                                                      0.01*7
                                                      o.oooi*  m>
                                 27  (TZ)
                                                bard (HW)
                                                or soft
                                                (3W) syn-
                                                thetic
                                                water, or
                                                •eavater
                                                tor aona
                                                •paelas
                                                                                         The  plsclcldes  Antlaycln  A  and     HoKland
                                                                                 Rotenone Here found  to  be  compatible nhen  (t969
                                                                                 •Ixed >nd furthereore appeared  to have  an  5725
                                                                                 additive effect  In cnbination.  That Is
                                                                                 both compounds Here  "ore toxic  In the
                                                                                 presence of  the  other than alone.
                                                                                        sane  as above
        Rapid fish kill occurred In a
otlQotrophic situation and toxlctty
persisted for at least 10 days following
application.  Plankton Has also reduced.
Later the lake Has successfully stocked
•Ith cutthroat trout.  The rapidity of
kill and persistence Indicated that the
Antlaycln concentration Has hlqher than
necessary.  The authors recoooendrd
further research.

        The dyes Rhodanlne B and
Fluoresceln sodlun Here found to be
relatively non-toxic In ppe
concentrations Hhlle antlnycln Has toxic
at oob levels.  The author states that
neither dye at field use concentrations
should significantly Influence the
activity of Antl*ycln A aqalnst fish.

       saae as above
                                                                                       sane as above
HOHI and
(1969).
ANIC-5T2S

Rabe, et al
(1969),
AMIC-573Z
                                                                                                       Harking
                                                                                                      (1969).
                                                                                                      AHIC-5720
                                          Harking
                                          (1969).
                                          ANIC-S7Z9

                                          Harking
                                          (1969).
                                          ANIC-57Z9
        One hundred sixty-four            Alabaster
pesticides, netting aaents. and           (1969).
alscellaneous Hater pollutants showed a   AHIC-542?
Hide range of toxiclty spanning 12 orders
of eagnitude.  Knowing the toxiclty and
percentage of all coaponents of a
foraulatlon did not result In easy
predictability of the toxlclty of a
alxture of Materials.  Soeetiees
-------
                                 Field   Field
Compound              Organlsa    Study  Location
                                                       Toxlclty,
                                                       Active
                                                       Ingredient,
                                                         POU
                Experimental
                Variables.
                Control led
                or Noted
                                                                                                  Comments
                                                                                                                           Reference
Aauaclene lap
Aquaclene 100
•quaclene 100
Aauaclene
                     Plmephales    BSA
                     or owe I as
                     Pimephales    USA
                     prone I as
                     Biochemical   L
                     oxygen deaand
                     Cardlua edule BSA
                                                       35.0  (T%»
                                                       *.Z  (NSC)
                                                       8*0,00
                                                       33-100  «T2»
•quaclene
                     Crangon
                     crangon
                                   BSA
                                                       100-330  (TZ>
                soeeles    pesticides Here most toxic In hard Mater
                           and sometimes the opposite Has true.
                           Testing the actual material as sold Mas
                           found to be essential.

                c,d,e,f            Toxlclty of six oil spill
                           dlspersants Has determined along Kith
                           800 values.  Pond Hater Mas used as
                           diluent and oil Has Included In the
                           experiment.  Oil markedly reduced
                           toxlcity of all disoersants.  Data are
                           given as "most probable** gft-hr TL sub m.

                dd,e, f           sane as above
                                                                       c,d,e,f            same as  above
                a>t(contin-         One hundred-forty surface active
                uoua aer-  aoents, solvent emulsifiers, Pesticides,
                atlon, sea-polychlorlnated blohenyls. Pure
                water, and Inorganic, and organic cheitlcals Here
                •Jaiiy      evaluated against as many as ten marine
                solution   organisms.  The authors noted that most
                renewal)   published data of this type deal Kith
                           toxlcity of chemicals to freshwater
                           organisms.

                a«(contln-        same as above
                uous aer-
                ation, sea-
                water, and
                daily
                solution
                renewal)
                                                                                                                         71 Mich
                                                                                                                         <19*>9),AMIC-
                                                                                                                         7909
                                                                                                                         711 IIch
                                                                                                                         (19«i9),AHIC-
                                                                                                                         2909

                                                                                                                         ZlIllch
                                                                                                                         (1969I.AH.T.C-
                                                                                                                         2909

                                                                                                                         Portmann,  at
                                                                                                                         al  (1971),
                                                                                                                         •iic-7701
                                                                                                                          Portmann,et
                                                                                                                          at  1197II,
                                                                                                                          •MIC-7701
•quatheI
                     Horone
                     saxatllli
                     Cflngarllngsl
                                   BSA    —
710 (Tl>)        a,c,d,e,f.         All compounds Here Investigated   Wellborn
                p          becauso of their probable usage in        (1971),
                           hatchery production of Mhite bass.        AMIC-5571
                           Comoounds that can be used at recommended
                           concentrations Mere Aquathol, Casaron,
                           LIndane, and Terraaycln concentrate.
                           Those that should not be used Mere
                           Acrlflavlne, Baylusclde, Malachite green
                           oxalate, and Malathlon.
-------
                                Mere Is vlrens BSA
                                                                 0.00011-0.OOOVI, 8",c,e,
                                                                                 and
                                                                                 synthetic
                                                                                 seanater
           Ar he tine DOT
Fundulus      BSA
heteroclItus
Rasbora       BCFA
heteroaorpha  and
              BSA
                                                                 0.00032-0.00035 a*«c,e.and
                                                                                 synthetic
                                                                                 seanater
                                                                     A  laboratory  procedure  based  on
                                                             Standard Methods  lor  9«>-hr  loxlclty
                                                             determinations  of  cruel*  ell  and
                                                             oll-dlsper*«nt  Mixtures  was  described.
                                                             The dlsoersants varied considerably  In
                                                             toxlclty,  ranging  fro* 0.01  to  7.1 inl/l,
                                                             TLSfl for 9fi  hr.  These did not  differ
                                                             significantly  fro* ?
-------
  Compound
                       Organise)
              Field  Field
              Study Location
Toxlclty.
Active
Ingredient,
  Ppa
Experimental
Variables,
Control led
or Noted
                                                                      solution
                                                                      renewal)
                                                                                                 Comments
                                                                                                                           Reference
•rector
                     t9onus        BSA   —
                     cataphraetus
                                 greater than 10 a«(contln-
                                                      ITZI
                                                                      uoua aer-
                                                                      ation, sea-
                                                                      water, and
                                                                      dally
                                                                      solution
                                                                      renewal)
                                                                                        sane as above
                                                                     Portmann. at
                                                                     at (1971),
                                                                     »HIC-7701
tree Ior 12*«
                     Cardlua edule BSA   —
                                                      greater than Itt ,a»(contln-
                                                      IT2)            uous aer-
                                                                      ation, sea-
                                                                      wetar, and
                                                                      dully
                                                                      solution
                                                                      renewal)
                                                                                        sane as above
                                                                                                                et
                                                                                                      al C1971I.
                                                                                                      »HIC-770l
•roc Ior 1?*8
                     Crangon
                     crangon
                                   BSA    —
                                                      O.OS-1.0  (T2)'
                                                 a«(contin-
                                                 uous aer-
                                                 ation, aaa-
                                                 wator, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                        sa*e as above
                                                                     Portmann, et
                                                                     al  (1971),
                                                                     AHIC-7701
•rector 175* (plus
Gorexlt 766*1
Salno sal
IparrI
                              ar   t
                                                      *  (K 90 hr)
•rocIor 125* <»lth
eorexlt 76«*,
colloidal solution!
Caemarus
ocean Icus
                                   BSA   ~
0.001-0.01
(threshold
concentration)
                a*,e               Aroclors t?^<> and 1721 Mere
                (nixed tap evaluated lor toxic effect with Corexlt
                or         766*  (Height ratio 1:19) a« an
                seanater)  enulslfylnq aqent.  Since only tito fish
                           were used for each exposure,  me author
                           notes that the results are only
                           preliminary.  However, RGB's  appeared to
                           be less toxic to Atlantic salnon parr
                           than chlorinated hydrocarbon  pesticides.
                                                     Zltko
                                                     (1970>,AMIC-
                                                     ?3
 a«( weekly-
 solution
 chan^o,
 aeawater)
        Aroetor 1?;* solutions or
suspensions with Corexlt 766* at varied
concentrations In seaxater resulted in
varying toxlclty of the Aroclor.  Corexlt
•as not lethal at 1900 po« but caused
WHdlsh
(1970),AMIC-
69
-------
•roc I or 125*  (tilth   Gammarus
corexlt 766
-------
  Compound
                       Organism


                     (Juvenile)
                                   Field  Field
                                   Study Location
             Toxlctty,
             Active
             Ingredient,
               Ppm
                Experimental
                Variables.
                Controlled
                or Noted
                                                        Comments
                                                                                                                            Reference
Aroclor 1251.
                     Aqonus
                     eataphractus
                                        heoatopancreas Has narked  (up to 510       AHIC-261.5
                                        PPM).  The biological half-life for this
                                        chemical Has found to be 17 days with
                                        tissue distribution In the shrimp being
                                        similar to that of DOT.  Delayed
                                        mortality Kith no prior poisoning
                                        symptoms Has also observed.  Considerable
                                        additional data are oresented.

             greater than 10 a«(contin-         One hundred-forty  surface active  Portmann, et
             (T2I            UOU3 aer-  agents, solvent emulsl tiers. oestlcidesf  al  (1971),
                             at! on, sea-pol ychlorlnated blphenyls, pure           AHIC-7701
                             water, and Inorganic, and organic chemicals Here
                                        evaluated against as many  as ten marine
                                        organisms.  The authors noted that most
                                        published data of this type deal with
                                        toxiclty of chemicals to freshwater
                                        organisms.
                                   BS»   —
                                                                       solution
                                                                       renewal)
Aroclor 1251.
                     Card!urn edule BSA
                                                      qreater  than  10  »(contln_
                                                                       uous aer-
                                                                       ation, sea-
                                                                       water, and
                                                                       daily
                                                                       solution
                                                                       renewal)
                                                                                         same as above
                                                                                  Portmann, et
                                                                                  al  (1971),
                                                                                  »HIC-770t
Aroclor IZSt
                     Crangon
                     crangon
                                   BSA   —
                                                       3-10  (T2)
                             a«( contin-
                             uous aer-
                             ation, sea-
                             water, and
                                                                       solution
                                                                       rene-..-al )
                                                                                         saae as above
                                                                     Portmann, et
                                                                     al
                                                                     (1971),AMIC-
                                                                     7701
Aroclor 1251.
                     Parallchthys  FH
                     sp.
Cscambla
Bay, Fia.
t. 5-181,
Iros1 due)
        Residue analysis of dead and
dying animals  led to the source ol  the
PCS Mhich Has  an accidental leakage from
an Industrial  clant.  The concentrations
of the PCR in  Hater and sediment nere
less than 0.03-1.86 and less than 0.001
ppm, respectively.  Bioassavs shOH<*d
juvenile shrimp to be the most
suse*Dtlbl» species* but inhibition of
shell qroHth of oysters Mas the most
sensitive parameter studied.  Continued
surveillance and long-term testing at
sublettal concentrations Her* pointed out
as urgently needed.
Duke, et al
 (1970),
AMIC-720
-------
tractor 125*
•roclor 125*
•roc I or 125*
•roclor 125*
•roclor 125*
troclor 125*
•roctor 129%
•roc I or
•roclor 125*
•reel or 125*
•roclor 125*
•roclor 125*
Laqodon
rhonboides
()uvenll«)

Penaeus
duoraru*
(Juvenile)

Crassostrea
vlrglnica
P»naeus
duorarui*
(Juvenile)

Penaeus
duoraru*
(Juvenile)

CalIinectes
saoidus
(Juvenile)

CalIinectes
saoldus
(Juvenile)

Mlcroooqon
undulatus
                     Brewoortla
                     oatronus
                     Laqodon
                     rhomholdes
                     Cynosclon
                     nebulosus
                     Penaeus
                     setlferus
                                   BS«
                                   BS»   —
                                   8S«
                                   BCHCF —
                                   BCMCF —
                                   BCHCF
                                   BCHCF —
                                   FM
                                   FM
                                   FH
                                   FM
                                         Eseambla
                                         Bay, Fla.
                    Esc**bla
                    Bay, Fla.
                    F«canbla
                    Ray, Fla.
                    fscant la
                    Bay, Fla.
                    Fscaabla
                    Bay, Fla.
                                                      17 (residue)
                                                      3.9  (residue)
                                                      0.1  (SB*)
                                                      0.1105 172
                                                      oercent K?0)
                                                      0 (residue)
                                                      0.005 (Soercent
                                                      K20)
                                                      23 (residue)
                                                      1? (residue)
                                                      5.7-11(residue)  —
                                                      10 (residue)
                                 7.5-20(residue)  —
1.5-2.5
(residue)
                                                                                        sane as above
                                                                                        sane as above
                                                                                        sa»e as above
                                                                                        sane as above
                                                                                        same as above
                                                                                        sane as above
                                                                                        sane as above
                                                                                        sane as above
                                                                                        same as above
                                                                                        same as above
                                                                                        sane as above
                                                                                        sane as above
                                                                           et
                                                                          70),
                                                                     •NIC-730

                                                                     Duke, et
                                                                     •L(1970),
                                                                     AMIC-720

                                                                     DuKe, et al
                                                                     (1970),»MIC-
                                                                     720

                                                                     Duke, et al
                                                                     (1970) ,
Oukr, et
• LU970),
•MIC-7JO

Duke, et al
(1970),
AMIC-720

Duke, et
•1(19701.
AMIC-720


Duke, et al
(1970) ,
ANIC-720

Duke, et a I
(1970),
AHIC-720

Duk*, et al
(1970),
•MIC-72D

Ouke, et al
(1970),
AHIC-720

Duke, et al
(1970),
-------
>
I
Compound

•roc I or 135*


•rector 125*


•roc lor 125*


•roc lor 1260








•roc lor 1260






•rector 1260






Aroelor 1262



Field Field
Organise Study Location

Calllne-ctes FH Escaabla
sapldus Bay, Ft a.

Laqodon BSA —
rhomboldes
(Juvenile)
Penaeus BSA —
duorarua
(Juvenile)
Agonus BSA
cataphractu*







Card tun edule BSA —






Crangon BSA -—
erangon





Agonus BSA —
cataphractui


ToxlcJty,
Active
Ingredient,
Po«

1.0-7.0
(residue)

0.1 (NTE)


0.01 (KZ>


less than 10
«T2)







less than 10
(T2)





less than 10
(T2)





less than 10
(T2)


Experimental
Variables,
Controlled
or Noted Coaeents

— sane as above


•— same as above


sex* as above


a»(contlii- One hundred-forty surface active
uous aer- agents, solvent enulslf lers, pesticides.
at ion, aea-DOlychlorinated Mohenyts, pure
water, and Inorganic, ana organic cheirlcats x»re
daily evaluated against as nany as ten narine
solution organisms. The authors noted that most
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organises.
a«lcontln_ saee as above
uous aer-
ation, aea-
wator, and
daily
solution
renewal )
a* (con tin- see* as above
•uous aer-
ation, sea-
water, and
daily
solution
renewal)
aUcontin- *»«• »* »bove
uous aer-
ation, sea-
water, and
Reference
AMIC-720
DuKe, et I
(1970J,
AMIC-720
DuKe« et
AL(1970),
AMIC-72,0
OuKe, et
AK1970),
AMIC-720
Portnann,
at (1<)71)
AHIC-7701






Portaann,
al (19711
AHIC-7701




Portwann,
al (1971)
AMIC-7701




Portaann,
at (1971)
ANIC-7701



ll








et
t







• t
t





• t
t





• t
•


-------
•roc Ior 1262
                     Cardlum edule BS»   —
                                                       less  than 10
                                                       IT2)
                                                 daily
                                                 solution
                                                 renewal)

                                                 a«(contin-
                                                 uous aer-
                                                 ation,  sea.
                                                 water, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                        same as abovo
                                                                                  Portmann, «t
                                                                                  at (1971).
                                                                                  •MIC-7701
•rector 1Z6Z
                     Crangon
                     erangon
                                   BS»   —
                                                       less Than 10
                                                 a«(contin-
                                                 uous aer-
                                                 ation, aea-
                                                 wator, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                        same as above
                                                                                  Portmann. at
                                                                                  at (1971),
                                                                                  »MIC-77fll
Arsenic
                     • losa
                     pseudo-
                     harengui
                                   FL
Arsenic
•rsonic
•r sonic
Arsenic
                     Coregonus     FL
                     artedll
                     Coregonus     FL
                     eluoeaformls
                     Coroqonus     FL
                     ttoyl
Prosoplum     FL
cyllndraeeum
                    Croat LaKos
                    - Superior,
                    Michigan,
                    and Erie
                                                      O.OZ3(resldue>  —
Grcit LaHes
- Superior,
Michigan,
and Erie

Great LaKos
- Superior,
Michigan,
and Erlo

Groat Lakes
- Superior,
Michigan,
and Erlo

Great Lakes
- Superior,
                                                      0.069lroslduel  —
                                                      O.Olt(resldue)  —
                                                      0.063(rosldu*>
                                                      0.0056(resldue) —
                                                Trace element content of fish
                                        from Lakes Superior, Michigan, and Erie
                                        Has determined by activation analysis.
                                        Whole body and liver residues Here
                                        determined.  Concentrations varied with
                                        species and lake.  Other elements found
                                        Here*  antlnony - 5 to 100 ppb,  barium -
                                        0«2 opm, cesium - 3 ppb, lanthanum - 1 to
                                        20 OPb, mercury - 10 opb,  rhenium - 0.5
                                        to 5 ppb, rubidium - 0.06  to 6 ppm,
                                        scandlu* - 7 ppb, selenium - 0.1 to 2
                                        ppb, silver - 0.001 ppb.

                                               same as above
Lucas, et
(1970).
 4MIC-3778
                                                                                                                                     at
                                                                                        same as abovo
                                                                                        same as abovo
                                                                                        sane as above
                                                                                                      Lucas, et at
                                                                                                      (1970),
                                                                                                      AMIC-3778
                                                                                                      Lucas, et at
                                                                                                      (1970),
                                                                                                      •MIC-3778
                                                                                                      Lucas, at al
                                                                                                      (1970),
                                                                                                      AMIC-3778
Lucas, et al
(1970),
-------
s
Compound

Arsenic
Arsenic
Ar sen i c
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Organism

Salvellnus
namaycush
Osmerus
mordax
Carasslus
auratus
No tr op Is
hudsonlus
Percopsls
pmlseomayeus
Roccus
chrysops
Perca
f lavescens
Stizostedlon
vl treum
vltreum
Coregonus
clupeaformls
Field
Study

FL
FL
FL
FL
FL
FL
FL
FL
FL
Field
Location
Hlchiqan,
and Erie
Great Lakes
- Superior,
Mlchiqan,
and Erie
Great Lakes
- Superior,
Hlchiqan, and
Erie
Great Lakes
- Superior,
Hlchiqan,
and Erie
Great Lakes
- Superior,
Hlchiqan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Michigan, and
E.-le
Great Lakes
- Superior,
Hlchiqan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
Hoose Lake,
Can.
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments

0.0l>9(resldue) ~ same as above
0.020 (residue) ~ same as above
0.006(resldue> — same as above
0.0035(resldue) -- same as above
O.OZ9(resIdue) — same as above
0.098(resldue) — same as above
0.007(resldue) — same as above
0.098(resldue) ~ same as above
0.09 (residue) -- Concentrations of 13 toxic
elements in dressed fish fro* heavily
Industrialized and non-industrial ized
Reference
AMIC-3778
Lucas, et al
(1970),
AHIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
SMIC-377S
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Uthe.et al
(1971),
AMIC-3819
-------
•runic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
AsuliM (K s»ltl
                     Coregonus      FL
                     clupeaformls
                     Esox  luclus    FL
                     F.SOX  luelus    FL
                     F.SOX  luclus   FL
Lake
Ontario*
Can.

Hoose Lake,
Can.
                                          Lake  St.
                                          Pierre, Can.
                                                       0.7 (residue)
                                                       0.05 (residue)   —
                                                       0.09 (residue)   —
                     Osmerus
                     •ordax
                     Perca
                     flavescens
                                   FL
                                   FL
                                          L»ke  Erie.
                                          Can.
Lake Erie,
Can.
Lake Erie.
Can.
                                                       0.0?  (residue)   —
                                                       0.19  (residue)   —
                                                       0.05  (residue)   —
                     Rasbora       8CFA
                     heteromorpha  and
                                   BS»
             5.260 (Tl,
             hardxater)
a*,c,e,f .
hard  (HW)
or soft
(SH)
synthetic
a II u 1 1 on
nnt<>r, or
Asuluej IK salt)
                     ffasbora       BCF»
                     heteromorpha  and
                                   BS*
             i,roo (Ti,
             soltnater)
                                                                       for some
                                                                       soecles
a*,c.«,f.
hard (HW)
or soft
ISM)
synthetic
dilution
Hater, or
seanater
                                                                                  areas Mere deternlned.   Only aercury
                                                                                  exceeded regulatory limits,  and
                                                                                  concentrations of  most  elements Here
                                                                                  essentially the sane in fIsn fro* both
                                                                                  areas.

                                                                                         sa«e as above
                                                                                         sane as above
                                                                                         sa«e as above
                                                                                         same  as  above
                                                                                         sane  as  above
                                                                                         sane  as  above
        One hundred sixty—four
            Hwttinq agents, and
miscellaneous Hater pollutants shoned a
Hide range of toxielty spanning 12 orders
of magnitude.  Knoxlnq the toxielty And
percentage of all components of a
formulation did not result In easy
predictability of the toxielty of a
mixture of materials.  Sometimes
pesticides Here most toxic In hard Hater
and sometimes the opposite Has true.
Testing the actual material as sold was
found to be essential.

       same as above
                                                      Uthe, etat
                                                      (197H,
                                                      •MIC-3B19

                                                      Uthe, et at
                                                      (19^1) ,»MIO
                                                      3819

                                                      Uthe, e.t
AMIC-S819

Uthe, et al
(1971), *MIC
3814

Uthe, et al
(1971
3819

Uthe, et
AL(1971),
(NIC-3819

Alabaster (
69),
4HIC-5I.2S
                                          Alabaster(19
                                          69),
                                          AMIC-5«i2S
-------
Field Field
Compound Organise Study Location


Asuntol (sheep dip) Rasbora BCFA —
hater oner oha and
BSA







Atlas 1401 Cardlua «dul« BSA —







Atlas 1901 Crangon BSA —
crangon





Atlas 1901 Pandalus BSA
•ontagul





Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
PPM or Noted Comments
for some
species
0.0<>6 (TZ> a*,c,e,t, sa*e as above
hard
(HHlor
soft (SHI
synthetic
dilution
Hater, or
seawater
for some
spec les
33-100 (T2) a»(contln- One hundred-forty surface active
UOU3 aer- aoents, solvent eiiulsl f iers, pesticides.
ation, sea- po' ychlorlnated blohenyls« pure
water and morqanlc, ana orqanic cheitlcals were
diily evaluated against as many as ten narlne
solution organisms. The authors noted that nost
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organlsns.
100-330 (TZ) ac(contin- sane as above
uoua aer-
ation, sea-
water, and
daily
solution
renewal)
33-100 «T8) a*(contin- sane as above
uoua aer-
ation, see-
water, and
dally
solution
renewal)
Reference


Alabaster,
(1969) ,AHIC-
51.25







Porfnann, et
al
(1971J,AMIC-
7701





Port«ann, at
al (1971),
AHIC-7701




Portaann, et
al (1971).
AHIC-7701




Atlavar
                     Rasbora       BCFA
                     h«tero*orpha  and
                                   BSA
1,300 (T2)       ft*,c,e,f,           One hundred sixty-four            Alabaster
                bard (HWJ   pesticides, netting aqents,  and           (1969),
                or sort    ulscel laneous water pollutants snowed  a    AH.IC-5<>25
                     syn-   Hide range of toxlclty spanning 12 orders
-------
          Atrezlne
                                Carelnu*
                                •aenas
                                              SSA   —
                                                                 100  ITZ)
                                                                         than
          Atraxine
                               Cardlua adula 8SA    —
                                                                greater than
                                                                108
u>
 tbetlc     of magnitude.   Knowing the toxlclty and
 dilution   percentage of  all  components of  a
 water, or  formulation did not  result In easy
 seawater   predictability of  the toxlclty of a
 Tor sosie   Mixture of materials.  Sometimes
 species    pesticides Here most toxic In hard  water
            and sometimes  tn*  opposite Has true.
            Testing the actual  material  as sold was
            found to be essential.

a,»(coatln-     '     One hundred-forty  surface active
uoua aer-   agents, solvent enulslflerst pestlcldest
ation, sea- polychlorlnated blphenylst pure
water, and  Inorganic, and organic chenlcals were
dally       evaluated against  as many  as ten marine
solution    orqanlsas.  The authors noted that  aost
renewal)    published data of  this type  deal  Hlth
            toxlclty of cheelcal* to freshwater
            organises.
a«Icontin-
uous aer-
ation,  sea.
utter,  and
dally
solution
renewal)
                                                                                                  same as above
                                          Portxann, et
                                          al  (1971),
                                          •NIC-7701
                                          PorTmann, et
                                          a I (1971),
                                          •MIC-7701
          Atrazine
                               Crangon
                               crangon
                                             BS«   —
                                                                10-33  (T2t
a* (contin-
uous aer-
ation, aea.
water, and
Oally
solution
renewal)
                                                                                                  saae as above
                                          Porfmann, at
                                          al (19711,
                                          •MIC-7701
          Avatfex 8H
                               •asbora       BCFA
                               heterenorpha  and
                                             BSA
                                                                6 (T2)
a«,c,e,f.
bard  (KW)
or soft
(SV)  syn-
thetic
dilution
miter, or
sea water
for some
species
        One hundred sixty-four            Alabaster
pesticides, HCftlno aqents, and           (1969),
miscellaneous water oollutants showed a   AHIC-S4K
Hide range of toxlclty scanning 12 orders
of magnitude.  Knowing Tne toxlclty and
percentaoe of all components of a
formulation did not result In easy
predictability of the toxlclty of a
elxture of Materials.  Sometimes
pesticides Here most toxic In hard Hater
end sometimes the opposite was true.
Testing the actual Material as sold Has
found to be essential.
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Organism Study Location Ppm
Avadex Rasbora BCFA ~ B.Z (TZ)
heteromorpha and
aSA







Az Inphosme thy) Fish (not — — greater than
specified) 0.01-0.1 (K)



Experimental
Variables,
Control led
or Noted Comments
a»,c,e,f ,
hard (HHI
or soft
(SH)synthe
tic
dilution
Hater, or
soanater
for so*e
species
—




same as above









Approximate toxlcltlvs of
numerous pesticides commonly used In
Orl-talr Here summarized. An excellent
brief, general discussion of toxlclty
testing Is also pri-s»nt.
Reference
Alabaster
(1969),
AMIC-5I.Z5







Mawdeslev-
Thomas(1971l
AMIC-1056


        Az Inphosme thy I
I
UJ
                             Carclnu*
                             •aenas
                                           USA
                                                              0.033-0.1  (TZ)
                at(contin-         One hundred-forty surface active
                uous aer-  agents, solvent emulslflers, pesticides,
                atlon, see-polychlorlnatod blohenyls, pure
                water, and. Inorganic, and organic chemicals Here
                dally      evaluated against as many as ten marine
                solution   organisms.  The authors noted that most
                renewal)   published data of this type deal with
                           toxlclty of chemicals to freshwater
                           organisms.
        tzlnohosaethy I
                             Cardlun edute BSA   —
                                                              greater
                                                              (TZ)
                                                                       than  10
                a«(contin-
                uous aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)
                                                                                                 sa«e as above
                                                     Portmann, et
                                                     al (1971),
                                                     ANIC-7701
                                                     Portmann, et
                                                     al (19711.
                                                     AHIC-7701
        »2lnphos«ethyl
                             Crangon
                             crengon
                                           BS«   —
0.0003-0.001
(TZ)
a«( contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
                                                                                                 same as above
Portmann, et
al (1971),
»HIC-7701
        AZlnphotMthyl
                             LIvanda
                                           BSA
0.01-0.03 (TZ)  a»(contin-
                                                                                                 saac as. above
                                                                                                                                    Portmann, et
-------
                                llmanda
                                                                                 uous aer-
                                                                                 ation,  sea-
                                                                                 water,  and
                                                                                 daily
                                                                                 solution
                                                                                 renewal)
                                                                                                      al  (1971),
                                                                                                      AMIC-7701
          AzlnDnosmethyl
Panda 1 us
montaqul
                                             as*
          Azlnphos ««thvl
Rasbora       BCFA
heteromorpha  and
              8SA
0.0003-0.001
CT2)
                                                                0.076  (T?)
U)
          Bacterial •ndotexlns Salmo
                               qalrdnerl
                               (1.00-5(10 q>
                                                                10  (NTEt
          Bacterial tndotoxlns Oncorhynchus
                               klsutch
                               C.00-500 q>
          Balan
                               Gammarus
                               fasclatus
                                             BS»   ~
                                                                10 (NTE)
                                                                1.1 IT%)
a«(contln-        same as above                      Portmann, at
uoua aer-                                            al (1971),
ation, sea-                                          AMIC-7701
water, and
daily
solution
renewal)

a*,Cte,f,          One hundred sixty-four            Alabaster
hard (HH>  pesticides, Netting aqents. and           (1969),
orsott     mlscpl laneous Mater ootlutants showed a   AMIC-5«»?S
(SW)       Hide ranqe of toxlclty soannlnq 12 orders
synthetic  of maonltude.  Knoxlnq the toxlclty and
dilution   oercentaqe of all conoonents of a
xater, or  formulation did not result In easy
seauater   predictability of the toxlclty of a
for some   mixture of materials.  Sometimes
species    pesticides Here most toxic In hard Hater
           and soiretlmes the opposite Has true.
           Testinq the actual material as sold Has
           found to be essential*

™                 Salmon and trout were Injected    Medemeyer*
           Hlth endotoxins preoared from Eseherlchla et at
                                                            coll and Aeromonas salmonicida.  No
                                                            significant cardiovascular response or
                                                            effect on liver tryptoohan pyrroles*
                                                            activity in vitro occurred.  It Has
                                                            concluded that metabolic effects of
                                                            bacterial endotoxins In salaonids are
                                                            qualitatively different from those of
                                                            hlqher vertebrates.

                                                                   same as above
                                                                     (1968),
                                                                     AMIC-3771.
                                                                                                      Wedemeyer,et
                                                                                                      al (196B),
                                                                                                      AHIC-377*
                                                                    Of the aquatic Heed herbicides    Sanders
                                                            evaluated, Olclone Has the most toxic,    (1970),
                                                            Oaphnia Has generally the most sensitive  AMIC-WSJ
                                                            organism.  All of the Crustacea Here
                                                            affected by «uch lower concentration
                                                            levels of herbicides than Indicated by
                                                            the Tl sub 50.values.  All ot the animals
-------
             Coaoound
              Field  Field
  Organise    Study Location
Toxlclty,
Active
Ingredient,
  Pom
Experimental
Variables,
Controlled
or Noted
                                                                                                            Consents
                                                                                                                                      Reference
          Banner 0601
Crangon       BSA   —
crangon
                                                                 10-33 (T?)
          Banner OG02
Crangon
crangon
                                              BS*
                                                                 10 «TZ>
>
I
                           represent Important food chain links.

                a«(contin-         One hundred-forty surface active
                uous aer-   aqents, solvent emutsiflers, pesticides,
                ation, raa-polychlorln»ted blohenyts, pure
                water, and inorganic, and organic chemicals were
                daily      evaluated against as aany as ten Marine
                solution   organisms.  The authors noted that aost
                renewal)   published data of this type deal with
                           toxlclty of chemicals to freshwater
                           organisms.

                a«(contln-        saae as above
                uous aer-
                ation, sea.
                water, and
                dally
                solution
                renowti)
                                                                                                                                      Portaann,  et
                                                                                                                                      a I  (1971).
                                                                                                                                      AHIC-7701
                                                                                                                                      Portaann,  et
                                                                                                                                      al  (1971).
                                                                                                                                      ANIC-7701
           ••mar 0603
Crangon
crangon
                                              BSA
                                                                 19-33 IT?>
                                                                                 a«(contin-
                                                                                 uous aer-
                                                                                 ation, sea-
                                                                                 water, and
                                                                                 daily
                                                                                 solution
                                                                                 renewal)
                                                                                                   saae as above
                                                                     Portaann, et
                                                                     al (1971),
                                                                     AMIC-7701
           tanner 060*
Crangon
crangon
                                              BSA   •—
                                                                 10-33 ITZ1
                                                                                 a«(contin-
                                                                                 uous aer-
                                                                                 ation, sea.
                                                                                 water, and
                                                                                 dally
                                                                                 solution
                                                                                 renewal)
                                                                                                   saae as above
                                                                     Portaann, et
                                                                     al (1971).
                                                                     ANIC-7701
           •arban
                                Rasbora
                                heteroMorpha
              BCF*
              and
              BSA
0.91 (TZ)       a*,c,e,f.          One hundred sixty-four
                hard (HH)  pesticides, wetting agents, and
                or         miscellaneous water pollutants showed a
                SOFT(SH)    wide range of toxiclty spanning 12 orders
                synthetic  of Magnitude.  Knowing the toxlclty and
                dilution   percentage of.all components of a
                                                     Alabaster
                                                     (1969).
-------
        Barium
                             Paralabrax
                             elmthrafus
                                           FH
>
        Barium
        Barium
        Barlua
        Barlua
        Barlua
        Barium
                             Paralabrax    FN
                             clathratus
                             Paratahrax
                             clathratus
                             Paralabrax
                             clathratus
                             Paralabrax
                             elathratus
                             clathratus
                             Paralabrax
                             clathratus
                             (gravid
                                           FN
                                           FN
                                           FN
Scattergood  ? (dorsal
Steam PI not, muscle
LosAngeles,  residua)
Cal.
water, or  formulation did not result In easy
seawater   predictability of the toxlelty of a
for some   mixture of materials.  Sometimes
species    pesticides Here most toxic in hard water
           and sometimes the ooposlte was true*
           Testlnq the actual material as sold was
           found to be essential.

—                 Fish collected froin an effluent   Staoleton
           ploe of n stenm olant and from offshore   t!968)«
           waters of Catallna Islana were analyzed   HHIC-5980
           for trace element content.  Trace element
           content of the effluent  water was at
           least 5 times greater than that of normal
           sea water for cadmium, coooer, nickel,
           zinc? and chromium.  Livers of fish from
           the effluent were nearly twice the size
           of those from the ocean.  Greatest
           differences in concentration occurred
           with aluminum, cadnlun,  and nickel.
           Silver, barium, lithium, and lead showed
           the least differences.  The author
           concluded that trace element analysis of
           tissues could be used to determine the
           •ffect of pollutants on  Marina organises.
Catatlna     1.7 (dorsal
Island, Cal. muscle
             r«sldu«)

Scatterqood  !.<> (ventral
Steam Plant, muscle
LosAnqeles,  raaidua)
Cal.

Catallna     1.3 (ventral
Island, Cal. Muscle
             r»iidu«)

Scattergood  7.8 (gonads
Steam Plant, residue)
lostnqeles,
Cal.

Catalina     Z.6
Island, Cal. (gonads
             raaldua)

Catatlna     2.2
Island, Cal. (qonads
             residua)
                                                                                                same as above
                                                                                                same as above
                                                                                                same as abova
                                                                                                saac as abova
                                                                                                same as abova
                                                                                                same as abova
                                                     S taoleton
                                                     (196M,
                                                     Staoleton
                                                     (196!) .AM.IC-
                                                    Staoleton
                                                     (1968).
                                                    A1IC-S9SO

                                                    Staoleton
                                                     (1948).
                                                    ANIC-5980
                                                    Stapleton
                                                     (1968).
                                                    AHIC-5989

                                                    Stapleton
                                                     (1968).
                                                    AHXC-S980
-------
>
           Coaoound
         •awlua
         •arlua
         Barlua
         ••rlu*
         •arlua
         •arlua
         Barlua
         •arlua
         •asol  AM
Organise
Paralabrax
el athratus
Paratabrax
cl athratus
Paralabrax
elathratus
Paralahrax
elathratus
Paralabrax
elathratus
Paralabrax
elathratus
Paralabrax
elathratus
Paralabrax
el athratus
Cranqon
cranqon
Field
Study
FH
FM
FM
FN
FH
FM
FM
FM
as*
Field
Locat Ion
Seatterqood
Stean Plant,
LosAnqeles.
Cal.
Catal Ina
Island, Cal.
Seatterqood
Steaa Plant,
LosAnqeles,
Cal.
Catal ina
Island, Cal.
Scattergood
Steaa Plant,
LosAnqeles,
Cat.
Catallna
Island, Cal.
Seatterqood
Steam Plant,
LosAngeles,
Cal.
Catal Ina
Island, Cal.

Toxicity,
Active
Ingredient,
Ppa
!.<• (liver
residue)
1.8
(liver
residua)
2.8 (Intequaent
residue)
1.6
(Integuaent
raaidua)
1.2 (heart
residue)
2
(heart
residua)
5.8 (eyeball
residue)
9.1
(eyeball
residua)
10-33 (T2I
Experlaenta
Variables,
Controlled
or Noted
—
— —

~

— —

— —
a«( contin-
uous aer-
ation, sea-
water, and
solution
renewal)
1
Coaaents
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
One hundred-forty surface active
agents, solvent eaulslflers, pesticides,
polychlorlnated blohenyls, pure
Inorqanlc, and orqanic che»lcals nere
evaluated aqalnst as nany as ten aarlne
organises. The authors noted that aost
published data of this tyoe deal with
toxlclty of ehealcals to freshwater
organ ISMS.
Reference
Staoleton
(1968).
ANIC-S980
Staoleton
11968),
Staoleton
(1968).
AMIC-MSO
Staoleton
11968) ,
AMIC-5980
Staoleton
11968),
AHIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5989
Staoleton
(1968).
AMIC-S980
Portnann, et
at
(1971), AHIC-
7781
-------
         ••sol 99
                              Rasbora
                              hateroaerpha
              BCFA
              and
              BS»
                   1.2 
NO
         Bayer 39(07
Rasbora       BCFA
heteromorpha  and
              BSA
                                  1*  (TZ,
                                  hardwater)
         Bayer 39DD7
Rasbera
heteromorpna
BCFA
and
BS*
                                 7.5 (T2,
                                 softwater)
         BayIuseIda
Moron*
saxatllis
If IngerlInqsl
                                            BSA   —
                                                               0.78 (T3)
                                   »",cTe,f ,
                                   hard
                                   (HH)or
                                   soft (SW)
                                   synthetic
                                   dilution
                                   water,  or
                                   seaxafer
                                   tor some
                                   soecies
                                                 hard
                                                 (HH)or
                                                 sott (SH)
                                                 synthetic
                                                 dilution
                                                 •at«r.  or
                                                 scaMater
                                                 for  son«
                                                 soecles

                                                 a,c.d,«,T.
                                                 P
                                                                                                 same as above
                                                                                                      Alabaster
                                                                                                      (1969),
                                                                                                 same as above
                                                                                                      Alabaster
                                                                                                      (1969),
                                                                                                      AMIC-5«i2S
                                                      All  compounds were Investigated   Wellborn
                                              because of their probable usage in        (1971),
                                              hatchery production of white cass.        AMIC-5571
                                              Compounds that can be used at recommended
                                              concentrations were Aquathol, Casaron,
                                              Llndane, and Terramycln concentrate.
-------
Compound

Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Organism

Orconectes
nals
Procambarus
slmulans
Channel
catfish
Roccus
saxatllls
Dragonf 1 les
(larvae!
Whirligig
beetles
BacKsNimmers
Ictaturus
punctatus
Toxlclty,
Active
Field Field Ingredient,
Study Location Ppm

FP Pratt, 0.1 (Kit!
Kansas
FP Pratt, 0.1 (K<.)
Kansas
FP Pratt, 0.1 (NTEO
Kansas
FP Pratt, 0.1 CNTEU)
Kansas
FP Pratt, 0.1 (K*l
Kansas
FP Pratt. 0.1 (Km
Kansas
FP Pratt, 0.1 (KO
Kansas
BSA — 1.66 mi
Experimental
Variables,
Control led
or Noted Comments

a,b,c,d,e,
* ,9.P
a,b,c,d,e,
f ,9,P
a,b,c,d,e,
f ,q,p
a.b,c,d,e.
a,b,c,d,e,
f ,9,P
a,b,c,d,e,
f ,9,P
a,b,c,d,e.
a,
synthetic
Those that should not be used were
Acrlflavlne, Baylusclde, Malachite green
oxalate, and Halathlon.
Baytex applied at various rates
up to ?50 PDb resulted In significant
reduction of crayfish. Ponds treated at
less than 100 ppb had to be retreated to
eradicate crayfish. This chemical
appears to have utility in fish culture
for controlling crayfish.
same as above
same as above
same as above
save as above
sane as above
same as above
Organochlor Ine insecticides Here
the most toxic compounds.
Reference

Ray, et al
(1970) ,
AMIC-51.33
Ray, etal
(1970) ,
Ray, et
al (1970),
AHIC-S
-------
>
•p-
          Baytax
          Bayt«x
          Baytex
          Baytex
Baytex
          Baytex
                     let slur us
                     •el as
                     Carass 1 us
                     auraTus
                               Cyprlnus
                               carplo
                     Plneohales
                     eronelas
                     Lepools
                     •aerochlrus
                               leoonls
                               •Icroloohus
                                             BS»   —
                                             BSA   —
                                             BSA   —
                                             8S»
                                   BS»
                                             BS«
                                                                1.62
                                                                     (Tl.)
                                                                1.16 (Tfc)
                                                                     (Tli)
                                                      1.38 (U)
                                                                1.8S (Tit)
a.
synthetic
test water

a.
synthetic
test Mater

a»
synthetic
test water

a,
synthetic
test Mater

8,
synthetic
test Mater

a,
synthetic
test water
                                                                                           centrarchlds would likely be safe for
                                                                                           cvorlnlds and Ictalurlds.  Sate levels
                                                                                           for Ictalurlds or cyprlnlds would
                                                                                           probably be hazardous for centrarchlds
                                                                                           and salBonlds.  The use of goldfish In
                                                                                           bloassays was discouraged.

                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  saae as above
                                                                                        sane as above
                                                                                                  sane as above
HaceK, et
al(1970).
AMIC-5510

HaceK, et
• K19TO),
AMIC-5510

HaceK, et
al(19ro) ,
• NIC-5511)

XaceK, et
81(1970).
AHIC-5510

HaceK, et
• H1970),
                                                                                                                           HaceK, et
                                                                                                                           al (1970) .
                                                                                                                           ANIC-5510
          Bsytex
          Baytex
          Baytex
          Baytex
          Baytex
                               Mlcrooterus
                               salnoldes
                     Salae
                     galrdnerl
                                             BSA   ~
                                             BSA   —
                               Sal no trutta  BSA
                     Oncorhynchus  BSA
                     Klsutch
                     Perea
                     flav«se«n<
                                             BSA   —
                                                                0.93
                                                                1.33 (Tl.)
                                                                1.3Z (T%)
                                                                1.6S (Tit)
a,
synthetic
test Mater

a.
synthetic
test water

at
synthetic
test water

a.
synthetic
test water

a.
synthetic
test water
                                                                                                  saae as above
                                                                                                  sane as above
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                  sane as above
HaceK, et
al (19/0),
ANIC-5519

HaceK, et
al (1970),
AMIC-SSIO

HaceK, et
al (1970).
AMIC-5510

HaceK, etal
(1<<70) ,
AHIO5S10

HaceK, et
al (1970).
AHIC-5510
          Baynood %I
                               Rasbora
                                             BCFA
                                                                B«0 (TZ)
                                                                                a*,c,e,f,
                                                                                                   One hundred sixty-four
                                                                                                                                     Alabaster
-------
15
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
CoBDOundJ Organism Study Location Pom or toted Comments
heteroMorpha and hard (HH>
BSA or
SOFT(SH)
synthetic
dilution
water, or
seawater
for some
species



inazolln Rasbora BCFA — 325 ITZ) a«,c,e,f.
heteromorpha and hard (HW)
BSA or soft
(Sif) syn-
thetic
dilution
water, or
•eawater
for - aoma
•paclea



>nsullde Cammarus BSA — !.«. (T%) a*
fasclatus
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wide range of toxlclty soannlng 12 orders
of magnitude. Knowing the toxlclty and
percentage of all coxoonents of a
formulation did not result In easy
predictability of the toxlcity of a
mixture of materials. Sometimes
pesticides were most toxic In hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wide ranoe of toxlclty scanning 1? orders
of magnitude. Knowing the toxiclty and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of materials. Sometimes
pesticides were most toxic in hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
Of the aquatic weed herbicides
evaluated, Dlclone was the most toxic.
Reference
(1969).
AHIC-51.25










Alabaster
(1969),
AHIC-5V25










Sanders
(1970),
          •HC  (Plus  llndane)   Hhlta sucker  FRL    Nice,
states 0.01-0.2?
       residua (SB)
Oaphnla was generally the most sensitive
organism.  All of the Crustacea were
affected by much lower concentration
levels of herbicides than indicated by
the TL sub SO values.  Alt of the animals
represent Important food chain links.

        The Bureau of Sport Fisheries
continued Its fish monitoring program by
collecting 1<»7 composite fish samples
from 50 nationwide monitoring stations
during the fall  of 1969.  Fish were
analyzed for residues of 11
organochlorlne Insecticides, Holds, and
PC9-S.
                                                                                                                                     Henderson,
                                                                                                                                     et al
                                                                                                                                     (1971),
                                                                                                                                     AHIC-H.07
          BMC (olus Itndane)   Tel low parch  FRL   Misc. states 0.01-0.31
                                                                                                   same  as above
                                                                                                                                     Henderson,
-------
                                                       residue (SB)
                                                                                                                            • t al
                                                                                                                            (1971),
§MC fptuc  llndenel   Chain
                     pickerel
FRL   Mite. states 0.07
                   residue (SBt
BMC  (plus  llndanel    White catfish FRL   Misc.  states 0.33 residue
                                                       CSB)
                                                                                         saae as above
                                                                                         save as above
Henrterson,
et  al
(19711,
»MIC-HD7

Henderson,
et  at
                                                                                                                            *Nic-i«»o7
BMC fetus  llndanel   White  perch    FRL   Hlsc.  states 0.18-0.26
                                                       residue ISO)'
                                                                                         saae as above
                                                                                         Henderson,
                                                                                         et at
                                                                                         (19711 ,
                                                                                         »MIC-1«.07
BHC  (plus  llndanel   Goldfish      FRL   Hlsc.  states 0.51 residue
                                                       (SB)
                                                                                         saae as above
                                                                                         Henderson,
                                                                                         • t al
BHC lotus  llndane)    Puapklnseed   FRL   Hlsc.  states 0.09 residue
                                                       (SB)
                                                                                         saee as above
                                                                                         Henderson,
                                                                                         et  al
0HC (plus  llndane)   largeaouth     FRL   Hlse.  states 0.01-0.47
                     bass                              residue (SB)
                                                                                         saae as above
                                                                                         Henderson,
                                                                                         et  al
                                                                                         (19711 ,
                                                                                         4HTC-1U07
BMC (otws  llndane)   Brown         FRL    Misc.  states 0.01-«.37
                     bullhead                          residue (SB)
                                                                                         sane as above
                                                                                        Henderson,
                                                                                        et  al
•MC (plus  llndane)   Carp
FRL   Hlsc. states D.01-0.99
                   residue (SB)
                                                                                         saae as above
Henderson,et
al (1971),
• NIC-11.07
•MC (plus  llndanel   Channel
                     catfish
FRL   Hlsc. states 0.01-1.50
                   residue (SB)
                                                                                         saae as above
Henderson,
et al
(1971),
BMC (plus  llndane)   Redhorse       FRL    Misc.  states 0.02-0.10
                     sucker                            residue (SB)
                                                                                         saae as above
                                                                                         Henderson,
                                                                                         et  al
                                                                                         (1971),
                                                                                         AHIC-1<»07
-------
  Compound
                                   Field  Field
                                   Study Location
Toxlclty,
Active
Ingredient,
  Pom
                                   Experimental
                                   Variables,
                                   Controlled
                                   or Noted
                                                                                                  Comments
                                                                                                                            Reference
BHC lolus  llndane)    Gizzard shad  FRL    Hlsc.  states  0.06-0.10
                                                       residue (SB)
BHC (plus  llndaneI    Spotted
                      sucker
BHC talus  llndane)    Bluegllls
BHC (plus  llndane)    Striped
                      mullet
FRL   Hlsc. states 0.01-0.03
                   residue (SB)
FRL   Hlsc. states 0.01-0.02
                   resIdue(SB)
FRL   Hlsc. states 0.?8-1.1<»
                   residue  (SB)
BHC (Plus  llndane)    Blue catfish   FRL    Hlsc.  states O.lt residue
                                                       (SB)
BHC (plus  llndane)    Rock bass      FRL    Hlsc.  states 0.01-0.1<.
                                                       reslduelSB)
BHC (Plus  llndane)    Freshwater     FRL   Hlsc.  states 0.01 residue
                      drum                              (SB)
BHC (plus  llndane)    Bloater
BHC (plus  llndane)    Lake
                      •hitefIsh
BHC  (plus  llndane)    Lake  trout
                                    FRl    Hlsc.  states 0.03-0.08
                                                       residue (SB)
FRL   Hlsc. states 0.05
                   residue(SB)
                                    FRL    Hlsc.  states 0.01-0.01
                                                       residua (SB)
                                                     same as above
                                                                                         same as above
                                                                                         same as above
                                                     same  as above
                                                                                         same as above
                                                     same  as above
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                                     Henderson,
                                                                     et al
                                                                     (1971) .
                                                                     *HIC-1<»07

                                                                     Henderson,
                                                                     et al
                                                                     (1971),
                                                                     AHIC-l«i07

                                                                     Henderson.
                                                                     et al
                                                                     (19711,
                                                                     AHIC-H.07

                                                                     Henderson,
                                                                     et al
                                                                     (1971),
                                                                     »HIC-1<»07

                                                                     Henderson,
                                                                     et al
                                                                     (1971),
                                                                     ANIC-11.07

                                                                     Henderson,
                                                                     et al
                                                                     (1971),
                                                                     AHTC-1*07

                                                                     Henderson,
                                                                     et al
                                                                     C19M»,
                                                                     AMIC-K.07

                                                                     Henderson,et
                                                                     al (1971),
                                                                     AHIC-11.07

                                                                     Henderson,et
                                                                     al (1971),
                                                                     AHIC-H07

                                                                     Henderson,
                                                                     et al
-------
>

V/l
        •HC (plus llndane)   Unite crapple FRL   Hlse. state* 0.07-2.19
                                                              residue  (SB)
        SHC telu* llndane)   Blojiouth
                             buffalo
        •HC Cplus Itndanal   Saallaouth
                             buffalo
                                   FRL    MISC.  State*  0.03-0.07
                                                       residue  (SB)
                                   FRL   Hlse. states 0.08 residue
                                                      (SB)
        BHC lotus llndane)   Ftathead      FRL   Misc. states 0.02 residue
                             catfish                          (SB)
BHC lotus llndane)   Coldeye
        BHC lolus llndane)   Hal leva
        BNC lolus llndane)    Saucer
FRL   Misc. states 0.02-0.08
                   residue (SB)
                                           FRL   Nlse. states 0.01 residue
                                                              (SB)
                                   FRL   Hlse. states 0.01 residue
                                                      (SB)
        BMC (plus llndane)    Flannelaouth  FRL   Hlse.  states 0.02 residue
                             sucker                           (SB)
        BMC (plus llndane)    BlaeK
                             bullhead
                                   FRL   Hlse. states 0.01 residue
                                                      (SB)
       BHC (Plus llndane)    Hhlte bass    FRL   Hlse.  states  O.tl  residue
                                                              (SB)


       BMC lolus llndane)    Black crapple FRL   Misc.  states  0.01-0.03
                                                              residue  (SB)
                                                                                                 saae  as above
                                                     sane  as above
                                                     saae as above
                                                                                                saae as above
                                                                                        saae  as above
                                                                                                saae as above
                                                                                                saae as above
                                                                                                saae as above
                                                                                                saae as above
                                                                                                sane as above
                                                                                        saae as above
 (1971),
 AHIC-H.07

 Henderson,
 et  al
 (19711,
 AMIC-1407

 Henderson,
 et  al
 (1971) ,
 AHIC-H07

 Henderson,
 et  al
 (1971),
 ANTC-l«t07

 Henderson,
 et  al
 (1971),
 AHIC-1%07

 Henderson, at
 al  (197U,
 AHIC-U.Q7

 Henderson, et
 al  (1971),
 AHIC-1W07

 Henderson, et
 al  (19711,
 AHIC-1V07

 Henderson,
et al
 (1971),
 AHIC-1%07

 Henderson, et
 al  (1971),
 A MIC- 1*07

Henderson, et
at  (1971),
 AMIC-ld07

Henderson,
et al
                                                                                                                                   AMIC-H07
-------
            Conoound
            Field  Field
Organise    Study Location
                                                       Toxlclty,
                                                       Active
                                                       Ingredient,
                                                         Ppn
                                   Experimental
                                   Variables,
                                   Controlled
                                   or Noted
                                                                                                            Comments
                                                                                                                                      Reference
k
BHC (olus llndan*)    Largescale
                      sucker
BHC (plus IIndanel   Small mouth
                     bass
FRL   Hlsc. states 0.01-0.1Z
                   residue (SB)
FRL   Hlsc. states 0.01 residue
                   (SB)
          BHC (olus llndan*)   Northern       FRL    Hlsc.  states 0.01  residue
                               squaw fish                         (S3)
          BHC (Dlus  IIndane)    Chlselnouth    FRL    Hlsc.  states 0.03-0.03
                                                                 residue (SB)
BHC (olus  llndan*)    Rainbow trout  FRL   Hlsc.  states 0.01 residue
                                                       (S3)


BHC (olus  IIndane)    Brldgello     FRL   Hlsc.  states 0.03 residue
                      sucker                            (SB)
          BHC  (plus  llndan*)    Arctic
                                grayling
          BHC  (olus  IIndane)    Round
                                MhlteTish
          BHC  (olus  IIndane)    Longnos*
                                sucker
                                    FRL    Hlsc.  states 0.13 residue
                                                       (SB)
                                    FRL   Hlsc.  states 0.0* residue
                                                       (SB)
                                    FRL    Hlsc.  states 0.01-0.03
                                                       residue (SB)
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                                   same as above
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                                                                      Henderson.
                                                                                                                                      et  al
                                                                                                                                      (19711 ,
                                                                                                                                      Henderson,
                                                                                                                                      et al
                                                                                                                            AMIC-K.07

                                                                                                                            Henderson,
                                                                                                                            et al
                                                                                                                            (1971),
                                                                                                                            AMIC-11.07

                                                                                                                            Henderson,
                                                                                                                            et al
                                                                                                                            (1971),
                                                                                        Henderson,et
                                                                                        al  (1971),
                                                                                        AMIC-11.07

                                                                                        Henderson,
                                                                                        et  al
                                                                                        (1971),
                                                                                        AHIC-1".07

                                                                                        Henderson,
                                                                                        et  al
                                                                                        (1971),
                                                                                         Henderson,
                                                                                         et  al
                                                                                         (1971),
                                                                                         AMIC-K.07

                                                                                         Henderson,
                                                                                         et  al
                                                                                         (1971),
                                                                                         An-IC-K.07
          BHC
                               Puntlus  tlcto —•
                                                                 70 (Tit)
                                                                                 a,c,d,e< f
                                                                                                    Of the pesticides Investigated,   Bnatla
-------
8HC
                     Carclnus
                     •aenas
                                   BS*    —
                                                                                  the  most  toxic Has  Klofos  followed In      (1971),
                                                                                  decreasing order  by Sumlthlon.  Halathlon,  «HIC-5*23
                                                                                  Formlthlon,  Dlmecron, Sevln,  and  BHC.  The
                                                                                  author  cites the  need for  more  selective
                                                                                  Pesticides nontoxic to  fish  or
                                                                                  antagonistic agents for  reducing  fish
                                                                                  toxlcl ty.
                                 greater than    a*(contin-         One hundred-forty surface active
                                 100  (12)        uous aer-  agents, solvent emulslflers, pesticides,
                                                 ation, sea-Polychforlnated blphenyls, pure
                                                 water, and Inorganic, and organic chenicals Here
                                                 daily      evaluated against as many as ten marine
                                                 solution   organisms.  The authors noted that most
                                                 renewal)   published data of this type deal with
                                                            toxlclty of chenlcals to freshwater
                                                            organisms.
BHC
                     Cardlum edule BSA
                                                      greater
                                                      (TZ)
                                                               than  10
                                                 a»(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                        same  as above
                                                                      Portmann, et
                                                                      al (1171),
                                                                      »HIC-7701
                                                                      Portmann, «t
                                                                      al  (1971),
                                                                      »HIC-7rot
BHC
                     Crsngon
                     crangon
                                   BS*
                                                      0.001-0.003
                                                 a*(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                        same  as above
                                                                      Portmann,  at
                                                                      al  (1971).
                                                                      AMIC-7701
Bis hydroxymethyl)
Ohosphlnlc acid
Plmeohates
oromelas
                                   BSA
Bis (dimethyl thlo   Phormldlum
carbomoyl) dlsulflde amblguum
.29.8 ITI»>        a»,d,e,o,           Malathlon and Its hydrolysis      Bender
                 and Fa     products Here evaluated  with the finding  (1969),
                            that  one such product (dlethyl  funaratc)   AHIC-3787
                            Has more toxic than lalathlon to fathead
                            minnows.  Synerglsm occurred between
                            Halathlon and two products of hydrolysis.
                             Continuous exposure resulted In
                            Increased toxlclty.

 O.S-10.0         —                  Of 71. chemicals  evaluated as      Otto  (1970),
 (f>6percent                 alqicldes, only 9 were more toxic than    AHIC-49Z
 growth                      CuSOfc.   None Inhibited growth of
 Inhibited  1<>1               mat-forming algae for more than ? weeks.
                            CuSO"» formulated with certain watting
                            aqents  Has more toxic than CuSOfc alone.
                            Cooper  chloraalne Has also found to  be
-------
                        Organism
                                   Field  Field
                                   Study location
                                 Toxlclty,
                                 Active
                                 Ingredlentt
                Experimental
                Variables,
                Controlled
                or Noted
                                                                                                 Concents
                                                                                                                           Reference
Bis Itrl-n-butyll
tin avlde
•eraseeu
Phormldlum
amtaiguum
                     Sal BO
                     galrdnerl
                                   L     ~
              8CF»
              and
              BSA
1.5-10.0 HOD
percent

Inhibited 1U)

l.tOO CTZI
                                                                                 •ore toxic than CuSO*.  No wetting agents
                                                                                 Mere found to b« Inhibitory at the
                                                                                 concentrations Investigated CO.05 and
                                                                                 0.005 DP*).  Also reported are factors
                                                                                 affecting growth of algae in canals to
                                                                                 determine whether there were leads to
                                                                                 controlling algae by environmental
                                                                                 management.  No practical environmental
                                                                                 •eans Mere found*

                                                                                        same as above
                                                                    Otto  11970).
                                                                    ANIC-89?
Bewrben
                     Betta
                     splendens
                                   L     —
                                                      2*50  ISB 6 hr)  a*
                     Carclnus
                                   BSA   —
                a*,c,e,f«           One  hundred  sixty-four             Alabaster
                hard IHH)   pesticides,  wetting  agents,  and           (1969),
                or         alscellaneous water  pollutants  showed a   AMIC-5%?S
                SOFT(SM)    Hide range of toxlclty spanning 12 orders
                synthetic   of magnitude.  Knowing the toxlcity and
                dilution    percentage of all  components of a
                Hater, or   formulation did not  result in easy
                seaiiater    predictability of  the toxlclty  of a
                for some    mixture of materials.  Sometimes
                species    pesticides were most toxic In hard mater
                           and sometimes the  opposite was  true.
                           Testing the actual material  as  sold was
                           found to be essential.

                                   The effects  of ethanol  and        Raynes,  etal
                           bourbon on the aggressive response of
                           SJanese fighting fish were determined.    (1968),ANIC
                           Fthanol Increased  gill show                57l£
                           (aggressiveness) and bourbon and bourbon
                           congeners decreased  It.  The authors
                           tentatively concluded that the  delayed
                           effect  of the congener resulted from
                           Involvement of a different physiological
                           mechanism and that this may be  related to
                           hangover effects In  man.

10-33        a»(contln-          One hundred-forty surface active  Porteann,  et
                uous aer-   agents, solvent emulsltiers, pesticides,  at  (1971),
                ation,  se«-oolychlorlnated blphenyls, pure           AHIC-77tl
                water,  and  Inorganic, and organic chemicals were
                daily       evaluated against  as many as ten aarine
-------
BP 1002
                     Cardlun edule BSA
                                                       33-100  tT2)
                                                                      solution    organisms*   The authors noted that nost
                                                                      renawal)    published data of this type deal with
                                                                                  toxielty of chemicals to freshwater
                                                                                  organises.
                                                 a*(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 wator, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                         sane as above
                                                                     Portnann, et
                                                                     •I  (1971),
                                                                     AHIC-7701
BP 1902
                     Cranqon
                     cranqon
                                   BSA
                                                       3.3-10  (T21
                                                 at-( contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                         sane as above
                                                                     Portnann, et
                                                                     al  (1471),
                                                                     AHIC-7701
BP 1002
                     Llmanda
                     llnanda
                                   8SA
                                                       10-33  (T2)
                                                 a«(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                         sane as above
                                                                     Porfnann, et
                                                                     at  (1971),
                                                                     &MIC-7701
BP 1002
                     Ostrea edulIs BSA
                                                      33-100  (T2)
                                                 a*(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                         sane as above
                                                                     Portnann, et
                                                                     al  (1971),
                                                                     *MIC-7701
BP 1002
Panda I us
•ontsqul
                                   BSA
                                                      3.3-10  (T?>
                a*(contin-
                uous aer-
                ation, sea-
                vatcr, and
                daily
                solution
                renewal)
                                                                                         sane as above
                                                     Portnann, et
                                                     al (1971),
                                                     ASIC-7701
   110OX
Agonus
catapnractus
                                   BSA    —
greater than
10,000 (TW)
a«-( contin-
uous aer-
                                                                                         sane as above
Portnann* et
al (1971),
-------
          Coapound
            11MX
            llltX
Ml
O
         BP lltO
         BP lift
            lift
Field Field
Organise Study Location





Cardlua edule BSA —






Crangon 8S» —
crangon





Agonus BSA
cataohraetus





Cardlua «dula BS»






Crangon BSA —
crangon





Toxlclty, Experimental
Active Variables.
Ingredient. Controlled
Pom or Noted Comients
ation, sea.
water, and
daily
solution
renewal)
greater than a«(contin- same as above
10.000 m> uoua aer-
ation, sea-
water, and
daily
solution
renewal)
greater than ae(contin- saae as above
10.000 (T«) uoua aer-
ation, sea-
viator, and
dally
solution
renewal)
1000-3300 ,AMIC-
7701



Port»ann, et
al (1971).
AHIC-7701




-------
                     Fundulus
                     heteroclItu*
                                   BSA   ~
                                 0.00001-0.00022 a*,c,e,and
                                 
-------
Vfl
ro
Compound


Broelne



Broalne



Broalne



Brenephos












Broaoxynll (K salt!








Broaoxynll |K salt!


Field
Organise) Study


Carasslus FL
auratus


Roc c us FL
chrysops


Stlzostedlon FL
vltreum
vltreua

Rasbora BCFA
neteroaorpha and
BSA










Rasbora 6CFA
heteronorpha and
BSA






Rasbora BCFA
heteroeorpha and
BSA
Toxlcity,
Active
Field Ingredient,
Location ppa
HIchlqan,
and Erie
Great Lakes O.Kreslduel
- Superior,
HIchlqan,
and Erie
Great LaKes O.SIreslduet
- Superior,
Mlchl gan,and
Erie
Great LaKes O.B(resIdue)
- Superior,
Hlchlgan,
and Erie
— 0.62 (T2)












— 60 (TZ,
hardwater)







— 5.9 !T2,
soft Ha tar)

Experlmenta
Variables,
Controlled
or Noted


——



__



— _



a»,c,e,f,
hard IHW)
or soft
13WJ syn-
thetic
dilution .
water, or
aeawater
for aoao
species



a*,c,e,f ,h
ard (HH)
or soft
(SWI
synthetic
dilution
Mater, or
for some
species
a*,e,e,f.
hard (HH)
or soft
1
Coaaents


sane as above



sane as above



sane as above



One hundred sixty-four
pesticides, wrttlna aqents, and
miscellaneous water pollutants showed a
wide range of toxlcity spanning 1Z orders
of magnitude. Knowing the toxlcity and
percentage of al 1 components of a
formulation did not result In easy
predictability of the toxiclty of a
mixture of materials. Sometimes
pesticides were nost toxic in hard water
and sometimes the opposite mas true.
Testing the actual naterlal as sold Has
found to be essential.
sane as above








sane as above


Reference
AH1C-3778

Lucas, et al
(1970) ,
AMIC-3778

Lucas, .et al
(1970>,
AMIC-S778

Lucas, et al
(1970»,
AHIC-37TB

Alabaster
(19691,
AMIC-51.25










Alabaster
(1969),»HIC-
5*25






Alabaster
119691,
AHIC-5I»Z5
-------
                Ul
ftasbora       8CF»
heteroaorpha  end
              BSA
                                                                8.65 ITZI
          Bvsan 99
 I
\n
u>
Rasbora       BCFA
heterooorone  and
              BSA
                                  1.8  III,
                                  hardwater)
          »u*an
Rasbora       BCFA
hetaroaorpha  and
              BSA
                                 t.z ITI,
                                 SoftMeter)
         Cadaiua chloride  las  Agonus         BSA
                               cataphraetus
                                                                33 mi
                                                                                (SU)
                                                                                synthetic
                                                                                dilution
                                                                                water, or
for SOB*
soeeles

a'.c,«,f ,
hard
(HH)or
soft  ISM)
synth* tie
dilution
Mater, or
seanater
for so«e
so«cl«s
        One hundred sixty-four            Alabaster
pesticides, wettlnq aqents, and           (1969),»MIC-
•Iscellaneous Hater oollutants showed a   5425
wide range of toxlclty soannlng 12 orders
of naqnltude.  Knowlnq the toxlctty and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty of a
• Ixtur* of Materials.  Sometimes
pesticides Mere »ost toxic In hard Mater
and sonetlaes the opposite Mas true.
Testing the actual •aterlal as sold Has
found to be essential.
a«,c,e,f,
hard (KW)
or soft
ISW) ayn-
thatte
dilution
water, or
aaawater
for soee
opoclas

a*,c,e,ft
hard
IHM)or
soft (5M)
synthetic
dilution
Mater, or
seaMater
for sone
species

a»(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
                                                                                                  saae as above
                                          Alabaster
                                          C1969),
                                          »MIC-5«.?5
                                                                                                  saae as above
                                          Alabaster
                                          (19K9
                                          5425
                                                                     One hundred-forty surface active Port"»nn, «t
                                                             aoents, solvent enutslflers, pesticides, al I197D,
                                                                                            ooIych1 orInated blohenyls?  oure
                                                                                            lnorqanic«  and organic  chemicals  Mere
                                                                                            evaluated  against  as nany us  ten  narlne
                                                                                            organisms.   The authors noted that  >ost
                                                                                            published  data of  this  type deal  nlth
                                                                                            toxlclty  of  chenicats to  freshwater
                                                                                            organlsBS.
                                                                                                                                     AHIC-7701
-------
 I
vn
 •P-
Toxlclty,
Active
Field Field Ingredient*
Coaoound Organise) Study Location Ppm
Cadmium chloride (as Cardlun edule BS» — 3.3 (Ti>)
cadalum)





Cadalua chloride (as Crangon 8S» — 1.0 (T2>
cadalumt crangon





CadBlua chloride Fundulus L — 50 (SB2)
heteroclltus

Exoerlnental
Variables,
Control led
or Noted Comments
at (con tin- sa«e as above
uoua aer-
ation, sea-
water, and
dally
solution
renewal)
a»(contln- sane as above
uous aer-
ation, sea-
water, and
daily
solution
renewal )
**iC Abnormalities observed Included
Intestine, Kidney, gill filaments, and
resolratory lamellae. The earliest and
Reference
Portaann, et
al (1971),
AMIC-7701




Portaann, et
al (1971),
ANIC-7701




Gardner, et
al (190).
AMI C- 3827
          Cadelua  sultate  las  •croneurla    8SA
          Cd>
         Cadailua sulfate  (as   Epheaerella    8SA
         Cdl
         CadBlua sultate  las   Hydroasyche    BSA
         Cd)
                                                                32 ITld)
                                                                2 (Tt>
                                                                32 (T10)
•*,c,d,e
  most severe was the Intestine (and mucus
  within one hr).  Eoslnooh1 11 a occurred
  after it hr exoosurc, and
  lymohocytethrombocyte  Irregularities
  occurred after 12 hr exoosure.   The
  authors suggest broader study of
  blood/natholoqy as a means  for developing
  a Hater pollution classification simitar
  to those used In mammalian  toxicology.

f         Ephenerella (mayfly)  Mas the most Narnlck,  et
  sensitive aquatic Insect of  those         al(196.
                                                     •HIC-3767

                                                     Marnlck. et
                                                     al(1969),
                                                     •HIC-3767
-------
         Cadvlua
                              »los»
                              paeudo.
                              harangua
                                            FL
         Cadaltw
 I
VJl
          Cadalua
         Cadalua
         Cadalua
         Cadalua
                               Coregonus     FL
                               artedli
                               Coregonus     FL
                               clupeaforals'
                               Coregonus     FL
                               hoy I
                               Prosoolua     FL
                               cylIndraeeu*
                              Salvellnus    FL
                              naaaycush
                                            FL
                                            FL
                                            FL
                              aordax
                              Carass1us
                              auratus
                              Notrepls
                              hudsenlus
Great Lakes
- Superior.
Michigan,
•nd
                                                                0.00006
 Great  Lakes
 - Superior,
 Nlchlqan,
 and Frle

 Great  Lakes
 - Suoerlor.
 Michigan,
 •nd Erie

 Great  Lakes
 - Suo«rlort
 Michigan,
 •nd Erie

 Great  Lakes
 • Suoerjort
 Mlch_lqant
 and Erie

 Great  Lakes
 - Superior,
 Michigan,
 and Erie
                                                                0.0016(resldue) —
                                                                O.OOOZtresldue)  —
                                                                O.OOOS(resldue)
                                                               O.OOOklreslduel —
                                                               0.003(residue)  —
                                   Trace  element content  of  fish
                           Iron Lakes Superior, Michigan, and  Erie
                           Mas deternlned by  activation analysis.
                           Whole body ana Iiver residues  Here
                           deternlned.  Concentrations varied  Mlth
                           species and  lake.  . Other  etenents found
                           were!  antlnony  -  5 to  100 Don, bartun -
                           0.2 Don, cesium  -  3 opb,  lanthanu*  — 1 to
                           20 pob, nercury  -  10 ppb, rhenlua - 0.9
                           to 5 pob, rubldlu* - 0.06 to 6 DO*,
                           scandlua - 2 cob,  selenlua - 0.1  to 2
                           OOb, silver -  0.001 oob.

                                  saae as above
 Lucas,  et  ml
 (1970),
  M1IC-3T78
Great Lakes  0.00007
- Superior,  realdu*)
Michigan, and
Erie
Great Lakes
- Superior,
Nlchlqan,
and Frle

Great Lakes
- Superior,
Michigan,
and Erie
             O.OOlUresldue)
O.OOOllfesldue)  —
                                                                                                  sane  as abova
                                                                                                 saae  as  above
                                                                                                 saae as above
                                                                                                 sa«e as above
                                                                                                 saae as above
                                                                                                 saae as above
                                                                                                 sane as above
                                                                     Lucas, et at
                                                                     I19TOI,
                                                                     *MIC-3778
                                                                     Lucas, et al

                                                                     •MIC-J778


                                                                     Lucas, et al

                                                                     4MIC-3778
                                                                     Lucas, et at
                                                                     (14701,
                                                                     •WIC-3770
                                                                     Lucas, et al
                                                                     (1970).
                                                                     •NIC-377B
                                                                     Lucas, et al
                                                                     (19701,
                                                                     »HIC-3778
                                                                     Lucas, et al
                                                                     (1970),
                                                                     AHIC-3778
Lucas, et al
(1970).
AHIC-3778
-------
Comoound Organism
Cadmium Percoosls
omlscomaycus


Cadmium Roccus
chrysoos


Cadmium Perca
II avescens


Cmdmlum Stlrostedlon
Jt> wltreum
1 vl treum
O\
Cadmlu* Coregonus
clupeaformis

Field Field
Study Location
FL Great Lakes
- ^uoerior.
Hichl qan.
and Frle
FL Great Lakes
- Superior,
f ich I qan, and
Erie
FL Great Lakes
- Superior,
Hlchl qan.
and Erie
FL Great Lakes
- Superior,
Michigan,
and Erie
FL Moose Lake,
Can.

Toxlclty, Experimental
Active Variables,
Inqredlenf, Controlled
Pom or Noted Comments
0.0001 (residue) — - same as above



0.000? (residue) — same as above



0. 0005 (residue) -- same as above



0.0002(resldue) -- same as above



0.05 (residue) -- Concentrations of 13 toxic
elements in dressed fish from heavily
Industrialized and non-industrialized
Reference
Lucas, et i
(1"70) ,
AMIC-3778

Lucas, et
(19701,
AHIC-3778

Lucas, et
(1970),
4MTC-377S

Lucas, et
(1970) ,
AMIC-3778

Uthe.et al
(1971) ,
AHIC-3819

al



al



al



at






Cad'Iui
Cadilui
Cadmium
Cadmium
                     Coregonus     FL
                     cluoeaforvis
                     Esox luclus   FL
                     Esox lucius   FL
                     Esox lucius   FL
Lake         0.05 (residue)
Ontario,
Can.

Moose Lake,  0.0? (residue)
Can.
                                         Lake St.     0.09  (residue)
                                         Pierre, Can.
                                         Lake Frle,   0.05  (residue)
                                         Can.
                                        areas were determined.  Only mercury
                                        exceeded regulatory limits, and
                                        concentrations of most elements Here
                                        essentially the same In fish from both
                                        areas.

                                               same as above
                                                                                        same as above
                                                                                        same as above
                                                                                        same as above
Uthe.et al
(1971),
AMIC-3819

Uthe, et al
(1971) ,«>1IC-
3819

Uthe, et

»HrC-3819

Uthe, et al
11971),I
3819
-------
CadBlua
Cadalua
                     Osaerus       FL     Lake  frit,    0.16  (residue)
                     •ordex               Can.
Perca         FL     lake  Eric.    8.05  (residue)
fl*v«sc«ns           Can.
                      Paralabrax    FH    Scatterqood   3 (dorsal
                      clathratus           Steam Plant,  muscle
                                          Los Angeles»  residue)
                                          Cat.
                                                                                         saae  as  above
                                                                                         same as above
Cadalua
Paralabrax    FH
Clathratus
Paralabrax    FH
clathratus
                                          Catallna      3  (dorsal
                                          Isl»nrtt Cat.  ousel*
                                                       residue)

                                          Seatterqood   k  (ventral
                                          Sf«»»  Plant,  Muscle
                                          Los Anqelest  residue)
                                                                    Fish collected  fro« an ettluent
                                                            ploe  of a  steao  olant and  fro» offshore
                                                            Maters of  Catatlna Island  Here analyzed
                                                            for trace  element content.  Trace element
                                                            content of  the effluent Hater Has at
                                                            least 5 times qreater than that of noraal
                                                            sea water  for cadmium,  corner, nlcHel,
                                                            zinc, and  chromium.  Livers of fish fro"
                                                            the effluent were nearly titlce the size
                                                            of those from the ocean.  Greatest
                                                            differences In concentration occurred
                                                            •1th  aluminum, cadmium, and nickel.
                                                            Silver, barium,  lithium, and lead Shooed
                                                            the leest  differences.  The author
                                                            concluded  that trace element analysis of
                                                            tissues could be used to determine the
                                                            effect of  pollutants on aarlne organises.

                                                                   same as above
Uthe, et
»L«l«Tl>,
AHIC-3819

Uthe. et
*L(147ll,
• HIC-3819

Staoleton
(1968).
»«IC-5988
                                                                   saae as above
                                                                                                                           Staoleton
•HIC-S980

Stuoteton
(1968),
»MIC-S980
Cadmlua
Cadalua
Cadalua
CadBlua
Paralabrax    FH    Catallna     ? (ventral
etathratus          Island, Cal. Muscle
                                 residue)

Paralabrax    FH    Scattergood  10 (gonads
clathratus          Straa Plant, residue)
                    Los Anqeles,
                    Cal.

Paralabrax    FH    Catallna     6 (qonads
clathratus          Island, cat. residue)
Paralabrax    FH    Catallna     3
clathratus          Island, Cal. (gonads
(gravid                          residue)
feaales)
                                                                                        same as above
                                                                                        same as above
                                                                                        saae as above
                                                                                        same as above
Staoletoo
(19681,
•HIC-9989

Staeleton
(1968),
»MIC-5980
Staoleton
(1968),
»MIC-S980

Staeteton
(1968),
•HIC-S988
-------
SJI
CD
           Coaoound
         Cadalua
         Cadalua
         Cadalua
         Cadvlua
         Cadalua
         Cadalua
         Cadnlua
         Calclua chloride
Organise,
Paralabrax
elathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
el athratus
Paralabrax
cl athratus
Paralabrax
cl athratus
Paral abrax
elathratus
Paral abrax
elathratus
Lepoals
•acrochlrus
Toxlclty,
Active
Field Field Ingredient.
Study Location Ppa
FH Seatterqood 11 (liver
Steaa PI ant • residua)
Los Anqeles,
Cal.
FM Catal Ina 2t (1 Iver
Tslandt Cal. residua)
FH Scattergood 6 (integuaent
Steaa Plant, residue)
Los Angel es«
Cal.
FH Catal Ina I (Integument
Island, Cal. residue)
FH Scattergood .
*HIC-59»8
— sane as above Staateton
(19f.»),
»Hic-5g»o
sane as above Staoleton
(1966),
•MIC-5980
— sa*e as above Staoleton
(1968),
AMIC-5980
sa»e as above Staoleton
(19681,
•HIC-598D
-- saae as above Staoleton
(1968),
AMIC-5980
saae as above Staoleton
(19681,
AHIC-S980
a«,e» and This study xas conducted to Patrick, at
aynthetle determine the relative toxlcltles of ?0 al (1968).
dilution coamon constituents of Industrial wastes AHIC-5720
water to a fish, an alaa, and an Invertebrate.
                                                                                          The experiments were conducted over a
                                                                                          10-year period for varied purposes.  The
                                                                                          authors recoaaend bloassays with at least
                                                                                          three eoaoonents of the food neb.
-------
Catclun chloride
Nltzschla
linear Is
Calclu*) hypochlorlte  Phormldlum
 (as  CD               amblguua
                                    BS»,
                                    L
                                    L      —
3,130 (T5)
a*,e, and
synthetic
dilution
water
                                                                                         sa»e as above
                                                       0.5>tO.O (NTE1  —
         oxide  (olu*
SulfurIc acid)
Ictalurus
punctatus
                                    •      •»«
?*,200-30,*00
IK?. 5-9 PPX
001
a'.c.e'
o
Calcium oxide (plus  Ictalurus     L
Sulfur 1C acid)       punctatus
Calclua sulfata
                     Lepovls
                     •acrochlrus
              BS*.
              L
                                 367-509(67
                                 percent K
                                 2?-2«, 5-9 ppm
                                 DOI

                                 2,980 (Tbl
                                                                         ,c,e*,f,
                a«,e,  and
                synthetic
                dilution
                Water
                                                     Patrick, et
                                                     al (1968).
                                                     mC-5720
                   Of 7i> chemicals evaluated as      Otto  (19701,
           alqlcldes, only 9 were more toxic than    AMTC-892
           CuSnfc.  None  Inhibited growth of
           nat-fornlng alcae for more than 2 weeks.
           CuSOU formulated Kith certain Netting
           aqents was more toxic th^n CuSO<» alone*
           Coooer ch I or-anlne was also found to be
           more toxic than CuSOi*.  No Netting aqents
           were found to be Inhibitory at the
           concentrations Investloated 10.05 and
           0.005 ppi»» .  Also reported are factors
           affecting growth of alqae In canals to
           determine whether there were leads to
           controlling alcae t>v environmental
           management.  No practical environmental
           means were found.

                   Large and small catfish Here      Sparks, et
           subjected to a neutral synthetic Maste    al (1969),
           aonroxlmatIng that being dumped py the    AMIC-5902
           Sunflower Army Ammunition Plant into the
           Kansas River.  There were no apparent
           differences between the resoonses of the
           large end small  fish.  Fish In the
           neutral  mixture swam continuously with
           particles of the mixture clinging to the
           mucus of the skin.  Also,  the  mucus
           stripped away In places,  and stranos of
           mucus extended from the gills.   The
           degree of  coating of the skin,  stripping
           of  the mucus,  and mortality depended on
           the amcunt of  solids Kept  In suspension
           by  aeration.

                  same as above                      Sparks,  et
                                                     all 1969),
                                                     4NIC-590?
                   This study was conducted to
           determine the relative toxlcltles of 20
           common constituents of Industrial wastes
           to a fish, an alga, and an Invertebrate.
           The experiments were conducted over a
           10-year period for varied purposes.  The
           authors recommend bloassays with at least
           three components of the food web.
                                                     Patrick,  et
                                                     at  (1968),
                                                     AHTC-57ZO
-------
  Coaoound
Calclua sulfate
Calciu*
Organism.
Mltzschla
line arts
Paralabrax
Clathratus
Fiald
Study
BS«,
L
FH
Field
Location
—
Scatfergood
Staa* Plant,
Los Angelas,
Toxieity,
Active
Ingredient,
Ppa
3,308 (T5>
7Z8 (dorsal
muscle
residue)
Experimental
Variables,
Control led
or Noted
a,*, a, and
synthetic
dilution
water
oioe of
waters
Comments
seme as above
Fish collected from an effluent
a steam plant and from offshore
of Catalina Island Here analyzed
Reference
Patrick, at
al (1966).
•MIC-5720
Staoleton
(1968),
ANIC-S9.80
                                         Gal.
Calclua
 Calclua
Calcium
Catclua
Cafclua
                     Paralanrax
                     elathratus
                     Paralahrax
                     Clathratus
                     Paralabraic
                     elathratus
                     Paralabrax
                     Clathratus
                     Paralaprax
                     elathratus
                                   FH
                                   FM
                                   FH
                                   FN
PH
Catalina     «67 (dorsal
Island, Cal. auscle
             residue!

Scattergood  1020 (ventral
Steam Plant, museI*
Loskngetes,  residue)
Cal.

Catalina     5*3 (ventral
Island, Cal. muscle
             residue)

Scattarqood  (53 (gonads
Steam Plant, residue)
los »nqa\%$,
Cal.

Catalina     565 (gonads
I*l«nd, C«l.
                                              for  trace  element  content.  Trace element
                                              content  of  the effluent  Mater Has at
                                              least  5  times greater  than that of normal
                                              sea  water  for cadmium, cooper, nickel<
                                              Zinc,  and  chronluff.  Livers of fish from
                                              the  effluent Mere  nearly tulce the size
                                              of those from the  ocean. Greatest
                                              differences In concentration occurred
                                              Hlth aluminum, cadoilu*.  and nlcKel.
                                              Silver,  barium,  lithium, and lead shooed
                                              the  least  differences.   The author
                                              concluded  that trac* aleaent analysis  of
                                              tissues  could be usad  to determine the
                                              effect of  pollutants on  marina organisms.

                                                     save as abova
                                                     same as abova
                                                     saaa as abova
                                                     same as abova
                                                     same as abova
Staoleton
(1968>,
•HIC-5980

Staolefon
(196BI ,
•HtC-5980
                                                                                        Staoleton
                                                                                        (196M,
                                                                                        Staoleton
                                                                                        (19661,
                                                                                        AHIC-5980
                                                                                        Staoleton
                                                                                        (196»),
                                                                                        tmc-sm
-------
Calclua
Calcium
Calcium
Calcium
Calcium
Calctun
Calcium
Calcium
Calcium
GanaI bank
•••dHlller
                     Paralabrax
                     clathratus
                     (gravid
                     Paralabrax
                     clathratus
                      Paralabrax
                      elathratus
                     Paralabrax
                     clathratus
                      Paralabrax
                      elathratus
                     Paralabrax
                     el athratus
                     Paralabrax
                     elathratus
                     Paralabrax
                     clathratus
                     Paralabrax
                     clathratus
                                   rn
                                   FM
                                   FH
                                   FH
                                   FM
                                   FM
                                   FH
                                   FM
Rasbora       BCFA
hataroaorpha  and
              BSA
                    Catallna     550  (qonads
                    Island. Cat. residua)
                    Scatterqood  155  (liver
                    Steaa Plant, residual
                    Los Angeles,
                    Cat.

                    Catallna     Z65  (liver
                    Island. Cat. residue)
                    Scatterqood  1158
                    Steam Plant. (Integument
                    Los Angeles, residue)
                    Cal.
                    Catallna
                    Island. Cal.  (Integument
                                 residue)

                    Scatterqood   380  (heart
                    Steam Plant, residual
                    Los Anqeles.
                    Cal.

                    Catallna     tBO  (heart
                    Island. Cal. residue)
                    Scattergood  19.000 (eyeball
                    Steaa Plant, residue)
                    Los Anqeles,
                    Cal.
                    Catallna
                    Island. C
?6,200(evebatl   —
residue)
                                                                                        sane as above
                                                                                        sane as abova
                                                                                        saae as above
                                                                                        same as abova
                                                                                        same as abova
                                                                                        same as above
                                                                                        same as above
                                                                                        saae as abova
                                                                                        same as above
                                                      610 (T2)
                a*,c,e,»,
                hard(HH)
                or soft
                (SM)
                synthetic
                dilution
                water, or
                seawater
                for some
                species
        One hundred sixty-four
pesticides, nettlno agents, and
mlsce I laneous Mater oollutants showed a
Hide range of toxiclty soanning 12 orders
of magnitude*  Knowing the toxiclty and
percentage ot all comoonents of a
femulation did not result In easy
predictability of the toxiclty of a
mixture of materials.  Sometimes
pesticides were moS't toxic In hard water
and sometimes.the opeoslta was true.
                                                                     Staoleton
                                                                     11968) .
                                                                     AMIC-5980
                                                                     Staoleton
                                                                     (1968).
                                                                     Staoleton
                                                                     (1968).
                                                                     AMIC-S980

                                                                     Staoleton
                                                                     (1968),
                                                                     AMrC-5989
                                                                     Staoleton
                                                                     (1968),
                                                                     AMIC-5980

                                                                     Staoleton
                                                                     (196M,
                                                                     AMIC-5980
                                                                     Staoleton
                                                                     (1968),
                                                                     AMTC-S988

                                                                     Staoleton
                                                                     (1968),
                                                                     AMIC-5980
Staoleton
(1968),
AMIC-5980

Alabaster
(1969),
-------
            Compound
                                Organism
Field Field
Study Location
Toxlclty.
Active
Ingr«di«nt(
Ppm
Experimental
Variables.
Control led
or Noted Conments
Reference
         Caotan
          Captan
                     Fish loot
                     specified)
                     Brachydanlo
                     rerle
                     (larvae!
                                            *     J><>
                                                                greater  than
                                                                8.1-1.0  
-------
          Cartoaryl
                               (1.37 ql
Salao Clark I
11.30 9)
                                             BCF»  —
                                                                t.2 mi
          Cartarvt
          Carbaryl
                               Satno         8CF»
                               qalrdnerl
                               II.ZV 9}
Oncorhyncnus  SCFA
klsuter  <.*>0
                                                                1.1.7
                                                                1.3
U)
          Carbaryl
                               ictalurus
                               punctatus
                                             BS»
                                                                15.80 (U)
         Carbaryl
Tctalurus
•etas
                                             BS»   —
                                                                20.00 (Tl>)
e.f.I.o,
aulfato,
copper,
manganese,
Iron, and
chroralun

»*»c,*,
e,r,l,o,
aulTate,
coppor,
manganese,
Iron, and
chromium
                                                                                                  saa* as above
                                                                                                  saa* as abov*
                                                                                                  sa«e as above
                                                                                                                                      I1971J.AHIC-
                                                                                                                                      181Z
                                                                                                                                      Post,  et  al
                                                                                                                                      (1971),»H1C-
                                                                                                                                      1813
                                                                                                       Post, et al
                                                                                                       (197D,
                                                                                                       AMIC-1812
                                                                                                                                     Post, et al
                                                                                                                                     (1971),
                                                                                                                                     AM.IG-181Z
oulTato,
copper,
nanganaae,
Iron, and
chromium

a»,c,d,
•,f,l,o,
3ulfat«,
coppor,
manganese,
Iron, and
chromium

a(                 orqanochior |n« insecticides were  MaceKtet al
synthetic  the "lost toxic co*Dounds,                 <197C)«
test Hater orqanoohosofiates lnte>-n*d late, carbanates AMIC-S510
           the I *ast toxic.  Brown trout MSS the
           soeclrs most su^ceotlble TO
           orqanochlorlnesi coho salmon the most
           susceptible to carbamat rs( and goldfish
           were tb* least susceotlble ol all
           soecles.  Safe concentrations established
           bv bioassavs tilth sal nonld* or
           centrarcMds wouM  likely be safe for
           cyorlnlds and ictalurlds.  *>aT» levels
           for Ictalurlds or cyorinlds xould
           probably be hazardous for centrarchtds
           and salnonlds.  The use of qoldflsh In
           blo»ssavs Has discouraged.
                                                                                                  sa*e as above
                                                                                synthetic
                                                                                test Mater
                                                     MaceK, etal
                                                     (1970).
                                                     •MIC-5510
-------
Compound
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbon dioxide
Field Field
Organism Study Location
Carasslus BSA —
auratus
Cyprlnus BSA
carpi o
Plmrphales BSA
prove las
Lepomls BSA —
macrochlrus
Lepomls BSA
mlcroloohus
Hlcropterus BSA
sal noliles
Sat no BSA
galrdnerl
Salmo trutta BSA —
Oncorhynchus BSA —
Klsuten
Perca BSA —
f lavescens
Salmo BSA —
galrdnerl
(yearling)
Toxlclty,
Active
Ingredient,
Ppm
13.20 (TV)
5.?S (TV)
1V.60 (TV)
6.76 (TV)
11. ZO (TV)
6.VO (TV)
V.3V (TV)
1.95 (TV)
0.76 (TV)
0.75 (TV)
35 (SRI)
Experimental
Variables,
Control led
or Noted Comments
a,
synthetic
testnater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
synthetic
test water
a, c, bi-
carbon-
ate, and
total
aollds
saae as above
same as above
saae as above
same as above
same as above
sane as above
same as above
same as above
same as above
same as above
Bicarbonate In blood serum of
brook trout rose to 5 times greater than
that of contra Increase Mas slow, being
half complete at 6 hr. Sodium and
Inorganic phosphate Mare not affected,
but serua chloride Increased. The
Reference
Macek.et al
(1970),
AMIC-5510
Macek, et
al(1970).
AMIC-5510
Macek.et al
AMIC-5510
Macek.et at
(1970),
AMIC-5519
Macek.et al
119701 .
AMIC-5510
Macek.et al
AMIC-5510
Macek, etal
AM.IC-5510
Macek, et
at (1970),
AMIC-5510
Macek.et al
(1970) ,
AMIC-5510
Macek. etal
(1970),
AMIC-5510
Lloyd, et al
(1967),
AMIC-*7?1
-------
          Carbophenoth 1 on
                               Rasbora       BCF»
                               heteromorpha  and
                                             BS»
                                                                    ITZ»
          Carbyne
                               Rasbora      - BCFA
                               heteromoroha  and
                                             8S»
                                                                0.9 ITZI
vn
                a*,c,e,f,
                hard  (HH)
                or
                SOFT(SW)
                synthetic
                dilution
                water, or
                s*awater
                for soaa
                species
                a»,c,e,f,
                bard (HW)
                or soft
                (SW; syn-
                thetic
                water, or
                sea, water
                for sone
                species
            authors note that the data Indicate an
            environmental stress not related to
            problems of osmotic adaptation.

                    One hundred sixty-four            Alabaster
            pesticides, wettlnq aqents. and           (1969),
            Miscellaneous water pollutants showed a   AHIC—5
            Hide range of toxlcltv spanning 12 orders
            of maanltude.  KnoMlnq the toxlelty and
            percentaae of all components of a
            femulation did not result In easy
            predictability of the toxlclty of a
            mixture of Materials.  Soaetlnes
            pesticides «*re nost toxic in hard Hater
            and soaetlmes the opposite Mas true.
            Testing the actual  aaterlal as sold was
            found to be essential.
                                                                                                  sane as above
                                                      Alabaster
                                                      (1969).
                                                      •NIC-S12S
         Carbyne
                               Rasbor*       BCF*
                               heteronorpha   and
                                             BS*
                                                                l.k
         Carbyne
                              Asterlas      BSA
                              rubens
J.3-10 (K 1
HRI
         Carbyne
                              Cardluin edule BSA   —
                                                               100
a*,c,e,f,
hard (KM)
or  soft
13W) sjn-
thetlo
dilution
water, or
•eawater
for some
species

a«( contin-
uous aer-
ation,  sea-
water,  and
dally
solution
renewal)
               c»(contin-
               uous aor-
                                                                                                  saae  as above
                                                                     Alabaster
                                                                     (1969).
        One hundred-forty surface active
aqents. solvent enulslflers. pesticides.
polych1 orInated biphenyls. pure
inorqanic. and organic chemicals were
evaluated against as many as ten marine
organisms.  The authors noted that aost
published data of this type deal with
toxlclty of chemicals to freshwater
organisms.

       same as above
Portmann. at
al (1971),
AHIC-7781
                                                     Portmann, et
                                                     al (1971),
-------
Compound





Carbyne






Casol





Casol


Casol

Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organise Study Location Ppn or Noted Comments
ction, sea-
water, and
daily
solution
renewal)
Crangon BS* ~ 3.3-10 (T2) a*(cont*n- sa»e as above
crangon uous aer_
atlon, sea-
water, and
dally
solution
renewal)
Plmephales BSA — 12.0  (HSC) c,d,«, f same as above
cromelas

Biochemical L -- 610,000 c,d,e,f same as above
oxygen demand
Reference
AMIC-77B1




Portmann, et
al (197.1),
AHIC-7701




Zllllch
1 1 QftQl .
\ 1 7OT I ,
AHIC-Z909




711 llch
(19b9»,»1IC-
2999
711 llch
(1969),
Casoron G
                     Rasbora       BCFA
                     heteronorpha  and
                                   BSA
                                                      100 (TZ)
a»,c,o,f,
hard (KW;
or soft
ISW) syn-
the tic
dilution
water, or
seawater
for sorre
species
        One hundred sixty-four            Alabaster
pesticides, Mettlnq aoents, and           (1969),
nlscel laneous Hater oollutants showed a   AMIC-51.75
Hide ranae of toxlclty scanning 12 orders
of Magnitude.  Knowing the toxlclty and
percentage of all components of a
formulation did not result In easy
predictability 'of the toxlclty of a
mixture of materials.  Sometimes
pesticides Here most toxic In hard Hater
and sometimes the ooposlte was true.
Testing the actual •aterlal as sold was
found to be essential.
-------
Casoron 133
                      Rasbora
                      heteroaorpha
BCTA
and
BSA
                                                       13 tTZ)
Casoron
                      Horone
                      saxatltls
                      (fInqerlInqs)
                                    BSA   —
                                                       6,208 (Tit)
Casoron
                      Cardlua edule BSA   —
                                                       qreater than
                                                       100 (T2)
Casoron
                     Cranqon
                     crangon
                                    BS*   —
                                                       3.3-10 
a*,c,e,f,         same as above                       Alabaster
hard  (HtO                                             (1969),
or                                                    AHIC-5«?%
SOFTfSH)
synthetic
dilution
Mater, or
seaNater
for some
spec las

a,c,d,e,f.         All compounds were  Investigated    Ncltborn
D          because of their probable usaqe  In         (1971),
           hatchery production of Mhite bass.          AHIC-5571
           Compounds that can be used  at recommended
           concentrations Here Bquathol, Casaron,
           I. Ind^ne, and Terramycln concentrate.
           Those  that should not be used Mere
           Acrlflavlne, Rayluseldv, Halachlte qreen
           oxalate, and Malathion.

ao-(coritin-         One hundred-forty surface active   Portaann, et
uous aer-  aqents, solvent emulslflers, pesticides,   al  (1971),
ation, aea.-nolychlorlnated blphenyls,  pure            AHIC-7701
water, and Inorqanlc, and organic chenlcals were
daily      evaluated aqainst as many as ten narlne
solution   organisms.  The authors noted that Host
renewal)    published data of this type deal with
           toxlclty of chemicals to freshwater
           organisms.
                                   «•( contin-
                                   uous aer-
                                   ation, sea.
                                   water, and
                                                                                         sane as above
                                                     Portmann, «t
                                                     al C197U.
                                                     AHIC-7701
                                                                       solution
                                                                       renewal)
Cd CIZ . 2.9 HZO  (ax Crangon       BSA
Cd Z plus!           seotemsplnosa
                                                       0.3Z(T<>)
                                   a«,c,e,
                                   SSH
                                                      Although data cited
                                                                                                                      en at Elsler
                                                                                  70  C and 2.0  percent salinity,  varying
                                                                                  temperature and  salinity  Mere also
                                                                                  studied.  Hlqher temperature (20  C)  and
                                                                                  IOMer salinity  (5.0  oercenf)  resulted  In
                                                                                  greater susceptibility  of nuininlchoqs to
                                                                                  cadmiuir.  TL  sub 25, TL sub 50, and  TL
                                                                                  sub 7*> for 2
-------
CD
Com oun«
Cd CI2 . 2.5 H20
Cd 2 plus)
Cd CI2 . 2.5 H20
Cd 2 plus)
Cd CI2 . 2.5 H20
Cd 2 plus)
Cd CI2 . 2.5 H2t
Cd 2 plus)
Cd CI2 . 2.5 H20
Cd 2 plus)
Cd CI2 . 2.5 H2D
Cd 2 plus)
Cd CI2 . 2.5 H20
Cd 2 plus)
Cd CI2 . 2.5 H20
Cd 2 plus)
Cd CI2 . 2.5 H24
Cd 2 plus)
Cd CI2 . ?.5 H20
Cd 2 plus)
Field Field
Orqunlsa Study Location
(as Fundulus BSA —
h« tercel Itus
(as Paqurus BSA —
lonqlcarpus
(as Palaeaonetes BSA —
vu 1 gar 1 s
(as Asterlas BSA —
forbesl
(as My a arenarla BSA —
(as Carclnus BSA —
aaenus
(as Urosalolnx BSA —
elnerea
(as Fundulus BSA —
(as Hytllus BSA
edutis
(as Cyprlnodon BSA —
varlegatus
Toxlclty,
Active
Ingredient,
Pom
55. 0 (Tl.)
0.32 (Tl.)
0.1.2 (Tl.)
0.82 (T<>)
2.2 (Tl.)
fc.l (Tl.)
6.6 (Tl.)
21.0 (Tit)
25.0 (Tl>>
50.0 (Tl,)
Experiaental
Variables.
Control led
or Noted
a'.c.e,
SSM
a»,c,e,
SSH
a»,c,e,
SSH
SSM
a»,c,e,
SSM
a*,c,e,
SSM
a*,c,e,
SSM
a»,c,e,
SSM
a*,c,e,
SSM
a",e,e,
SSM
Comments
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
sane as above
Reference
Elsler
(1971),
AMIC-1621
Elsler
(1971),
A1IC-1621
ElsJer
(11711,
AMIC-1621
Elsler
AMIC-1621
Elsler
11971) ,
AMIC-16?!
Elsler
(1971).
AMIC-1621
Elsler
(1971),
AMIC-1621
Elsler
(1971),
AMIC-1621
(1971),
AMIC-1621
Elsler
(1971),
AMIC-1621
-------
Cd CI2  . 2.5  H2«  (•«  Nasser 1us
Cd 2 Plus)            obsoletus
                                    BS*   —
Cd CI2  .  2.*  HZO  (M  Nereis  vlrens BSA
Cd 2  Plus)
Chevron Ml-fl
                      Steel head
                      trout
                      tfIngerlInqs)
                                    BS*   —
                                  ID.5  (Tl>)
                                                       11.0(11.)
                                                       3.2 mi
                                                  a'.C.C,
                                                  SSH
                                                 a*,Cte,
                                                 SSM
Charron KI-O
Chloral hydrate
Coho aalnon   BSA.   Hood Canal
(flngerllAga) in  .  Hoodaport,
              •Itu  Wash.

Negaprlon.    BSA   —
brevlrostrls
11-3 Kg)
                                                      0.001 (K)
                                                       300  (SB  1  hr>
CM or iaIn*
                     Caaaaru«
                     p««udo-
                                   BCF
                                                       0.22  (T<»)
                                                 a»,c,d,e.
                                                 f,r»,a
CMeraaln*
CMoraaln*
Plaephalas    BCF
prone I as
                     Daphnla aaqna BCF
ChloraBphenlcol      Kercanarla    L     —
0.15 (T3)
0.09-0.15  (TV)
                                                      0.001  (K 3-9)
                                                      TI..S  »T2>
a«,o,d,e,
                                                 (O.o.d.e,
                                                 f.wt.a
                                                                    saa«  as  above
                                                                    sa»«  as above
                                                                     Elsler
                                                                      (1971),
                                                                     »MIC-162l
                                   Evaluation of 11 oil dlsoersants
                           resulted In a ranking for each and a
                           recommendation for use according to the
                           ranking.  Banking Has based on toxlclty
                           and oil dispersal effectiveness.  Corexit
                           776U appeared to have the least toxlclty
                           nlth fair to good oil dispersion
                           capablllty.

                                  sane aa above
                                                                                                      Tracy,  *t
                                                                                                      at(1969),
                                   Data from study of druq effects
                           on young lemon sharks were treated
                           mathematically to demonstrate
                           apollcablllty of classical rate theory to
                           the study of chemical shark deterrents.
                           Tncaoacltat Ion (narcosis) Has the orl»ary
                           parameter timed for effectiveness.  This
                           •as usually quite rapid for the more
                           effective druqs*

                                   Chloranlne toxlclty Mas very
                           carefully studied uslnq Height reduction
                           and reoroductlon over 15 to ?1 Heek
                           exoosure periods.  Loss of Height and
                           ability to reproduce were observed at
                           concentrations less than that observed
                           for toxlclty.  The loHest chloramlne
                           concentration having no significant
                           effect was less than 3.d pob for Gammarus
                           and 0.017 ppb for the fathead minnon.

                                  same as above
                                                     Tracy, et al
                                                     (1969),
                                                     AMIC-383U

                                                     Baldrldoed?
                                                     69).
                                                     •MIC-3$3>
                                                     Arthur, et
                                                     al (1971),
                                                     attIC-3?90
                                                                                        saae as above
                                                                                         The effect of 52 pesticides on
Arthur, et
al (1971).
AMIC-3299

Arthur, et

AMTC- 3290

Davis, et al
-------
  Compound
                       OrqanlSB
              Field  Flaltf
              Study Location
Toxlcity,
Active
Ingredient,
  Pen
Experimental
Variables,
Control led
or Noted
                                                                                                 Comments
                                                                                                                           Reference
                     •ercenarla
                     (egqs)
Ctilora'ohenlcol
C.ttloraaoh«n(col
Mercenarla
•ercenarla
(larva*!

Phornldlu*
anblguua
                                                      SO.O  (Tl?)
                                                      0.5-10.0  (NTE)  —
CM or ax
                      Sal BO
                      galrdncrl
              BCFA
              •nd
              BS»
                                                       1,800  (T?)
                 a«,c,e,f.
                 hard  (KW)
                 or soft
                 (3W)  syn-
                 thetic
                 dilution
                 water, or
                 •eawator
                 for some
                 spaeies
                                                            etrbryonle development of clams and
                                                            oysters «as reported.  Synerolstlc        (1969), AHIC-
                                                            effects Mlth solvents Here also reoorted* 5990
                                                             Most of the -compounds affected
                                                            development more than survival*  Sone,
                                                            however, drastically reduced larval
                                                            growth.  The authors oolnt out the
                                                            necessity of evaluating the effects of
                                                            pesticides on all life staqes of an
                                                            organism and note the oossiblllty of
                                                            selecting chemicals  for oest control that
                                                            Mould not have serious effect on
                                                            shellf ish.
                                                                                        same  as above
                   Of 7<» chemicals evaluated as
           alqlcidest only <5 Here more  toxic than
           CuSO"t.  None  Inhibited growth  of
           mat-tormina alqa? for more than ? weeks.
           CuSni*  formulated nith certain  wettlnq
           aqents  was more toxic than CuSO,
                                                                        AMIC-892
Alabaster
(19691,
-------
Ch Ionian*
CM or dan*
                     Nhlt* sucker  FRL    Misc.  stares  0.13-0.1.1,
                                                       residue  (SB)
                     Mhlt* perch   FRL    HIsc.  states
                                                       1.7?  residue
                                                       (SB)
                                                            Testlnq the  actual  material  as sold  was
                                                            found  to be  essential.

                                                                     The  Bureau  of Sport  Fisheries
                                                            continued Its  fish  monitoring  orogram by
                                                            collectlnq li»7  composite  fish  samples
                                                            from 50 nationwide  monitoring  stations
                                                            during the fall of  1969.   Fish were
                                                            analyzed for residues of  11
                                                            organochlorlne  Insectlcidest  llplds,  and
                                                            PCB-s.

                                                                    same  as  above
Henderson,et
al  (1971),
• NIC-i*or
                                                                                                       Henderson.
                                                                                                       et  al (19M),
                                                                                                       AMIC-1U07
CMordan*
                     Largemouth
                     bass
                                   FRL    Misc.  states
                                 0.95 residua
                                 (SB)
                                                                                         same as above
Henderson,
etal  (1971),
»MIC-l
-------
Compound
Organism
Field Field
Study Location
Toxlclty,
Active
Ingredient,
Ppa
Experiment*)
Variables,
Control led
or Noted
Comments Reference
Chtordan*
                     Lepomls
                     evanellus
                     (Resistant)
                                   BS»   —
                                 3.2B IT2»
                                                                                  1*07

                                                Green sunflsh  from Betzonl, Miss.  HIncheM,  et
                                        were resistant to CMordane,  Meptaehtor,   al(1970),
                                        Llndane, and  Strobane.  but not  to          «NIC-5*71
                                        Parathlon.  Golden shiners fro" the sane
                                        location were resistant to Llndane and
                                        Strobane,  tolerant to  CMordane and
                                        Heptachtor, and susceptible to  ParatMon.
                                         Lack  of resistance to  Parathlon
                                        Indicated lack ot  agricultural  usage  of
                                        orqanochosphates In that  area.   Resistant
                                        fish oere compared to  susceptible ones
                                        collected at  StarKvIlle.
Chiordan*
                     Lepomls
                     eyanellus
                     (Susceptible)
                                   as*    —
                                 B.09  (T2)
                                                                   sane as above
                                                                                                      MlncheM, et
                                                                                                      al(1970>t
                                                                                                      4NIC-5UT1
CMordane
Chiordan*
Chiordene
Notemlaonus
crysoleucas
(Resistant)

Notemlgonus
crysoleuces
(Susceptible)

Palaemonetes
Kadlfthensls
(resistant!
                                   BS*    —
                                   BSA    ~
                                   BS»
                                                       2.33  (TZ)
                                                            (T2I
                                                      0.0779-0.33*
CMordane
Copapeda
I Cyclop a
blcuspldus
Cyclops
varicans,
Buerelopa
                                   FL
                                   and
                                   BSA
State
Colleqe.niss
                                                       0.30  (KZ)
                                                                                         sane as above
                                                                                         sane as above
                                                                                                                                    et
                                                                                                                           al
                                                                                                                           • HIC-51,71
                                           HlncheM,
                                           eta)  (1970),
                                         '  AHIC-SI.T1

        Bloassays Mere conducted Mlth     Naavl, et  al
       from three areas of Intensive      (1970),
pesticide use and fro" an unexoosed area. AMIC-SS19
 Previously exposed shrimp Mere from 1 to
?5 times more resistant than unexposed
shrimp.  Both types of shrimp Mere also
exposed In caqes to Maters of the
contaminated areas.  Susceptible shrimp
suffered 6f> percent more mortality Than
did resistant shrimp.  The toxlclty ot
the Insecticides ranked In descending
order Mas as follOMs!  most toxic,
Endrln, DOT, Methyl oaratnlon, Parithloni
medium toxlclty, Guthlon, Llndane,
Toxaohene, Strobanet lease toxic
CMordane, Sevln, and Heptachlor.

         The response of                    Nagvl, et  at
 pe^t lcl
-------
Cnlordane
 Cnlordane
 CMer««
Chlorfenvlnphos
Cnforfenvlnphos
                     •gills.
                     Macro cyclops.
                     albldus,
                     Orthocyclops
                     oodeatus)
Cooepods
ICvcloos
blcusoldus*
Cyiloes
varlcans.
Cyclone
vernal is,
Eucyelops
•Sills,
Hacrocycloos
atbldus,
Orthoeycloos
•onestus)

TubI fax
tubIfex
                                   FL
                                   and
                                   BSA
                     Betzonl,
                     Hiss
                                                       B.30  I96p*reent
                                   Ft
                                   and
                    8*lzenli
                    Hiss.
Salao         BCFA   —
galrdnerl     and
              BSA
                                                      1.50  25
                                                                                 wide range of  toxlcity  soannlng 1? orders
                                                                                 of  magnitude*   Knowing  the  toxlcity and
                                                                                 percentage of  all  eonoonents of a
                                                                                 formulation  did not  result  In easy
                                                                                 predictability of  the toxlcity of  a
                                                                                 •Ixture  of materials.   Sometimes
                                                                                 pesticides were most toxic  In hard Hater
                                                                                 and sometimes  the  opooslte  Has true.
                                                                                 Testing  the  actual material  as sold MBS
                                                                                 found  to be  essential.
                                                                                       save  as  above
                                                                                                      Alabaster
                                                                                                      (1969),
                                                                                       same  as above
                                                                                                     Alabaster
                                                                                                     <19691,AHIC-
-------
Chlorine
. Toxlclty,
Active
Field Field Ingredient,
ind Organise) Study Location Pom
t Plmephales BSA Grand River, 0.07-0.15 (Tl>)
cromelas (ML) Wyoming,
Experimental
Vviahtes,
Control led
or Noted Comments
synthetic
dilution
Mater, or
seawater
tor SOB*
species
-- The Indicated toxic levels of
chloride occurred In S.8
-------
        ChlortMaald
                             Rasbora
                             heteromorpha
              BCF»
              and
              8SA
                                                              30 ITZI
        Chroaates  (as
        chroalua)
Aqonus
cataohractus
                                           •BSA   —
                                                              33-100 
-------
   Comoound
                        Organism
                                    Field  Field
                                    Study Location
             Toxlclty,
             Active
             Ingredient,
Experimental
Variables.
Control led
or Noted
                                                                                                 Comments
                                                                                                                           deference
 Chromic  chloride (as  Aeronmurla
 Cr»
 Chromic  chloride  las  Ephemerella
 Crl
 Chromic chloride  las Hydroosyche
 Crl
Chromium  trloxlde    Phormldlum
(»« Crl              ambiguum
                                    BS»    ~
                                   L      —
                                                       SZ (T7)
                                                       2 IT»>
                                                          m>
                             a*,c,d,e,f        same as above
                                                       0.5-10.0  (NTE)  —
Chromium
                     llosa
                     paoudo-
                                   FL
Creat Lakes
- Superior,
Michigan,
and Erie
                                                      1.1 (residue)
•*,c,d,e,f         Eohemerella (mayfly) Mas the most NarnicK,  «t
           sensitive aauatlc Insect of those
           studied, and cooper the most broadly
           toxic metal.  The authors suggest that
           aquatic Insects may not be as sensitive
           to heavy metals as fish.

a>.c,d,e,f        same as above                      Varnlck,  et
                                                     •1(1964),
                                                     »HIC-3767

                                                     Warnlck,  et
                                                     •1(1969),
                                                     •NIC-3767

                   Of 7  ppb,  rubidium  -  0.06 to  6 pom,
           scandlun -  2  ppb, selenium  -  0.1 to 2
           OOb,  silver -.0.001 pob.
-------
Chroalue.
Chromium
Chroalu*
Notropls      Fl    Great Lakes  5.5
hudsonlus           - Superior,
                    Michigan,
                    and Erie

PereoDsls     FL    Great Lakes  ?.Mresldue)
omlscomaycus        - Superior,
                    Mlchioan,
                    and Erie

Coregonus     FL    Moos* Lake,  0.03 (res)<1ue)
ctupeatornls        Can.
 Chromium
 Chromium:
  Chromium
  Chromium
  Chromium
  Chromium
  Chroalum
                      Coregonus     FL
                      elupeaforals
                      Esox locius   FL
                       Esox  luclus   FL
                       Esox luclus   FL
                       Osmerus       FL
                       •ordax
                       Perca         FL
                       flaveseens
                       Paralabrax    FH
                       clathratus
                     Lake         0.03 (residue)
                     Ontarl».
                     Can.

                     tjoose Lake,  0.04 (residue)
                     Can.
                                           Lake St.     0.03  (residue1)
                                           Pierr*, Can.
                                           LaKe Erie,   0.03 (residue)
                                           Can.
                      Lake Erie,   0.03 (residue)
                      Can.
                       Lake Erie,   0.07  (residue)
                       Can.
                       Scattergood  1.3  (dorsal
                       Steam Plant, Muscle
                       Los Angeles, residue)
                       Cat.
                                                                                         saae as above
                                                                                        sane as above
                                                                                         Concentrations of 13 toxic
                                                                                 elements In dressed fish from heavily
                                                                                 Industrialized and non-IndustrialIzed
                                                                                 areas Mere determined.  Only aercury
                                                                                 exceeded regulatory Units, and
                                                                                 concentrations of aost elements  Mere
                                                                                 essentially the saae  In  fish fro* both
                                                                                 areas.

                                                                                         saae  as  above
                                                                                         saae as above
                                                                                          saae as above
                                                                                          saae as above
                                                                                          saae as above
                                                                                          sane as above
                                        Lucas, et al
                                        (1970),
                                        •HIC-J77B
                                        Lucas, et al
                                        (1970J,
                                        AHIC-J778
                                        Uthe, et
                                        •LdPTl),
                                        1HIC-J819
                                         Uthe,  etal
                                         (1971),
                                         »MIC-3»19

                                         Uthei  et al
                                         (1S71),A1IC-
                                         3819

                                         Uthe, et
                                         »L(197t),
                                         A1IC-3»19

                                         Uthe,  et al
                                         (t
-------
Coaoound
Chromium
Chro«lua
Cnro«lua
Cnroalue
ChroBlua)
Chroalue
Chroaiua
Chroaiua
OrqanlsB
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
cl athratus
Paralabrax
cl athratus
Parat abrax
clathratus
Paralabrax
clathratus
Flald
Study
FN
FH
FM
FN
FH
FM
FN
FH
Toxlclty, Experimental
Active Variables,
Field Ingredient, Controlled
Location Ppa or Noted Consents
Scattergood  (ventral — saae as above
St«ai» Plant, muscle
Los Angeles, residue)
Cal.
Catallna 1.% (ventral ~ - saae as above
Island, Cal. muscle
residue)
Scatterqood 2 (gonads -- saae as above
Steaa Plant, residue)
Los Angeles,
Reference
Stapleton
(1S68J,
AMIC-S98B
Staoleton
(1968) ,
ANIC-5950
Staoleton
(1961),
ANIC-S9SO
Staoleton
(196M,
AHIC-S980
Staoteton
(1968),
AMIC-S980
S tao 1 eton
(1968),
AMIC-5989
Staoleton
(1«68),
ANIC-S980
Staoleton
(1968),
AMIC-S988
cat.
-------
          Chroalua
          Ctiroaluo
          Cnroalua
                               Paralabrax    FH    Catallna      ?.3  (gonads
                               clathratus          Island, Cal.  residue)
Paralabrax    FH    Catallna      7.6
Clathratus          Island, Cal.  (qonads
(gravid                           residual
females)

Paralabrax    FH    Scattergood  1  (liver
clathratus          Steam  Plant,  residue)
                    Los  Angeles,
                    Cal.
>
          ChroBlua
          Cnroaiu*
           Citric ccld
                               Paralabrax     FH
                               clathratus
                                Paralabrax    FH
                                clathratus
                                Paralabrax    FH
                                clathratus
                     Catallra     1.5 (liver
                     Island,  Cal. residue)
Scattergood  1.9 (Integuaent —
Stean Plant, residue)
Los Angeles,
Cal.

Catallna     1.* (Integuaent —
Island, Cal. residue)
 Carclnus
 •aenas
                                              BS»   —
                                                                 160 CTZ)
           CI
                                Fundulus      BS»
                                heteroclitus
                                  o.ooom-o.ooi?
                                  (TO
           ct
                                Nereis vlrens BSA   —
                                  0.0003-0.0007
                                  
                                                                                                  saae  as above
                                                                                                  saae as above
                                                                                                   saae as above
                                                                                                   sane  as above
                                                                                                   sane as above
                                                                                                   saae as above
                                                                                Stapleton

                                                                                ANIC-5981)

                                                                                Staoleton
                                                                                (196M,
                                                                                AMIC-59SH


                                                                                Staoleton

                                                                                AMIC-5980
                                                                                 Staoleton
                                                                                 (1968),
                                                                                                      Staoleton
                                                                                                      (1966),
                                                                                                      Staoleton
                                                                                                      (196S),
                                                                                                      AMIC-S9M
                             a«lcontin-
                             uous eor
                    One  hundred-forty surface active Portaann, et
            aqents,  solvent enulsitl«rs, oestlcldes, al
ation, sea- oolychlorlnated blohenyls, oure
water, and  inorqanlc,  and organic cheivicats nere
daily       evaluated  against  as many as ten marine
solution    organisms.   The authors noted that most
renewal)    published  data of  this tyoe deal »ith
            toxlclty of  chemicals to  freshwater
            organises.
a*»c»e»            A laboratory procedure based on
and        Standard Methods for 96-hr toxlclty
synthetic  determinations of crude oil and
seanater   oll-dispersant mixtures Has described.
           The  dlspersants varied considerably in
           toxlclty, ranging from 0.01 to 7.1 ml/1,
           TLSO for 96  hr.  These did not differ
           significantly from  ZVO hr  values.  The
           dlsoersants  H«re designated as CX, no,
           CI,  00,  AO,  PC, MM, TN, BP, and  NA nlth
           no further  description of  their  chemical
           nature  or source.   Only a  fex bloassays
           Mere conducted Hith shrlmo.  HollusKs and
           echlnoderms  Here suggested as suitable
           test animals. The  authors stated  that
           the  method  could be used  to  test any
           product  for  toxlclty  In seawater.
                                                                                                                                      (1971),AHIC-
                                                                                                                                      7701
                                                                                  LaRoche, et
                                                                                  al (1970),
                                                                                  AMIC-'.'.S
                                                                                 a*,e,e,
                                                                                 and
                                                                                 synthetic
                                                                                 seawater
                                                                                                   saae as above
                                                                                  LaRoche,et
                                                                                  al (1970),
                                                                                  ANIC-I.1.5
-------
Cleanoxol
Cleanosol
Clopnen A30
Toxlclty, Experimental
Activ* Variables,
Field Field InqredlenT, Controlled
Organism Study Location Pp« or Noted Comments
Cardlua edule BSA — 10-33 (T2) ao(eontln- One hundred-forty surface active
uoua aer- agents, solvent emulsi f lers, pesticides.
ation, sea-oolychlorlnated blphenyls, pure
water, and Inorganic, and organic chenlcats Mere
daily evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal)" published data of this type deal with
toxlclty of chemicals to freshwater
organisms*
Crangon BSA — 33-100 (TZ> a»(eontin- same as above
crengon uous aer-
ation, sea-
water, and
dally
solution
renewal )
Panda (us BSA — 33  a«(contin- same as above
montagul uous aer-
ation, sea-
water, and
daily
solution
renewal }
Agonus BSA — greater than 10 a«(contin- One hundred-forty surface active
eataohractus (T2t uous acr- agents, solvent enulslfiers, pesticides.
ation, sea- polychlorlnated blphenyls, pure
Reference
Portmann, et
al (19711,
AMIC-7701






Portmann, et
al (1971).
ANIC-7701




Portmann, et
al (1971),
AMIC-7701




Portmann, et
al (1971),
AHIC-7701
                                                                      water, and Inorganic, and organic chevlcals Here
                                                                      daily      evaluated against as many as ten marine
                                                                      solution   organisms*  The authors noted that most
                                                                      renewal)   published data of this type deal with
                                                                                 toxlclty of chemicals to freshwater
                                                                                 organisms.
Cleohen A30
                     Cardlum edule BSA   —
                                                                      a«I contin-
                                                                      uous aer-
                                                                      ation, sea-
                                                                      water, end
                                                                      daily
                                                                      solution
                                                                      renewal)
                                                                                        same as above
                                                    Portmann,  et
                                                    al  (1971),
                                                    AMIC-7701
Clophen A30
                     Crane, on
                     crangon
                                   BSA   —
                                                      0.83-1.0  (T2>
a«(contin-
uous aer-
ation, sea-
water, and
                                                                                        same as above
Portmann, et
al (1971),
ANIC-7701
-------
                                                                       "dally
                                                                        solution
                                                                        renewal)
Clophen A60
Agonus
cataohractus
                                    BSA    —
                   greater  than ID  ae(contin-
                   (TZ)             uous aer-
                                    ation, sea-
                                    water, and
                                    dally
                                    solution
                                    renewal)
                                                                                          sine  as aboye
                                                     Port»ann,et
                                                     al (1471).
                                                     ANIC-7701
Clophen A60
                      Cardlu* «dul« BSA    —
                                  greater than 10 a«(contln-
                                  ITZ)            uous aer-
                                                  ation, sea.
                                                  water, and
                                                  dally
                                                  solution
                                                  rene-jal)
                                                                                          sane  as  abov«
                                                                                       Portwann,  «t
                                                                                       at(1971),
                                                                                       •HIC-7701
Clephen »60
Crangon
eranqon
                                    BS»    —
                   greater than 10 a«(contin-
                   CT2)            uous aer-
                                   ation, sea-
                                   water, and
                                   daily
                                   solution
                                   renewal)
                                                                                          saae  as  above
                                                     Portaann, et
                                                     al (197U,
                                                     *HIC-7701
Clophcn A M
Crangon
cr»ngon
                                    8SA
                                                        1.8-3.3  (TZ)
                                   &«•( contin-
                                   uous aor-
                                   atlon, sea-
                                   water, and
                                   dally
                                   solution
                                   renewal)
                                                                                          saae  as above
                                                     Portiann, «t
                                                     at (1971),
                                                     4MIC-7701
Clophen A 50
Crangon
erangon
                                     BSA    —
                                                        3.3-10  (TZI
                                   a«(contin-
                                   uous aer-
                                   ation, sea-
                                   water, and
                                   dally
                                   solution
                                   renewal)
                                                                                          saae  as  above
                                                     Portnann, et
                                                     al (1971),
                                                     AHIC-7701
CN«  Co, Nit Cr* and  Plueo
2n                   premelas
BSACF Grand River
IHL)  at
                                  betMeen
                                  1.25-3.75
a,c,e, eon-        A mobile bloassav unit was
ductiylty, utilized to conduct this study of
           municipal Nastexater containing the
           Indicated toxicants.  River Mater was
           used as diluent.  The conclusion H»S
           reached that svneralstlc or additive
           toxic effects occurred since toxlclty was
           greater than that of any of the Ions
           singly.
Zllllch
(1969).
-------
Compound Organism

CM, Cut Nl • O, and Catostoous
In commersonl
Toxiclry,
Active
Field Field Ingredient,
Study Location Ppn
Wyoming, Mich percent (T3)
loan
BSACF Grand River between
(HL) at 1.25-3.75
Wyoming, Mich percent (T3)
loan
Experimental
Variables,
Control led
or Noted Comments
Btt.Cu.Cr,
OH, and Zn
&>C,e, con- sane as above
duotlvlty,
Jtt,Cu,Cr,
ON, and Zn
Reference
AMIC-2906
71 Mich
(1969),
ANIC-2906
 Cobaltous sulfate
 fas Co)
 CobaItous sulI ate
 (as Co)
Cobaftous  sulfate
(as Co)
Cobalt
Acroneurla    BSA   —           32 )         a*,c,d,e,f
                                 32 (T7)          a*,e,d,e.r
                                                                                 sensitive  aquatic  insect  of  those
                                                                                 studied, and coooer  the most broadly
                                                                                 toxic  metal.  The  authors sugqest  that
                                                                                 aquatic  Insects nay  not be as sensitive
                                                                                 to heavy metals as fish.

                                                                                        same as above
                    Great lakes  0.029(r*sldue)
                    - Superior,
                    Michigan,
                    and Erie
                    Great Lakes
                    - Superior,
                    Michigan,
                    and Erie

                    Great Lakes
                    - Superior,
                    Michigan,
                                                      0.020(residue)  —
                                                      0.023(resldue)  —
                                                                   same as above
        Trace element content of fish
from Lakes Superior, Michigan, and Erie
Has determined by activation analysis. .
Whole body and liver residues Here
determined.  Concentrations varied with
species and lake.  Other elements found
nerei  antlnony - 5 to 100 ppb, bariu* -
0.2 opn, cesium - 3 ppb, lanthanum - 1 to
?0 DOb, mercury - 10 ppb, rhenium - 0.5
to 5 ppb, rubidium — 0.06 to 6 ppm,
scandium - 2 ppb, selenium - o.l to 2
ppb, silver - 0.001 ppb.

       same as above
                                                                                                      al(1969).
                                                                                                      AMIC-3767
Harnick, et
al(1969),
AMIC-3767

Warnick, et
al(1969),
AMIC-3767

Lucas, et al
(1970),
 AMIC-3778
                                          Lucas, et
                                          (1970),
                                          AMIC-3778
                                                                                                                al
                                                                                        same as above
                                          Lucas, et al
                                          (1970),
                                          AMIC-3778
-------
                                           and Erie
Cobalt
Cobalt
Cobalt
 Cobalt
 Cobalt
 Cobalt
 Cobalt
  Cobalt
  Cobalt
  Cobalt
Coreqonus      FL
hoyl
ProsODlu"      FL
eylIndraccua
S»lv»lInu*
naaaycush
 Os uterus
 •ordax
 Notropls
 hudsonlus
 ftoccus
 cnrysops
                                     FL
                                     FL
                                     FL
 Pereopsls     FL
 oalscooaycus
                                     FL
 Perea         FL
 flavescens
 Stlzostedlon   FL
 vlTreum
 vltreu*
  Paralabrax    FH
  elathratus
Great Lakes  0.036(residue)
- Superior,
Hichlqan,
and Erie

Great Lakes  0.0<»7(resldue>
- Superior,
Mlcnlq*n,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie

Great Lakes
- Superior,
Hlchlqan,
and Erie

Great Lakes
- Superior,
Michigan,
and Erie

Great Lakes
- Superior,
Michigan,
and Erie

Great Lakes
- Superior,
Michigan,
and Erie

Great Lakes
- Superior,
Michigan,and
Erie
 Great Lakes  0.0<.5  —
                                                        0.013(rasldue)  —
                                                        0.033(resldue>  —
                                                        O.OZ3(resldue)
                                                        0.0<>3(rasldue>  —
                                                        O.lZO(rasldue)  —
                                                                                          saae as above
                                                                                          saae as above
                                                                                          saae as above
                                                                                          saae as above
                                                                                          same as above
                                                                                          sane as above
                                                                                          sane as above
                                                                                          saae  as above
                                                                                           saae  as above
                                                                                 Lucas,  et  al
                                                                                  CITO) t
                                                                                 •MIC-^778
                                                                                  Lucas,  et  al
                                                                                  (19701,
                                                                                  AMIC-3778
                                                                                  Lucas, et at
                                                                                  (1970),
                                                                                  »«1IC-377*
                                                                                  Luc«s, et al

                                                                                  AMIC-377*


                                                                                  Lucas, et al

                                                                                  »«IC-377n
                                                                                  Lucas,  «t  al
                                                                                   (1970) ,
                                                                                   •MTC-3778
                                                                                   Lucas,  et  al
                                                                                   (lc'70),
                                                                                   4HIC-3778
                                                                                   Lucas, et al
                                                                                   (1170),
                                                                                   AMIC-3779
                                                                                   Lucas, et al
                                                                                   (1170),
                                                                                   AMIC-3778
                                                 Fish collected fron an effluent   Staoleton
                                         pipe of a steam plant and froa offshore   (1968),
                                         waters of Catallna Island Mere analyzed   AHIC-5980
                                         for trace aleaent content.  Trace element
-------
           Compound
Field Field
Organise Study Location
Toxlclty,
Active
Ingredient,
Ppa
Experimental
Variables,
Control led
or Noted Comments Reference
>
         Cobalt
         Cobalt
         Cobalt
        Cobalt
        CobaIt
        Cobalt
        Cobalt
 Paralabrax    FH    Catallna      2.3  (dorsal
 clathratus          Island, Cal.  muscle
                                  residual

 Paralabrax    FH    Scatter'qood   1.2ventral
 elathratus          Steam  Plant,  muscle
                     LosAngeles,   residue)
                     Cal.

 Paralabrax    FH    ratalIna      *.3  (ventral
 clathratus          Tslandt Cal.  auscle
                                  residue)

 Paralabrax    FN    Scattergood   3.6  (gonads
 clathratus          Steam  Plant,  residue)
                     LosAnqeles,
                     Cat.

 Paralabrax    FN    Catallna      li.lt  (qonads
 clathratus          Island. Cal.  residue)
Paralahrax    FN    Catallna      3.7(qonads
clathratus          Island, Cal.  residue)
(qravld
feaales)

Paralabrax    FH    Seattergood   l.t  (liver
clathratus          Stean Plant,  residue)
                    LosAnqelKS,
                    Cal.
                                                                                          content of the effluent  water Mas at
                                                                                          least 5 times greater than that  of  noraal
                                                                                          sea water for cadmium, coooer, nickel,
                                                                                          zinc, and chromium.   Livers of t ish from,
                                                                                          the affluent Here nearly titlce the  size
                                                                                          of those from The ocean.  Greatest
                                                                                          differences in concentration occurred
                                                                                          with aluminum, cadmium,  and nickel.
                                                                                          Silver, barlufft lithium, and lead shoned
                                                                                          the least differences.  The author
                                                                                          conduced that trace element analysis of
                                                                                          tissues could be used to determine  the
                                                                                          effect of pollutants on marine organisms.

                                                                                                 same as abov*
                                                                                                 sane as above
                                                                                                 same  as above
                                                                                                 sane  as  above
                                                                                                 saae  as above
                                                                                                same  as above
                                                                                                 saae as above
Stapleton
U96M ,
AMIC-5980

Staoleton
(19681,
AMIC-5980
Staoleton
(106*1,
AMIC-S980

Staoleton
(1968),
AMIC-S980
Staoleton
(19S8),
•1IC-S9SO

Staoleton
(1968),
AMIC-59H8
                                                                                                                                    Staoleton
                                                                                                                                    (19681,
                                                                                                                                    ANIC-S980
-------
       Cob*It
        Cobalt
        Cobalt
        Cobalt
Paralabrax    FM
clathratus
                             Paralabrax     FH
                             clathratus
                             Paralabrax
                             clathratus
                              Paralabrax    FM
                              clathratus
                                                  Catalina     1.9 (liver
                                                  Island,  Cal.  residue)
                     Scattergood   1.8  (integument
                     Steam  Plant,  residue)
                     LosAngeles,
                     Cal.

                     Catallna      1.it  (Integument
                     Island* Cal.  residue)
                     Scattergaod   1.7  (heart
                     Steam  Plant,  residue)
                     LosAngeles,
                     Cal.
                                                                                                 same as above
                                                                                                 sane  as above
                                                                                                 saae  as  above
                                                                                                 same as above
                                                                                                     Staoleton
                                                                                                     (1968).
                                                                                                     AMIC-59RO

                                                                                                     Stapllt Mill
                                                                                                     eton  (10.681,
                                                                                                     AMIC-5980
                                                                                                     Staol eton
                                                                                                      (1168),
                                                                                                     AMIC-5980

                                                                                                     Staoleton
                                                                                                      (1968),
                                                                                                      AMIC-S980
CD
        Cobalt
        Cobalt
        Cobalt
                              Paralahrax .   FH    Catalina     1.2 (heart
                              clathratus          Island, Cal. residue)
Paralabrax    FH    Scattergood  5.2 (eyeball
clathratus          Steam Plant, residue)
                    LosAngeles,
                    Cal.
                              Paral abrax
                              clathratus
        Cocoaalne dlacetate  Phormld-lum
                              amblguum
                                            FH
         Coco
         •onoethanoIam1 d«
         (plus ethylene
         oxide, ethoxy
                     Catallna     5.1  (eyeball
                     Island,  Cal.  residue)
                                            L     —
                                                               D.5-10.0 (NTF»   —
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                              Cardlum edule BS»   —
                                  greater than
                                  100 (T2)
                                                                     Of  7<» chemicals  evaluated  as
                                                             alqlcldes,  only 9 Here more toxic  than
                                                             CuSOU.   None Inhibited growth of
                                                             mat-forming algae for  more than ?  weeks.
                                                             CuSO>> formulated with  certain wetting
                                                             agents  Has  more toxic  than CuSOt» alone.
                                                             Coooer  ehloraiMne was  also found to be
                                                             more toxic  than CuSO<>.  No netting agents
                                                             were found  to be Inhibitory at the
                                                             concentrations investigated (0.05  and
                                                             0.005 DPI").  Also resorted are factors
                                                             affecting growth of algae in canals to
                                                             determine whether there  were leads to
                                                             controlling algae by environmental
                                                             management.  No practical environmental
                                                             means were  found.
                                                 ao(contln-         One hundred-forty surface active
                                                 uoua aer-  aqents, solvent emulslflers, pesticides,
                                                 atlon,  sea- polychlorlnated bienenyls, pure
                                                 water,  and Inorganic, and organic chemicals were
                                                                                                      Staol eton
                                                                                                      (1968),
                                                                                                      AMIC-5980

                                                                                                      Staoleton
                                                                                                      (1968),
                                                                                                      AMIC-5980
                                                                                                      Staoleton
                                                                                                      (1968),
                                                                                                      AHIC-SS80

                                                                                                      Otto(1970l,
                                                                                                      AMIC-892
Portmann, at
al (1971),
AMIC-7701
-------
  Compound


•onocthanolamlde)
Coco
•onoethanolamlde
(olus ethylene
oxide, ethoxy
•one* thanoIami de)
              Field  Field
  Organism    Study Location
Toxlclty.
Active
Ingredient,
  ppm
                                                                       Experlmental
                                                                       Variables.
                                                                       Controlled
                                                                       or Noted
                                                                                                  Comments
                                                                                                                           Reference
Cr angon
cr angon
                                   BS»   —
greater than
100 -( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                         same  as  above
Portmann, et
at C1971),
*»*IC-7701
Coco
•onoe thanoIam 1 de
•plus ethylene
oxide* ethoxy
monoethanoIamide)
Carelnus
maenas
                                   BS»    —
greater than
100  
a«(contin-
uous aer-
ation, sea-
vrater, and
daily
solution
renewal)
                                                                                         same as above
Portmann. et
al (1971),
•HIC-7701
Coco
monoethanoI am1de
Coca
•one* thane Iam1de
Compass
                     Cardlurn edule BS*    —
Crangon       BS»
erangon
                     Card1urn edule 6S»   —
greater than    a^lcontin-         same  as above                      Portmann,  et
100  IT2)        uoua aer-                                            al  ei<»71),
                atlon, sea-                                          »MIC-7701
                va t«r, nnd
                daily
                solution
                renewal)

greater than    ac-tcontin-         same  as above                      Portmann.  et
100  CT2J        uoug aor-                                            al  (1971),
                ation, sea-                                          »«IC-7701
                water, and
                daily
                solution
                renewal)

greater than    a<-(conti:i-         On*  hundred-forty  surface  active  Porfmann,  et
100  ITZI        uous aor-  agents, solvent emulslflers,  pesticldest  al  (1971),
                ation, 3ea-00'vch1orln»f*d blohcnyls, pure           »MIC-7701
                water, and Inorganic, and organic chemicals Here
                daily      evaluated against as many  as  ten marine
                solution   organisms.   The authors noted that most
-------
Compass
                     Crangon
                     erangon
                                   BSA   —
                                 greater than
                                 100 (T2J
                                                renewal)    pub! Ished data of  this type deal  tilth
                                                            toxleltv of chemicals to treshtiater
                                                            organises*

                                                 acleontln-        sane as above
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 daily
                                                 solution
                                                 renewal)
                                                     Portmann, et
                                                     al (1971),
                                                     AMT.C-7701
Compass
                     Carclnus
                     •aenas
                                   BSA   —
                                 qreater than
                                 100 (TZ)
                                                 a*(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 vater, and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                        sane as above
                                                     Portmann, et
                                                     al (197.1).
                                                     ANIC-7701
Cooper's My dlo
(new typel
Rasbora   •    BCF»
heteromorpha  and
              BSA
                                                      3.55 (TZ)
Copper chloride (»s
Cut
Leoomls
macrochlrus
              BSA,
              L
                                                      1.Z5 (Ti.1
Copper chloride (as
Cu)
Nltzschla
linear Is
              BSA,
              I
                                 0.81 ITS)
                                                 a*.c,<>, t*
                                                 hard(HH)
                                                 or soft
                                                 (SH)
                                                 synthetic
                                                 dilution
                                                 Hater, or
                                                 seaxater
                                                 for so*e
                                                 species
a»,e, and
synthetic
dilution
water
a.*,a, and
synthetic
dilution
water
        One hundred sixty-lour            Alabaster,
          , netting aqents, and           (iqS9),AHIC-
«i Isce I laneous water DO! lutants showed a   5"»?5
Hldf^ ranqe of toxlclty scanning 12 orders
of magnitude.  Knowing the toxlclty and
percentage of al I co .chemicals evaluated as
                                                                                                                           Otto  (1970),
-------
Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient,
f>p«
Experimental
Variables.
Control led
or Noted Comments
Reference
                     amblguua
                                 percent groMth
                                 lnhlbltedl<>>
Copper salts
Copper salt of
endothall
                     Fish (not
                     specified!
Pnormldlua
aablguua
                                   t
                                 greater than
                                 0.1-1.0 IK)
                                                      0.5-10.0 I.MTE1  —
           alqlcldes,  only 9  Here more  toxic than      AMIC-892
           CuSOit.   None  Inhibited growth of
           •at-tor«Inq algae  Tor more than Z Meeks.
           CuSO<»  formulated with certain wetting
           agents  Has  more toxic than CuSOit alone.
           Copoer  chtcrattine  Mas also found to be
           •ore toxic  than CuSO<>.  Mo wetting agents
           Mere found  to be Inhibitory  at the
           concentrations investigated  (0.05 and
           0.005  DOW).  Also  reported are factors
           affecting growth of algae in canals to
           determine whether  there t»er« leads to
           controlling algae  by environmental
           Management.  No practical environmental
           means  Here  found.

                   Approximate toxlcltles of         MaNdesley-
           numerous pesticides commonly used In      Thomas(19M>
           Britain  were summarized. An  excellent     AHIC-1056
           brief,  general discussion of toxlclty
           testing  is  also present.

                   PI  71, chemicals evaluated as      Otto  (1970),
           alglcldes>  only 9  Here more  toxic than    AHIC-39?
           CuSO<».   None  inhibited growth of
           mat-forming algae  for more than 7 oeeks.
           CuSOd  formulated with certain wettlnq
           agents  MBS  more toxic than CuSOfc alone.
           Cooper  chloramlne  was also found to be
           •ore toxic  than CuSQ<>.  No Hefting agents
           Mere"found  to be inhibitory  at the
           concentrations investigated  10.OS and
           0.00?  pp»).   Also  reported are factors
           affecting growth of algae In canals to
           determine whether  there Mere leads to
           controlling algae  by environmental
           •anage*ent.   No practical environmental
           •cans  were  found.
Copper sodiun
cltratfl (as Cu)
Uateralpor*
eueullata
(larva*}
                                                      0.63 (T 2 hr)
ato,l, and
salinity   data:
         Ihls study was conducted to
      Ine gpoclea of marine Inrvaa
suitable for use in test screening
antifoulIng cheoieals.  A salina (brine
ahrlav) appeared to have the best
potential for this purpose.  A salina
larvae sensitivity urns greatest starting
at age 2O-80 hr, and tolerated relatively
low pH ($.0).
Wisely, et al
(1967),
AMIC-5703
-------
Copper sodlua
citrate (aa Cu)
Copper sodluB
citrate (as Cu)
Copper sodlua
citrate  (as Cu)
Copper sodium
citrate  (aa Cu)
Copper sul late plus
•Ihylaryl
oolyoxethylene
alycols
Bugula
nerltlna
(larvae)

Splrorbla .
lamellosa
(larvae)

Oaleolaria
caeapltoaa
(larvae)

Kytilua
edulla
planulatua
(larrae)

Phormldlum
amblguu*
                                   •     ^^
3.90 IT 2 hr)



0.1*8 (X 2 hr)



2.90 (» 2 hr)



23 (T 2 hr)
0.5-10.0 (100
percent growth
Inhibited !<•>
a.c.l, and
salinity
a,c,l, nnd
salinity
a,c.l, and
salinity
a.c.l, and
salinity
as above
                                                                                        aaaa aa above
                                                                                        same aa above
                                                                                        sane aa above
                   Of  74  chemicals  evaluated  as
           alqlclces,  only  9  Here more  toxic  than
           CuSOU.   None  Inhibited growth of
           •at-formlng algae  for  more than ?  weeks.
           CuSOt  formulated Kith  certain wetting
           agents  was  more  toxic  than' CuSO<»  alone.
           Copoer  chloranlne  was  also found  to be
           iiore toxic  than  CuSO
-------
I
Compound
Copper sul fat* plus
Calclu* salt of
polyoxyethylene
Copper sul fat* plus
Dodecy leth*r of
polyethylene glycol
Copocr sul fate plus
Cnulslflable
polyethylene
Copper sul fate plus
Cthoxylated isooctyt
phenoxy polyethoxy
•thanol
Copper sul fat* plus
Cthoxylated nonyl
phenyl ether
Copper sul fate plus
Potyoxyethfene nonyl
phenyl ether
Copper sul fat* (as
cooper)
Field Field
Organise Study Location
Phor»Idlu« L —
anblguu*
Phornldlua L ~
amnlguu*
Ptiornidlu* L
anblquun
PnoraldluB L —
anblguun
Phornldlua L —
aablguua
Phoraldlua L
aabiguua
Carclnus 8S» —
•aenas
Toxlclty,
Active
Ingredient.
Pp«
0.9-10.0 (100
percent tjroxth
Inhibited !<•)
0.5-10.0 (50
percent qroxth
Inhibited lit)
0.5-10.0(?S
percent growth
Inhibited l
-------
Copper sut fat* (as
copper)
                     CardluM edule BSA
                                                       1.0 (T2I
                                                 «*(contin-
                                                 uous aer-
                                                 ation,  sea-
                                                 water,  and
                                                 daily
                                                 solution
                                                 renewal)
                   saaa as above
                                                      Portnann,  et
                                                      al  (1971) i
                                                      AHIC-7701
Copper cut fat* (as
capper)
Cranqon
crangon
                                   8S»    —
                                                       19 mi
•«(contin-
uous  aer-
ation,  sea-
water,  nnd
daily
solution
renewal)
                                                                    saae  as above
                                          Portnann, «t
                                          al  (1971),
                                          ANIC-7701
Copper sulfate (as
cepptr)
                     Ostrea edulls BSA   —
                                                       too  ITZ>
                                                 a»(contin-
                                                 uous aer-
                                                 ation,  sen-
                                                 water,  and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                         sane as above
                                                      Portaann, et
                                                      al  (1971),
                                                      AMIC-7701
Copper sul fate las
copperl
Panda Ius
    •9«it
              BSA   —
                                                          (TZ)
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                         sane  as  above
                                          Portnann, et
                                          al  (19711,
                                          AHIC-7701
Copper sul fate las
copper)
Copper sulfate
Cut Plus*
               (as
Platlcthys
fIesus
Sal HO
galrdnerl
(eggs and
speral
                                   BSA   —
                                                      1.0-3.3  IT2)
                                   LCF
                                                      1.0  (NTE)
a«( contin-
uous aer-
ation, sea-
water, and
dally
solution
ronewal)

i.c.f
                                                                                         sane  as  above
                                          Portnann, et
                                          a» (197l>,
                                          AMIC-7701
        Data were given In mq/t which xas Shax, et al
taken to be the equivalent of DP*.        (1971),
Fertilization rates were statistically    *XIC-1<»<>«
Slnllar in both test (Cu and Nl) and
control waters*  The rate of hatching Has
significantly different for eggs exposed
to Cu and the-rate of development Has
-------
          Comoound
Field Field
Organ Is* Study Location
ToxleMy,
Active
Ingredient,
Ppn
Experimental
Variables,
Control led
or Noted Comments
Reference
VO
fU
        Cooper sulfate  (as    Acroneurla    BSA
        Cut
        Copper  sulfate  (as    Ephemeral la   BSA
        Cut
        Copper  sulfate  (as    Hydroosyche   BSA
        Cut
Copper sulfate (as   Pnoraldlu*    L
Cut                  aabiquue
                                                              8.3
                                                               0.32  (T2>
                                                              32  ITU.)
0.5-10.0 163
percent qrowth
inhibited!*)
                                                                                 Increased.  The authors concluded that In
                                                                                 hard waters neither Cu nor Nl Is likely
                                                                                 to Impair fertilization In rainbow trout.

                                                                      a»,c,d,e,f         Ephemerella (mayfly) was the most Harnlek, et
                                                                                 sensitive aquatic Insect of those
                                                                                 studied, and copper the most broadly
                                                                                 toxic metal.  The authors suggest that
                                                                                 aauatlc insects may not be as sensitive
                                                                                 to heavy metals as fish.

                                                                        ,c,d,e,f        same as above
                                                                              a*,c,d,e,f
        Copper sul fata
                              Pseudopleuro  LCF
                              neetea
                              aaericanus  (3
                              yr)
                                                               0.180  (SRI
                                                                                 ,c,e
                                                                                                same  as above
                                                                                                                                   at  (1969),
                                                                                                                                   AHIC-3767
                                          Warnlck,
                                          etal
                                          AHIC-3767

                                          Marnlck,
                                          etal (19<>9>.
                                          AHIC-3767

        Of 71, chemicals evaluated as      Otto (1970),
alqlcldes, only 9 were more toxic than    AMIC-892
CuSOii.  None Inhibited growth of
mat-forming algae for more than Z weeks.
CuSOU tormulatert with certain wetting
agents was more toxic than CuSOC» alone.
Cooper chloramlne was also found to be
more toxic than Cu30U.  No wettlnq agents
were found to be Inhibitory at the
concentrations Investlaated (0.05 and
0.005 com).  Also reported are factors
affecting growth of alqae In canals to
determine whether there were leads to
controlling alqae by environmental
management.  No oractical environmental
means were found.

        Winter flounder were exposed to   Baker
varied concentrations ol cooper and       (1969),
selected tissues examined by light and    ANIC-3763
electron microscopy.  Medium to high
concentrations of copper resulted In
fatty liver decoslts, kidney necrosis,
hemoooetlc tissue destruction, and gill
architectural changes as determined by
Iiqht microscopic analysis.  Seven
additional organs or structures were
-------
Copper sul fat*
Copp*r sulfat*
                     Pseudopleuro  LCF
                     n«ot«s
                     aaerlcanus  13
                     vrl

                     Plaephales    BS*
                     proaelas
                                                       0.560-3.3
                                                       0.08*.  CT4.)
Copper sulfate       Plaephales    BCF»
                     prove I as
Copper sulfat*       Plaephales    BCFCH
                     proaelas
Copper sulfat*       lepoals       L
                     aacroeMrus
                                                      o.ors mi
                                                      0.018 (T
                                                      HO)
                                                      1-5 CSBl)
Copper sulfat*
                     Trachtnotus   BS*
                     caroltnus
                     (|uv*nll«)
                                                      !.«.-?. 0 ITU
                                                                                  apparently  unaffected.   Low  levels of
                                                                                  eoooer  caused  varied  anoaalles  In oil I
                                                                                  taaellae  as determined by electron
                                                                                  •icroscopy.

                                                                                         saae as above
                                                                      •«(old,al          CooDer at 1B.<> Dob affected
                                                                      f, acidity survival• growth, and scanning.  Loner
                                                                      conduc-    concentrations also reduced growth and
                                                                      tlvlty,    soawnlrq but apparently not eaq
                                                                      and Cu     hatcnabllIty.  The naxlnu* acceptable
                                                                            <     toxicant concentration 9>,
                                                                                                                           •HIC-3763
                                                                                                                           Mount, et
                                                                                                                           (1969),
                                                                                                                           »«IC-376S
                                                                                                                                     al
                                                                                        sane as above
                                                                                                                           Mount, et al
                                                                                                                           11969),
                                                                                                                           »NIC-3T65
                                                                                                                           Mount, et al
                                                                                                                           (1969),
                                                                                                                           AM1C-376S
a«,o.d,e,
t, acidity,
conduc-
tivity,
and Cu

*«,e,d,o,
f, acidity,
conduc-
tivity,
and Cu

a*,c,e,f           Coooer caused a respiratory       0"H»ra
           Increase as concentration levels were     (1971),
           Increased.  Oreovrry from Initial stress  »MIC-3793
           by copper was delayed at higher
           concentrations.  The author su99ests the
           f lotting Hater fish resplroneter techniaue
           as » fast Hnd sensitive tool for
           evaluating pollutants.

a,c,e,f,I,         In this study of ponpano salinity Birdsonq, et
and        Mas controlled at 10, ?0, and 30 ppt and  al  (1971),
sulfate,   Investloated as a variable,  (crlflavln,  AMIC-S570
sod 1UK,    formalin, and potassium permanganate uere
calcluH.   slightly nore toxic at the highest
POtasslua, salinity, Hhll* copoer sulfate Mas
•agneslum, slightly less-toxic.  These compounds ar*
-------
  Compound
Toxlclty,
Active
Field Field Ingredient,
Organise Study Location ppn

Experimental
Variables,
Control led
or Noted Comments Reference
carbonate, used as cronhylactic bacterial
blcarbon- treatments. All appeared to be
ato, reasonably safe to use exeeote possibly
sallalty potassium permanganate.
Copper sulfate
Copper sul tat*
Copper sulfat*
Copper sulfat*
Copper sulfat*
Copper sul fat*
                     Oncorhynehus
                     tshaxytscha
                     (eggs)
                                   BCF»
                                                      0.08 (NTE)
                                                                      a*,e,d»f
OneorMynchus  BCFA
tshaNytscha
(fry)
                     Poccus
                     saxatllls
                     (fIngerlInqs)
                     Orconeetes
                     rustlcus
                                   BS»
                                   BCFA  —
                     Orconect*»    BCFCH —
                     rustlcus
                     Oreonectes    BCFCH —-
                     rustleus
Copper (as Coooer    Canp*toaa     BCF*  —
sulfat*)             dec 1 SOB       andCH
                                                                    Chinook salmon egqs Mere more      Hazel,  et  al
                                                            resistant to copper sulfate than were      (1970),
                                                            fry.   Growth xas also Inhibited.  Adverse AMIC-5572
                                                            effects on fry Mere noted at
                                                            concentrations as low as  0.02  ppn.   The
                                                            authors recommend further laboratory and
                                                            In situ studies.
O.Oi. (93
percent K)
                                                      0.62
                                                      3.0 (T«»)
                                                                      a*,c,d,f
                                                                                        same as above
                                                                                                                           Hazel, et al
                                                                                                                           (1970),
                                                                                                                           AHIC-557?
                                                 B.e,c,d,e,          Striped bass flngprllnas Mere     Met (born
                                                 r,pt 8Jld   anoarently much none sensitive to         (19*91,
                                                 iron       therapeutic and herbicldal  compounds than &MIC-5723
                                                            many freshwater fish.

                                                 a*,c,«,f,a         Adult crayfish Mere found to be   Hubscnnan
                                                            more resistant to coocer sutfate than the (1967),
                                                            young.   Several life stages were studied, AMIC-5985
                                                            and additional exoosure variations were
                                                            included in the exoerImentation.
                                                            Mortality of neMly-hatched  crayfish
                                                            occurred at 0.1?? pom, and  growth Mas
                                                            Inhibited at concentrations down to 0.015
                                                            ppn over a 70-day period.   Sublethal
                                                            effects of cooper Mere Hell established
                                                            and the procedure appears  to be a good
                                                            one.
                                                      1.0 (TU)
                                                      0.015 (SB)
                                                      1.7 (TV)
                                                                      a*,c,e,f,Q
                                                                      a*,c,e,f,q
                                                                                        same as above
                                                                                        sane as above
                                                  ,c,d,e,f          Survival, qroHth,  reproduction,
                                                            and feeding Mere the responses used to
                                                                     Hubschman
                                                                     (1967) ,
                                                                     AMIC-5985

                                                                     Hubschman
                                                                     (19675 ,
                                                                     AMIC-5985

                                                                     Arthur, et
                                                                     al (1970),
-------
vi)
vn
         Copper  (as  Copper
         sulfate)
         Copper  (as Copper
         sulfate)
         Copper  (as  Cooper
         sulfate)
Campeloaa
dec 1 sun
BCFA
and
CH
Physa Integra BCFA
              and
              CH

Physa Integra BCFA
              and
              CH
Cooper (as Cooper
sulfate)
Cooper (as Copper
sulfate)
Cooper (plus
PHENOL >
Gammarus
paeudo-
llan*«ua
Gammarus
paeudo-
llnaaaua
Sal «o
galrdnerl
BCFA
and
CH
BCFA
and
CH
BSA
          Cooper (plus  Zinc,
          nickel)
Sat «io
galrdnerl
                                             BSA
0.008-0.011(8
(NTE6 Hh)
                                                                0.019 (T)
                                                 a,c,d,e,f
                                                 a,c,d,e,f
                                                                                a,c,d,e,f
                                                                                a,c.d«e«(
                                                                0.008-0.01 oom.  Safe limits for
                                                                                           Gammarus were O.OIH6-0.008 In a
                                                                                           continuous flok system and fl.01Z9-0.OZ39
                                                                                           In a static system.
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
Arthur, et
at (liroi,
AMIC-967

Arthur, et
al (1470),
AKIC-8S7

Arthur, et
al (1970),
ANIC-867

Arthur, et
al (1970),
ANIC-K67

Arthur, et
al (1970),
AMIC-867
                                                                                                   PalnboH trout Here exposed to     Brown, et
                                                                                           copoer, phenol, zinc, or nlcKel solutions al(1970),
                                                                                           to determine i>8-hour LC90 values for      AHTC-S994
                                                                                           mixtures of copoer and phenolt copper,
                                                                                           zinc, and phenol> and copper, zinc, and
                                                                                           nlcKel.  It Has concluded that acute
                                                                                           lethal toxlcltles of the mixtures could
                                                                                           be adequately described by summations of
                                                                                           the fractional toxlcltles.
                                                                                                  same as above
                                                                                        BroHn,«t al
                                                                                        (1970),
                                                                                        AHIC-599%
-------
Toxlclty, Experimental
Active Variables.
Field Field Ingredient, Controlled
Comoound Orqanlsm Study Location Ppm or Noted Convents
Copper (plus zinc, S*lao BSA — 0.6-Z.<>0 (T2) a.c.e
phenol) qalrdnerl

Cooper A lose FL Great Lakes 0.9Cresldue)
pa«udo- - Superior,
harongu* Michigan,
and Erie








same as above


Trace element content of fish
from Lakes Suoerlor, Michigan, and Erie
Mas determined by activation analysis.
Whole body and liver residues were
determined* Concentrations varied Hlth
species and lake. Other elements found
Here! antimony - 5 to 100 cob, barium -
0.7 oom, cesium - 3 oob, lanthanum - 1 to
20 pobt mercury - 10 oob, rhenium - 0.5
to •> pob. rubidium - 0.06 to 6 opm.
scandium - ? ppb. selenium - 0.1 to 2
ODb, silver - 0.001 oob.
Reference
RroMn.et al
(1970) ,
AMIC-5S9U
Lucas, et al
11970).
ANIC-3778









Copper
Copper
Copper
Copper
Copper
Copper
                     Coreqonus     FL
                     artedll
                     Coreqonus     FL
                     clupeaformls
                     Coreqonus     FL
                     hoy!
                     Prosoplum     FL
                     cyl Indraceum
                     Salvellnus    FL
                     naaaycush
                     Osmerus       FL
                     mordax
Great Lakes
- Suoerlor,
nichlqan,
and Frle

Great Lakes
- Suoerlor,
Michigan,
and Erie

Great Lakes
- Suoerlor,
Michigan,
and Erie

Great Lakes
- Suoerlor,
Michigan,
and Erie

Great Lakes
- Suoerlor,
Michigan,
and Erie

Great Lakes
- Suoerlor,
Michigan,
end Erie
                                                      12(resldue)
                                                      5.*(residueI
                                                      <».9(resldue)
                                                      3.8
-------
Copper
Copper
Copper
Copper
Copper
Copper
                     Car-ass 1 us      FL
                     auratus
                     Notroois      Fl
                     hudsonlus
                     Percoosls     FL
                     omlscomaycus
                     Roecus
                     chrysops
                                   FL
                     Peres         FL
                     I lavescens•
SHzostedlon  FL
vltreum
vltreum.
Great Lakes  l
-------
Compound
Copper
Copper
Copper
Copper
Organise
Esox tuclus
Osmerus
•ordax
Perca
f lavescens
Sal vel Inus
Toxlclty, Experimental
Active Variables.
Field Field Ingredient. Controlled
Study Location Ppm or Noted
FL Lake Erie, 0.7 (residue) --
Can.
' FL Lake Erie. 0.8 (residue) —
Can.
FL Lake Erie. 1.3 (residue)
Can.
BDFCH — 0.018 (NTE) a*.c,d*e.f
Comments Reference
sane as above Uthe, et at
3819
sane as above Uthe* et al
(1971), MIC-
3819
same as above Uthe* et al
3819
A concentration of 17.5 ppb McKIm, et a
                      fontlnalIs
                      (eqgs)
Copper
Copper
Copper
SalvelInus
fontInalis
(Juveniles)

SalvelInus
fontlnalls
(adults)
                                   BDFCH
                                   BOFCH —
                                                      0.017 (K)
                                                      0.1 ITI.I
           cooper did not adversely affect survival, (1970),
           qroHth, or scanning of brook trout.       ANIC-38Z1
           However, this concentration level had
           drastic effect on Juvenile trout.  The
           coooer also delayed yolk sac absorption
           and delayed fry development.  The maxlaun
           acceotable toxicant concentration (NATO
           was calculated to be between 9.5 to 17.fc
           ppb copper.

a**c*d*e*f        same as above                      «cKlm,et al
                                                     (1970),
                                                     AMIC-3821

a'.c.d.e.f        sane as above
                     Paralabrax    Fn    Scattergood  2 (dorsal
                     clathratus          Stean Plant* nuscte
                                         LosAngeles.  RESIDUE)
                                         Cal.
                                                                    Fish collected from an effluent
                                                            oio* of a steam plant and from offshore
                                                            Haters of Catallna Island Mere analyzed
                                                            for trace element content.  Trace element
                                                            content of the effluent Hater Has at
                                                            least 5 times qreater than that of nornal
                                                            sea xater for cadmium, cooper, nickel,
                                                            zinc, and chromium.  Livers of fish from
                                                            the effluent Here nearly twice the size
                                                            of those fron the ocean.  Greatest
                                                            differences in concentration occurred
                                                            with alumlrun* cadmium* and nickel.
                                                            Silver, barlun, lithium, and lead shoxed
                                                            the least differences.  The author
                                                            etal
                                                     (1970),
                                                     4MIC-3S31

                                                     Stapleton
                                                     (1968),
                                                     ANIC-5980
-------
Copper
Copper
Copper
Copper
Copper
Copper
Copper
Paral abrax    FH    Catal Ina     ?  (dorsal
clathratus          Island, Cal. muscle
                                 residua)

Paral abrax    FH    Scattergood  Z  (ventral
elathratus          Steam Plant, muscle
                    LosAngeles,  residua)
                    Cal.
                     Paral abrax    FN
                     clathratus
                     Paral abrsx    FH
                     clathratus
                    Catal Ina     2 (ventral
                    Island, Cat. muscle
                                 residue)

                    Scatter-good  6 (gonads
                    Steam Plant, residual
                    losAngeles,
                    Cal.
                     Par a! abrax    FH    Catal ina     5  (gonads
                     clathratus          Island, Cal. residue)
Paralabrax    FH    CatalIna     5
elathratus          Island, Cal. (gonads
(gravid                          residue)
females)

Paralabrax    FH    Scattergood  5 (liver
clathratus          Steam Plant, residue)
                    LosAnoeles,
                    Cal.

Paralabrax    FH    CatalIna     6 (liver
clathratus          Island, Cal. residue)
                                                                                  concluded that trace element analysis  of
                                                                                  tissues could  be  used to determine  the
                                                                                  effect of pollutants on  marine  organisms.

                                                                                         same as above
                                                                                         same  as  above
                                                                                         same  es above
                                                                                         same  as above
                                                                                         same  as above
                                                                                         same  as above
                                                                                        same  as  above
                                                                                         same  as  above
                                                                                                      Staoleton
                                                                                                      (1168),
                                                                                                      AHIC-5980

                                                                                                      Staoleton
                                                                                                      (1468),
                                                                                                      Staoleton
                                                                                                      (1965) »
                                                                                                      Staoleton
                                                                                                      (106(0 .
                                                                                                      Staoleton
                                                                                                      (196.1),
                                                                                                      AHIC-5980

                                                                                                      Staolcton
                                                                                                      (1
-------
  Compound
                       Organise
Field Field
Study Location
Toxlcltv,
Active
Ingredient,
Pp«
Experimental
Variables!
Control led
or Noted
Comments Reference
Copper
Capper
Copper
                     Paralabrax
                     clathratus
                     Paralabrax
                     clathratus
                     Paralahrax
                     clathratus
                     Selmo
                     galrdnerl
                                   FM
                                   FN
                                   FN
                                   BS»
Cal.

Catallna     1? (heart
Island. Cat. residual
Scatterqood  a (eyebal I
Steaa Plant, residue)
LosAngeles*
Cal.
Catallna
IsI andf Cal<
V Ceyeball
residual
                                                      0.75 (TZ)
                                                                      a.e.e
Corexlt 766*
                     Plmeohales    BSA
                     pr one I as
                                                      3200
                                                                      c,d,e,f
Corexlt 7664
Corexlt 766%
Corexlt 7664
                     Plmephales
                     prone I as
                                   BS*   —
                     Biochemical   I
                     oxygen deaand
                     Steel head
                     trout
                     (fingerlings)
                                   BS*   —
                                                      180  (MSC)
                                                      380,000
                                                      15.8 (T4)
                                                                      c.d.e.f
                                                                      c.d.e.f
                                                                                        sane as above
                                                                                        same as above
                                                                                        sane as above
                                                                     Staoleton
                                                                     (1968),
                                                                     Staoleton
                                                                     (I960),
                                                                     AMIC-5980
Staoleron
(1968),
*HIC-S960
                                                RalnbOH trout Mere exposed to     Brown, et at
                                        eoooer, Dhenol, zinc, or nickel solutions
                                        to determine ".S-hour LCSO values for      (1970) ,*MIC-
                                        • Ixtures of cooper and phenol I copoer,    599I>
                                        zinc, and phenol I and cooopr, zinc, and
                                        nickel.  It was concluded that acute
                                        lethal toxlcltles of the mixtures could
                                        be adequately described by summations of
                                        the fractional toxlcltles.
                                                Toxlclty of six oil spill
                                        dlspersants Has determined along with
                                        BOO values.  Pond Mater was used as
                                        diluent and oil Mas Included In the
                                        exoerlment.  Oil narked Iy reduced
                                        toxiclty of all dlsoersants.  Data are
                                        given as **nost probable" 96-hr TL sub a.

                                               saae as above
                                                                                        saae as above
                                                                     milch
                                                                     (1969I.AHIC-
                                                                                  71lllch
                                                                                  
-------
Corexlt 766I|.



Corexit 7661).



Corexlt 766V
Coho salmon   B3A   Hood Canal
(flngerllnga) In    Hoodaport,
              »ltu  Wash.
Pacific
oyster
(larvae)
B3A   Hood Canal
In    Hoodaport,
situ  Wash.
                     Card luii edule  as*   —
UO.O (K)



UO.0-80.0 (SB)
                                                       3300-10, OJ»U
                                                       (TZt
Corexlt 766V
                     Cra r>g on
                     er anqon
                                   BS«    —
                                  3300-10,000
                                  ITZ)
                                               776t, appeared to have the least toxlelty
                                               .With fair to qood oil dispersion
                                               capability.

                                                     same aa above
                                  sane aa above
                                                  **(contln-         One hundred-forty surface active
                                                  uous ear-  agents, solvent enulslflers. pestleldest
                                                  ation, aea-Dolychlorlnated biohenyls, cure
                                                  water, and Inorganic, and organic chemicals were
                                                  dally      evaluated against as many as ten aarlne
                                                  solution   organises.  The authors noted that nost
                                                  renewal)   published data of this type deal with
                                                             toxlelty of chemicals to freshwater
                                                             organises.

                                                                    sam* as above
                                    a* Icontin-
                                    uous  aer-
                                    ation,  sea-
                                    water,  end
                                    dally
                                    solution
                                    renewal)
Tracy, at ai
(1969),
AKIC-363I*.

Tracy, et al
(1969),
AMC-33314.
                                                                                         Portnann,  et
                                                                                         al  f19711,
                                                                                         •HIC-7701
                                                                      PortBann,  et
                                                                      al  (1971).
                                                                      4HIC-7701
Cerekif 766*
                     Lieanda
                     I Inland*
                                   BS»   —
                                                       1000-3300  (TZI
                                                  a»(contin-
                                                  uous aer-
                                                  ation,  sea-
                                                  wator,  and
                                                  dally
                                                  solution
                                                  renewal)
                                                                                         seme as above
                                                                                         Portxunn,  et
                                                                                         al  (1971).
                                                                                         •HIC-7701
Corexlt 766<>
                     Sal no salar
                     loarrl
CorelIt 766%
                     Gannarus
                     oceanlcus
                                   8S»   —
                                 500  (NTCVt       a*.e                Aroclors IPS", and 1??1 Mere       71tKo
                                                  Inlxed  tap evaluated for toxic effect with Corexlt   (1970),
                                                  or          76f>«. (Height ratio »;!
-------
  Compound
CorexIt 766H
Corexlt 6666
Couaaphos
Toxlclty, Experimental
Active Variables,
Field Field Ingredient. Controlled
Organism! Study Location Pom or Noted Comments


Gammarus BSA —
oceanlcus



Crangon BSA —
crangon


0.19 (SB) a*
(weeklysol
utlon
change.
seawater)
3300 (TZ) a*{ contin-
uous B.CC-
concentrations down to 0.19 pom. The
author notes a possible synerglstlc
effect between the two compounds.
same as above




One hundred-forty surface active
agents, solvent emulslflers, pesticides.
Reference


Mlldish
(1970).
AHIC-R9


Por tmann,
al
ation, sea-Pol ych lorlnated blohenyls, pure (1971), MI






Rasbora BCFA —
heteromorpha and
BSA










water, and
daily
solution
renewal)


0.046 (T2> a*,c,e,f.
hard (HW)
or
SOFT(Stl)
synthetic
dilution
water, or
seawater
for some
species



inorganic, and organic chetricals were
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wide range of toxlclty spanning 1? orders
of magnitude. Knowing the toxicity and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of materials. Sometimes
pesticides were nost toxic In hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
7701





Alabaster
(1969),
AMIC-5I.Z5










Co-*al
                     Norone
                     saxatllls
                     (fingerI Ings)
                                   BSA   —•
                                                      6Z
Co-DaI
                     Mercenarla
                     mercenarla
                     (eggs)

                                                      9.12 (T2)
a,c,d,e,f,         All  compounds were Investigated   Me 11 born
p          because of thelP probable usaoe In        (1971),
           hatchery production of white bass*        AH.IC-5ST1
           Comnounds that can be used at recommended
           concentrations were Aouathol, Casaron,
           Llndane, and Terramycln concentrate.
           Those that should not be used wepe
           Acrlflavlne, Raylusclde, Malachite green
           oxalate, and Malathion.

--                 The effect of 52 pesticides on    Oavls,  et al
           embryonic development of clams and
           oysters was reported.  Synerglstic        (1969),AMIC-
           effeets with solvents were also reported. 5990
            Host of the compounds affected
-------
k
U)
         Co-ffal
         Co-Ral
        Co-Rat
Craln* OS*
                              Hercenarla
                              mercenarla
                              (larvael
                              Crassostrea
                              vlrglnlca
                              (eggs)
Crassostrea
vlrolnlca
(larvael

Crangon
crangon
                                   BS»
                                                                    (T 12)
                                                               0.11 IT?)
                                                               greater than
                                                               l.O  (T  iv)
                                                      330-1000 IT2)
        Cresol*
                              •genus         BS»
                              cataohraetus
                                                               10-33  (T2)
        Crcsols
                     Carclnus
                     aa«nas
                                                               10-100  
-------
  Ceaoound
Cresols
Creselm
Cr»ssauard
Crotothane
CFOM solvent N
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism, Study location Pom or Noted Comments
Cardlum edule BSA —






Pleuroneetes BSA
olatessa







Crmngon BSA
crangon
greater than a«(contin-
100 tT2) uous aer-
ation, soa-
watcr, and
dally
solution
renewal }
10-33 (T?> a»( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)


3.3-10 IT*) a*lcontln-
uous asr-
same as above






One hundred-forty surface active
aqents, solvent emulslflers, pesticides.
Pol vchlorlnated blphenyls, pure
Inorganic, and organic chemicals Mere
evaluated aqalnst as many as ten marine
organisms. The authors noted that most
published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
One hundred-forty surface active
aqents, solvent e*uls 1 f lers, pesticides.
Reference
Portmann, et
al (10711,
A«I C- 77 01




Portmann, et
• 1 (1471),
AMIC-7701






Portmann, et
al
ation, sea-oolychlorinated blphpnyls, oure (iq71),AHIC—






Pasbora 8CFA —
heteromorpha and
BSA









Crangon BSA
crangon

wator, euid
daily
solution
renewal )


0.07 (T2) a«,c,e,f.
hard
(HM)or
cnffr ICU1
soil I^HV
synthetic
dilution
Hater, or
seawater
for some
species



33-100 IT?> a»( contin-
Inorqanic, and orqanlc chemicals Mere
evaluated aqalnst as many as ten marine
organisms. The authors noted that most
Published data of this type deal with
toxlclty of chemicals to freshwater
orqnnlsms.
One hundred sixty-four
pesticides, wettinq aqpnts, and
miscellaneous water pollutants Showed a
of magnitude. Knowlnq the toxlclty and
percentage of all comoonents of a
formulation did not result in easy
predictability of the toxlclty of a
mixture of materials. Sometimes
pesticides Mere most toxic in hard Mater
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
One hundred-forty surface active
uous aer- aqents, solvent emulslflers, pesticides.
ation, sea-
polychlorlnat ed blohenyls, oure
7701





Alabaster,
tl9&9>,»«IC-
Si.?S









Portmann, et
al (1371),
AHIC-7701
                                                                      water, and Inorqanic,  and orqanlc chemicals  Here
                                                                      dally      evaluated aqalnst  as  many  as  fen  marine
                                                                      solution   orqanlsms.   The authors  noted  that  most
                                                                      renewal)   published data of  this type deal  with
                                                                                 toxiclfy of  chemicals to freshwater
                                                                                 organisms.
-------
            Cr, Nit Cut CN, and  Plnephales     BSACF  Grand  River   between
            Zn                   prone I as       (ML)   at            1.25-3.75
                                                      Hyo»lnq,Mlch  oercent (T3)
                                                      Iqan
            Cr, Nit Cut CH, and  Catostoeus
            In                   conncrsonl
            CS
                     Wolffls.
                     papullfera
                                   BSACF Grand River  between
                                   CHU  at           1.25-3.75
                                         Uyonlnq.Hlch percent  (T3)
                                         I gen
                                                                  100 (K)
                                                                                          A mobile'bloassav unit Has
                                                                                  utilized to conduct  this study ot
                                                                                  Municipal Hastenater containing the
                                                                                  indicated toxicants.  River wafer  Has
                                                                       a,c,e,      used as diluent.   The conclusion M»S       71IIIch
                                                                       conductIvl  reached that synerglstlc or additive       (1969),
                                                                       ty. Nit     toxic effects occurred since toxlcltv Has  AHIC-?9P6
                                                                       Cu, Cr,     greater than that  ot any ot the Ions
                                                                       CN, and  7n  singly.
                a,c,e.
                conductlvi
                ty. Nit
                Cu, Cr,
                CN, and 7n

                Hunter'a
                modlum
                diluted
                1:5
                                                                                                     saae as above
                                                                      711llch
                                                                      (1969),
                                                                      ANTC-294J6
                                     All conpounda wore harmful to    Worthier, at
                            duckweed to gone decree.  Decreased       el,(1971),
                            populations were noted at non-lethal      AMIC-3233
                            concentrations and some compounds
                            (Mmlathlon and 2,^-D) caused toratoganlc
                            effects at concentrations as low as 1 ppm.
            CuCIZ  ?H?0  (as Cu)
\n
                                  Platv*onas
                                  subcordl-
                                  formla
                                                a      ^^
            CuCI? ?H20  (as Cu)    Porphrrldlu>  L
                                  cruentua
                                                                   approx.1.0 (K)
                                                                   appro*.  0.5(K)
                                                                       5SM and
                                                                       NSW
                                                                      SSN  and
                                                                      NSM
                                   NT* stimulated algal  tiroHth In    FrlcKson, at
                           cultures without added copper and reduced al  (19701,
                           toxlclty ot copper at all  levels of       »Mlc-fc«.9
                           cooper addition.  See information on
                           CuCI2.H20 (as Cu) under authors cited for
                           •further Information.
                                                                                                     saae as above
                                                                     Erlcfcson, at
                                                                     al  (1970),
            CuCie  2H20  (as Cu)    Skeletone»a    L      —
                                  costatua
                                                       aporox.  0.15    SSM  and
                                                       (K)             NSM
                                                                                                     saae as above
                                                                     Erlckson, et
                                                                     al  (1970),
CuCI2 2H20  las Cu)   ••ohldlnlun   L     —
                     carterI


CuCIZ 2N20  (as Cu)   Chactoecros   L
                     so
CuCIZ 2M29 (as Cu)   Cyrlotella    L     —
                     nana


CuC12 2H20 (as Cu)   Dunalialla    L
                     tortioleeta
            CuC12 2B20 (as Cu)   Isochryala    L
                                 Salbana
                                                                   less than  8.05   SSM and
                                                                   (K)              NSH
approx. 0.05    SSM and
(K)             NSH
approx. 0.15    SSM and
(K)             NSH
U50 (5o percent  S3K and
K)               KSW
Approx. 0.2 K)   SSM and
                 NSW
                                                                                                     sane as above
                                                                                                     saae  as  above
                                                                                                     saae  as  above
                                                                                                    SUM as above
                                                                                        sane  as  above
                                                                     Erlckson, et
                                                                     al  (19701,
                                                                                                                                        Erlckson, et
                                                                                                                                        • I  (147«t.
                                                                                                                                        Erlckson,  at
                                                                                                                                        al  (1970),
                                                                     Erickscn, et
                                                                     al (1970),
                                                                     AKIC-U49

                                                                     Erlckaon, et
                                                                     al (1970),
                                                                     AKIC-IA9
-------
>
I
Compound
CuC12 2H20 (as Cu)

CuC12 2H20 Us Cu)


CuCIS 2H20 (as Cu)

CuC12 23120 (as Cu)

Cunllate RQ Z*










Cunllate RQ Z*








Cunllate RO 2*






Organism
Monochrysls
Lutheri
Nannochlorls
oculata

Nltzschla
cloaterlum

Ollsthodlacus
luteus
Salmo
galrdnerl









Rasbora
heteromoroha







Rasbora
heferomorpha





Toxiclty,
Active
Field Field Ingredient,
Study Location Pom
L

L


L

L

BCF» —
and
BSA








BCFA —
and
BSA






BCF4 —
and
BSA




Approx. 0.5
(K)
Approx. 0.5
(K)

Approx. 0.05"
(K)

Approx. 0.05

0.9 trz.
hardMater)









!.<» ITZ,
sof tnater)







0.9 (T2,
nardHater)





Experimental
Variables.
Control led
or Noted Comments
SSM nnd
NSW
SSM and
NSW

SSM and
NSW

SSM and
NSW
a* c e f
hard
(HH ) or
SOft 
synthetic
dilution
orseawater
for some
soecles
a*,c,e,f ,
hard(HH)
or soft
(SHI
synthetic
dilution
Mater,
same a a above

same as above


same as above

same as above

One hundred sixty-lour
pesticides, wetting agents, and
MUe range of toxlclty scanning 1? orders
percentage of all components of a
formulation Hid not result In easy
predictability of the toxlclty of a
mixture of materials. Sometimes
pesticides Mere most toxic in hard Mater
and sonetlmes the oooosite xas true.
Testing the actual material as sold Mas
found to be essential.
same as above








same as above






Ret erence
Erlckson, et
al (1970),
Erlckson, et
al (1970),
AKIC-uV?
Erlckson, et
E! (1970),
AKIC-U49
Erickson, et
£l (1970),
Alabaster
<1969),A1IC-









Alabaster
<1969I .AKIC-
51.25






Alabaster
(1969) .A1IC-
5425




-------
Cuprlc ammonium
sulfate  (as Cu)
Phormidlum
amblguum
Cuprlc chloram In*
Cuorle sulfate
                     Phormldlum
                     anblquum
                     Salve IInus
                     fontlnalIs
                     16-8 in.)

                                   BCFA  --
Cuprlc sulfat*
Cuerlnol
SalvelInus
fontlnalls
(6-8 In.)

Cranqon
crangon
                                   BCFCH
                                   BSA
                                                                       orseawater
                                                                       for some
                                                                       species
0.5-10.0 (16
Percent growth
inhibited!!*)
                                 0.5-10.0  (100
                                 percent growth
                                 Inhibited !<•>

                                 0.038-0.069(59
                                 6 and Zl)
        Of 7i» chemicals evaluated as
alqlcldes, only 1 were more toxic than
CuSOU.  None  Inhibited growth ot
mat-forcing algae »or more than 2 weeks.
CuSCKf formulated with certain wetting
agents was Jiore toxic than CuSOit alone.
Coop**r chloramine was also found to be
more toxic than CuSOU.  No wetting agents
were found to be inhibitory at the
concentrations investigated (0.05 and
0.005 CP">>.  Also reoort-d are factors
affecting growth of  algae in canals to
determine whether there were leads to
controlling algae by environmental
management•  No Dractica! environmental
»e-ans were found.

       same as above
                                                       0.017-0.033(58
                                                       337)
                                                       3.3-10  (TZ)
                a*(c«»tfta         The seven blood characteristics
                           of brook trout studied were red blood
                           count, hematoerlt, hpmoaloblnt plasma
                           chloride, plasma qlut^mic oxalscetlc
                           transanina<;e« osmolarltv, and total
                           protein.  Statistically slonlflcant
                           changes were noted in 5 characteristics
                           after 6 days.  Measurable decrease in
                           plasma glutamlc oxaMcetic transaninase
                           was the only change noted after long-tern
                           exposure to lower concentrations.  The
                           authors state that fish blood study can
                           be used as a treasure of their physical
                           condition and lonq-ranqe forecasting of
                           reproductive success and survival.

                a*tcQ        same as above
                a«(contln-         One hundred-forty surface active
                uous aer-  agents, solvent emulsiflers. pesticides,
                ation, aea-oolychlorlnated blphenylst Pure
                water, and inorganic, and organic chevieals were
                daily      evaluated against as many as ten marina
                solution   organisms.  The authors noted that most
                renewal)   Published data of this type deal with
                           toxlclty of chemicals to  freshwater
                           organisms.
Otto (197fl»,
  ANIC-89.?
                                                                     Otto  (1970),
                                                                     AMIC-892
                                          McKlm, et at
                                          (1970).
                                          ANIC-3H28
                                          HcKlm, et al
                                          M<*70) ,
                                          AtIC-3828

                                          Portmann, et
                                          al (1471),
                                          AMIC-7701
-------
             Compound
           Co.
           Zn
               HI, Cr,
           Cu,
           Zn
               HI, Cr,


Organise
CH, and Pimeohales
crone las







CNt and Catostomus
commer son I



Field Field
Study Location
BSACF Grand River
(ML) at
Wyoming, Mich
Iqan





BSACF Grand River
(ML) at
Wyoming, Mich
Igan
Toxlcity.
Active
Ingredient ,
Pp-
between
1.25-3.75
percent (T3)






between
l.?5-3.TS
percent (T3)

Experimental
Variables.
Controlled
or Noted Consents
a,c,e, con- A mobile bloassay unit Has
ductlvlty, utilized to conduct this study of
Kl,Cu,Cr, Municipal wastewater containing the
CH, and Zn Indicated toxicants. River water was
used as diluent. The conclusion was
'reached that synerglstlc or additive
toxic effects occurred since toxlclty Has
greater than that of any of the Ions
singly.
•,0,0, con" sa»e as above
ductlvlty.
Nl.Cu.Cr,
CH, and Zn


Reference
711 llch
(1969),
AMIC-2906






Zllllch
(1969) .
ANIC-2906

>
I
           ex
Fundulus      BSA
heteroclItus
0.00051-0.00225 a*,c,e.
(TO            and
                synthetic.
                seawater
           CX
           Cyanides
                                Nereis vlrens BS»   —
                                Leoouls       BSA
                                aacrochlrus
                                                                 0.00078-0.0071
                                                                 (TO
                                                                 0.11
                                                 a*,c,e,
                                                 and
                                                 synthetic
                                                 seawater

                                                 a*»e, and
                                                 synthetic
                                                 dilution
                                                 •ater
        A laboratory procedure based on
•Standard Methods Tor 96-hr toxlclty
determinations of crude oil and
oll-disoersant mixtures was described.
The dlsoersanfs varied considerably In
toxlclty, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr.  These did not differ
significantly from 2
-------
Cyanides
Cyclohexlmlde
                     Physa         BS»
                     heterostrooha
                     Phormldlum
                     •mblguuB
Oalaclda
                     ftasbora
                     heterooorpha
              BCFA
              and
              BSA
                                                      620 (TZI
Oalapon
Oafapon
Fish (not
specified!
Rasbora
heteromoroha
BCF»
and
BSA
                                                      greater than
                                                      100-1000 (K>
                                                      greater than
                                                      500 (TZ,
                                                      hardwater)
                                                  a»,e,  and
                                                  synthetic
                                                  dilution
                                                  Hater
                                                                    same  as above
                                  0.5-10.0  (66
                                  percent growth
                                  inhlbltadl
                                       ,,,
                                   bard (HWJ
                                   or soft
                                   (SWJ syn-
                                   the tic
                                   dilution
                                   water, or
                                   sea, water
                                   for sona
                                   spaeles
a'.c.e.f,
hard (HW>
or soft
(SM)
synthetic
dilution
Hater, or
seawater
(or some
                                                                                        Patrick, «t
                                                                                        al  (1968),
                                                                                        ANIC-5720
                                                     Otto  (1970),
                                                     AHIC-B92
                                                      OT 7i» chemicals evaluated as
                                              atgicldes, only 9 Here more  toxic than
                                              CuSO(».  None Inhibited growth of
                                              ma t-f orminq algae for more than 2 weeks.
                                              CuSOU  formulated with certain wetting
                                              aaents was more toxic than CuSO* alone.
                                              Coooer chloramlne Mas also found to be
                                              more toxic than CuSO25
Hide range of toxlclty scanning l? orders
of magnitude.  Knowing the toxlclty and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of materials.  Sometimes
pesticides were most toxic In hard water
and sometimes the ooooslte was true.
Testing the actual material as sold was
found to be essential.

        Aooroxlmate toxlcltles of         Mawdesley-
numerous pesticides commonly used In      Thomas
Britain were summarized. An excellent     ( 19711 ,A1IC-
brlef, general discussion of toxlcity     1056
testing is also present.

        One hundred sixty-four            Alabaster
pesticides, wettlnq agents, and           (1969),
miscellaneous water pollutants showed a   AMIC-5V25
wide range of toxlcity spanning 12 orders
of magnitude.  Knowing the toxicity and
percentage of all components of a
formulation did not result in easy
predictability of the toxlclty of a
mixture of Materials.  Sometimes
-------
          Compound
                               Organism
                                           Field  Field
                                           Study Location
Toxiclty,
Active
Ingredient,
  PP»
Experimental
Variables.
Control led
or Noted
                                                                                                         Comments
                                                                                                                                  Reference
                                                                              species
        Oalapon
                             Rasbore       BCF*  —
                             heteroeorpha  and
                                           BS«
>
I
        Oalapon
                             Cardlum edule BSA   —
*3 «T3,
sot t water)








greater than
100 (TZ)





a*.c,». 1,
hard
(HH)or
soft (SHI
synthetic
dilution
water, or
sraMater
tor so>e
species
a«( contin-
uous aer-
ation, sea.
water, and
dally
solution
renewal )
        Oalapon
                             Crangon
                             crangon
                                           BSA
greater than
100 (TZI
                           pesticides Mere most toxic In hard Mater
                           and sometimes the opposite Mas true.
                           Testing the actual  material  as sold was
                           found to be essential.

                                  same as above
                                                                                                                                   alabaster
a«{contin-
uous aer-
ation, soa-
water, and
daily
solution
renewal)
                                   One hundred-forty surface active
                           •an»nts. solvent emulsIflers. pesticides.
                          .polychlorlnated blphenyls. cure
                           Inorganic, and organic cheirlcals Here
                           evaluated against as many as ten marine
                           organisms.  The authors noted that most
                           published data of this type deal with
                           toxlclty of chemicals to freshwater
                           organisms.

                                  sane as above
                                                     Portm»nn, et
                                                     al (1971),
                                                     AMIC-7701
Portmann, et
al Cig71),
•«c-rroi
        Oalapon
                             Platlcthys
                             flesus
                                           BSA   —
greater than
100 (TZI
a«(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                                sane as above
Portmann. et
al (1971),
AMIC-7701
        DBP
                             Palaenonetes  BCF
                             Nadlakensls
                                                              O.OB (residue)   a*
                                   Magnification of  DOT and Aldrln
                           tagged with C-14 occurred rapidly.
                                                     Johnson, et
                                                     al
-------
        08 P
        ODD «C-1* label led)
                             Palaemonetes, BCF
                             Kadtaken*Is
                             Sorghum
                             ha I oanse
L
(Mod-
el
•oo sr
•tarn)
                                                               O.OOOl  (SB3)
1 Ib per A
(NTE)
a,c»g,
standard
reference
water and
sand
>
        000 fC-lt labelled)
                             Estlqmene
                             acrea
L
(Mod-
el
ecosT
•tea)
1 Ibper A
CK-NTEI
                                                                              standard
                                                                              reference
                                                                              water and
                                                                              sand
                                                                                          Bloloqlcal magnification factors of 2900
                                                                                          to 11*»»100 depending on the species Mere
                                                                                          found for ODT, and ZZ,HOD to IM.DOO for
                                                                                          Aldrln.  Harked degradation of DOT as
                                                                                          determined by analysis for ODT
                                                                                          •etabolltes occurred.  The authors
                                                                                          conclude that aauafIc Invertebrates
                                                                                          Influence Quality and Quantity of
                                                                                          Insecticide residue passed via the fish
                                                                                          food chain.

                                                                                                 same as above
                                                                                         U97i),A1IC-
                                                                                         3S20
        This snail  laboratory model
ecosystem procedure was develooed to
study pesticide biodegradabiI 1ty and
ecoloolcal maqnl»leaf Ion.  The food-chain
pathways In this system Mere?  (1)
sorqhuir - caterplller (larva), (?)
caterolller (excreta) - flerloqonlum, (3>
Oedoqonlum - snall<  d) Estlamene
(excreta) - diatoms* C5) Diatoms -
plankton, tfi)  Plankton - Culex (larva*),
(7) Culex - Cambusla.  The fish is the
too of the food chain.  Using
isotoplcally labeled orstlcide^ (1
Ib/acre application rate), residues Mere
determined for only selected organisms
(snail, mosquito, and fish) and water.
Reoroduclbl11ty appeared to be good.  The
authors state that the method gives a
good estimation of the potential  toxlclty
of pesticides and their breakdown
products to a variety of organisms and is
suitable for computer modeling.

       sane as above
Johnson,et
at (1971),
AMIC-3S20

Metcalf, et
al (1971),
AMIC-K.95
                                                     Metcalf, et
                                                     al  (1971),
        000 (C-l* label ltd)  Physa soo
                                           L
                                           (Mod-
                                           el
                                           ecosr
                                           sten)
                                                              5.6  (residue)
                                   standard
                                   reference
                                   water and
                                   sand
                                                                                                 same  as above
                                                                     Metcalf. et
                                                                     at (1971).
                                                                     AMIC-H95
-------
Coeoound
000 (C-l* labelled)




ODD (C-l* labelled)


ODD CC-1» labelled)




000 (C-lt labelled)




000 (C-l» labelled!





000 IC'lt labelled)




ODD 
-------
          ODD'(C-1»  label!•«)   H»t«r
                                   X
                                    (Hod-
                                   •1
                                                                 0.006
                                                                 (residue)
                                                                                 standard
                                                                                 reference
                                                                                 water and
                                                                                 •and
                                                                                                   *••• as above
                                                                                  detcalf,  at
                                                                                  al  (197H,
                                                                                  •HIC-U95
          000  fo.0")
                                •nqullia
                                rostrata
                                   FRl
                                          St. John,
                                          N.B.,  Can.
                                                       0.19 (residue)   —
01
000 ,
4MIC-371S
                                   S(n«ol«s of Hiiter, silt, hot ton    Houbry, et
                           debris, bottom organisms, and fish were   »l
                           taken in 1966 from a creek adjacent to an (1968),*HIC-
                           orchard which had heen treated in         3753
                           1963-10&5 with various chlorinated
                           hydrocarbon pesticides.  No residues were
                           found In water samples.  Silt samples
                           contained 0.003-0.013 ppm endrln and
                           0-0.005 po* dteldrln. Endrln residues of
                           0.011-D.075 pan and 0.(IO?-I).006 pp*
                           dleldrln were found In debris samples.
                           Oesolte United control data, residue
                           analyses indicated that contamination of
                           the environment studied was United.
-------
>
H
        ODD
        000
        ODD
000
        000
        000
        000
Organism
Phlnlchthys
atratulus
Gamnarus so*
Salvel Inus
fontlnalls
Semotl lus
atromacul atus
Cottus balrdl
Stalls sp.
(larva*)
Car ass lus
auratus
Field Field
Study Location
FS Knlqhts
CreeK, Oun
County,
Misc.
FS Knlqhts
Creek, Oun
County,
wise.
FS Knights
CrreK, Oun
County,
Nlsc.
FS Knlqhts
CreeK, Oun
County,
Misc.
FS Knlqhts
CreeK , Oun
County,
Wise.
FS Knlqhts
CreeK, Oun
County,
Misc.
L —
Toxiclty, Experimental
Active Variables,
Ingredient, Controlled
Ppa or Noted Comments
0.78 -- sane as above
(tat
residue)
0.007 (Hhole — sane as above
bodyresldue)
residua)
0.26-1. flii -- saae as above
(fat
residua)
0.53-0.67(f at — same as above
residue)
O.V-0.<>7 (fat -- saae as above
residua)
0.003 -- sane as above
(Hholebody
residue)
0.1-0.8 a* Goldfish Mere exoosed to
(residua) Increasing concentrations of DOT and
Reference
Moubry, et
al <196«),
AMIC-3753
Moubry, 
-------
            ODD
            ODD
            000
           DOO
 Palaemonetes  BCF
 ka4IaVensIs
 (adult)

Daphnla maqna BCF
 (adult)
                                 Pal»emonete«   BCF   —
                                 Kadlakensls
                                 (adult)
                                                                  0.0* (residue)  a*
                                                                  0.0001  (SB3)
                                 0.0001  (SBJ)
                                                                                                                                       JOnnson, at
                                                                                                                                       81(1971),
                                                                                                                                       Johns on, et
                                                                                                                                       al  (10711,
                                Archoplltes   FL    Clear Lake.   316  Cflash
                                Interruotus         Cat.          residue!
                                                                                                    sa>e as above
                                                                                                    saae as above
                                                                   same as above                      Johnson,et
                                                                                                      al  (1971),
                                                                                                      »Hic-3s?o

                                                                    Residue analysis results mainly   Linn, et al
                                                            for TOE in fish, birds, and plankton from, (1969),'
                                                            1959 through 1965 were reported.  The     AMIC-5521
                                                            residues primarily resulted from
                                                            application of DOT to farmland and for
                                                            gnat control.  In some cases, data for a
                                                            single animal In one year Here given.
                                                            Primary emphasis Mas on largemouth bass
                                                            and white catfish.  The general level of
                                                            TOE contamination in birds and fish
                                                            declined markedly from 1958 to 1965.
                                                            This decline correlated directly tilth
                                                            strict limitation by permits  of DOT
                                                            applications during the latter years.
V/l
           000
           000
           000
Orthodon      FL
•ierolepi-
dotua

Pomoxls       FL
nlgromaeulatu
s

•echnophorus  FL
oeel .
                                                                     •HIC-55?!
-------
Comoound
000
000
000
000
000
000
ODD
000
000

Organism
•rehoolltes
Interruotus
Ictalurus
catus
Ictalurus
catus
Lavlnla
exl llcauda
Lenomls
cyanel lus
Leo om Is
cyanel lus
Mlcrooterus
salmoldes
Mlcroot^rus
sal mo ides
Perca
f 1 avescens
Field Field
Study Location
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FL Clear Lake,
Cal.
FLR 93 sampling
Mass.
Toxlclty,
Active
Ingredient,
3,972 (fat
residue)
1.3-1S<» (flesh
residue)
220-2.350 (fat
residue)
less than 1-2
(flesh
residua)
2 (flesh
residue)
103 (fat
residue)
0.2-111 (flesh
residue)
28-1.37 (fat
residue)
0.2«.-5.7

Experimental
Variables,
Control led
or Noted Comments Reference
-- same as above Linn, etal
AMIC-5521
-- same as above Linn, et
-- same as above Linn, et
ANIC-5521
-- same as above Llnn,et al
(1969).
AMIC-5521
-- same as above Linn, et al
(1969),«MIC-
5521
same as above Linn, et al
(1969) , 4MIC-
5521
sane as above Llnn.et at
same as above Linn, etal
(1959),
AMIC-5521
™ Fish Indigenous to Massachusetts Lynan, et a:
and DOT metabolites during 1965-1967. AMIC-3839
                                                                                 Generally there Has  an Increase  In
                                                                                 oestlclde content  during  the  three  year
                                                                                 period.
000
                     Leooals
                                   FLR   93 samollng  0-6.T
                                                                                        same as above
                                                                                                                           Lyaan,  et  at
-------
ODD
DOO
000
090
000
000
ODD
000
OOO
OOO
000
000
gibbosus


Catostomus    FLR



              FLR



              FLR



              FLR
                     letalurus
                     nebulosus
                     Cyprlnus
                     carolo
                     Esox niger
                     Noteniqonus   FLR
                     Senotilus     FLR
                     corporal Is
                                   FLR
                     •aerochlrus
                     Anhlonlltes   FLR
                     ruoestrls
                     Seaotllus     FLR
                     atronaculatus
Mlcrooterus   FLR
dolomieui
                     • losa
                     ps*udo-
                     harengu*
                                   FLR
FunduIus      FLR
het*roelItus
stations In
Mass.

93 saaoling
stations in
Mass.

93 saMoling
stations in
Mast.

93 sanotlnq
stations in
Mass.

93 sampling
stations in
Mass.

93 sanpllnq
stations in
Mass.

93 S4niol inq
stations in
Mills.

93 sainDl ing
stations in
Mass.

93 saopling
stations in
Mass.

93 sampling
stations in
Mass.

93 sanDling
stations In
Mass.

93 saiiDlinq
stations In
Mass.

93 sanoling
stations In
Mass.
                                                       (residue)
                                 8.03-12.5
                                 (residue)
                                                       1.2  (residue)
                                 0.?«.-!.9
                                 (residue)
                                                       0.30  (residue)  —
                                 B.15-2.7
                                 (residue)
                                 D.07-1,.3
                                 (residue)
                                                       (residue)
                                 0.30-10.8
                                 (residue)
                                 o.ie-o.61.
                                 (residue)
0.20-0.90
(residue)
                                                      0.88  (residue)
1.7-3.6
(residue)
                                                                                         sane  as  above
                                                                                         sane  as above
                                                                                         saae  as above
                                                                                         saae  as  above
                                                                                         ja»e  as  above
                                                                                         saae  as  above
                                                                                         saae  as  above
                                                                                         saae  as  above
                                                                                         saae  as  above
                                                                                         saae  as above
                                                                                         saae  as  above
                                                                                         saae as above
                                                                     (19*8),
                                                                     *MIC-3839

                                                                     Lyaan. et al
                                                                     (19M),
                                                                     IMIC-3839

                                                                     Lywsnt et al
                                                                     (1968).
                                                                     »HIC-3839

                                                                     Ly»an. et al
                                                                     <1«68) t
                                                                     *MIC-3839

                                                                     ly»an, etal
                                                                     (1951),
                                                                     4MTC-3SJ9

                                                                     Lyn^nt «t al
                                                                     (1968).
                                                                     •MIC-3839

                                                                     Lynn, et at
                                                                     (196M.
                                                                     »MIC-3839

                                                                     Ly«an, et al
                                                                     Lynan, et al
                                                                     (196S) i
                                                                     •HIC-3839

                                                                     Lyman, et al
                                                                     (19S8><
                                                                     tMIC-3839
                                                                                                              et  al
                                                                                                       (196S).
                                                                                                       •HIC-JSJ9

                                                                                                       lynan,  et  al
                                                                                                       (19fi8) ,
                                                                                                       »MIC-3839

                                                                                                       Lvoan,  et  al
                                                                                                       (1968),
                                                                                                       AMIC-3839
000
                     NotroDls
                                   FLR    93sa«Dllnq   0.8-2.0
                                                                                         saae  as above
                                                                                                                            Lyaan,  et al
-------
CD
Conoounl


000


000


000


ODD


ODD

Organism
cornutus

Roccus
amerlcanus

Pomoxls
nlgro-
maculatus
Leoomls
aurl tus

Phinichthys
atratulus

Cyprlnus
carpio
Field Field
Study Location
stations In
Mass.
FLR 93 sampling
stations in
Mass.
FLR 93 sampling
stations in
Hiiss.
FLR 93 sampling
stations In
Mass.
FLR 9* samollnq
stations In
Mass.
FR St. Lawrence
Plver,
Toxlclty,
Active
Ingredient,
Ppm
(residue)

O.I.-1.3
(residue)

10.7 (residue)


0.1.6 (residue)


O.VO (residue)


0.38(0.1.0 Don
max tissue
Experimental
Variables,
Control led
or Noted Comments Reference
(19MI,
AMIC-3839
-- same as above Lyman, et
(1968) .
AHIC-3839
same as above Lyman, et
(IQftft) ,
AMIC-3839
same as above Lyman, et
( 196(1) .
AMIC-3839
~- same as above Lyman, et
( 1968) ,
AMIC-3839
-- Residues of Onn were measured In Fredeen,
nater, mud, molluscs, and fish during and al (1970)



al


al


al


al


et
,
                                                  Montreal,    residue)
                                                  Canada
                                        after ODD aoollcatlon In 1967.  Samoling  AHIC-53".
                                        DOlnts Here above the point of
                                        aoollcatlon and 10 and 0 DDK
Plver,       max tissue
Montreal,    residue)
Canada

St. Lawrence 0.3X0.5? pp>
River,       max tissue
Montreal,    residue)
Canada

St. Lawrence 0.3S (0.<><>PD*
River,       max tissue
Montreal,    residue)
Canada
                                                                                                 sane as above
                                                                                                 same as above
                                                                                                 sane as above
Fredeen, et
al
(1970) .ACIC-
Fredeen, et
al (1Q70).
AMIC-5J1.
Fredeen, et
al (1978),
4MIC-53".
-------
000
000
000
OOD
ODE IC-1V labelled)
                     F.SOX  luclus    FR
                     Amblootltes
                     Plsldlum sp.  FR
                     Caopeloea sp. FR
                     Sorqhu»
                     ha loans*
L
Uiod-
el
ecosr
staa)
St. Lawrence 0.3S  (1.31
River,       pommax tissue
Montreal,    residue)
Canada

St. Lawrence 0.34(0.25 pp»
River,       max tissue
Montreal,    residue)
Canada

St. Lawrence 0.38  (O.OOlppm
River,       max tissue
Montreal,    residue)
Canada

St. Lawrence 0.38  (O.ZZppm
River,       max tissue
Montreal,    residua)
Canada

             1 IB par A
             (NTEJ
a.e.g.
standard
reference
Mater and
sand
OOE IC-lt labelled)
                     Estlqaene
                     aerea
L
(Mod-
el
eeosy
•torn)
             1 Ibper A
             (IC-NTE>
a.c,q,
standard
reference
Mater and
sand
                                                                                         sane as above
                                                                                         sane as above
                                                                                         same as above
                                                                                         same  as above
                                                                                                                            Fredeen, et
                                                                                                                            at  11970),
                                                                                                                            AMIC-531.
                                                                                                                            FreSeen, et
                                                                                                                            al
                                                                                                                                 1, 4MIC-
                                                                                                                            Fredeen, et
                                                                                                                            al  (1970),
                                                                                                                            •MIC-53*
                                                                                                                            Fredeen, et
                                                                                                                            al  (1970),
                                                                                                                            AMIC-53H
        This snail laboratory model
ecosystem procedure was (level ooed to
study cestlcide blotleqradabl 11 ty and
ecological magnification.  The food-chain
oathwavs In this system were!  (1)
sorqhuw - caterpllier (larva), (2)
caterolller (excreta) - Oeioaonlu", (3)
Oerloqonlun - snail, (i») Estlqmene
(excreta) - diatoms, (5) Diatoms -
plankton, (6)  Plankton - Culex (larvae),
(7) Culex - Ranbusia.  The fish Is the
too of the food chain.  Using
Isotoplcally labeled oesticldes (1
Ib/acre application rate), residues Mere
determined for only selected organises
(snail, mosquito, and fish) and Mater.
ReoroduclblI 1ty appeared to be good.  The
authors state  that the method gives a
good estimation of the potential toxlclty
of pesticides  and their breakdown
products to a  variety of organisms and Is
suitable for computer modeling.

       same as above
Metcalf, et
al (1971),
4MIC-K.95
                                          Metcalf, et
                                          al (1971),
                                          AMIC-1U95
OOE IC-1* labelled)  Physa spp
X
Ufed-
                                                       (residue)
                                                                        .,
                                                                      standard
                                                                                         same  as above
                                                                                  netcalti
                                                                                  al
                                                                                                                                     et
-------
Compound



OOE (C-lf. labelled)




OOE IC-1* labelled)




OOE (C-lV labelled)




OOE CC-1* labelled)




OOE JC-1* labelled)





OOE IC-1* labelled)





Organism



Daoftnla maqna




Culex ololens
qulnque-
fasolatua


Oedogonlum
cardlacum



Gambusla
afflnls



Diatoms
(Kavlcula,
Cosclnodla-
CU3, Dlp-
lonesa, and
Olatoraella}
Protozoa
(Suclearla,
Coleps,
Vortlcella,
and
Paxamaeium)
Field Field
Study Location
al
»eoay-
stea)
L
(Mod-
el
e co ays
tern)
L
(Mod-
el
eeosy
atea.)
L —
(Mod.
el
eeosy
stem)
L * *
(Mod.
el
ecosy
atom)
1
(Mod.
el
ecosy
a tea)

L
(Mod-
el
ecoay
stem)

Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
reference
Hater and
sand
1 Ib per A a.ctq,sfan same as above
(K-NTE) dard
reference
Hater and
sand
169. 9 (residue) a,c,q< same as above
standard
reference
Hater and
sand
1 Ib per A a,c,g, sane as above
(NTE) standard
reference
Hater and
sand
1*9.8 a,c,q1 same as above
(residue) standard
reference
Hater and
sand
1 Ib per A a,c,9, same as above
(NTE) standard
reference
Hater and
sand

1 Ib per A a,c,q, sane as above
(NTEI standard
reference
Hater and
sand

Reference
(1971) ,«MIC-
1*95

"etcalf. et
al (1<»71J,
»NIC-li»95


Metcalt. et
al (1971),
AHIC-1*9S


Hetcalt, et
al (1971) ,
AMIC-1*95


Hetcalf, e»
al (1971),
*HtC-l*95


Metcalt, et
al (1971),
AMtC-ll.95



Me Teal f, et
al (1971),
AMtC-l*95



-------
          Dor IC-l* labelled)
Rotirera      L
(Aaplanchnop-  (Hod.
us, Kotomat-  el
t*, Buclarla, ecosy
Scardlum)     stem)
          DOC  IC-lfc  labelled)   Hater
                                             L
                                             (Hod.
                                             el
                                             •COSTS
                                             t«m)
1 Ib per A
(NTEI



0.008
(rasldua)



a,e,q«
standard
reference
water and
sand
«»o.E»
standard
reference
water and
sand
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                                                     Mefcalf, et
                                                                                                                                     •I(1971),
                                                                                                                                     ANIC-H.95
                                                                                                      Metcalf.  et
                                                                                                      al  (19711.
         oor to.o-i
Anquitla      FRl   St. John,    0.5  {residue)
rostrata            N.B., Can.
E
DOC ID.P-I
DOE lo.O-)
oor lo.o-)
DOE ID. 0-1
DOE lo.o-)
not io.o->
OOE lo.o-l
DOC lo.o->
Esox nlqer
Sal»o salar
Clupea
harenqus
Seonber
scoabrus
Mytl lus
edulls
Gadus "Orhua
Urophycls
tenuls
Hlppo-
glossoidea
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
St. John,
N.R. , Can.
St. John,
N.B., Can.
St. John,
N.B., Can.
St. John,
N.P., Can.
St. John,
N.R., Can.
St. John,
N.P. , Can.
St. John,
St. John,
N.R., Can.
0.16 (residue)
0.22 (residue)
0.06-0.21.
(residue)
0.07 (residue)
0.0?(resldue)
0.01 (residue)
0.02 (residue)
0.01 (residue)
        PCB**s were found In hlqher
concentrations than orqanoch)orine
pesticides In all fish analyTrrt.  Th*
authors point out that PCB Is less toxic
In an acute sens* than organochlorlnes,
that little Is Known of sublethal PCB
effects, and that More Knoxtedqe of PCB
distribution and effects Is needed.

       sane as above
                                                                                                  sane as above
                                                                                                  saae as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  save as above
                                                                                                  sane as above
                                                                                                                                     Zltko(1971),
                                                                                                                                     AMIC-3715
                                                                                                      7ltKo
                                                                                                      (1<»71>
                                                                                                      371S

                                                                                                      ZltHo
                                                                                                      (1971)
                                                                                                      3715

                                                                                                      3Tltho(1971)
                                                                                                                                     4MIC-371S
                                                                                                                                     371S
                               Dlatessoldes
                                                                                                      AMIC-3715

                                                                                                      Zltko
                                                                                                      C1971).
                                                                                                      AMIC-3715
          DOE lO.D-t
                               Sebastodes    FRL
                                                   St.  John,
                                                                trace
                                                                                                  sane as above
                                                                                                                                     71tko(1971),
-------
>
Coaoound

ooe

ooe
ooe
ooe
ooe
ooe
ooe
one
one
ooe
ooe
Organise
aarlnus
Carp

Channe 1
catfish
Radhors*
sucker
Gizzard shad
Spotted
sucker
Blueqltls
Redbreast
sun fish
Striped
aullet
Blue catfish
Dock bass
Freshwater
drua
Field
Study

FRL

FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
Toxlclty, experimental
Active Variables.
Field Inqradlent, Controlled
Location Po« or Noted
N.fl., Can. (residue)
NIsc. states 0.03-2.93 —
residue (SB)

Misc. states 0.0<>-<>2.3
residue (SB)
Hlsc. states 0.03-0.36
residue (SB)
Hisc. states 0.27-1.5",
residue (SB)
Hlsc. states 0.29-0.1.5
residue (SB)
Misc. states O.Dt-O.Bl
residue (SB)
Misc. states 0.02 residue ~
(SB)
Misc. states O.OR-<,.55
residue (SB)
Misc. states 1.87 residue
(SB)
Misc. states 0.08-0.60 —
residua (SB)
Misc. states 0.26 residua —
(SB)
Coaments

saae as above

saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
siae as above
saae as above
saae as above
saae as above
Reference
•HIC-3711
Henderson,
et al
11,07
Henderson,
et al (1971),
»MIC-1<»07
Henderson, et
al (1971),
Henderson,
et al (1971),
• 1IC-11.07
Henderson,
et al I19'l>,
»MIC-1<»07
Henderson,
*MIC-1'»07
Henderson,
et al (1971),
Henderson,
etal (1971),
Henderson,
et 3IC19M),
«MIC-1<»07
Henderson,
MIC-H.07
Henderson,
et al 11971),
AMIC-1407
-------
         OOE
         OOF
                              Bloater
                                            FRL   Misc.
                                               states  l.OT-3.52
                                                       residue  CSB)
                     lake          FRL
                     unite*Ish
                    Misc. states  0.3* residue
                                  (SB)
                                                                                                 sane as above
                                                                                                 sane as above
Henderson et
aidant,
»MIC-1<«07

Henderson,
etal  (1971),
         OOE
                              lake trout    FRL   Misc.
                                               states  0.0*-fl.98
                                                     •  residue  (SB)
                                                                                                 sane as above
                                                                                                       Henderson,
                                                                                                            (1171),
K
         OOE
        ooe
OOE
        OOF
                              HMte crapple FRL   Misc.
                                               states 0.03-9.23
                                                      residue  (SB)
                     Biqaoutn      FRL
                     buttalo
                     Saatlnouth    FRL
                     buffalo
                              Flath«ad       FRL
                              catfish
                                                  Misc.
                          states 0.19-0.62
                                 residue  (SB)
                    Misc. states O.V6 residue
                                 (SB)
                                         Misc. states 0.82 residue
                                                      (SB)
                                                                                                 sane as above
                                                                                                 sane as above
                                                                                         saae  as  above
                                                                                                 same as above
                                                                                                       Henderson, et
                                                                                                       • I  (19711,
Henderson, et
at
Henderson, et
al 11971).
»Mic-i«.n7

Henderson,
etal  (1971).
        OOE
                              Goldeye        FRL   Misc.
                                               states 0.03-0.29
                                                      residue (SB)
                                                                                                 same as above
                                                                                                       Henderson,
                                                                                                       et  al tl<)71),
                                                                                                       »MIC-1<»07
        DOE
        oor
        ooe
                              Hal I eye
                              Sauaer
                                            FRL   Misc.
                                               states 0.05 residue
                                                      (SB)
                                   FRL   Misc. states 0.36 residue
                                                      (SB)
                              Flannelaouth  FRL   Misc.  states 0.13 residue
                              sucker                           (SB)
                                                                                                 sane as above
                                                                                                 same as above
                                                                                                 saee as above
                                                                                                       Henderson,
                                                                                                       et  al
                                                                                                       1*07

                                                                                                       Henderson, et
                                                                                                       al (1971),
                                                                                                       4MTC-H07

                                                                                                       Henderson, et
                                                                                                       al  (1971),
                                                                                                       AMIC-1487
        ooe
         ooe
• lack
bullhead
                                   FRL   Misc. states 0.03-0.0<>
                                                      residue (SB)
                     tthlta bass    FRL   Misc. states 0.13 residue
                                                      (SB)
                                                                                                 saae as above
                                                                                                 sane as above
Hendersor»»et
al (1971),
»MIC-1*07

Henderson,
et al(1971),
-------
Conoound

OOE
OOE
OOE
OOE
OOE
OOE
OOE
OOE
DOE
OOE
OOE
Orqanls*

Black crapple
Larqescale
sucker
Saul mouth
bass
Northern
squaii fish
Chlselnouth
Klanath
sucker
RalnboH trout
Brldqellp
sucker
•rctlc
qrayl Ing
found
•hltef Isn
Lonqnose
sucker
Toxlelty, Experimental
Active Variables.
Field Field Ingredient, Controlled
Study Location Ppa or Noted

FRL HIsc.
FRL Misc.
FRL HIsc.
FRL Misc.
FRL HIsc.
FRL HISC.
FRL Misc.
FRL MISC.
FRL HIsc.
FRL MISC.
FRL HIsc.

states 0.40-0.94
residue (SB)
States 0.12-0.47
residue (SB)
states 0.30-0.94
residue (SB)
States 0.48-1.87
residue (SB)
states 0.14-0.70
residue (SR)
states 0.02 residue
(SB)
states 0.08-0. SO
residue (SB)
states 0.15 residue
(SB)
states 0.25 residue —
(SB)
states O.Z7 residue
(SB)
states 0.01-0.94 ~
resldue (SB)
Comments

saae as above
saae as above
saoe as above
sane as above
save as above
sane as above
saae as above
saae as above
sane as above
saae as above
saee as above
Reference
•MIC-1407
Henderson.et
at (1971),
*MIC-I497
Henderson, et
al (1971),
•MIC-1407
Henderson, et
al (l«7l).
Henderson, et
a) I197H,
•NTC-1407
Henderson,
etal Ctfl'l),
•NIC-14D7
Henderson,
etal (1971),
•MIC-14B7
Henderson, et
al (1971),
•WIC-1497
Henderson, et
al (1971),
•MIC-1407
Henderson,
etal (1071),
•MIC-1407
Henderson,
etal 11971),
•MIC-1407
Hen Person, et
al (14711,
•HIC-1407
-------
OOE
                     WMt« sucker   FRL    Misc.  states 0.05-1..8?
                                                       residue  (SB)
DOC
                     Yellow perch  FRL    Misc. states  0.03-2.1.1
                                                       residue  (SBI
                                                                                                   The  Bureau  of Sport Fisheries
                                                                                          continued  Its  fish  Monitoring orogra« by
                                                                                          collecting 147 composite  fish sanoles
                                                                                          fro*  50  nationwide  monitoring stations
                                                                                          durlnq the fall ot  1464.  Fish were
                                                                                          analyzed for residues of  11
                                                                                          orqanochlorlne Insecticides, llplds. and
                                                                                          PCB-s.

                                                                                                 same  as above
                                          Henderson.
                                          et al
                                          •1971).
                                          1MIC-IV07
                                                                                                                                    Henderson,
                                                                                                                                    etal  (19T1),
r
Ml
OOE
OOE
DOE
OOE
DOE
OOE
                     Chain
                     pJeKerel
                                            FRL   Misc. states 0.06 residue
                                                               CSS)
                     Mhlte catfish FRL   Misc. states  0.38-0.86
                                                       residue  (SB)
                     Mhlte perch   FRL   disc, states 0.6«.-10.9
                                                      residue  (SBI
                     Goldfish
                                   FRL   Misc. states 1.Z4 residue
                                                      (SBI
                     Puaptilnseed   FRL   Misc. states 0.33 residue
                                                      
-------
   Compound
Field  Field
Study location
Toxlcity.
Active
Ingredient,
  Pom
Experimental
Variables,
Controlled
or Noted
                                                                                                  Comments
                                                                                                                            Reference
 ODE
 DOE
 oor
 DOE
 ODE
 ODE
ME
                      Slat Is so.    FS
                      (larvae)
                      Gawmarus so.  FS
                      Salvellnus    FS
                      fontlnallt
                      Scootllus     FS
                      atromaeulatus
                      Cottus bairdl FS
                      Rhlnlchthys   FS
                      atratulus
                     Enqraulls     FH
                     •ordax
      Knlqhts
      CreeK, Dun
      County,
      Wise.

      Knlqhts
      Creek, Oun
      County,
      Misc.

      Knlqhts
      Creeh , Dun
      County,
      Misc.

      Knlqhts
      Creek, Oun
      County,
      Misc.
      Knlqhts
      CroeK,
      County,
      MlfSC.
                                                 Oun
0.005
(Hholebody
residue)
                                                       O.OKwhole
                                                       bodyresldue)
                                                       reaidua)
0.3-l.Mfat
residue)
1.0Z-1.53(fat
residue)
                                                       0.6-0.7 (fat
                                                       residue)
                                              0.011-0.075 pom and 0.003-0.006 ppm
                                              dleldrln were found In debris samples.
                                              nesoite limited control  data, residue
                                              analyses Indicated that  contamination of
                                              the environment studied  xas limited.

                                                     same as above
                                                                                         same as above
                                                                                         same as above
      Knlqhts      1.92(fat
      CreeK, Oun   residue)
      County,
      Misc.

     Pacific       0.06-0.17(res
     Northwest     Idue)
     Coast, Grays
     Harbor,
     Mash.
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                     Houbry, et
                                                     al
                                                                     Noubry, et
                                                                     a I (1468),
                                                     Houbrvt et
                                                     a I  (1968),
                                                     Houbrv, et
                                                     al  (1468),
                                                                     Houbry, et
                                                                     al  (1«6«),
                                                                     Houbry, et
                                                                     at  (1<>68>.
                                                                     AHIC-3753
                                   Pesticides  from  the  Columbia      Stout
                          River  Into  Puget  Sound apparently          11968),
                          contaminated  fish const It ut inn commercial  «NIC-378I>
                          catches  in  Pacific  Northwest waters.
                          Residues In these marine products  were
                          substantially  lower than the FDA
                          tolerance for  beef  (7 pom).   Fish  from
                          locations near the  mouth of  the Columbia
                          River  had higher  pesticide content than
                          ones caught farther away.
-------
                                          Hash.
DOE
our
OOE
ODE
DOE
ooe
DOC
ODE
OOE
Sohastodes FM
f 1 av 1 -Jus
Sehastodes FM
ftavlfius

Platlehthys FM
stet latus
Gadus FM
•acroceohalus
Cancer FH
Cancer FM
•aqlster
Parophrys FM
vetulus
Herlucclus FM
eroductus
Herlucclus FM
oroductus
Paclf Ic
Northwest
Coast,
Hecate
Strait. B.C.
Paclf Ic
Northwest
IlMaco,Wash.
Pacific
Northwest
Coast,
Rlalne,
Hash.
Pacific
Northwest
Coast,
Blalne.
Pacific
Northwest
Coast,
destruction
Island,
Hash.
Paelf Ic
Northwest
Coast,
I)wacor
Hash.
Pacific
Northwest
Coast ,
Rlalne,
Hash.
Pacific
Northwest
Coast ,
Sarasota
Passage.
Hash.
Pacific
Northwest
0.07-0.08
(residue)
(residue)

O.OZ(resldue)
0.01 (residue)
0.039(resldue>
0.03-0.0e  as above
                                                                                         sane  as above
                                                                                        sane as above
                                                                                        sane as above
                                                                                        saae as above
                                                                                        sane as above
                                                                                        sane as above
                                                                                                                           Stout
Stout
(19*8),
Stout
 (1968).
AMIC-3784
Stout
 (1968),
AMIC-37BI.
Stout
(19681,
Stout
(1968) ,
                                                                                                                           Stout
Stout
(1968),
«MIC-378*
Stout
(1968).
-------
Compound

ODE
DOE
DOE
oor
DOC
DOC
ODE
Organism

Her lucclus
produc tus
Her lucclus
produc tus
(f Ishmeal)
Sebastodes
alutus
Carasslus
auratus
Trlturus
erlstatus
Rana
temporarla
Daphnia maqna
(adult)
Field Field
Study Location
Coast t Fort
Susan, Wash.
FH Pacific
Northwest
Coast, Caee
Foul Heather,
Ore.
FN Pacific
Northwest
Coast,
Aberdeen,
Wash.
FH Pacific
Northwest
Coast.
Hecate
Strait, B.C.

L —
L
BCF —
Toxlclty,
Active
Ingredient,
Pon

0.07(resldue)
O.Z7 (residue)
0.01 (residue)
fc.7-8.2
(residue)
O.Z3-0.fH
(residue)
0.001-0.01
•icrogram
(residue)
l.S (residue)
Experimental
Variables,
Control led
or Noted Comments

same as above
sa.«e as above
sane as above
a* Goldfish were exposed to
Increasing concentrations of DOT and
residues determined after 21 days of
exoosure* Host DOT ha*1 been converted to
ODE. Phenobarital had no significant
effect on Insecticide residues.
— DOT caused hyperact Ivlty In
exoos'ed tadpoles. This caused Increased
caoture lunges of newts thus Increasing
the predatory efficiency of the newts.
DDT had no apparent effect on the newts.
~ save as above
a* Magnification of DDT and Aldrln
taqqed with C-l,100 depending on the species were
Reference
4MIC-378I.
Stout
(19M).
ANIC-37**
Stout
(19681,
AHIC-378*
Stout
(196S),
•MIC-378*
Young, etal
(19711 ,
AHIC-3796
Cooke
(1971) ,
ANIC-381*
Cooke
(1971),
AHIC-3SH
Johnson, et
al
(1971), AMIC-
3830
found for DOT, and 22,800 to 1 ".1,000 for
Aldrln.  narked degradation of DDT as
determined by analysis for DOT
metabolites occurred.  The authors
-------
          DOC
                               Gaonarus
                               faselatuv
                               lalultl
                                             BCF   —
                                                                0.* (residue)   a*
                                                                                           conclude that aquatic Invertebrates
                                                                                           Influence quality and quantity of
                                                                                           Insecticide residue passed via the fish
                                                                                           food chain.

                                                                                                  saae as above
                                                                                                      Johns on v et
                                                                                                      at
                                                                                                      (1971). AKIC-
                                                                                                      3830
          DOE
          09E
Palaeaonetes  BCF
kadlakensis
(adult)
Hexaqenla
bltineata
(nyaph)
                                             BCF   —
                                                                0.7 (residue)   a*
                                                                I.I. (residue)   a>
                                                                                                  saae as above
                                                                                                  saea as above
                                                                                                      Johnson, et
                                                                                                      al (1971),
                                                                                                      Johnson, et
                                                                                                      al
                                                                                                      (19M)
t
§
          OOF
          ooe
Isehnora
vertically
Inaiadt
                                             BCF   ~
Llbetlula sp. BCF
Inniadt
                                                                8.2 (residual   a*
                                                                O.OZ (residue)  a*
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                      Jchnson,
                                                                                                      al
                                                                                                      3820

                                                                                                      Johnson, et
                                                                                                      al (19711,
                                                                                                      4HIC-3*?1)
          ooe
ChlrononuS    8CF
sp. I larval
                                                                0.1 (residue)   »•
                                                                                                  saae as above
                                                                                                      Johnson, et
                                                                                                      al
                                                                                                                                     38ZO
          ooe
Daohnla vaqna BCF
(adultt
                                                                0.0001 (SB3)    a*
                                                                                                  sane as above
                                                                                                      Johnson,et
                                                                                                      al  (1971),
          ooe
          DOC
          ooe
          ooe
                               Ganearus
                               fasclatus
                               (adult)
                                             BCF   ~
Palaenonetes  BCF
kadlakensls
(adult)
Hexaqenla
blllneata
(nynoh)

Ischnura
vertical Is
(naiad)
                                             BCF   —
                                             BCF   ~
                                                                0.0001 ISB3)    a»
                                                                0.0001 (SB3)    a*
                                                                0.0001 (SB!)    a*
                                                                0.0001 (SB3)    a*
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                      Johnson,«t
                                                                                                      al  (19711,
                                                                                                      a«IC-3S20

                                                                                                      Johnson,«t
                                                                                                      al  (1971),
                                                                                                      AHIC-3820

                                                                                                      Johnson,et
                                                                                                      al  (1971),
                                                                                                      4MIC-3823

                                                                                                      Johnson, «t
                                                                                                      al  (1971),
                                                                                                      »MIC-38?0
-------
Compound
OOF
DOE
ODE
Organise
Llbellula sp.
(naiad)
Chlronomus
sp. (larva)
Hlcropterus
Field Fl«ld
Study Location
8CF
BCF —
FL Clear Lake,
Toxlclty,
Active
Inqredlent.
PD«
0.0001 (SB3)
0.0001 (SS3)
0.3-9 (flesh
Experimental
Variables.
Control 1 ed
or Noted
a»
a*
—
Comments Peference
sane as above Johnson, et
al (1971),
ANIC-3820
same as above Johnson, et
al (1071),
AMIC-382D
Residue analysis results mainly Linn, et
OJ
o
         ODE
                               Mlcropterus   FL
                               sal no Ides
Clear Lake,
Cal.
82 Itat
residue)
                                        tor TDF In fish, birds, and olanhfon fron AL(1969),
                                        19S9 throuqh 1965 Here reoorted.  The     AHIC-5521
                                        residues urlmarlly resulted Iron
                                        aoollcatlon of DOT to Tarmland and Tor
                                        gnat control*  In some cases* data for a
                                        slnqle animal in one year- xore qlvcn.
                                        Primary emphasis was on larqemouth bass
                                        and Hhlte catfish.  Th«. general level of
                                        TOE contamination In birds and fish
                                        declined markedly from 195ft to 196S.
                                        This decline c-prrelated directly with
                                        strict limitation by Demits of DOT
                                        apollcatlons durlnq the latter years.
                                                                                                  same as above
                                          Linn, et al
                                          (19691 .AMIC-
         DOE
         OOE
          OOE
          DOE
                               Aechmophorus  FL
                               occidental Is
                               Larus sop.    FL
                               Larus         FL
                               del attar ensls
                               Perca         FLR
                               llavescens
Clear Lake,
Cal.
                                                   Clear Lake,
                                                   Cal.
Clear Lake,
Cal.
93 samolIng
stations In
Mass.
33-3,360 (tat
residue)
             300-<»OZ
             (residue)
9?-2700 (fat
residue)
0.35-3.6
(residue)
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
        Fish Indiqenous to Massachusetts
freshwater streams Here analyzed for DOT
and DOT metabolites durinq 196S-1967.
Generally there Mas an Increase in
pesticide content during the three year
period.
                                          Linn, et
                                          AL(l<"i9>,
                                          AMIC-55?!

                                          Linn, et at
                                          11969),
                                          AMIC-55?!

                                          Linn, et al
                                          (1969),A1IC-
                                          5521
Lyman, et
(1968),
AMIC-3S39
                                                                                                                                               al
-------
r
H
U)
         ODE
         DOE
         OOF
         DOC
         one
DOE
                     Ltoomls
                     qlbhosus
                              Catostomu*
                              eownersonl
                               Ictalurus
                               nebulosus
                              Cyprlnus
                              carplo
                              ESOK nlqer
                                            FLR
                                            FLR
                                             FLR
                                            FLR
                                            FLR
Not*nlqonus   FLR
ervsolvueas
93 sanpl 109
stations In
Mass.

43 sanollng
stations In
Mass.

93 sane) Ing
stations In
Mass.

93 sanding
stations In
Mass.

93 saniDl Ing
stations In
Mass.

93 sa»Dl Inq
stations In
                                 0.16-3.9
                                 fresldue)
                                                       (residue)


                                                       D.9 (residue)
                                                       1.6-U.8
                                                       (residue)
                                                       o.g
-------
           Compound
ro
         DOE
         DOC
         DOE
         OOf
         00r
         OOE
         OOC
        OOF
Organism
Notrools
cor nut us
POCCUS
amerlcanus
Pomoxls
nl£po~
•teulatus
Fundulus
dlaphanu
Notropls
ana tost anus
Leoomls
aur Jtus
Phlnlebthys
atratulus
Cvprlnu*
carple
Field
Study
FLR
FL*
FLR
FLR
FLR
FLR
FLR
FR
Field
Location
93 sampling
stations In
Mass.
93 sampling
stations In
Mass.
93 sampling
stations In
Mass.
93 sampling
stations In
Mass.
4J sampling
stations In
Mass.
93 sampling
stations In
Nass.
93 sampling
stations In
Pass.
St. Laurence
Plver,
Toxlclty,
Active
Ingredient,
Pom
0.50-2.6
(residua)
tt.3k-l.it
(residue)
1.9* (residue)
2.35 (residue)
0.53 (residue)
O.it6 (residue)
0.*8-0.50
(residue)
0.36(0.32 ppm
max tissue
Experimental
Variables,
Controlled
or Noted Comments
— same as above
same as above
™ same as above
~ same as above
same as above
same as above
same as above
-- Residues of DDO Mere measured
Hater, mud, me II uses, and fish during
Reference
lyman, et al
(1468),
AMlC-^839
Lynan, et al
(146*),
AMTC-3839
Lyman, et al
(1958).
AHIC-383<»
UVSP, »t at
(J968),
AMIC-3S39
Lyman, et al
(19&8),
AHIC-3839
Ly«an,et al
(1968) ,
AHIC-S839
Cyan, et al
(14<>«),
' AMIC-3839
In Fredeen, et
and al (1470) ,
                                                  Montreal,    residue)
                                                  Canada
                                       after 000 application  In  1967.  Sampling  ANIC-53fe
                                       points  »<>re  above  the  oolnt of
                                       application  and 10 and <»S mi doMnstream.
                                       Resllues from unKnoHn  sources Here
                                       detected uostrean.  Downstream residues
                                       Here more than tMice those obtained
                                       upstream (0.156 versus 0.369 ppm).  The
                                       highest concentration  In  an Individual
                                       fish was 1.81 ppm.
         oor
         ooc
                              Amelurus
                              nebulosuv
                              P«rca
                              flavescens
                                            FR
                                            FR
St. Lawrence 0.38(0.12 ppa
Plver,       max tissue
Montreal,    residue)
Canada

St. Lawance 0.38 (O.Olppm
River,       max tissue
Montreal,    residue)
Canada
                                                                                                 same as above
                                                                                                 saae as above
Fredeen, et
al (1470).
ANIC-53i»
Fredeen, et
al (1970),
•NIC-53*
-------
         DOE
         DOE
         OOE
         ooe
         OOf
                              Esox  luclus    FR
tebloollte*
rupestrl*
                                             FR
                              PlsMlum sp.  FR
                              Caeoeloma sp. FR
                              Catostomus
                              Connerson I
                                            FR
h
to
         DOT (C-l* labelled)  Oaphnla maqna BCF
                              (adult I
 St. Lawrence  0.38  (0.<»3
 River.        ppmmax  tissue
 Montreal,     residue)
 Canada

 St. Laurence  8.3*10.05 ope
 River,        max  tissue
Montreal,    residue)
Canada

St. Laxrence 0.38 (0.0>iDDa
River,       max tissue
Montreal,    resldu)
Canada

St. Lanrenee 0.38 <0.09pom
River,       «ax tissue
Montreal,    residue)
Canada

St. Laxrence 0.38(0.3? op*
River,       eax tissue
Montreal,    residue)
Canada

—•           6.7-9.2
              (residue)
         DOT  (C-lt labelled!   Culex plotens RCF   —
                              (larva)
         DOT tC-lt labelled)   Daphnla oaqna BCF   —
                              (adultl
                                                               13.9 (residue)   a*
                                                               0.0001 (SB3)     a*
                                                                                                  same as above
                                                                                                  saae as above
                                                                                                 saxe as above
                                                                                                 same as above
                                                                                                 same as above
                                                                    Maqnlf(cation of DOT and Aldrln
                                                            taqqed xlth C-IU occurred rapidly.
                                                            Bloloqlcal magnification factors of ?900
                                                            to 1ft, 100 dependlnq on the species nere
                                                            found tor DOT, and ?Z,ftOO to 11.1,000 for
                                                            Aldrln.  Marked deqradatlon of DOT as
                                                            determined by analysis for DDT
                                                            metabolites occurred.  The authors
                                                            conclude that aquatic invertebrates
                                                            Influence quality and quantity of
                                                            Insecticide residue passed via the fish
                                                            food chain.

                                                                   same  as above
                                                                                                                                     Fredeen,  ef
                                                                                                                                     al  (1970).
                                                                                                                                     Fredeen,  et
                                                                                                                                     al
                                                                                                      Fredeen,  ef
                                                                                                      al  (1970),
                                                                                                      Fredeen,  et
                                                                                                      al  (1970),
Fredeen, ei
al
(1970),^TC-
53",

Johnson, er
  al  (1971),
«HIC-38?0
                                                                                                 seme as above
                                                                                                     Johnson,«t
                                                                                                     al  (1471),
                                                                                                     4HTC-38ZO

                                                                                                     Johnson,*t
                                                                                                     al  (1971),
         DOT (C-lt labelled)   Cammarus      BCF   —
                              tasclatus
                              (adult)

         DOT (C-l* labelled)   nrconeetes    BCF   —
                              nals (adult)
                                                               0.0001 (SH3)     a*
                                0.0001 (SB3)    a*
                                                                                                 same as above
                                                                  same as above
                                                                                  Johnson,*t
                                                                                  al (1971),
                                                                                  4HTC-JS20

                                                                                  Johnson,et
                                                                                  al (1971),
                                                                                  Amc-3820
         DOT (C-1V labelled)   P«l»e«onetes  BCF
                              kadlakensls
                              (alult)

         DOT «C-1* label led!   Hexaqenla     RCF
                              blllneata
                                                               0.0001 (SB3)     a*
                                O.OOOKSB3)     a*
                                                                                                 saae as above
                                                                  saaa as above
                                                                                  Johnson, et
                                                                                  al  (1971),
                                                                                  AHT.C-3B20

                                                                                  Johnson,et
                                                                                  al  (1971).
-------
Compound

DOT (C-l* label ledl
DOT (C-m labelled)
DOT (C-l«. labelled!
DOT (C-l* labelled)
DOT (C-l* labelled)
DOT (C-l* labelled)
DOT (C-l* labelled)
DOT (C-l* labelled)
Field Field
Oraanlsm Study Location
(nynoh)
Slphlonurus BCF
sp (nymph)
Ischnura BCF —
vert leal Is
Inalad)
LI Del tula sp. BCF —
(naiad)
Chlronotus BCF —
sp. (larva)
Cut ex Plolens BCF
(larva)
Gavmarus BCF ~
faselatus
(adult)
Orconectes BCF —
nals (adult)
Pala««on«tes BCF —
kadlakensls
(adult)
Toxlclty,
Active
Inqredtent,
Pp.

0.0001 ISB3)
O.OOOKSB3)
0.0001 (SB3)
0.0001 (SB3)
0.0001 (SB3)
1.3-1.7
(residue)
O.Z (residue)
0.3-0.5
(residue)
Exo«rt««ntal
Variables.
Controlled
or Noted Comments

a* same as above
a* sane as above
a* same as above
a* same as above
a* same as above
a* same as above
a* same as above
a* same as above
Reference
AMTC-382H
Johnson, et
al (1971),
ANrC-3»»0
Johnson, et
al 11971),
AMIC-7S70
Johnson, et
al (1971),
*HIC-3«?0
Johnson, et
al 11971),
»MIC-*»21
Johnson, et
al (1971),
»MIC-3»?0
Johnson, et
al (1971),
*HIC-X8'9
Johnson, *t
al (1971),
*NIC-3B?0
Johnson, et
al (1971),
4HIC-38ZO
-------
        DOT  IC-1%  labelled)  Hexagenla      BCF    --
                             blllneata
                             (nymoh)

        DOT  IC-1»  labelled)  Slphlonurus    BCF    —
                             sp.  (nvmoM
        DOT (C-l»  labelled)  Ischnura      BCF    —
                             vertical Is
                             (naiad)

        DOT IC-lt  labelled)  Libel lula sp. BCF
                             
                    0.3-1.7
                    (residue)
                    1.1  (residue)
                    0.2-0.1.
                    (residue)
                    O.OU-0.1
                    (residue)
                                  save as above
                                                      sa*e  as above
                                  same as above
                                  same as above
                                                                     Johnson, et
                                                                     at  (19711,
                                                                     »MIC-3»?0

                                                                     Johnson, et
                                                                     al  (107U,
                                                                     Johnson, et
                                                                     al  (1971),
                                                                     Johnson, et
                                                                     al (1971),
        DOT (C-t* labelled)  Chlronomus
                             sp. (larva)
        DOT IC-lt labelled)  Estl
-------
ON
Compound
DOT IC-1* labelled)





DOT IC-1* labelled)




DDT IC-1* labelled)



DOT IC-1* labelled)




DOT IC-1* labelled)




DDT IC-1* labelled)




DOT IC-1* labelled)




DOT IC-1* labelled)




Orqanlsa
Protozoa
(Huclearla,
Coleps,
Vortieella,
and
Paramecium)
Rotifers
(Aaplanchnop-
ua, Notomat-
ta, Euclarls,
Scardlum)
Hater



Physa spp




Oaphnla naqna




Culex plplens
quinque-
faseiatua


Oedogonlue
cardlecue



Ca.busla
•ffinls



Field Field
Study Location
I.
(Mod-
el
a co ay
stem)

T. «
(Hod-
el
a COST
a tan)
L
(Mod-
el
ecoar
•tea)
L
(Mod-
al
•COST
•tern)
L —
(Mod-
el
ecogr
stem)
I* •—
(Mod.
el
ecosys
teal)
L "*"
(Mod-
el

•tea?
I ~
(Mod-
el
•OOST
•teal)
Toxlcity.
Active
Inqredienf ,
Ppi»
1 tb per A
(NTE)




1 Ib per A
(NTE)



0.00*
(residue)


?e.9 (residue)




1 Ib per A
IK-NTCI



8.9(resldue)




1 Ib per A
(NTE)



5*. 2 (residue)




Experimental
Variables.
Control led
or Noted com«ent*
a.c.q, same as above
standard
reference
Hater and
sand

a.c.q, sane as above
standard
reference
Mater and
sand
»,c,g, sane as above
standard
reference
water and
sand
a.c.q, sa»e as above
standard
reference
Hater and
sand
a,c,q, sane as above
standard
reference
Hater and
sand
a,c,q, save as above
standard
reference
Mater and
sand
a.c.q. sea* as "above
standard
reference
Mater and
sand
a.c.q. see* es above
standard
reference
Mater end
•end
Reference
Hetcalf, et
al (1971).
AMIC-1'»9';



Metcalf, et
81(1971),
AMIC-l"»9S


Metcatf, et
al (1971).
AIIC-1't'W

Metcalf. et
al (1971) ,
AMIC-U95


Metcalf, et
al (19711.
AMIC-l*^


Hetcalf, et
al (197H,
ANIC-1*95


Hetcalf. et
81(1971),
ANIC-l'.OT


Hetcalf. et
el (1971).
•mc-i*«/s


-------
          DOT IC-l«t labelled)
          DOT JC-1* labelled!
                               (ItavlcuLa,    (Mod-
                               Coaclnodla-   al
                               cua,  Dip-     ecosy
                               lonaaa, and   at«m)
                               Olatoaalla)
                               S»lweI Inus
                               fontin*lls
                                             BCFCM —
H
U)
         ODT    labelled)
         DOT  to,o-»
                                    lInus
                               fontlnal Is
                              Rasbora
                              heteromorpha
                                             BCFCH —
              BCFA
              and
              BSt
         DOT  (olus DOT
         analogs)
LlmnephlI us
rhombleus
I larvae)
                                             FS
                                                                1 Ib per *
                                                                (NTE)
                                  0.000003
                                  (0.0?56ppm
                                  accumulation
                                  120  d)
                                                  a,e.g.
                                                  standard
                                                  reference
                                                  water and
                                                  sand
                                                                                                  sane as above
                                                                                  Metcalf, et
                                                                                  al  (1971),
                                                                                  »HIC-1«.95
                                  0.0US mg  par Kg a
                                  (1.92PPM
                                  accumulation
                                  120 d)
                                   This study was an attempt to
                           evaluate, under laboratory conditions,
                           the relative Importance of food and water
                           as sources of DDT for fish and to relate
                           these observations to natural
                           environments.  To simulate conditions in
                           Lake Michigan, fish were exposed to water
                           containing 3 ctus or minus 0.3 pot ODT,
                           and others were fed 3 plus or minus 0.15
                           ppm DOT (0.01»<< mg/Hq/day) for 120 days.
                           Whole hody accumulations were determined
                           throughout the test by measuring C-l*
                           radioactivity in fish.  The re-suits show
                           that fish accumulated 3.5 percent of the
                           DOT available in the water and 35.5
                           percent of that available in food.  It is
                           concluded that the food chain Is the
                           major source of ODT in fish.

                                  same as above
                                                                                  Hacek, et al
                                                                                  (1970),
                                                                                                                                            et  al
                                                                                                                                     AMIC-8i.li
                                                                0.03  (Tl)
Knights
Creek• Dun
County,Wise.
0.02". (whole
body residue)
a»,c,e,f.          One hundred sixty-four            Alabaster
hard (HH)  pesticides, wettlnq *grn*s» and           (1969),
or         miscellaneous water pollutants shoxed a   AMIC-5U25
SOTTISH)   wide range of toxlcity sosnninq 1? orders
synthetic  of magnitude.  Knowing the toxiclty and
dilution   percentaoe of all co-noonents of a
water, or  formulation did not result in easy
seawater   predictability of the toxiclty of a
for some   mixture of materials.  Sometimes
species    pesticides were most toxic in hard water
           and soiretimes the opposite was true.
           Testing the actual material as sold was
           found to be essential.

                   Samoles of water, silt, bottom    Houbry, et
           debris, bottom organisms, and fish were   al (19681,
           taken In 19fi6 from a creek adjacent to an »»IC-3753
           orchard which had been treated in
           1963-1965 with various chlorinated
           hydrocarbon pesticides.  No resloues were
-------
  Comoound
                       Organism
                                   Field  Field
                                   Study Location
                                 Toxlclty,
                                 Active
                                 Ingredient,
                             Experimental
                             Variable*.
                             Control led
                             or Noted
                                                                                                 Comments
                                                                                                                           Reference
DOT (otus DOT
analogs)
DOT (olu« DOT
analogs)
DOT (olus DOT
analogs)
DOT (otus DOT
analogs)
ODT (olus DOT
analogs)
DOT (olus DOT
analogs)
DOT (olus 01T
analogs)
DOT (olus DOT
analogs)
DOT (olus DOT
analogs!
Stalls sp.    FS
(Iftrvae)
                     Canoarus SO*
SalvelInus
fontlnalls
                                   FS
Senotllus     FS
atromarulatus
                     Cottus balrdl FS
Phlnlchthys   FS
atratulus
Salvellnus    FS
fontinalIs
Semotllus     FS
atromaculatus
                     Cottus balrdl FS
Knlqhts
CreeKt Dun
County,
Misc.

Knlqhts
Creek. Dun
County,
Wise.

Knlqhts
CreeK. Dun
County,Misc.

Knlqhts
CreeK, Oun
County,Wise.

Knlqhts
Creek,
OunCounty,
Hlsc.

Knlqhts
CreeK, Oun
County,Hlsc.

Knlqhts
CreeK, Oun
County,Wise.

Knights
CreeK, Oun
County,Hlsc.

Knlqhts
CreeK,
0.016 (whole
body residue)
                                 0.001-0.013
                                 (whole body
                                 residue)
0.01.2-0.155
(Hhol« body
residue)

0.061-0.076
(whole body
residue)

0.03*«),
amc-3753
                                                                     Moubry, et
                                                                     al  (146ft) ,
                                                                     AMIC-3753
Moubry, et
a I  (14681.
»HIC-3753

Mouhry,et a)
(196S) ,
4MIC-3753

Noufry, rt
al  (19681,
&MIC-3753
Noubry. et
al (1968),
4HIC-3753

Houbry, et
al (11681,
Moubry, et
al (1968),
4MIC-37S3

MouS>ry, et
al (1968),
-------
         DOT to I us DOT
         analogs)
                     Phlnichthys
                     atratulus
DOT fplus 20 percent Rasbora
non-l»nlc            heteromorpha
••ulslfler, 60
percent naphtha)
                                            FS
                                            BCFA
                                            and
                                            8S»
                                          DunCounty,
                                          wise.

                                          Knights      ?.»  (fat
                                          Creek, Oun   residue)
                                          County,Misc.

                                                      0.11  CT2)
                                                                                                                                    AMIC-3753
r
\o
09T (olus ?Q percent Rasbora
non-Ionic            hetero«oroha
eeulsitler, 60
percent naphtha. In
acetonel
                                            BCFA
                                            and
                                            USA
                                                               0.02 (T2)
                                                                      a«,c,e,f,
                                                                      hard (KW)
                                                                      or soft
                                                                      ISW) syn-
                                                                      thattc
                                                                      dilution
                                                                      water, or
                                                                      aeawater
                                                                      for some
                                                                      spedes
                                                                      hard (HW)
                                                                      or soft
                                                                      ISW)  syn-
                                                                      thetic
                                                                      water, or
                                                                      aeawater
                                                                      for some
                                                                      species
                                                                                                 seme as above
                                                           vi et
                                                     a I  (19&»),
        One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water oollutants showed a
Hide range of toxiclty scanning 1? orders
of magnitude.  Knowing the toxiclty and
percentage of all components of a
formulation did not result in easy
predictability of the toxlcity of a
mixture of materials.  Sometimes
pesticides were most toxic In hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.

       same as above
                                                     Alabaster
                                                     (19f-9>,
                                                     Alabaster
                                                     (1964),
DOT lotus ?•> percent Rasbora
           agents)   heteromorpha
                                            BCFA
                                            and
                                            USA
                                                               10.7 (Tl)
         DDT fplus 3 percent
         eaulslfler, *«
         percent naphtha)
                     Vasbora
                     heteromorpha
                                   BCFA
                                   and
                                   BSA
                                                               0.11 CT3)
                                                                      a*,c,e,f ,
                                                                      hard (HW)
                                                                      or soft
synthetic
dilution
water, or
seawater
for some
species

a*,c,e,f ,
hard (HH>
or soft
(SKI
synthetic
dilution
water, or
seawater
-------
Toxiclty.
Active
Field Field Ingredient,
Comoound Organism Study Location Ppm
OOT (Dlus 77 percent fiasbora 8CFA — 8.0 CT3)
China clay, f hetero»orpha andBS
percent calcium A
sul fate)






OOT (olus 77 oercent Pasbora BCFA — 0.001 
or soft
ISH)
synthetic
dilution
Hater, or
seawater
torsome
species
Httc,o,r, same as above
bard (ITW)
or »of t
(SO ayn-
thetlc
water, or
aeawater
for sone
•pecles
a'.c.e.f.K Rloassays conducted
.l.n.and simultaneously Indicated Trot DDT Has
magnesium, considerably more toxic to fathead
sul fates, minnows under static conditions than
Iron. under continuous flow conditions.
calcium Decreasing oxygen and increasing
Reference
Alabaster
(1969).
SMIC-SUZS







Alabaster
C1969).
AMIC-^fcZS






llneer. e
al (1970)
AMIC-5S09



OOT <»,o~->
                     Plm«onales
                     proaelas (3
                     ca)
                                   8CF»  —
greater than
0.0V (tit
a»,c,*.f.h
.l.n.and
maqneslu*,
sul fates.
Iron.
                                                                                 metabolites may have enhanced DDT
                                                                                 toxiclty.  An Identical  study with Endrin
                                                                                 resulted In only sliqhtly higher toxiclty
                                                                                 under continuous flow conditions.
                                                                                 Average pH, oxygen,  and  ammonia nitrogen
                                                                                 nere foltoued throughout the experiments.
                                                                                  The results xere comprehensively
                                                                                 discussed taking into consideration many
                                                                                 contributing factors.

                                                                                        same as above
Llneer, et
al (1970),
AMIC-5509
-------
                                                                                calclu*
         DOT  le.e-t
                              tnqullla
                              r«»trat»
                                            FRL
                                          St.  John,
                                          M.B.,  Can.
                                                                0.29  (residue)   —
f
DOT lo.o-»



DOT 


DOT IO,o"l


DOT Co.D~>
                              FSOK nlqer    FRL    St. John,
                                                   N.n., Can.
                              Saleo salar   FRL   St. John,
                                                  H.R., Can.
                                                                0.08  (residue)  —
                                                                O.oa  (residue)  —
Cluoea
harenqus
                              Scoaber
                              seonbrus
                                            FRL
                                            FRL
St. John,
M • n • f C 8H •
St. John,
N.R., Can.
0.05-0.15
(residue)
0.07 (residue)
—
                              ftasbora       BCF*  ~
                              heteroaorpha  and
                                            BS*
                                                               0.013  (Tl)
                                                                      av,c,e,f,
                                                                      hard  (HH)
                                                                      or
                                                                      SOFT(SW)
                                                                      synthetic
                                                                      dilution
                                                                      •ater, or
                                                                      seawater
                                                                      for son*
                                                                      soeeles
         DOT (0,0", C-t*
         labelled)
                     Gamhusla
                     afllnls
                                            •      ^^
                                                               o.oooo<»i(SBZ)
                                       q)
                                                                     PCR"s  »*r«  found  In  h'lqher
                                                            concentrations than orqanochlorlne
                                                            oestlcldvs  In  all fish  analyzed.  The
                                                            authors  point  out that  PCP Is  less  toxic
                                                            In  an  acute  sense than  orqanochlorlnes,
                                                            that tittle  Is known  of sublethat PCS
                                                            effects,  and that wore  knowledge  of  PC8
                                                            distribution and effects  Is  needed.

                                                                   sane  as above
                                                                                                  sane  as  above
                                                                                                  sane  as above
                                                                                                  sane  as above
                                                                                                                                     •NIC-3715
                                                                                                                                     ?ltko
                                                                                                                                     3715
                                                                                                                                     Zltko
                                                                                                                                     3715
                                                                    One hundred sixty-four
                                                            pesticides, netting agents, and
                                                            •iseellaneous water oollutants showed a
                                                            wide ranqe of toxlclty so*nnlnq 12 orders
                                                            of •aanltude.  Knowinq the toxlclty and
                                                            percentage of all coiioonents of a
                                                            formulation did not result In easy
                                                            predictability of the toxlcity of a
                                                            •Ixture of materials.  Sometimes
                                                            pesticides were most toxic In hard water
                                                            and soiretloes the opposite was true.
                                                            Testlnq the actual material as Sold was
                                                            found  to be essential.

                                                                    DOT-reslstant mosauitofisn were
                                                            collected fro* a cond at Salinas,
                                                            California.  Smaller fish  (100 •,
                                                                                                      AMIC-371S

                                                                                                      Alabaster
Murohy
(197H,
AHIC-180S
-------
"i Plus 20 Rasbors BCFA —
percent o,o~ODT» hetvrooorpha and
BSA






DOT lo,o~, plus 20 Salmo trutta BCFA —
percent o,o"OOT» (alevln) and
BSA







DOT (o,o~, olus 28 Rasbora BCFA ~
pereent o>p**OOT) heteroaorpna and
BSA

o.aoon«.i(o.oi-o a*
.Ob po" Hhole
body residue 2
dl
0.0031 a*,c««.t.
(T2,herd«ater) hard (HH)
or soft
(SH)
«yntnetlc
dilution
water, or
seattater
tor so»e
soecles



0.0005<» •>,€,«, f,
(TZ,soTt«at«r) hard (HW)
or soft
UW) syn-
thetic
water, or
•eavater
for some
•peel e a
0.0035 (T2) a>,e,e.t.
hard (HH)
or sott
(SWI
synthetic
dilution
Hater, or
seaiiater
tor some
species
0.017 IT?) a*,c,e,f.
hard (HH)
or sott
CSHI
sane as above



One hundred sixty-tour
pesticides? wettlnq sqenls, and
miscellaneous vater pollutants showed a
nidi" ranqr ot toxielty soannino 17 orders
of naqnlturte. Knoxlnq the toxlcity and
percentage of all conoonenfs of a
formulation did not result in easy
predictability of the toxlcity of a
mixture of natvrials. Sometimes
pesticides Mere most toxic In hard Hater
and sometimes the ooooslte MBS tru*.
Testlno the actual material as sold Mas
found to be essontl'al.
sane as above








same as above









same as above



Reference
Murohy
(1971).
AMIC-1005

Alabaster
(1969),
AMIC-5^25










Alabaster
(1969).
ANIC-^25






Alabaster
(1969) .
AMIC-SU21;







Alabaster
(I960) ,
AHIC-5<>25

-------
          DOT 
          DOT  (18  percent)
                               heteromorpha
              BCFA  —
              and
              BSA
                                                                0.17  (T2>
VjJ
         DOT
          OUT
                               Fish (not
                               specif Ie-1)
                               Unite sucker  FRL
                                 greater than
                                 0.0001-0.001
                                 (Kl
                                                   disc, states 0.09-2.90
                                                                residue I SB)
synthetic
dilution
water, or
seaMater
tor some
species

a>,c,e. f.
hard  (HU)
or soft
(SH)
synthetic
dilution
xater, or
seaxafer
tor some
soecles
    %
a'.c.e.t•
hard (HH>
orsolt
(SKI
synthetic
dilution
water, or
seaiiater
Tor some
species
                                                                                                   sane as above
Alabaster
(1969),
                                                                                                   saae  as  above
                                                                                         Alabaster
                                                                                         (196r
                                                     AMIC-1056
                                                                                                       Henderson,et
                                                                                                       a I  (1971),
                                                                                                       AHIC-H07
         DOT
                               Redhorse
                               sucher
              FRL   Misc. States t.02-0.25
                                 residue (SB)
                                                                                                  sane  as above
                                                                                         Hendprson,et
                                                                                         al
         DOT
Gizzard shad  FRL   Misc. states 0.13-0.IS
                                 residue (SB)
                                                                                                  same  as  above
                                                                                                                                      Henderscn,
                                                                                                                                      etsl  (1971),
         DOT
                               Spotted
                               sucker
              FRL   Misc. states 0.1<» residue
                                 (SB)
                                                                                                  same  as above
                                                                                         Henderson,
                                                                                         etal  (1171),
                                                                                         AHIC-1I.(I7
-------


1







Coaoound
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Organise
Striped
aullet
Blue catfish
Pock bass
Freshwater
drua
Bloater
Lake
Mhlfeflsh
Lake trout
Mhlte craeola
flleaouth
buffalo
Saaltaouth
buffalo
Flatneatf
catfish
Field
Study
FRL
FRL
FP.L
FRL
FRL
FRl
FRL
FRL
FRL
FRL
FRL
Field
Location
Misc.
Misc.
Hlsc.
MISC.
MISC.
HlSC.
MISC.
MISC.
MISC.
HiSC.
Misc.
states
states
states
states
states
states
states
states
states
states
states
Toxlclty, CxDeriaental
Active Variables,
Ingredient, Controlled
Poa or Noted
0.30-1.12
residue (SB)
O.Ot residue
(SB)
0.06-0.«>9 ~
resldue (SB)
0.31 residue —
(SBI
0.59-1. 80 —
residue (SB)
0.20 residue —
(SB)
0.01-O.VS —
residue (SB)
t. 04-0. 20 —
residue (SB)
n. 11-0. si
residue (SB)
0.50 residue
(SB)
0.6* residue —
(SB)

saae as
saaa as
saae as
saae as
saae as
saae as
saae as
saaa as
saae as
saae as
saae as
Coaaents
above
above
above
above
above
above
above
above
above
above
above
Peference
Henierson,et
al (197t>,
Hen-Jerson,
etal (1971),
«MIC-t«t57
etal U97t),
etal (19711,
*t al (jo'l),
4MIC-1I.07
etal (197H,
Henderson,
etal 119711,
at (19711,
Henderson, et
at (l«7l>.
at (19711,
•HIC-11.07
Henderson, et
al (1471).
AHIC-1407
-------
         DOT
                              Co Move
                                            F»L
                                                  Misc.
                                  0.0?-0.3<.
                                  residua  (SB)
                                                                                                  sane as abov*
                                                                      Henderson,
                                                                      *t s Ml 971),
                                                                      ANIC-11.07
         ODT
                              Hal I eye
                                            FRL   Misc.  states
                                  O.Od-O.ZO
                                  residue  (SB)
                                                                                                  sane as above
                                                                      Henderson,
                                                                      *t al (1971).
                                                                      AM.IC-1«.07
         DOT
                              Sauqcr
                                            FRL   Misc. states
                                  0.18 residue
                                  (S3)
                                                                                                  sane as above
                                                                      Henderson,et
                                                                      31(1971),
                                                                      AMIC-t<.07
         DOT
                              Flannelnouth  FRL
                             . sucker
                                                  Misc. states
                                  0.19 residue
                                  (SB)
                                                                                                  sane as above
                                                                      Henderson,et
                                                                      81  (1171),
                                                                      AMIC-H.07

\n
         DOT
         DOT
        OUT
                              Black         FRL
                              bullhead
                                                  Misc. states
                              Mhl-te bass    FRL   Misc. states
                              Black cr*DDle FRL   Misc. states
                                  0.01-0.03
                                  residue  (SB)
                                  O.?l residue
                                  (SRI
                                  0.22-0.25
                                  residue  (SB)
                                                                                                  sane as above
                                                                                                  same as above
                                                                                                  sane as above
                                                                      Henderson, et
                                                                      al  (1971),
                                                                      Henderson,
                                                                      et al (l«'l),
                                                                      AMIC-IU07

                                                                      Henderson, et
                                                                      al (1971),
                                                                      AMTC-li.97
        DOT
                              Larqescale    FRL
                              sucker
                                                  Misc. states
                                  0.05-0.45
                                  residue  (SB)
                                                                                                  sane as above
                                                                      Henderson,et
                                                                      al  (1971),
                                                                      AN!C-1<.07
         DOT
•>nallnouth    FRL
bass
                                                  Misc.' states
                                                               residue  (SB)
                                                                                                  sa*e as above
                                                                      Henderson»«t
                                                                      al  (1971),
                                                                      ANIC-11.07
         ODT
Northern      FRL
SduaNtIsh
                                                  Misc. states
fl.05-0.10
residue ISB)
                                                                                                  sane as above
Henderson,et
al (1971),
AMIC-1<»07
         DOT
                              Chlselnouth   FRL   Misc. states
                                  0.07-0.09
                                  residue  ISB)
                                                                                                  sane as above
                                                                      Henderson,
                                                                      etal  (1971),
                                                                      AMIC-H07
         DOT
                              Klanath
                              sucker
                                            FRL   Misc. states
                                  0.02 residue
                                  (SB)
                                                                                                  sane as above
                                                                      Henderson,
                                                                      etal  (19711,
                                                                      AMIC-ldO?
         DOT
                              Rainbow trout FRL    Misc.  states
                                  0.03-0.07
                                  residue  (SB)
                                                                                                  sane as above
                                                                      Henderson,et
                                                                      al  (1971),
                                                                      AHIC-H07
-------
CoBoound
DOT
DOT
DOT
f* DOT
H
DOT
DOT
DOT
DOT
DOT

DOT
DOT
Field
Orqanls* Study
Brldq-llp FRL
sucker
•re tic FRL
grayllnq
Pound FRL
whltef ish
Longnose FRL
sucker
Vel low perch FRL
Chain FRL
olckerel
HMte catfish FRL
White perch FRL
Goldfish FRL

Blueqllls FRL
Redbreast FRL
sunf Ish
Toxiclty, Exoerl mental
Active Variables,
Field Ingredient, Controlled
Location Ppm or Noted
Misc. states 0.39 residue —
(SB)
Misc. states 0.21 residue ~
(SB)
Misc. states 0.31. residue
(SB)
Misc. states 0.01-0.10
residue (SB)
Misc. states 0.03-2.56
residua (SB)
Misc. states 0.08 residue —
(SB)
Misc. states 0.21-0.31
residue (SB)
Misc. states 0.63-1.30
residue (SB)
Misc. states 0.65 residue
(SB)

Misc. states 0.0<»-0.2<» —
residue (SB)
Misc. states 0.03 residue — —
(SB)
Comments
sane as above
same as above
same as above
same as above
saee as above
same as above
same as above
same as above
same as above

same as above
sane as above
Reference
Henderson,
etal (1971),
AHic-i'.n''
Henderson,
etal (1971),
SHIC-li.07
Henderson,
etal 119711,
Henrterson.et
al (1071),
AMIC-K.07
Henderson, et
al (1971),
Henderson,
et al (1971),
SMIC-11.C7
Henderson, et
al C197D,
AMIC-1J.07
Henderson, et
al (19711,
Henderson,
et al
1*07
Henderson,
etal (1971),
AMIC-11.07
Henderson, et
al (1971),
-------
 DOT
 DOT
 DOT
 DOT
DOT
 DOT
DOT
DOT
DOT
                      Pumofclnseed   FRL
Largemouth    FRL
bass
Broun         FRL
bullhead
                      Carp
                      Channel
                      catfish
                                    FRL
                                    F«L
                      Gambusla      85*
                      •ftints
                    Misc. states 0.23 rasldue
                                 (SB)
Misc. states O.OS-1.57
             residue (SB)
Misc. states 0.06-0.1.2
             residue ISB)
                    Misc. states 0.01-0.96
                                 residue (SB)
                    Misc. states O.OZ-5.07
                                 residue (SB)
                                                       0.0* pob (SB)
                     Wolffla
                     papullfera
                      Salve IInus
                      tontlnalls
                      (1.15  q>
                                    BCF«  —
                                100  (K)
                                                       7.1,
                      SalvelInus
                      tontlnalls
                                    BCF»   —
                                                       11.9 (Tit)
                             Hunter's
                             medium
                             dllutod
                             1:5
                                                 ae, C,d,
                                                 e,f,l,O,
                                                 aulfato,
                                                 copper,
                                                                       Iron,  and
                                                                       Chronlua
                                                 a*,c,d,
                                                 e.f.l.o,
                                                 sulfato,
                                                 copper,
                                                                                         saute  as  above
                                                                                          sane  as  above
                                                                                         sane  as  above
                                                                                         same  as above
                                                                                         same  as above
                                           Henderson,
                                           et al (19?!) >
                                           AMTC-K.H7

                                           Henderson, et
                                           al (1071),
                                           Henderson, «t
                                           at  (1<»M>,
                                           A--hr    Murohy
period  at  ?(l  C  thin  at •» r.  yt  was shown [1971>,AwiC-
that  only  live  fish  take UP  nOT, that      1*78
uptake  was related to  resoiration rate
and that small  fish  are more efficient
than  larger fish  In  removing PflT from
water.   One Implication of  this  study  is
that  at  warmer  Temperatures  HOT  is taken
up more  rapidly,  thus  suggesting that
thermal  releases be  carefully  controlled.

         All compounds ware harmful  to    Worthley, et
duckweed to aons degree.  Decreased       al (1971),
populations wore iiotoU at non-lethal      AMIC-3233
concentrations and some compounds
(Malathion and e,l\.-D)  caused terstogenle
effects  at concentrations as low as 1 ppm.

         Four  Insecticides were evaluated  Post,  etal
on four  fish species at two  body  weights.  (1971),
 Standard  method bloassay orocedures were AH.IC-181?
followed.   Symotomology was  also
reoorted.   Generally,  toxlclty was
significantly different at the two body
weights, i.e., more  toxic at trie  lower
body weight, except  for Malathion.
well-defined experimental conditions were
said to  result In  truer measurement  of
toxlclty.
                                                                                         sa«e as above
                                                                                  Post, et al
                                                                                  (1971),
                                                                                  AMIC-181Z
                                                                       Iron,  and
                                                                       cltro.-nlum
-------
  Coeaound
            Field  Fl«ld
Orqanlsa    Study Location
                                                      Toxlclty,
                                                      Active
                                                      Ingredient,
                                                        Pp»
Experimental
Variables.
Controlled
or Noted
                                                                                                 Convents
                                                                                                                           Reference
DOT
                      Salvo ctarkl
                      (0.33 0)
                                   BCF»  ~
                                                      B.0001 IT4)
DOT
                     Salvo elarkl  BCFA
                     11.29 q)
                                                      1.37 (TO
DOT
                     Sal mo
                     qalrdnerl
                     10.*1 ql
                                   RCF»
                                                      0.0092 IT4I
                                                                      e,r,l,o,
                                                                      aulfate,
                                                                      copper,
                                                                      manganeae,
                                                                      Iron, and
                                                                      Chromium
                                                                                        sane as above
                                                                                                    Post, et al
                                                                                                    (19M),
                                               8,f,l,0,
                                                                      copper,
                                               Iron,  and
                                               eiiromluai
                                               •0,0, d,
                                               •ff.l.O.
                                               aulfata,
                                               copper,
                                                                      Iron, and
                                                                      chromium
                                                                                        saae  as above
                                                                                        saoe as above
                                                     Post, et al
                                                     (1971),
                                                     •HIC-1S12
                                                     Post, et al
                                                     (19711,
                                                     AMIC-1812
DOT
DOT
ftOT
                     Oncorhynchus
                     kisutch  18.5
                     9>
                     Oncorhynchus
                     kisutch (1.65
                     9>
                                   BCFA  —
                                                      0.011 (TO      a,*.
                                                                                        save  as above
                                   BCFA  —
                                                       0.019
                     Arte*la spp.  L     ~
                               0.00001 and
                               0.000001
                               (sublethall
                                               eopper,
                                               manganese,
                                               iron, and
                                               chromium

                                               a«.e.d,
                                               »»f,ifO«
                                               sulfate,
                                               copper,
                                               nangenase,
                                               iron, and
                                               chromium
                                                                                         saae  as  above
        Arteaia sop oooulations exposed
in 19R6 to the indicated DOT
concentratlons and studied for up to 
-------
 DOT
                      Sebastodes
                      sp.
                                    FO
nor



DOT


DOT


DOT


DOT



DOT



DOT



DOT



DOT



DOT
PanufIrua
Interruotus
Paralabrax
nebulIfer

Anlsofreals
davidsonl
                                   FO
              FO
FO
PlaelOMtapon FO
putenruv
Haliofls
rufeseens
              FO
Strongylocent FO
rotus
franclseanus

Hlnnltes      FO
•uitlruqosls
Haliotls
corrugate
Kellctla
fcelletll
              FO
              FO
Plants fulgae F
and hlahvr
aouatlc
                     Pacific
                     Ocean,  Cal.
                    0.1.6  (liver
                    residue)
                                        bacKqround.   Brine shrlno nauolll  were
                                        apparently most sensitive to  DOT conoared
                                        to older stages.  Cyclic coexistence of
                                        pesticide residue and vulnerable stage of
                                        life cycle Influenced succeeding
                                        generations.

                                                Samples of marine animals  Here    Hunson
                                        collected fro* three locations off the    (1972).
                                        coast of Southern California  and analyzed AMIC-3096
                                        for residues  of chlorinated hydrocarbons.
                                         The data suggest that Kellet~s nhelk
                                        nould be a good Indicator organise for
                                        studying the  regional distribution of
                                        chlorinated hydrocarbons.
      Pacific      0.037 (nusde
      Ocean, cat.  residue)
Pacific
Ocean, Cal.

Pad f le
Ocean, Cat.

Pacific
Ocean, Cal.

Pacific
Ocean, Cal.
      Pacific
      Ocean, Cal.
      Pacific
      Ocean, Cal.
      Pacific
      Ocean, Cal.
      Pacific
      Ocean, Cal.
0.71
(I iverresldue)

0.%(liver
 residua)

8.21 (liver
residue)

less than 0.1
(liver
residue)

0.0*7-0.073
  (gonad
residua)

0.032 (gonad
residue)
             0.0<«Z
             (digestive
             gland residue)

             0.077
             (residue)
                                                                    saae  as above
                                                                    save  as above
                                                     save as above
                                                                    sane  as above
                                                                   saae as above
                                                                   save as above
                                                     sane as above
                                                                   sane as above
                                                                   save as above
                                                                                  Hunson
                                                                                                      Munson(ig73).
Munsontl97j),
4NIC-3096

Hunson
(l^Z),
»MIC-3fl<)6

Hunson
(197Z),
ANIC-304B

Munson
(1972),
»MIC-J09%

Munson
(1972I,
AHIC-309S
                                                                     Hunson
                                                                     (1<»7?I.
                                                                     3096
                                         Various      0.01 to 0.7<»
                                         oonds  and    (residue)
                                         streaasln
                                                      Plant, Invertebrate, fish, and    Dlaond,
                                              •ud samples were pooled, homogenized, and al
                                              analyzed for DOT.  Birds Here analyzed    AMIC-3291
-------
  Compound
                                   Field  Field
                       Organism    Study Location
Toxlcity,
Active
Ingredient,
  Ppm
Experimental
Variables.
Control led
or Noted
                                                                                                 Comments
Reference
                     plants)
                                         Maine
DOT
DOT
DDT
DOT
DOT
Invertebrates F
(Cimbarus
bar ton I,
freshwater
mussel'., and
s»al ler
anlf»at«t
Fish F
(Satvnl tnus
font Inalls
and Sevotl lus
atromaculatus
prtmarl ly)
Birds F
(H«aac»ryle
alcyon,
Mernus
merganser.
and
Lophortytes
cucul latus)
Muds F



Llmneohllus FS
rhonblcus
(larvae)

Various
ponds and
streams In
Maine



Various
ponds and
streams In
Maine


Variousoonds
and streams
In Maine





Various
ponds and
streams In
Maine
Knights
Creefc , Dun
County,
Wise.
0.03 to Z.
(residue)





0.21 to 9.
(residue)




«.Z to 10.
(residue)






0.03 to 0.
(residue)


O.OKxhole
residue)


ti






»i>





1







83



body



                                                                                 Individually.   The data  represent  the
                                                                                 range of DOT concentration  over  a  10-year
                                                                                 oerlod after one aoolIcatIon.  Highest
                                                                                 concentrations were found  immediately
                                                                                 after and 1 yr after anollcatlon with
                                                                                 considerably less txo  years and  after.
                                                                                 However, the residues  even  after 10  years
                                                                                 •ere still Hell above  those in brooks
                                                                                 never treated*  This study  further
                                                                                 demonstrated the persistence of  DOT  in
                                                                                 the environment and Its  tendency to
                                                                                 spread and concentrate In  food chains.

                                                                                        sane as above
                                                                                        same as above
                                                                                        same as above
                                                                                        same as above
                                                                                                                           Olmond,  *t
                                                                                                                           Olmondt  et
                                                                                                                           al  (1971),
                                                                                                                           •MIC-3Z91
                                                                                                                           al
                                                                                                                              ondf  et
                                                                                                                              (1971),
                                                                                                                           Dlmond,  et
                                                                                                                           al (19M>,
                                                                                                                           AMIC-3291
                                   Samples of Mater, silt,  bottom    Mpubry,  et
                           debris, bottom organisms, and fish Here   al  (1965),
                           taken In 1966 from a creek adjacent to an &MIC-J7SJ
                           orchard which had been treated In
-------
r
H
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Stalls so.    FS
Ilarva*)
                     Gammarus so.  FS
Salvelinus    FS
fontlnalis
Semotllus     FS
atronaculatus
                     Cettus balrdl FS
Rhlnlchthys   FS
atratulus
Sal welinos    L
fontlnal Is
119.2 c«)
Knlqhts
CreeH, nun
County,
Misc.

Knlqhts
Creek, Dun
County,
HIsc.

Knlqnts
Creek, Dun
County,
Misc.

Knlqhts
Creek, Oun
Countyt
Misc.

Knlqhts
Creekt Oun
County,
Misc.

Knlqhts
Creek, Oun
County,
Misc.
0.01  (Hhole
body
(residue)
                                 0.03(Hhole body
                                 residue)
0. «.-!.*
Ifat
residue)
0.1-0.6(tat
residue)
                                 0.5-1.5 (fat
                                 residue)
0.10
(tat
residue)
                                                       0.1-0.3  (SB1)
                                                                                  19*3-1965 Hlth various  chlorinated
                                                                                  hydrocarbon pesticides.   No  residues Here
                                                                                  found  in water samples.   Silt  sanoles
                                                                                  contained 0.002-0.013 DDK vndrln and
                                                                                  0-0.On; pom dleldrln. Endrin residues of
                                                                                  0.011-0.025 DP* and  0.002-0.006  DO*
                                                                                  dleldrln Mere  found  In  debris  samples.
                                                                                  Oesolte llnlted control  data,  residue
                                                                                  analyses Indicated that  contamination of
                                                                                  the environment studied  Has  Halted.

                                                                                         saae as above
                                                                                         saae  as  above
                                                                                         sane  as  above
                                                                                         sane  as above
                                                                                         sane  as  above
                                                                                         saae  as  above
Moubry, et
al (1Q68),
•1IC-3753
                                                                     Houbry, et
                                                                     a I  (t«6*>,
                                                                     AMIC-3753
Moubry, et
at (1968).
tloubry, et
al (196S).
                                                                     Moubry, et
                                                                     al  (1961),
                                                                     4MIC-375X
Moubry, et
al (I'?.*).
AMIC-3753
                                                Neurophyslologlcal function of
                                        brook trout Has affected by ?<»-hr
                                        exposure to DDT as determined by
                                        measurement of electrical activity of
                                        lateral lines.  Partially exposed lateral
                                        lines of freshly Killed fish were fitted
                                        Mlth electrodes.  DOT caused the lateral
                                        line nerve to become hypersensitive to
                                        experimental stimuli and affected
                                        behavioral responses of fish to
                                        tenoerature.  •
                                                                     Anderson
                                                                     fl«6S>,
                                                                     AMIC-3764
-------
           Comooun4
                                OrganIso
                                            Field   Field
                                            Study Location
                                 Toxlclty,
                                 Active
                                 Ingredient,
                                   Pp»
                Experimental
                Variables.
                Control led
                or  Noted
                                                                                                          Comments
                                                                    Reference
         DOT
rv>
         DOT
         DOT
         DOT
         DOT
                               Oncorhynehus
                               klsutch  (?.9
                               9>

                                                                0.33  (T31I
                              Oncorhynehus  L
                              kisutch (7.1.
Oncorhynehus  L
klsutch
(15.01. q)
                              Salvelinus
                              fontlnalls
                              (110-180 q)

                                                               1.3  (T65)
                                                                2.6  (T106J
                                                                0.02  (SB)
                              Parophrys
                              vetutus
                                            FH
         DOT
                              Herlucclus
                              product us
                                            FH
                    Pacific
                    Northwest
                    Coast.
                    Blaine,
                    Hash.
                    Pacific
                    Northwest
                                                                0.01  (residue)   —
0.01-0.06
(residue)
                                                                    A diet containing DOT fed to coho Buhler,  et
                                                            salmon resulted in median survival  times  al
                                                            directly proportional  to  body Height.      (197J
                                                            Suoolemental  feeding orolonqed lifesoan,  37*1
                                                            but mean survival  time remained a direct
                                                            function of  body lelqht.   Smaller salmon
                                                            Here more susceptible because Hold
                                                            content apparently failed to provide for
                                                            storaqe detoxification of DOT.
                                                            Considerable  addition*! data are
                                                            presented.
                                                                                                 same as above
                                                                                                 same as above
                                   Brook trout  conditioned  to I iqht
                           and shock rescontf to both  by  the
                           propeller-tall reflex.   Exposure to DOT
                           resulted In markedly delayed  ability to
                           learn.   The authors  state  that  DOT
                           spoarentlv affects the  CNS and  may cause
                           adverse effects on such behavioral
                           activities as territorial  defence and
                           migration.

                                   Pesticides from the Columbia
                           River Into Puget Sound  aooarently
                           contaminated  fish constituting commercial
                           catches In Pacific Northwest  waters.
                           Residues In these marine products were
                           substantially loner  than the  FDA
                           tolerance for beef (7 pom).  Fish fro*
                           locations near the mouth of the  Columbia
                           Plver had higher pesticide content than
                           ones caught farther  away.

                                  same as above
Buhlert et
al
(1970),AHIC-
3701

Buhler. et
al
Ct970»,AMIC-
3781

Anderson.et
al (1970),
AMIC-3782
Stout
(196S),
AM.IC.-37a!.
Stout
(1968),
-------
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Herluce lux
predue tus
HerluceIu«
product us
MeMucclus
croductus
Ifishaenl)
Sebastodes
alutus
Platlehthys
stetlntus
                                   FH
                                   FH
                                   FH
                                   FH
Gadus         FH
•acrocephalu*
Sebastodes
flavldus
Sebastodes
I lavtdus
                      Pfaephales
                                   FH
                                    FH
                                    BCF*
Coast*
Sarasota
Passage*
Hash.

Pacific      O.Ot-0.09
Northwest    (residue)
Coastt Fort
Susant Hash.
Pacific
Northwest
Coast* Cape
FoulHeather,
Or*.

Pacific
Northwest
Coast,
Aberdeen*
Hash.

Pacific
Northwest
Coast,
Hecate
Strait, B.C.

Pacific
Northwest
Coast,
Blalne,
Hash.

Pacific
Northwest
Coast,
Blalne*
Hash.

Pacific
Northwest
Coast*
Hecate
Strait. B.C.

Pacific
Northwest
Coast,
Ilwaeo*Hash.
                                                       O.OKresldua)
                                                       O.It  (residua)   —
                                                       O.It  (residual   --
                                                       O.ll(resldue)    —
                                                       (residua)
             O.OOH-0.05
             (residue)
             O.OI.-0.19
             (residue)
                                                       0.018 (TO
                                                                                         sane as above
                                                                                         «aaa as abova
                                                                                         sane as abova
                                                                                         sane as abova
                                                                                         saa* as abova
                                                                                         saae as above
                                                                                         same as abova
                                                                                         saae as above
                                                                                                                            1MIC-378V
Stout
(196S).
»MIC-378<.
                                                                                  Stout
                                                                                  (19f.8»,
                                                                                  •Hic-srs*
                                                                                  Stout
                                                                                  (1968),
                                                                                  4MIC-378*
                                                                                  Stout
                                                                                  (19«i9»,
                                                                                  •HIC-578*
                                                                                  Stout
                                                                                  (19*3),
                                                                                                                            Stout
Stout
(1968).
•MIC-378*
Stout
(1968).
*HIC-378«
                                                                                          LAS acted svnerglstlcalIv with    Solon* etal
-------
Compound

DOT
DOT
DOT
Toxtclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppn or Noted Comments
prone) as
Car ass 1 us L —
auratus
Car ass I us L --
auratus
S*l»o L
qalrdner I
(186-788 q)
oarathion to cause less survival of
fatheds but had an Indeterminate effect
with OPT and no svnerqistle effect with
Endrln.
1,5-180 (SR a* Goldfish were exposed to
5-?0) Inereasinq concentrations of DDT and
residues determined after ?1 days of
exposure. Most DDT had been converted to
ODE. Phenobarital had no siqnlflcant
effect on Insecticide residues.
0-0.1 a* ' same as above
(residue)
15 (SB 6 hr) »* In aquarium water, I* opm DOT
caused no apparent el ect roohysi ol oq leal
differences in lateral line preparations.
Reference
(1969) .
AHIC-3785


Young, et al
(1971), AMIC-
379«-
Younq, et
(1971) ,
AMIC-3796
Bahr, et
3808
al
al
DOT
DOT
DOT
DOT
                     Sal mo
                     qalMnerl
                     Trl turus
                     crlsfatus
                     Pans
                     temporarla
                     Ran a
                     teaporarla

                                   I      •«•
0.1-2.0 (NTE,
Intravenous)
0.67-1.<>
(residue)
0.05 (SB 5-19
hr)
0.5-1.2
• Icrograii
(residue)
 However, tremors antl byperexcl taM 11 ty
were observed after 1 hr.  Neural
discharge was not affected by intravenous
Injections, but tremors occurred at
concentration levels of 0.5 pon and
above.  The authors eonclule that
spontaneous activity of the lateral >Ine
Is not a sensitive Index for DOT
neurotoxle effet.

       same as above                      Bahr, et al
                                          (1971),»MIC-
                                          3808

        DOT caused hyperactIvlty In       CooKe
exoosed tadpoles.  This caused Increased  (1971),
capture lunges of newts thus Increasing   »MIC-3S1<,
the predatory efficiency of the newts.
DOT had no apparent effect on the newts.
                                                                                        sane  as above
                                                                                        same  as  above
                                          CooKe
                                          (1971),
                                          AMIC-381W

                                          CooKe
                                          (1971),
                                          AHIC-381*
-------
DOT
DOT
Carasslus     9SA
auratus (8-15
                     Car ass 1 us     BS»
                     auratus  18-15
                                                       1.0  (SB H.5hr>   a.q*
                                                       1.0  (T  10  hr>
                                                                                               expospd to DOT were killed   Aubln, et
                                                                                  and brain electrical activity recorded by al(19K9)»
                                                                                  means of Aq-AqCI  bioolar electrodes.      A«.IC-3S35
                                                                                  After ?.5 hr exposure,  fish dlsolaved
                                                                                  complete loss of  balance and swam
                                                                                  continuously on their sides.  Amplitude
                                                                                  and freauency of  spontaneous electrical
                                                                                  activity Mere altered.   This coincided
                                                                                  with permanent loss of  balance.   The
                                                                                  authors state that this is the first
                                                                                  record of a change in fish EEC following
                                                                                  DOT poisoning.
                                                                                         sane as above
                                                                                                      Aubln.  et  at

                                                                                                      C1«»69),«HIC-
DOT
                     Sal mo salar   L
DOT
DOT
DOT
DOT
Salv«tInus
fontInalIs
(yearlInq)

Salw«lInus
fontInalIs
                     Endomychura
                     craveri
                     (eqqs)
                     tmlonyehgra
                     craveri
                     (eggs)

                    Western
                    U.S.,
                    Pacific
                    Ocean,
                    Panama*
                    Hexlco,and
                    Antarctic

                    Western
                    U.S.,
                    Pacific
                    Ocean•
                                 0.02-0.20       a».q«
                                 (sai)
                                                       0.02-0.20
                                                       (SSI)
                                                      O.I.  (SBI
                                                                      a»,q«
                                                      39  (residue)
0.31-2.
-------
I
^3\
Comoound Orqanlsn



IT Thalasseus
eleqans
(eqgs)




JT Laru*
heermanl
(«qg«)




JT Pomoxis
annul »rl*





IT Pomoxl<;
nigro-
Ba.cula.t-.ia-




)T Leoomls
•aeroehlrus





9T Pyqoscells
ade 1 1 ae
Toxlclty, Experimental
Active Variables.
Field Field Inqredlent< Controlled
Study Location Pom or Noted Comments
Panama,
Mexlcotand
Antarctic
F Western 5.0 (residue) -- sane as above
O.T.,
Pacific
Ocean,
Panama,
Kazioo>and
Aatartlca
F Western <»t (residue) ~ saae as above
U.«J.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
F Western 1.83 (whole — saae as above
U.S., body residue)
Pacific
Ocean,
Panama,
Hoxlco, and
Antarctic
F Western 7.10 (whole -- same as above
U.S., body residue)
Pacific
Ocean,
Panama,
Mexico, and
An tar tic
F Western 5.9 (Hhole body — same as above
U.S., residue)
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
F Western 0.128 — same as above
U.S., (residue)
Reference



Rlsebrouqh,
et al
(1<>6M.
AMIC-3W.



Blsebrougn,
et al
(146ft),
AHIC-38M.



Sls»fcrouqh»
et al
(1968) ,
AMIC-3SH



"Isebrouqh,
et al
(1968),
AMIC-38M.



RIsebrouqh,
* t at <19«>8) ,
AHIC-38Vli




»lsebrouqh>
et al
-------
DOT
DOT
DOT
DOT
DOT
00 T
                      (eqgs)
                      Aechmorohorut  F
                      occidental is
                     FuI manus
                     qlaclalis
                     PutfInus
                     ereatoous'
                     Puf f inus
                     qriseus
                     Pufflnus      F
                     tenulrostrls
                      Oeeanodroma
                      homochroa
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama*
Haxlco, and
Antarctic

Western
U.S.,
Paclf1C
Ocean,
Panama*
Mexico* and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
PaclfIc
Ocean,
Panama*
Mexico* and
Antarctic

Western
U.S..
Pacific
Ocean*
Panama,
Mexico, and
?&.<.  (flesh
residue)
0.1.1-17.5
(whole body
residue)
3.0 (Hhole body
residua)
2.3-12.3 (Hhol«
body residue)
39 (whole body
residue)
99.3 (whole
body residue)
                                                                                         sane as above
                                                                                         sane as above
                                                                                         same as above
                                                                                         same as above
                                                                                         sane as above
                                                                                         same as above
Slsebrouqh.
et al
Risebrouoh,
et al
(196S),
Rlsebroucrh,
«t al
(1968),
AHIO384*
Risebrouoh,
et al
(t9f.fl).
Rlsebrouqh,
et al
(1968),
"Isebrough,
et al
(1968),
AMIC-38<.*
-------
>
Field
Coaioound Organism Study

)T Pelecanus F
oce I Cental Is
(eqqs)



)T Freqata F
paqnlf 1C ens
(eqgs)




)T Sula F
leucogaster





)T Phalacrocorax F
penici llatus
(eqqs)




)T Phalacrocorax F
oelaqlcus
(eqgs)




JT Anas F
cyanootera


Field
Location
Antarctic
W«tern
U.S.,
Pacific
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S..
Pacific
Ocean,
Panama,
Mexico. and
Antarctic
Western
U.S..
Pacific
Ocean,
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments

10.0-11.5 — same as above
(residue)




0.0087-0.03 — same as above
(residue)





8.2 (residue) -- saae as above






0.326 ~ same as above
(residue)





0.128 ~ same as above
(residue)





10.9 (Hhole — same as above
body residue)


Reference

Rlsebrouqh,
et al
*MIC-lU*



Rlsebrouqh,
et al
(19681,
AMIC-38H



Rlsebrouqh,
et al
( 1968) ,
AMIC-S8*^



Rlsebrouqh,
et al
(1968),
ANIC-3S«i«(



Rlsebrouqh.
et al
(1968),
A MIC— 38fc^



Rlsebrough,
etal (1968)
AMIC-3*M>

-------
         DOT
         DOT
6
VO
         DOT
         DOT
         DOT
         DOT
                              EI anus
                              teocurus
                              fwqgs)
Acclolter
cooper 11
Aaulla
chrysaetos
(eqqs)
                              Pandlon
                              hallaetus
Falce
cotumbarius
Falco
sparverlus
                    Panama,
                    Mexico,  and
                    Antarctic

                    Western
                    Pacific
                    Ocean,
                    Panama,
                    Mexico,
                                                           and
Antarctic

Western
U.S.,
PaclfIc
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
PaclfIc
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama.
Mexico, and
Antarctic

Western
U.S..
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pad Me
Ocean,
Panama,
Mexico, and
Antarctic
                                  0.31.-9.0
                                  (residual
25.2 (whole
body residue)
                                                                2.0  (residue)
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                 55.0  (whole
                                 body  residue)
2-9 (whole body
residue)
0.01. (whole
body residue)
                                                                                                  sa*e as above
                                                                                                  same as above
                                                                                                  sane as above
                                                                                   RIsebrouqh,
                                                                                   et al
                                                                                   (19S8),
Rlsebrough,
et al
(198B),
                                                                      P. isebrouqh,
                                                                      et  al
                                                                      (1968),
                                                                     Rlsebrouqn,
                                                                     et  al
                                                                     (196M ,
                                                                     SMIC-38«.l»
Plsebrouqh,
et al
(19SS),
AHIC-38I.I.
Rlsebrouqn,
et al
(1968),
AKIC-3S
-------



Comoound Organism
DOT Fat co
soarverlus
(eqqs)




Toxlclty, Experimental
Active Variables,
Field Fl-ld Tnqr*dlent, Controlled
Study Location Ppm or Noted Comments
F Western 0.2 (residue) — - sane as above
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic



Reference
Rlsebrouqh,
etal (19<>8),
AMIC-381,1.




DOT
DOT
DOT
DDT
                     Nyctlcor*x
                     nyctlcorax
                     (eqqs)
Larus         F
occidental Is
(eqqs)
                     St*rna
                     for^terl
                     (eqqs)
                     Hy
-------
DOT
DOT
DOT
DOT
DOT
DOT
Url» »8lge
(eqqs)
Ptychoranphus F
aleutleua
Synthllboraao F
hus antlquun
                     Cerorhlnca
                     •onocerata
                     Zenaldura
                     •aeroura
                     Tyto alba
DOT
Sturnella
neqlecta
Western
U.S.,
Pacific
Ocean,
Parana,
Mexico, and
Antarctic

W«a-t«rn
U.S..
Pacific
Ocean,
                                                       191  (residue)    —
                                                                                         saae  as above
                                                                     Rlsebrough,
                                                                     et al
Maxlco, and
Antarctic

Western
U.S.,
Pacific
Ocean *
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panana,
Mexico, and
Antarctic

Western
U.S..
Pacific
5.8 (Hhole body
residual
0.75 (whole
body residua)
                                 2.7 (whole body
                                 residue)
                                 0.19 (whole
                                 body residue)
                                 1.3-6.6 (whole
                                 body residue)
0.3-3.3 (whole
body residueI
                                                                                         sane as above
                                                                                         sane  as above
                                                                                         sa»e as above
                                                                                         sane  as above
                                                                                         sane as above
                                                                                         saae as above
Rlsebrouon,
et al
(1968*.
AHIC-38**
Risebrouoh,
et al
(19681,
AMIC-JSMi
                                                                     Risebrouqn,
                                                                     et al
                                                                     (1968),
                                                                     AHTC-38<><>
Risebrouqh,
et al
(1968).
-------
Compound


DOT













DDT






DOT






DOT






DOT

Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Orqanlsa Study Location Ppa or Noted Comments


Falco F
peregr Inus
(•99*>











Falco F
pereqrlnus
(1 Mature!




Faleo F
peregrlnus
11 •••tire)




Falco F
oereorlnus
ladult)




Falce F
oereqrlnus
Ocean,
Pana«a,
Hexlco. and
Antarctic
Western 0.02 (residue) —
U.S..
Pacific
Ocean,
Panama,
Mexico, and
Antarctic







Western 1.9-396 (flesh —
O.S., residue)
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western 6l.-5.ODO (fat
U.S., residue)
Pacific
Ocean,
Pnnana,
Hexlco, and
Antarctic
Western 85-137 (flesh
U.S., residue)
Pacific
Ocean,
Panaaa,
Mexico, and
Antarctic
Western 3,600 (fat
U.S., residua)


Pereqrjne falcons, falcon nrey.
and other predator species were collected
widely and analyzed Tor DOT, DOE, PCB,
and it few other pesticides to a lesser
degree. PCB and DDT were found to be
widely dispersed globally. pen was found
to be a powerful inducer of heoatic
enzymes that degrade oestradlot.
Reductions in thlcKness of ego shells.
eggshell weight, and water retention
occurred. All affect hatching success.
The authors state that the oer«grin« aay
be the first species entlrpated by global
eon tan I nation.
sa»e as above






saa,e as above






sane as above






saae as above

Reference
AMIC-38I><>

Rlsebrouqh,
et al
(1968),
»HIC-5««.i.










Rlsebrouoh,
et al
C19SM,A«IC-
381.1,



Visebrough,
et al
(l<»6«t.
AMIC-38",!.



Rlsebrouqh,
et al
(1968).
AMIO38«t



Rlsebrough,
et al
-------
         oar
        DOT
r
        DOT
        DOT
        DOT
                              taduttt
                             Podleaps
                             casplcus
                             LooHelanla
                             ••tanla
                             Halocyptena
                             •Icrosoaa
                             PIzonyx
                             vlvesl
                             Ictalurus
                             ounctatus
 Pacific
 Ocean,
 Panaaa,
 Mexico,and
 Antarctic

 Western
 U.S.,
 Pacific
 Ocean,
 Panaaa,
 Hex I co, and
 Antarctic

 Hestern
 U.S.,
 Pacific
 Ocean.
 Panaaa,
 Mexico, and
 Antarctic

 Western
 U.S.,
 Pacific
 Ocean,
 Parian a,
 Maxleo, and
 Antaretie

 Western
 U.S.t
 Pacific
 Ocean,
 Panama,
Mozloo, and
Antarctic
O.Z6-12.1
(•hole body
residue)
4.2  Cnhole body
residual
3.Z iNhole body
residue)
0.71 (nho(e
body residual
save as above
                                   RIsebrouq^,
                                   et al
                                   (19681.
sane as above
                                                                                                                                   et al
                                                                                                                                   C196S),
                                                                                                saae as above
                                                                                                                                   et al
                                                                                                                                   (19681,
                                                                                                saae as above
                                                                                                                                   et al
                                                                                                                                   (19651,
                                           ns»   —
                                                              0.016
                             a,                 Orqanochlorlne Insecticides were  Hacek, et al
                             synthetic  the nost toxic coaoounds,                 (1970),
                             test Hater orginochosohates  Interne.1lat»>,  earhanates AHIC-SS10
                                        the  least  toxic.   Proxn  trout »as  the
                                        species nost  susceptible to
                                        orqanochloPlr.es,  coho salmon  the nost
                                        susceotlble  to  carbaiates, and  goldfish
                                        Mert>  the  least  susceotlble of all
                                        species.   Safe  concentrations established
                                        by hioassays  xith salaonids or
                                        centrarchlds  Mould likely  be  safe  for
                                        cyorinlds  and ictalurlds.  Safe levels
                                        for  Ictalurlds  or cyprlnlds Mould
                                        probably  be hazardous for centrarchlds
                                        and  salaonlds.  The use  ot qoldflsh In
                                        bloassays Mas dlscouraqed.
-------





>
g





COBBOund
'DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Field Field
Organise Study Location
S*l*to trutta BSA
Oncorhynehus BSA --
Kisutch
Perca BSA
flavescens
Ictalurus BS»
•«las
C*rasslus BSA ™
aurst us
Cyorlnu* USA — -
earplo
PImeohales BSA •*-
prone! as
l«oo*ls SSA
Mcroehlrus
LeDomls 8S*
•Icrotophus
Mlcrooterus BSA —
salHoIdxt
SslMO BSA —
galrdnrrl
Toxlclty,
Active
Ingredient,
Pp«
0.003 (T<>t
0.00
0.009 (Ti>)
0.009 (Tit)
0.031 (T)
0.007 (Tl.)
Excerlnentat
Variables,
Control ted
or Noted
a,
synthetic
test water
a.
synthetic
test water
a,
synthetic
test Mater
a,
synthetic
test water
a»
synthetic
test water
9,
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
».
synthetic
test water
at
synthetic
test water
Comments
sane as above
same as above
saae as above
sane as above
saae as above
saae as above
sane as above
same as above
same as above
saae as above
saae as above
Deference
Macek, *T
at (1970),
»NIC-«:MO
HaceK, et
al (197Q1,
ANIC-5S10
Mace*, et
al(1970).
•MIC-5S10
MaceK, e»
al (1°70).
AMIC-5510
M»c*H, et
»l (1970),
»MIC-S«;ID
MaceK. et
al (1970) ,
«HTC-5510
Hacek, et
al (19701 ,
AMIC-SS10
Nac*K, et
al (197m ,
AMIC-5510
Hacek, et
»l (1970),
AHIC-5510
HaceK, et
•1(19701,
AHIC-5510
NaceK, et
•1(19701,
AHIC-9S10
-------
DOT
                     Pa I ae<*on« tes
                     kadlakensls
                     (resistant)
                                   BS*   —
                                                       0.0037-0.0068
DOT
DOT
                     Pa I aemone tes-  BSA
                     kadlafcensls
                     (non—
                     resistant)
                     Tctalurus
                     eatus
                                   FL
                    Clear Lake,
                    Cal.
                                                      0.0026  IT1)
             less than 1
             (flesh
             residua)
DOT
00 T
DOT
                     P«rca
                     flavescens
                     Lepomls
                     glbbosus
Catostomus
commersonl
                                   FLR
                                   FLR
                                   FLR
                    43 sanipt Inq
                    stations In
                    Mass.
             0.06-13.2
             (residue)
93 samol Ing  0-9.1
stations In  (residue)
Mass.

43 sampling  0-11.2
stations In  (residua)
Hass.
                                                                    Bloassays Mere conducted with     Naqvl, et al
                                                            shrlmn from three areas of Intensive      (1970)»
                                                            pesticide use and from an unexposed area. 4MIC-5519
                                                             Previously exposed shrimp Mere from 1 to
                                                            ?"? times more resistant than unexposed
                                                            shrimp.  Both types of shrimp Mere also
                                                            exposed In caaes to Maters of the
                                                            contaminated areas.  Susceptible shrimp
                                                            suffered 66 percent more mortality than
                                                            did resistant shrimp.  The toxiclty of
                                                            the insecticides ranked In descending
                                                            order was as follows:  most toxic,
                                                            Endrln, DOT, Methyl parathlon, Parathionl
                                                            medium toxiclty, Guthlon,  Llndane,
                                                            Toxaohene, Strobanei lease toxic
                                                            Chlordane, Sevin, and Heptachlor.
                                                                                        same  as above
                                                                                                      Naavl,et al
                                                                                                      (1970),
                                                                                                      AMIC-S519
        Residue  analysis results mainly   Linn, et
for IDE In  fish,  birds, *nd plankton  from *L11969),
11S9  through  1965  x^re reported.  The     *HIC-55?1
residues  primarily  resulted from
application of DDT  to  farmland  ar.d  for
qnat  control.  In  some cases, data  for a
single anliral  In  one year Here  given.
Primary emphasis  Mas on larqeirouth  bass
and Mhlte catfish.  The qeneral  level of
TD£ contamination  In birds and  fish
declined markedly  fro* 195S to  1965.
This  decline correlated directly Mlth
strict limitation  by permits of DOT
applications during the latter  years.

        Fish indigenous to Massachusetts  Lyman, et al
freshwater streams  Mere analyzed for OOT  (1968),
and DOT metabolites during 1965-1967.     *«IC-3»39
Generally there Mas an Increase In
pesticide content  during the three  year
period.
                                                                                        same as above
                                                                                        sane as above
                                          Lynan, et al
                                          (1968),
                                          A1IC-3839

                                          Lyman, et a!
                                          11969).
                                          AMIC-3639
-------
Compound
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Orqanlsn
Tctslurus
nebul osus
Cyorlnus
carplo
Esox nlqer
Not*»m 1 oonus
erysoleucas
Semotl lus
corporal Is
Leoomls
nacroehlrus
Amblopl Ites
ruoestrls
Seiotl lus
atpo^acul atus
Mlcrooterus
dolonlrul
Alosa
paeudo-
harangua
Fundu 1 us
heterocl 1 tus
Field
Study
FLR
FLO
FLR
FLR
FLR
FLR
FLR
FLR
FLR
FLR
FLR
Field
Locat Ion
93 samollnq
stations In
Mass.
93 sampling
stations In
Mass.
93 sampling
stations In
Mass.
93 sampl 1 ng
s tat 1 ons In
Mass.
93 sampling
stations In
Mass.
93 satnpl Ing
stations In
Mass.
93 sampl Inq
stations In
Mass.
93 samel Ing
stations In
Mass.
93 sampling
stations In
Mass.
93 sampling
stat 1 ons In
Mass.
93 sanpl Ing
stations In
Mass.
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pp» or Noted
0.32 (residue)
0.3-1.0
(residue)
0.02-1. D
(residue)
0-1.1
(residue)
0-2.8
(residue)
0-2.1.
(residue)
0.<>-8.3
(residue)
0.02-0.3
(residue)
0.2-B.6
(residue)
0.3<» (residue! —
0.7-2.8
(residue)
Comments
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
Reference
Lywan, et al
(19S8).
ANIC-3839
(1968),
AMic-3839
Lyan, »t al
(1968) ,
Lvman, et al
(19681.
Lyman, et al
ANIC-3S39
Lyman. et al
Lvman. et al
AHIC-3839
Lyman, ft al
(196S),
AHIC-3839
Lyman, et al
4HIC-3S39
Lyean, et al
(1968).
AMIC-3839
DOT
                     Notrools      FLR   13 sanollno  0.1-3.1
                                                                                       sane as above
                                                                                                                          Lynan,  et  al
-------
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
                      cornotus
                      Roccus
                      «t at
 <19«.R) .
 AMIC-3S39

 Lysn, *t al
       et al
      ,
AHIC-JS39

Lyxan, et al
                                                                                                      Lvoan, et al
Lyman, et al
                                                                    In studylnq control ot black fly,
                                                            tne Indicated aauatlc soecles were
                                                            studied at a series of six sanollnq
                                                            stations.  Mater Quality was unaffected
                                                            hy the DDT aopllcitlon.  No caoed fish
                                                            died,  hut Mild ones did apparently
                                                            resulting from inaestlon of dead
                                                            Invertebrate larvae.  Invertebrates were
                                                            collected by bottom sampling and bv drift
                                                            nets,  and fish by nettlncj and anqlinq.
                                                            Fish mortality could always be related to
                                                            at least a ten-fold Increase in DOT
                                                            residues In the fish.  DOT caused high
                                                            bottom fauna mortality by direct contact.
                                                             Caddisfty larvae Here more affected than
                                                            stonefly and mayfly larvae.  The author
                                                            stated that DOT larvicidlnq for black fly
                                                            control  was not successful because of
                                                            bar* to non-tarqet organises.

                                                                   sane »s above
Hatfleld
(1969),
AHIC-5770
                                                                                  Hatfletd
                                                                                  (1969),
                                                                                  AMIC-5770
-------
Coaoound
DOT
DOT
Organise
Simula*
venustu*
(larvae)
Botto*
Invertebrates
Field Field
Study Location
FS Bobby "s
Rrook,
Labrador,
Can.
FS Robby~s
Brook ,
Labrador,
Can.
Toxlclty,
Active
Inqredlent,
Pp«
0.1 (SB)
0.1 CK)
Cxoerlnental
Variables,
Controlled
or Noted
c,d,e,9
c«d,a,g
DOT
DOT
DOT

                                                      590 (SB)
                     •acrochlrus
                     (liver
                     •Itochondria)
                     Cooeoods
                     (Cyelons
                     talcusoMus,
                     Cyclops
                     varleans,
                     Cyclops
                     vernalIs,
                     Eucycloos
                     agllls.
                     Kacrocyclops
                     albldus,
                     OrthocyclODS
                     •odestus)
                     Cooepods
                     (Cyclops
                     blcuspldus,
                     Cvcloos
                     varlcans,
                     Cyclops
                     vernal Is,
                     Eucycloos
FL    State
and   College,
8S»   Hiss.
                                                      0.05 IK?)
FL
and
BSA
      Befzontt
      Hiss
0.05 191
oercent K2I
                                                                                                 Connents
                                                                                        sa«« as above
                                                                                        save as above
                                                                                        Reference


                                                                                        Hatfleld
                                                                                        I196<>>.
                                                                                        »«IC-5TTO


                                                                                        Hatfleld
                                                                                        (1«69),
                                                                                        AMIC-5770
                                   Oxygen uotakr by blu*?1"
                           mitochondria was inhibited in the
                           or«sence of  DOT and ^uccinic acid.
                           Increased hvdrolyslt of &TP also occurred
                           in the presence of  Mq and Hn ions.   ihe
                           author states that  the primary effect oT
                           DDT ancears  to be Inhibition of  electron
                           flow fro«. succlnlc  acid to the cytochroae
                           chain.

                                   The  response of
                           pesticide-resistant aouatle orqar.ls«s to
                           various pesticides  was co«oared to the
                           resoonse of  non-resistant softies.
                           Pesticide-resistant soecies w*r'
                           collected at Pelzonl and non-resistant
                           soecies at State College.  CoO«BOd«;.
                           clams, snails, and  sludae Hor«« fro*
                           Belzonl were considerably »ore tolerant
                           to oestlcldes than  the non-resl«tant
                           orqanlsms.  The authors note that  the
                           effect of increased tolerance 1" th*
                           orqanlsas Is an Increase In tn« a»ount of
                           pesticide residues  available to anlaals
                           of Mqher trophic levels.

                                  save  as above
                                                                                        Hlltlbran
                                                                                        (197U,
                                                                                        4MIC-59T5
Naqvlt «t
(1969),
Naavl, et al
(19691,
4NIC-5979
                     Macro cyclop*
-------
DOT
DOT
DOT
DOT
DOT
DOT
albldus,
OPthocveloo*
nodestus)

Tub If ex
tublf»x
                      Crassostre
                      vlrglnica
                      I tarvac)
                                    FL
                                    •nd
                                    BSi
                     AetTonl,
                     Hiss.
                                                       3.0 (NTE)
                                                       0.031. ITlfc)
                                    8SA
                      Gambusia
                      a«fInls
                      (female,  «i.3
                      c«,  1.9 q)
Leblstes      BS«
retIculatus
(nale, 1.8
», 0.? 9)
Tllapla       BS»
nossamblca
(*.<> en, 1.3
Kuhtla        BS*
saidvlcensls
U.3 en, 1.5
                                                       0.02 (Tl>)
                                                       0.003 (T4I
                                                       0.007 (T? pesticides on    Davis, et al
                                                             embryonic development of clans and
                                                             oysters Has reported.  Synerqlstlc        (1969)••NIC-
                                                             effects with solvents Here also reported. 5990
                                                              Most  of the compounds affected
                                                             develocnent more than survival.  Some,
                                                             however, drastically reduced larval
                                                             growth.  The authors point out the
                                                             necessity of evaluatlnq the effects of
                                                             pesticides on all  life stages of an
                                                             orqanisi* and note  the oosslbillty of
                                                             selecting chemicals for oest control that
                                                             Hould  not have serious effect on
                                                             shell fish.

                                                                     The five fish suedes are         Nunoqana. et
                                                             commonly found In  streams and estuaries   al  (1970),
                                                             In  semi-tropical areas.   G. af'lnls Mas
                                                             the most tolerant.   Varied sensitivity to
                                                             the toxicants Here  found.  K.
                                                             sandvlcensis MBS the most sensitive fish
                                                             studied.  The standard method procedure
                                                             Has fol totted.
                                                                                         sane as above
                                                                                         sane as above
                                                                                         sane as above
                                                                                                                            NunogaMa* et
                                                                                                                            al (19TO),
                                                                                                                            aMIC-6567
                                                                                                                            NunogaHa, et
                                                                                                                            al (1970),
                                                                                                       Nunooawa,  et
                                                                                                       al  (1970),
                                                                                                       »MIC-656T
DDT
Stolephorus   BSA
purpurea (3.6
em. fl.lt ql
                                 0.001 (T 12hr)  a.c,d,e.f,
                                                 1, salt
                                                 nater
                                                                                         sane as above
                                                                                                                                      et
                                                                                                                            al (1970),
                                                                                                                            *NIC-»>567
-------
I
Toxlclty,
Active
Field Field Ingredient.
Compound Organism Study Location Ppm
DOT Carclnus BSA — 0.3-1.0 (T2>
maenas
DOT Card I urn edule BSA ~ greater than
Experimental
Variables,
Control led
or Noted Comments
a* (con tin- One hundred-forty surface active
uous aer- agents, solvent enulslf iers, pesticides,
ation, sea- aolychlorlnated blohenyls, pure
water, and Inorganic, and organic cheirlcals were
da^y evaluated against as nany as ten marine
solution organisms. The authors noted that most
renewal) Published data of this type deal xlth
toxlclty of chemicals to freshwater
organisms.
10 ae(contin- same as above
uous aer-
ation, sea-
water, and
daily
solution
Reference
Portmann, et
at 11971),
AHIC-7701
Portmann, et
al (1971),
*«TC-7701
                                                                      renewal)
DOT
                     Pleuroneetes
                     PIatessa
                                   as*
                                                               0.003-0.01
                                                               m>
a«(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                        save as above
Portnann, et
al 11971),
AHTC-7701
DOT
                     Freshwater
                     drua
                                   Ft
DOT
                     Goldfish
                                   FL
                                                  Ore*t Lakes  0.6Z  (-hole
                                                   (Ontario,     body residue)
                                                  Huron,
                                                  Erl«,
                                                   Superior,
                                                  Michigan)
                                                  Great Lakea
                                                  (Ontario,
                                                  Huron,
                                                  Erie,
                                                  Superior,
                                                  Michigan)
                                                      0.70 (whole
                                                      body residue)
                   Fish fron lake Nlchiqan contained Relnert
           2 to 7 tl»es more POT (and DOT analogs)    (ig7fl),«MIC-
           and ni«ldrin r«>sl<1uvs than fish from fhe  196
           other Great Lakes.  Fish fro* Lake
           SuOTlor Invariably had the loxest
           accumulations of both chemicals.  The
           compounds tended to concentrate in fat
           (oils).  Considerable additional data are
           presented.  The author noted the need to
           reduce pesticide usage to a minimum and
           to replace these Insecticides with less
           persistent materials.
                                                                                        same as above
                                                     Relnert
                                                     (1970),
                                                     1HIC-196
-------
DOT
                     Klyl
                                   FL
                    Great Lakes
                    (Ontario,
                    Boron,
                    Brie,
                    Superior.
                    Michigan)
             3.38 (whole
             body residue)
                                                                                        sane as above
Relnert
(197DJ,
•HIC-19S
DOT
Lake herring  FL
Great Lakes  l.tt-3.91
(Ontario,    (whole body
Huron,       residue)
Erie,
Superior.
Michigan)
                                                                                        saae as above
Relnert
(1970) ,
196
DOT
Lake trout    FL    Great Lakes  6.6t-7.(>i>
                    (Ontario,    (whole body
                    Huron,       residue)
                    Brie,
                    Superior.
                    Michigan)
                                                                                        sane as above
                                                                                  Relnert
                                                                                  (1970),*HIC-
                                                                                  196
DOT
                     Lake
                     white fish
                                   FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior,
                    Michigan}
             D.<.5-5.0?
             (Hholebody
             residue!
                                                                                        saae as above
Relnert
(1970),«MIC-
196
DOT
                     Rock bass
                                   FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Erie,
                    Superior,
                    Michigan)
             O.ltO (whole
             body residue)
                                                                                        sane as above
Relnert
(1979),
•HIC-19S
DOT
Round         FL    Great Lakes  0.57 (whole
whiterIsh           (Ontario,    body residue)
                    Huron,
                    Erie,
                                                                                        sane as above
                                                                                  Reinert
                                                                                  (1970).
                                                                                  •MIC-196
                                          aupai-xur,
                                          Michigan)
-------
Field Field
Co*»oun4 Organise Study Location
Toxlclty,
Active
Ingredient,
PDH
Experimental
Variables,
Controlled
or Noted
Connents Reference
         DOT
                              Sea laoorey   FL
                                                  Great Lakes
                                                  (Ontario,
                                                  Huron,
                                                  Brie,
                                                  Superior.
                                                  Michigan)
                                 1.27  (whole
                                 body  residue!
                                                                                                saae as above
                                                                    Relnert
                                                                    (1970),
                                                                    AMIC-196
         DOT
                              SI lay sculoln FL
f
s
                   Great Lakes
                    (Ontario,
                   Huron,
                   Erie,
                   Superior,
                   Michigan)
                                                               0.22-2.33
                                                               (whole body
                                                               residue)
                                                                                                save as above
                                                                    'elnert
                                                                    (1970) ,
         DOT
                              Soottall
                              shiner
                                            FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Erie,
                    Superior.
                    Michigan)
0.25 (whole
body residue)
                                                                                                saae as above
Relnert
(1970),
AMIC-196
         DOT
Nine-coined   FL    Great Lakes  n.^3 (Hhole
stickleback         (Ontario,    body residue)
                    Huron,
                    Erie,
                    Superior,
                    Michigan)
                                                                                                sane  as above
                                                                                                                                   Relnert
                                                                                                                                   (1970),
                                                                                                                                   AMIC-196
         DOT
                              Stonecat
                                            FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior,
                    Michigan)
                                                               0.28 (whole
                                                               body residue)
                                                                                                saae  as above
                                                                    Relnert
                                                                    (1970),
                                                                    AHIC-196
-------
         DOT
                              Troutoerch
                                            FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Krle,
                    Superior.
                    Michigan)
0.9* (Hhole
body residue)
                                                                                                 sane as above
PeJnert
(1970),
•HIC-196
         DOT
Malleye       FL    Great Lakes  1.13-6.03
                    (Ontario,    (whole body
                    Huron,       residue)
                    Brie,
                    Superior,
                    Michigan)
                                                                                                 sane as above
                                                                     Relnert
                                                                     •1970),
                                                                     •MIC-196
         DOT
                              Hhlte bess
                                            FL
U)
                    Great Lakes
                    (Ontario,  .
                    Huron,
                    Erie,
                    Superior,
                    Michigan)
1.89-2.76
Iwho I* body
residue)
                                                                                                 sane as above
R«Inert
(1970),
4MIC-196
         DOT
                              Mhlte perch   FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Krle,
                    Superior,
                    Michigan)
it.'Si (whole
body residue)
                                                                                                 sane as above
ffelnert
(1970).
•MIC-196
         DOT
                              Uttlte sucker  FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior,
                    Michigan)
0.37-1.1*.
(•hole body
residue)
                                                                                                 saee as above
Relnert
(1070),
196
         DOT
                              YeII en oereh  FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior.
                    Michigan)
0.87-2.93
(•hole body
residue!
                                                                                                 saee as above
Beinert
(1970),AMIC-
196
-------
             Comoound
            Field  Field
Organism    Study Location
Toxlclty,
Active
Ingredient,
  Pom
ExoerlBcntal
Variables!
Control led
or Noted
                                                                                                            Comments
                                                                                                                                     Deference
           DOT
                                Fiierald
                                shiner
                                              FL
                 Great Lakes   0.9
-------
                                         Huron,
                                         Erie,
                                         Superior.
                                         Michigan)
                                                      residua)
DOT
Brown         FL    Great Lakes  0.28 (*hole     —
bullhead            (Ontario,    body
                    Huron,       realdue)
                    Erie,
                    Superior.
                    Michigan)
                                                                                        sane as above
                                                                                 Reinert
                                                                                 (1970),ftMIC-
                                                                                 196
DOT
                     Carp
                                   Ft
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior.
                    Michigan)
             1.93 (Hhola
             body residue)
                                                                                        saae as above
                                                                    Reinert
                                                                    (1<»70>.
                                                                    4MIC-196
DOT
Channel
catfish
                                   FL
Great Lakes
(Ontario,
Huron,
Brie,
Superior,
Michigan)
ft.90 (xhole
body residue)
                                                                                        sane as above
Reinert
(1970).
•HIC-196
DOT
coho sal-on   FL    Great Lakes  0.72 (whole
(flesh)             (Ontario,    body residue)
                    Huron,
                    Erie,
                    Superior,
                    Michigan)
                                                                                        sa«e as above
                                                                                  Reinert
                                                                                  (1970).»MIC-
                                                                                  196
DOT
 Coho sol won
 (eqos)
                                   FL
Great Lakes
(Ontario,
Huron,
Brie,
Superior.
Michigan)
2.12  (whole
body  residue)
                                                                                        saae as above
Reinert
(1970),»MIC-
196
-------
Coaoound

Field Field
Orgnnls" Study Location
Lake
Michigan)
Toxlclty.
Active
Ingredient,
Ppn

Experimental
Variables,
Control led
or Noted Comments

Reference

DOT
                     Cvorlnus
                     carplo
                                   FR
DOT
DOT
DOT
DOT
DOT
DOT
                     Catostotus    FR
                     commersonl
                     Amelurus      FR
                     nebulosus
                     Perca         FR
                     f lavescens
                     Csox luclus   FR
                     «»bI oolites   FR
                     ruoestrls
                     Ca«pelom» sp. FR
St. Lawrence 0.3(1(0.33 Don
River,       max tissue
Montreal,    residue)
Canada
St. Lawrence 0.38(1.33 apu
River,       max tissue
Montreal,    residue)
Canada

St. Lawrence 0.3MD.1? Don
Piver,       aax tissue
Hontreal,    residue)
Canada

St. Lawrence 0.38 (0.?Sppm
River,       max tissue
Montreal,    residue)
Canada

St. Lawrence 0.38 (0.38
River,       ppi»«ax tissue
Montreal,    residue)
Canada

St. Lawrence 0.38(0.02 POM
River,       nax tissue
Montreal,    residue)
Canada

St. Lawrence 0.36 <0.">0po»
River,       nax tissue
Montreal,    residue)
Canada
        Residues of ODD were measured In  Fredeen, et
water, irud, molluscs, and fish durlnq and at (1970),
after 1)00 application in 1967.  Sa«0ling  •MIC-53't
points were shove the point of
apotlcatlon and 10 and <•? «i downstream.
Residues fro* unknown sources were
detected upstream.  Qownstreao residues
were more than twice those obtained
upstream (0.156 versus 0.369 ppn).  The
hlqhest concentration in an Individual
fish was 1.R1 ppm.
                                                                                        sane as above
                                                                                        same as above
                                                                                        same  as above
                                                                                        sane  as above
                                                                                        sane  as above
                                                                                        sa»e as-above
                                          Fredeen, et
                                          al
                                          (1970).A1IC-
                                          Fredeen, et
                                          al (1970).
                                          AHIC-S3I.
                                          Fredeen, et
                                          al (1970),
                                          AMIC-531.
                                                                                                                           Fredeen, et
                                                                                                                           al  (1970),
                                                                                                                           AHTC-S3*
                                          Fredeen, et
                                          al
                                          (1970),«HIC-
                                          53«.

                                          Fredeen, et
                                          at (1970),
                                          ANIC-53ii
DOT
                     Cyprlnodon    BSA
                                                      0.015-0.02 (K>  a*.
                                                                                         Sensitivity of three generations  Holland, et
-------
         DOT
f
3
          00 VP
          00 VP
          00 VP
          00 VP
          DDVP
                               varleqatus
                               (90-70 ••)
                                                                                seaNater
                               tonthle
                                                   Trout Creek, 9.012-0.068
                                                   Hasatch      (Kl
                                                   County,Utah
                                                 Streaa
                                                 flow
                               (.•bee rohlta
                               (fry)
                                             BSA
                                                                11.? CT7>
                                                                                a,e,d,e,f
                               Labeo rohlta   BSA
                               fflnq.rllng)
Trichoqaster  BSA
fasclfttus
lyounq)

Trlchogaster  BSA
faselitus
(a>lult>
                               Ch*nna
                               punc tutus
                               tfry)
                                             BSA
                                                                22.* tT7)
                                                                1.8 «T7I
                                                                ?.«. (T7)
                                                                0.8 IT7J
                                                                                a,c,d,e,f
                                                                                a.c,d,c,f
                                                 a,c>d,«,T
of sheepshead nlnnoMs to DOT and Endrln   al 119701,
Mas determined.  Sensitivity to DOT       AHIC-726
varied seasonally.  Fish Mere bred in
ponds 15m X 5m X t.25m exposed to
pesticides In aauarla, and survivors used
for breeding.  The results for DOT Mere
not entirely clear due to the seasonal
variability.  Increased and decreased
sensitivity Mere recorded for the Fl
generation at different tines. Increased
sensitivity for the F7, and decreased for
the F3.  The authors stated that
incorporation of DOT in ova via llnids
•ay have caused increased sensitivity.
Endrln toxicity MBS decreased in the Fl
and Increased In the F? generation.

        Complete deoopulatlon Has found   Sonstelle
at the collection station ?ODD m          11969),
downstream from aoplicatlon point.        AMIC-96*
Insect mortality Mas Independent of DOT
concentration In areas of turbulent floM,
thus mortality Has not directly related
to HOT concentration in this field
situation.  Repopulatlon Mas Incomplete
after 57 MK.

        DDVP and Phosohamldon Mere shoMn  Konar
to be selective toxicants that can be     (1969> ,AM,IC-
used for eradication of undesirable       5*53
animals fro* ponds Mlthout injuring carp.
 OOVP seeeed superior since less Mas
needed. It Mas not influenced by
turbidity, and It detoxified more rapidly
than Phosohamldon.

       sane as above                      Konar
                                          «!<169l,AHtC-
                                          5U53

       saae as above                      Konar(19691,
                                                                                                  saae as above
                                                                                                  save as above
                                          Konar
                                          (19691, A1IC-
                                          51.57

                                          Konar
                                          (1969» ,
                                          AHIC-51.53
         OOVP
                              Puntlus
                                            BSA
                                                                6.2  (T7>
                                                                                                  saae  as  above
                                                                                                                                    Konar
-------
Comoound

OQVP
OOVP
DOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
Field Field
Organism Study Loeatloi
sophore
(adult)
*nabas BS* —
testudineus
Hetaropnaus- BS* —
tea foaailis
Esomus BS* —
danrlca
(Try)
Esomus BS*
danrlca
(adult)
Notoneeta sp. BS* —
Dytlscus sp. BS* — -
(1 arvae)
Dytlscus sp. BS* ~
(adult)
Spha»rod*ma BS* --
annul a turn
Panatra BS*
fl liforuls
Anisootera BSA ~
(nvmohsl
Cytilster sp. BS*
Toxlclty, Exoerlmental
Active Variables,
Inqredlent, Controlled
n Pom or Noted

11.7 (T7) a.c.d.e.f
17.8 (T7) a,c,d,e,f
2.8 (T7) a,c,d.e,(
18.? (T7) a.c.d.e.f
0.001 (T7) a,c,d,e,l
0.06<. (T7I a.c.d.e.f
0.35 (T7) a.c.d.e.f
0.085 (T7) a.c.d.e.l
0.13 (T7) a.c.d.e.l
0.15 (T7) a.c.d.e.f
0.21 (T7> a.c.d.e.f
Comments

same as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
Reference
(19*9) ,»HIC-
Konar
(1969) ,
Konar
Konar
(1969) ,*MIC-
Konar
(1969) .AHIC-
Konar
(1969) ,
Konar
(1969), *MIC-
51.53
Konar
51.53
Konar
Konar
(1969),
AMIC-51.53
Konar
(1969),*HIC-
51.53
Konar
(1969),
AHIC-St.53
-------
         ODVP
                              Neoa so.
                                            BSA   —
                                                               0.27 (T7)       a,c,       a,e,d,»,f
                                                                                                 Sao* as above
Konar
(1969).
         OOVP
         00 VP
                              Hydroonllus   BSA
                              SO.
                              Volvox
                                            BSA   —
                                                               0.39 (T7t       a,c,d,e.f
                                                               5.0 (NTE)       a,e,d.e,f
                                                                                                 sane as above
                                                                                                 sane as above
Konsr
(1969),
A1TC-5I.53

Konar
(1969).
         00 VP
                              Pandorlna     BSA
                                                               5.0 (NTE)       »,e,d,*.l
                                                                                                 sane as above
                                                                                                                                    IConar
                                                                                                                                    (1959),
s
         00 VP
         00 VP
         OOVP
                              Closterlun    BSA
                              Brachlonys    BSA
                              Gastrotrleha  BSA
                                                               5.0 (NTE)       a.c.d.e.f
                                                               9.0 (NTE)       a,c,d,e,f
                                                                .0 (NTE)       a.c.d.e.f
                                                                                                 same as above
                                                                                                 sane as above
                                                                                                 sane as above
                                                                                                                                    Konar
Konsr
(1969) ,
AMIC-5U53

Konar
(1969).
         OOVP
         OOVP
         DOVP
                              Cvorls
                                            BSA
                              Cyclops       BSA   —
                              Nauollus      BSA   —
                                                               1.0 (K>
                                                               0.5 (K>
                                                               0.5 (K)
                                                                               a,c,d,e,f
                                                                               a.e.d.e.f
                                                                               9,c,d,e,f
                                                                                                 sane as above
                                                                                                 sane as above
                                                                                                 sane as above
Konar
(1969),
AMIC-5I.53

Konar
(1969),
AMIC-SU53

Konar
(1969).
AHIC-51,53
         OOVP
         DOVP
                              Daohnla
                                            BSA   —
                              Cerlodaphnla  BSA
                                                               0.5 (K)
                                                               0.5 (K)
                                                                               a,c,d,e,f
                                                                               a,c,d,e,f
                                                                                                 sane as above
                                                                                                 sane as above
Konar
(1969),
AHTC-S4.5J

Konar
(1969).
AHIC-5W53
-------
Compound
OOVP
OOVP
OOVP
DOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
MVP
Field Field
Organise Study Location
Dlaptomus 8SA —
Nandus nandus BSA —
•Ufa rlta 8SA
Apohlonou* BSA —
cuchla
Mystus BSA —
vitatus
tlry»
Mystus BSA —
vitatus
(adult)
Puntlus BSA
sophore
lfry>
Chann* BSA —
punctatus
(1 Inqert lnq>
Cnanna BSA —
punctatus
(adult)
Mastocembelus BSA —
pancalus
Hacroqnatnus BSA ~
acu lea turn
Cttanna L —
punctatus
Toxlclty,
Active
Ingredient,
Ppm
0.5 (K)
2.6 CT7)
2.8 (T7)
3.1, (T7)
2.3 CT7)
6.6 
1.0 (T7)
1.8 (T71
2.9 (T7>
2.6 (T7)
3.6 «T7I
20 (SB1)
Experimental
Variables,
Control led
or Noted Comments
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e, f same as above
a,c,d,e, f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a* Snakehead fish eqgs Here
unaffected by OOVP concentrations of
Reference
Konar
(1969),
AMIC-SWS
Konar
(1989),
Konar
Konar
AHTC-SI.53
Konar
(1969) ,
Konar
(1969),
Konar
(1969),
AMIC-SI.53
(1969),»1tC-
Konar
(I960) ,ASIC-
5*53
Konar (1069),
AMIC-5»S3
Konar (19S9).
AMIC-"il,53
Konar
less (1969), AMIC-
-------
Oecamethonlu*
dl bromide
                      leqq*)
Channa
punctafus
(hatch!lnq«)

Neqaprlon
brevlrostrls
                                   L      —
                                   BSA
                                                        .5 IT2)
90 .0
                                                                                  ppm and stopped at 5.Q  ppm or more.   Eggs
                                                                                  and hatch!Ings survived Hell at  0.1  ppm
                                                                                  DOVP.

                                                                                         same as above                      Konar
•HIC-6T8S

Baldridqe
(1969).
*MIC-383?
*«              Data fro* study of drug effects
           on younq lemon sharks Here treated
           mathematically to demonstrate
           applicability of classical rate theory to
           the study of chemical shark deterrents.
           Incaoacltatlon (narcosis)  xas the orlnary
           parameter timed for effectiveness.  This
           Has usually quite rapid for the more
           effective druas.
                                                                    The effect o« 57 pesticides on    Davis, et «l
                                                            embryonic development of clans and
                                                            oysters Has reported.  Svnerglstlc        (1969)«»MIC-
                                                            effects Hlth solvents Here also reported. 5990
                                                             Most of the compounds affected
                                                            develocment more than survival.  Some,
                                                            honever, drastically reduced larval
                                                            growth.  The authors point out the
                                                            necessity of evaluating the effects of
                                                            pesticides on all  life stages of an
                                                            organise and note  the possibility of
                                                            selecting chemicals for pest control that
                                                            Mould not have serious effect on
                                                            shellfish.
                                                                                        same as above
                —                  Approximate toxlclties of
                           numerous pesticides commonly used  in
                           Britain were summarized.  An excellent
                           brief,  general  discussion of toxlclty
                           testing Is also present.

                «*(contin-          One hundred-forty surface  active
                uoua  aer-   agents, solvent emulslflers, pesticides,
                ation,  sea-DO I yen lorInated blohenyls,  pure
                water,  and  Inorganic, and  organic chemicals ner«
                           evaluated against as many as ten marine
                           organisms.  The authors noted that most
                           published data  of  this type deal tilth
Davis, et al

(1169),»HIC-
5990

HaHdeslev-Th
  om«s(197t)
AMIC-105%
                                                                                                                           Port»ann, «t
                                                                                                                           al (1971),
                                                                                                                           AMIC-7701
-------
Toxlcity, Experimental

Field Field
Coaoound Organise Study Location


Oeraol Crangon BSA —
crangon





0«r*ol Pandalv* BSA —
•ontagul





Oa Oe Tana ?? Rasbora BCF* —
hateroKoroha and
BS»










Oa Oe Tana (llauld) Rasbora BCF* —
heteroaorpha and
BSA







Active Variables,
Ingredient, Controlled
Poa or Noted
solution
renewal)
100-330 «TZ) a«(contin-
uous aer-
ation, sea-
uator, and
daily
solution
renewal)
108-330  a*,c,c,r.
hard
IHHIor
soft (SH)
synthetic
dilution
Hater, or
seanater
t or soae
species


Conaents
toxlclty of chemicals to. freshMater
orqanlsos.
saae as above






sane as above






On* hundred sixty-tour
DesticldeSf wetting agents, and
alscel taneous Hater pollutants shoxed a
wide ranqe of toxlclty soannlnq 12 orders
of miqnltude. Knowlna the toxiclty and •
percentage of al 1 comoonents of a
formulation did not result In easy
predictability of the toxlclty ot a
•Ixture of Materials. Sonetlnes
pesticides Here nost toxic in hard Hater
and sotet lines the opposite Has true.
Testing the actual material as sold Has
found to be essential.
saae as abova











Reference


Portnann, et
al (19711,
«HIC-r7«l




Portaann, et
al 11971),
•MIC-77C1




Alabaster,
(19691, AHIC-
5*?5










Alabaster,
(1969), AMIC-
5*25







-------
Da Oe Tana  (liquid!
Rasbora
heteronorpha
8Cf»
•nd
BSA
0.02 CT2 In
acetone!
Oe 0« Ten* (oast*)
                     Rasbora
                     heteroaorpha
              RCFA
              and
              BSA
                                                       10.7 (Tl)

0* 0* Tan*
(xettable)
Rasbora
heteronorpha
BCFA
and
BS*
0.001 IT2 tin
acetone)
Oa 0* Tana
(••tfabta)
ffasbora
heteronorpha
BCF*
and
flS*
                                                       8.2 IT2)
a*fc,«,f ,
hard (HW)
or soft
(SH)
synthetic
dilution
••atari  or
seanater
for son*
species

a*,c,e,f.
bmrd (HW)
or soft
(W)
thatia
dilution
vater,  or
MMmter
tor some
•paeles
                                                                       hard (HW)
                                                                       or soft
                                                                       (SHI
                                                                       synthetic
                                                                       dilution
                                                                       Mater,  or
                                                                       seaxater
                                                                       for some
                                                                       soecles
                                                                       hard
                                                                       IHW)or
                                                                       soft  (SH)
                                                                       synthetic
                                                                       dilution
                                                                       nat*r,  or
                                                                       saaHater
                                                                       for soaa
                                                                       spaclas
                                                                                         saaa as abova
                                                                                                                            Alabaster,
                                                                                                                            fl<96
                                                                     ANIC-892
-------
  Comoound
                       Organism
Field  Field
Study Location
                                                       Toxlclty,
                                                       Active
                                                       Ingredient,
Exo«rI mental
Variables,
Control led
or Noted
                                                                                                  Comments
                                                                                                                           Reference
Olazlnon
                     Pasbora
                     heteromorpha
BCFA
and
OS*
                                                       l.«»S  IT1)
Placlnon
 Olcamba
                     papulifera.
                      Gammarus
                      tasclatus
                                    BSA
                                                      100 (K)
                    greater  than
                    100.0  IT3)
a»,c,e,f,
hard (HW)
or soft
(SO syn-
thetic
water, or
aoawater
Tor son*
speclea
                                    Euntor'i
                                    medium
                                    diluted
                                    1:5
                                                                       a»
 Olcaajba
                      Paleomontes   BS»
                      kadiakens Is
                    greater  than
                    100.0  (T2)
more toxic thar CuSO»
miscellaneous wafer oollutanrs showed a   AHIC—5*>?5
wide ranoe of toxlcity scanning 12 orders
of magnitude.  Knowing the toxlclty and

formulation did not result in easy
prcrtlctabl11tv of the toxicity of a
mixture of materials.  Sometimes
pesticides were most toxic in hard water
and sometimes the ooposite was true.
Testing the actual material as sold was
found to be essential.

         All  compounds were harmful to
duckweed to  sons  degree.   Decreased
populations  were  noted at non-lethal
concentrations  and  some  compounds
(Kalathlon  and  2,l).-D)  caused  teratogenio
effects at concentrations as  low as 1 ppn.

        Of  the  aquatic weed herbicides
evaluated, Dlclone  was the most  toxic,
Daphnla was  generally the most sensitive   IV]
organism.  All  of  the Crustacea  were
affected by  much  lower concentration
levels of herbicides  than Indicated by
the TL sub SO values.  All of the animals
represent  Important  food  chain links.

       sane  as  above                      Sanders
                                           «1970),AHIC-
                                                     kiorthley, et
                                                     al  (1971),
                                                     AKIC-3233
                                                                                         Sander*
 Olcamba
Olcaaea
                      •sell us       8S»
                      brevlcaudus
                      Orconectes    BS»
                      nals
                    greater  than
                    100.0  (T2)
                    greater  than
                    100.0  IT?)
                                                                                         same as above
                                                                                         same as above
                                                      Sanders
                                                      11970),AMIC-
                                                      *53

                                                      Sanders
                                                      (1970>,AHIC-
                                                      *S3
Oleaaba
                      Oaohnla aagna BS*    —
                                                       greater than
                                                                                         sarnie as above
                                                                                                                            Sander*
-------
                                                                 loo.o
                                                                                                                                      (1970),*HIC-
          Olcamba
                               Cypridoosls   BS*
                               vldua
greater than
100.0 ITZ)
                                                                                                  sane as above
Sanders
(1970),»1IC-
          Oicamba
          Olcapthon
                               Leoonis       BS*
                               •acrochlrus
                               Mercenarla
                               •ercenarla
                               (eggs)

                                                                l-O.O tti)
                                                                     
                                                                5.7 (T2)
          OIeMot>«nll
                               Cal llhacfIs
                               sp.  (nymoh,
                               8-12 «•>
                                             8S»
                                                                10.3 (Tl>)
                                                                     Sanders
                                                                     (1970)t
                                                                     AMIC-WS3
                ~                 The effect of 5? pesticides on    Davis, «t al
                           embryonic development of clams and
                           oysters MBS reported.  Synergistic        (1969)»AHIC-
                           effects Mlfh solvents Here also reported. 5990
                            Most  of the compounds affected
                           develocment more than survival.  Some,
                           however, drastically reduced larval
                           gronth.  The authors point out the
                           necessity of evaluating the effects of
                           pesticides on all  life stages of  an
                           organism and note  the possibility of
                           selecting chemicals for pest control that
                           Hould  not have serious effect on
                           shell fish.

                —                same as above                      Davis, et al

                                                                     (1969),*HIC-
                                                                     599D

                a*,c,e,f.           One hundred sixty-four            Alabaster
                hard  (HM)   pesticides, netting agents, and           (1969),
                or         miscellaneous Hater oollutants shoned a    AHIC—5*»?5
                SOFT(SH)    Hide range of toxlcity spanning 12 orders
                synthetic   of  magnitude.  Knowing the toxlcity and
                dilution    percentage of all  components of a
                Hater,  or   formulation did not result in easy
                seanater    predictability of  the toxlcity of a
                for some    mixture of materials.  Sometimes
                species    pesticides Mere most toxic in hard Mater
                           and sometimes the  opposite Has true.
                           Testing the actual  material as sold xas
                           found  to be essential.

               ««,b»,c,f.          The toxlcity of  herbicides Olouat Wilson, et
                1,1, and    and Dichlobenll  to  aquatic invertebrates   al  (1969),
                fllllca,     and fish Mas determined  in aquaria        ANIC-5<>52
                Calcium,    containing substrates natural  to  each
               nagneslura.  soecles.  Dlouat was nulte toxic  to H.
                sodium,     azeteca but not  as  toxic  to other
               potassium,  organisms.  Olchlohenll  Has less  toxic to
                           M.  azeteeus but considerably more toxic
-------
Toxlclty, Exoerimental
Active Variables,
Field Field Ingredient, Controlled
Comoound Organism Study Location Po» or Noted Comments
blcarbon- to th*> remaining organism than OiQuat
ate. Hud lessened the toxlcltv ot both, but
carbonate, more so for Olquat. Oichtobenll had a
SUlfate, sublethal narcotizing effect on the
Iron, organisms that resulted In
dissolved Immobilization. It Has concluded that
solids, both herbicides could adversely affect
conduc- certain fish food organisms.
tanee
Olchlobvnll RalUbRctls BSA — 7.* (S8«.) **,b«,c,r, same as above
so. Cnymoh, 1,1, and
8-1? ••) silica,
calcium,
magnesium.
sodlun,
potassium,
blcarbon-
ata,
carbonate.
sulfate,
iron.
dissolved
solids,
conduc-
tance
Olchlobenli Leoonls BSA — lit. 7 (Tit) a»,b»,c,f, sane as above
•acrochlrus 1,1, and
silica,
calcium,
oagnesium,
sodium.
potassium,
bicarbon-
ate,
carbonate.
sulfata.
iron.
dissolved
solids,
conduc-
tance
Reference









Nllson, et
at (1969),
»MIC-5
-------
OleMobenll
Libel lull ip. ASA
(naiad. 16-24
qreater thanlOO a»,b»,c,f,
(T 1-M         1,1, and
                silica,
                calcium,
                magnesium,
                sodium,
                potassium,
                bicarbon-
                ate,
                carbonate,
                sulfate,
                Iron,
                dissolved
                solids,
                conduc-
                tance
                                                                                          sa>e as above
Wilson, «t
al (1969),
OlcMobenll
Libellul» so. BSA
(n*lad, .16-?«t
••I
greater ThanlOO »»,b»,c,f,
tse l-«»t        1,1, and
                silica,
                calcium,
                magnesium,
                sodium,
                potasslua,
                bicarbon-
                ate,
                carbdhate,
                solTata,
                iron,
                dissolved
                solids,
                conduc-
                tance
                                                                                          sane as above
Mil son, et
al (1969),
*MIC-5«>52
Olchlob«nl!
                                                       13.0  (TV)
                      so.  (larva,
                      15-2D ••»
                                                  a»,b«,c,f,
                                                  1,1,  and
                                                  silica,
                                                  calcium,
                                                  magnesium,
                                                  sodium,
                                                  potassium,
                                                  bicarbon-
                                                  ate,
                                                                                          saee as above
                                                                      Milton, «T
                                                                      al (19691,
-------
Toxlclty, CxDerlmental
Active Variables.
Field Field Ingredient, Controlled
Conoouno Organise Study Location Po« or Noted
carbonate,
sulfate,
iron,
dissolved
solids,
conduc-
tance
Olehlobenll Llnmeohl tus BSA — 13.BO (SB*) *».b»,c,f,
so. (larva. ^J; •nd
1S-?0 «•> silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
aulfate,
Iron,
dissolved
solids,
conduc-
tance
Olchlobenll Hlcrooterus BSA -- 1Z.5 ITU) •.*,b»,c,f,
salHoldes 1,1, and
silica,
calcium,
magnesium,
sodiun,
potasaiua,
bicarbon-
ate,
carbonate,
sulfate,
iron,
dissolved
solids,
conduc-
tance
Connents
same as above
sane as above
Reference
Wilson, et
at (196S),
Wilson, et
al  (1965),
-------
           Dletilobenll
                                Myalella
                                •zeteca
                                (adult. *-•
                                              BSA   —
                                                                 8.5  (TO
>
I
          Dlchlooenll
                                Hy*lelta
                                azteea
                                ••dolt, k-«
                                Mt
                                              BS»   —
                                                                 2.8  csav)
          OlcMebcnll
Enallaq** sp. BS»
(nal»d, 16-7*
•a)
                                                                 12.3 (SBl)
                                                  1,1,
                                                  •iliea,
                                                  calcium,
                                                  nagneaiua,
                                                  sodlun,
                                                  potassium,
                                                  bicerbon-
                                                  at«,
                                                  carbonate,
                                                  aulfata.
                                                  Iron,
                                                  dissolved
                                                  solids,
                                                  conduc-
                                                  tance
 •*,b«,c,r,
 1,1. and
 silica,
 calcium,
 •agneslun,
 •odium,
 potassium,
 bicarbon-
 ate,
 carbonate,
 sulfate.
 Iron,
 dissolved
 solids,
 conduc-
 tance

a*,D».e,f,
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
                                                                                                    SMC »s sbove
                                                       Mllson, et
                                                       al Il,
                                                       •HIC-Sl.52
                                                                                                         as above
                                                                                                                                       Wilson, et
                                                                                                    saae  as  above
Wilson, et
• I (19691,
-------
I
ToxIclTy, Experimental
Active Variables,
Fl^ld Field Ingredient, Controlled
Compound Organls" Study Location ._ Pp» or Noted Comments
carbonate,
solfata.
iron,
dissolved
solids,
conduc-
tance
DlcMobenll Fnallaqaa SP. BSA — 20.7 tT«»> m»fbV,c,r, sa«« as abov«
(naiad, 16-Z* 1,1, and
••) silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate.
Iron,
dissolved
solids,
conduc-
tance
Reference







Wilson, «t
al (1969),
«HIC-S«.52













         DlcMobonll
         Olchlobenll
         Olehlobenll
         Dlchlobcnll
                              Gamnarus
                              fasclatus
                                            RSA
18.0 (T2),  10.0  a»
                               Orconectes
                               nals
                              Paleonontes    BSA
                              kadlakensls
                               •sellus        BSA
                               brevlcaudus
                                                                9.0  (T2I
                                                                                8»
                                             BSA   —
                                   Of the aquatic weed herbicides
                           evaluated, Olclone was the most toxic,
                           Oaonnla was qenerally the most sensitive
                           orqanlsm.  All of the Crustacea Mere
                           affected by much lower concentration
                           levels of herbicides than indicated by
                           the TL sub SO values.  All of the animals
                           represent Import ant food chain links.

                                  same as above
Sanders
(t<970>.
                                                                                                                                     Sanders
                                                                3
-------
Olehlobenll
Dlchlobenll
Olchlobenll
Dlehlone
                      Daohnla  magna  BS»    —
                     Cyorldopsls    BSA
                     vldua
                     Leoomls       BSA
                     •acroehlrin
                     Sal«o         BCFA
                     galrdnerl     and
                                   BSA
                                                       10.0 CT21
                                                       7.a  
                                                 a*,c,e,f,
                                                 bard IHWJ
                                                 or soft
                                                 ISW) syn-
                                                 thetic
                                                 dilution
                                                 water, or
                                                 seawater
                                                 for some
                                                 opeeles
OleMon*
Gammarus      BSA
fasclatus
                                                       0.21.  (T2),  0.10 a*
Olchlone
Olehlon*
Olchlon*
OieMon*
                     Palconiontes
                     Asrltus       BS»
                     Orconectes    BSA
                     nals
                     Daphnla «aqna BSA   —
                                                      fl.1.5 (T2)
                                                      0.20 (T2)
                                                      3.2 IT2)
                                                      0.025 (T2>
                                                                                         san« as above
                                                                                         sane as above
                                                                                         sane  as above
                                                                                                                            Sanders
                                                                                                                            11970) ,
                                                                                                                            AMIC-1,53

                                                                                                                            Sanlers
                                                                                        same  as above
                                                                                         sane  as above
                                                                                        same as abova
        One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants shooed a
Hide range of toxlcity scanning 12 orders
of magnitude.  Knotting the toxlcity and
percentage of all eoitoonents of a
formulation did not result in easy
predictability of the toxlcity of a
mixture of materials.  Sometimes
pesticides Mere most toxic in hard Mater
and sometimes the ooooslte was true.
Testing the actual material as sold Has
found to be essential.

        Of the aauatlc Meed herbicides
evaluated. Olclone was the most toxic.
Daphnia Mas generally the most sensitive
organism.  All of the Crustacea Mere
affected by much lower- concentration
levels of herbicides than Indicated by
the TL sub SO values.  All of the animals
represent Important food chain links.

       same as above
AMIC-«t53

Sanders
I19TO) ,
AHIC-i.53

Alabaster
(1959),
AHIC-5V25
                                                                                                                           Sanders
                                                                                                                           <1970>,
                                                                                                                           AMIC-1.53
                                                                                                      Sanders
                                                                                                      C197P),
                                                                                                      ANIC-1.53

                                                                                                      Sanders
                                                                                                      <197t» •
                                                                                                      AMIC-
                                                                                        same as above
                                                                                                                           Sanders
-------
Compound

OrqanlSM
vldua
Field Field
Study Location

Toxlclty.
Active
Ingredient.
Ppa

Experlaental
Variables.
Controlled
or Noted

Coaioents Reference
(19701.
         Olchlon*
                              leooals
                              •acrochlrus
                                            BS»   —
                                                               0.12 
                                                                                                 sane as above
                                                                                                      Sanders
                                                                                                      <197d>,
         OlcMorfenthlon
•asbora       BCFA
heteroporoha  and
              BSA
                                                               1.9 (T2)
i
         Oichtorfenthlon
ftasbora       BCFA
heteroMorptta  and
              BSA
                                                               Z.I IT1)
                                                 •*»*»*»f.          One hundred sixty—four
                                                 bard (HW)  pesticides, wetting agents, and
                                                 or soft    Mlscellaneous water oollutants showed a
                                                            wide range of toxlclty soannlnq 1? orders
                                                            of  Maqnltude.  Knowlnq the toxlclty and
                                                            percentage of all  covoonents of a
                                                            (emulation did not result in easy
                                                            predictability of  the toxlclty of a
                                                            Mixture of Materials.  SoMetiws
                                                            pesticides Mere most toxic In hard Mater
                                                            and soMetiaes the  opposite was true.
                                                            Testlnq the actual  Material as sold Mas
                                                            found to be essential.

                                                                   saae as above
                                                                                                                                    Alabaster
                                                                                                                                    (1969),
                                                      ffn-
                                                 thotio
                                                 dilution
                                                 KBtor, Or
                                                 •mtrator
                                                 fOr aXNM
                                                 •paelea
                                                                               hard (HW)
                                                                               or soft
                                                                               (Stf) fjn-
                                                                               thotie
                                                                               ••tor, or
                                                                               •ewtmtor
                                                                               for aoo.
                                                                                                      Alabaster
                                                                                                      11469).
                                                                                                      ANIC-5W25
         Oletilorfenlhlon
                              Rasbora       BCFA
                              heteroBorpha  and
                                            as*
                                                               (.73 ITZ)
         Dlchlore«hen (Na
         «altl
Salao
qalrdnerl
              BCFA
              and
              BS*
                                                               O.Z2 tT2>
                                                 hard'(Hw)
                                                 or aoft
                                                 (SO «jn-
                                                 tfaatlo
                                                 dUutloa
                                                 «at*r( or
                                                 •eawater
                                                 for-aoa«
                                                 •p«oi«*
a*,c,e,f,
hard
IHMIor
                                                                                                 saae  as above
                                                                                                      Alabaster
                                                                                                      (1969).
                                                                                                 saae as above
Alabaster
119691.
-------
          Olchlorophen  INa
          «alf>
Rasbora
heteromorpha
8CFA
and
BSA
                                                                9.19 (T2t
soft (SH>
synthetic
dilution
water,  or
seawater
for son*
species

a»,c,e,f,
bud (HW)
or soft
(SO syn-
thetic
water,  or
seawater
for tome
•pecle*
                                                                   sane as above
Alabaster
(1969).A1IC-
I
         Olchlorvo*
Rasbora
heteromorpha
BCFA
and
RS*
                                                                    (TZ)
         Oleldrln  115 percent  Rasbora
         N.O.I                 hat«ro»orpha
              BCF»
              •nd
              BS»
                                                                t.a
         Dlaldrln
         Dial OrIn
                               Fish  (net
                               specified)
Poocllla
latlolnna
                                            BCr»   —
                                                 hard (HW)
                                                 or
                                                 SOFT(SH)
                                                 synthetic
                                                 dilution
                                                 water, or
                                                 seaitater
                                                 for so««
                                                 species
                                   a>,c,etf.
                                   hardCHW)
                                   or soft
                                   (SHI
                                   synthetic
                                   dilution
                                   •ater, or
                                   seauatar
                                   for so»e
                                   species
                                 qreater than
                                 B.D01-0.01 (K)
                   0.003 (partial  a*
                   K?)
                   On» hundred sixty-four
           pesticides, M»TTlnq sqents,  and
           miscellaneous Hater oollutants showed a
           Hide range of toxlcity soanninq 12 orders
           of maqnltude*  KnoH(n<| thi* toxlclty and
           percentage of all coxoonents of a
           formulation did not result In easy
           predictability of the toxlcity of a
           •Ixture of Materials.  Sometimes
           pesticides Mere most toxic In hard water
           and soretlaes the opposite was true.
           Testing the actual Material  as sold was
           found to be essential.

                  sane as above
Alabaster
(1969),
                                                                                                                                    Alabaster
                   Approximate toxlcltles of         Nawdeslev-
           numerous pesticides conaonly used In      Thoaas(197t)
           Britain were summarized.  An excellent      AMIC-1056
           brief,  general  discussion of toxicity
           testing is also present.

                   Studies ware conducted with fish  Lane, «t al
           weighing 2-5 g  in saawater at a           (1970),
-------
  Compound
              Field  Field
  Organise    Study Location
                                                       Toxtclty,
                                                       Active
                                                       Ingredient,
Experimental
Variables.
Controlled
or Not«
-------
                                                                (SB)
                                                                                                                                     ctal (1971),
         Oleldrln
Larqe»outh
bass
FRL   Hlse. states 0.01-1.59
                   residue  (SB)
                                                                                                  same as above
Henderson,
Ft al
(1971),
»MIC-l«i07
         Oleldrtn
                              Brown
                              bulI head
              FRL   Misc. states 0.01-0.25
                                 residue  ISB)
                                                                                                  sane as above
                                                                                         Henderson,et
                                                                                         •I  (1971),
                                                                                         AHIC-1<.7
         Oleldrln
                              Carp
              FRL   Misc. states O.fll-O.S*
                                 residue  (SB)
                                                                                                  same as above
                                                                                         Henderson,
                                                                                         etal  (1971),
r
         Dleldrln
         Oleldrln
Channel      . FRL   Misc. states  0.01-0.36
catfish                           residue  (SB)
R*dhorse      FRL   Misc. states 0.01-0.1?
sucker                           residue  (SB)
                                                                                                  sane as above
                                                                    same  as above
                                                                                         Henderson,et
                                                                                         al  (1971),
                                                                                         »MIC-H.t»7

                                                                                         Henderson,
                                                                                         et  al
                                                                                         (1971),
         Oleldrln
Gizzard shad  FRL   Misc. states  0.05-0.50
                                  residue  (SB)
                                                                                                  sane as above
                                                                                        Henderson,et
                                                                                        al
         Dleldrln
                              Sootted
                              sucker
              FRL   Misc. states 0.30 residue
                                 (SB)
                                                                                                  sa«e as above
                                                                                         Henderson,et
                                                                                         al  (1971),
         Oleldrln
Blueqllts     FRL   Misc. states 0.01-0.9;
                                 residua  (SB)
                                                                                                  sane as above
                                                                                         Henderson,et
                                                                                         al  (1971),
                                                                                         »MIC-1<»07
         Oleldrln
Redbreast     FRL   Misc. states 0.01 residue
sunfish                          (SB)
                                                                                                  same as above
                                                                                         Henderson,
                                                                                         et  at
                                                                                         (1971),
                                                                                         •MIC-1W07
         Dleldrln
                               Striped
                               mullef
              FRL   Misc. states  0.02-0.39
                                  residue  (SB)
                                                                                                  same as above
                                                                                         Henderson,
                                                                                         et  al
                                                                                         (19711,
                                                                                         4MIC-1I.07
         Oleldrln
                               Rock  bass
              FRL   Misc.  states  0.07 residue
                                  (SB)
                                                                                                  same as above
                                                                                         Henderson,
                                                                                         et  al (1971),
                                                                                         4MIC-1U07
         Oleldrln
                               Bloater
                                             FRL   Misc.  states O.fl?-0.37
                                                                                                  same as above
                                                                                                                                     Henderson,et
-------
Conoound

Oleldrin
Oleldrin
Oleldrin

Oleldrin
Oleldrin
Dleldrln
Oleldrin
Dleldrln
Dleldrln
Oleldrin
Dleldrln
Organise

Lake
nnltef Isn
Lake trout
White crapole

Blqiiouth
buffalo
SnallHOuth
buffalo
Flathead
catfish
Goldeve
Ha II eve
Sauger
Flannelnouth
sucker
Freshwater
drum
Field
Study

FRL
FRL
FRL

FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
Toxlclty, Experimental
Active Variables,
Field Ingredient, Controlled
Location Pp* or Noted Conaents
residue (SB)
Misc. states 0.03 residue -- saae as above
(SB)
Nlsc. states 0.02 residue — saae as above
(SB)
Misc. states 0.02-0.27 — saae as above
residue (SB)

Misc. states O.fl*-0.42 ~ saae as above
residue (SB)
Misc. states 0.12 residue — - saae as above
(SB)
Nlsc. states 0.03 residue — saae as above
(SB)
Misc. states 0.01-0. OS -- saae as above
residue (SB)
Misc. states 0.01-0.03 — saee as above
residue (SB)
Misc. states 0.01 residue ~ saae as above
(SB)
Misc. states 0.01 residue -- saae as above
(SB)
Misc. states 0.0l|. residue — ••»«> >» above
(SB)
Reference
al (1971).
H enters on, et
• 1 I107i>,
AMIC-H.07
Henderson,
etal (1971),
AMIC-H»0T
Henderson,
«t al
»MIC-1«»07
Henderson,
et Hi
(1971),
AMIC-1»07
Henderson, et
el 11171),
AMIC-ll.07
Henderson, et
el (1971),
»Mir-iuo7
Henderson, et
al (1971),
AMIC-1V07
Henderson, et
al (1971),
Henderson,
et al (197U,
AMIC-1W07
Henderson,
et al
(1971),
AMIC-IVOT
Henderson, et
•1 (1971),
AKIC-IU07
-------
          Oleldrln
                     Black         FRL    HIsc.  states 0.01-0.03
                     bullhead                          residue (SB)
                                                                                                   sane as above
Henderson,et
81  (1971),
MIC-11.07 .
          Oleldrln
          Oleldrln
                               White bass    FRL   Misc. states  0.02 residue
                                                                 (SB)
                               Black crapole FRL   Misc. states  0.02-0.36
                                                                 residue  (SB)
                                                                                                   saae as above
                                                                                                   save as above
                                                                                                                            Henderson,
                                                                                                                            et  81(19711,
                                                                                                                            *MIC-1<.07

                                                                                                                            Henderson,et
                                                                                                                            al  (1
-------
Coaioound
Dieldrln
Dleldrln
Dleldrln
Dleldrln
Eleldrla
Dieldrln
Dleldrin
Oleldrln
Dleldrln
Field Field
Organise Study location
Ict&lurua FRLO Iowa
punctatua
Ictlobus FHLO Iowa
cyprlnellus
Cyprinua FRLO Iowa
carpi o
Hicropterus FRLO Iowa
sal no Ides
Carplodea sp HILO Iowa
Pomoxia FRLO Iowa
nlgronaculatua
Pomoxls FRLO Iowa
annular! a
Stlzostedlon FRLO Iowa
vl treuii
Tsox luclus FRLO Iowa
Toxlclty,
Active
Ingredient,
0.03H.6
( accumulation,
SB)
0.028-0.614.
(accumulation,
S3)
0.015-0.56
(accumulation,
SB)
0.11-0.08
(accumulation,
SB)
0.313
(accumulation,
SB)
0.012
(accumulation,
SB)
0.059
(accumulation,
S3)
0.01-0.06
(accumulation,
SB)
0.05
(accumulation,
SB)
Expert Mental
Variables,
Controlled
or Noted Consents
JSdlble fleah of flah collected from
rivers, lakes, ponda, and reservolra
waa analysed. Flab taken in areas
receiving agricultural runoff showed
bigheat accumulation, especially In
bottom feeding flab.
— Sane aa above
— sane aa above
— sane aa above
same as above
same aa above
same aa above
sane as above
-- saee as above
Reference
Horrls, et
al (1971),
AKIC-1US2
Morris, et
al (1971),
AKIC-114.52
Korrla, et
al (1971),
Morris, et
al U971 j.
Korrla et
al 11971),
Korrls, et
al i 1971),
AK1C-1U52
Horrla, et
al (1971;,
AKIC-U*.52
Horrls, et al
tl97t>.
Horrls, »t
et
1*52
-------
           Dleldrin
           Dleldrfn
           Dieldrln
           Dieldrln
Xctalarus     PRLO  low*
•elas
Lepomls       FHLO  Iowa
Bacrochirua
                                Esoz luclus    PRLO  low*
                                Roccua
                                              FRLO  Iowa
             0.098
             (accumulation,
             SB)

             0.01I4.-0.03U
             (accuaulatlon,
             SB)

             0.05
             (accumulation,
             SB)

             0.091-0.175
             (accumulation,
             SB)
                                                                                                   aua  as above
                                                                                                  aaaa  as  above
                                                                                                  MOM as above
                                                                                                  sane as aboTa
                                          Korrls,  et
                                          al  (1971),
                                          AMIC-U4.52

                                          Korrls,  et
                                          al  (1971).
                                          AKIC-ll;52

                                          Korrls,  et
                                          •1  (1971).
                                          AHIC-11^2

                                          Morris,  et
                                          al  (1971),
I
          Oleldrln
          01*1drln
          Oleldrln
Anacystis
nidutans
          Oleldrln
          Oleldrln
                               lloatui
                                Leptodlus
                                f I or I (Janus
                                (larvae)
                                              a      ^^
                                             l_      •••»
P»nop*nus
ncrbstll
Clarviif)

Llaneohllus
rhOBblcui
(Iarvael
                                             •      —^
                                             FS
             0.5-1.8 (qrowth a»,c»,r
             Inhibited)      SN
                                                                 0.5-1.0 (groMth e*,c*.r
                                                                 Inhibited)       SH
                                                                 5-10 ppb(K)      ~
                                                                 5-10  DPb  (K)     —
             O.OBZ(Mhole
Creek, Oun   body residue)
County,
Misc.
  Batterton,
etal
                                                                                                      Batterton,
                                                                                                      et  al
                                                                                                      (19711,
        Metabolic products of Al
-------
  Comooun*
                        Organism
Field  Field
Study Location
Toxlclty,
Active
Ingr«di«nt,
  Ppm
Exoerlmental
Variables,
Control led
or Noted
                                                                                                  Comments
                                                                                                                            Reference
Oleldrln
01 eldrIn
01 eldrIn
Oleldrln
Oleldrln
 Oleldrln
 Oleldrln
 Oleldrln
 Oleldrln
                      Stalls so.     FS
                      (larvae)
                      Gamaarus sir*  FS
                      Salvellnus    FS
                      Iontlnalls
                      Senotllus     FS
                      atromaculatus
                      Cottus balrdl  FS
                      Rhlnlehthys   FS
                      atratulus
                      Salvellnus    FS
                      T ontlnalls
                      Semotllus     FS
                      atromaculatus
                      Cottus balrdl  FS
      Knights
      Creek, Dun
      County.
      Misc.

      Knights
      Creek , Dun
      County.
      MISC.

      Knights
      Creek, Dun
      County,Misc.

      Knights
      Creek, Oun
      County,
      Hlsc.

      Knights
      Creek, Oun
      County,
      Misc.

      Knights
      Creek, Dun
      County,Wise.

      Knights
      Creek, Oun
      County,Misc.

      Knights
      Creek« Oun
      County.
      Wise.

      Knights
      Creek, Oun
0.01T
(nhotebody
residue)
                                                       0.005-0.01!
                                                       (xholebody
                                                       residue)
0.008-0.011.
(uhole body
residua)

0.006-0.013
(whole body
residue)
                                                       0.007-0.017
                                                       (whole body
                                                       residue)
0 (Mholebody
residue)
0.18-0.?6(fat
residue)
0.17-0.3* (tat
residue)
                                                       0.3-0.7
                                                       (fat
                                                       residue*
                                                                                  0-0.005 DDK dleldrln. Fndrln residues ot
                                                                                  0.011-0.0?5 opin and O.OOZ-0.006. DP*
                                                                                  dleldrln were tound In debris samples.'
                                                                                  OesDlte United control data, residue
                                                                                  analyses Indicated that contamination of
                                                                                  the environment studied Has United.

                                                                                         same as above
                                                                                         sane as above
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                                                         sane as above
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                     Moubrv,  et
                                                     al  (H6S),
                                                     tMIC-3751
                                                                     (•oubry, et
                                                                     al  <1"6*).
                                                                     AHIC-37SJ
                                                     Houbry,  «t
                                                     al
                                                     Koubrv, et
                                                     al
                                                     (19SB) .AHIC-
                                                     3751

                                                     Houbry, et
                                                     al (11691,
                                                     4HIC-375J
                                                     Moubry, et
                                                     al (19SA1,
                                                     Moubry, et
                                                     al (1968),
                                                     4MIC-375J

                                                     Noubry, et
                                                     al (1968).
                                                     AMIC-37SJ
                                                                      Moubry. «t
                                                                      al  (1968).
-------
Dleldrin
OlelOVln
                     fthlnlehthys
                     atratulus
                     Leooals
                     cyanel I u*
                                   FS
                    County,
                    Mice.

                    Knights      ( (fat
                    CreeK, Dun   r«sldu«>
                    County.Mlsc.
                                   L     —
                                                      1.106  (K9I
Ololdrln
Oleldrln
Oleldrln
                     leooals
                     cyan*IIus
                                   L     —
                     cyanelIus
                      Fa Ico         F
                      peregrlnus
                      (eggs)
                    Woctorn
                    o.s..
                    Pacific
                                 $.7 (blood
                                 resIduo)
                                                      10.1 (brain
                                                      recldu*)
                                                       0.11  (roslduc)   —
                                         Haxloo,  and
                                         Antarctic
                                                                                        SOKO as above
                                                                    Tho blood and brains of groon
                                                            sunflsh that dl*d duo to exoosurc to
                                                            Oicldrln were analyzed for this ch«ntcal«
                                                             Survlvlnq »Ish had less Ololdrln In
                                                            blood and brains than dead fish.
                                                            Severity of ooisonlng syaptoas also
                                                            correlated with Oleldrln concentration.
                                                            Extraction efficiency froa blood and
                                                            brains Mas quite good (92-95 percent).

                                                                   sane as above
                                                                                        sa«e as above
                                                                                                                           •NIC-3753
                                                                                  Moubrv, «t
                                                                                  at (1968) i
                                                                                  •HTC-S753

                                                                                  Haqan, et  al
                                                                                  (1971J,
                                                                                  Hoqan,  et al
                                                                                                      Hogan,  et  al

                                                                                                      f H7H.MIIC-
                                                                                                      382".
                                                Hereqrlne falcons, falcon prey,   3is*t>rouo,h(
                                        and other predator species Mere collected et al
                                        Mldely and analyzed for DDT, OOF. PCR.    (1468).
                                        and a feM other pesticides to a lesser    (MIC-3BM
                                        degree.  PCR and OPT Mer* found to be
                                        Mldely dispersed globally.  PC9 MBS found
                                        to be a powerful Inducer of hepatic
                                        enzymes that degrade oestradlol.
                                        Reductions In thickness of egg shells.
                                        eggshell weight, and Hater retention
                                        occurred.  All affect hatching success.
                                        Tho authors state that the peregrine aay
                                        bo the first species entlrpated by global
                                        contamination.
Olaldrln
•quit a
chrysaetos
(eggs)
Western
U.S..
Pacific
Ocean.
Panana,
Mexico, and
Antarctic
0.00*7
(residua)
                                                                                        sane  as  above
Risebrough,
et al
                                                                                                                           AMIC-38«.<.
-------
ro
Conoound
Olelarlr.






Dletdrin






Oleldrln






Orqanisn
Fa Ice
peregrlnus
denature)




Falco
pcreqrlnus
(adult)




Falco
pereqrlnus
(adult)




Field Field
Study Location
F Western
U.S.,
Pacific
Ocean,
Panama,
Hexlco,and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Hexico.and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Parian a.
Mexico, and
Antarctic
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppn or Noted Comments
0.07-1.6 (Tat -- sane as above
residue)





0.31-3.7 (flesh — sane as above
residue)





O.I.1.-62.5 (fat — sane as above
residue)





Ref erence
Rlsehrouqn,
et al
(196S),
AMIC-38H



Rlsefcrou^n,
et at
(1968),
AHIC-3»«t<.



Rise&rouqh,
et al
(1968).
ANIC-36i.il



           01 el dr In
            Olcldrln
            Oleldrln
            Oleldrln
                                Endonychura

                                 craverl
                                 (eqqs)
                                 Petecanus
                                 occidental Is
                                 (eqgs)
Sula
leucoqaster
leqqs)
                                 Fa I CO
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico,and
Antarctic

Western
U.S..
Pacific
Ocean,
Panama,
Mexico,  and
Antarctic

Western
U.S.,
Pacific
Ooean,
Panama,
Mexico,  and
Antarctic

Western
                                                                  O.Ot  (residue)   —
                                                                                                    same  as above
                                 0.06-0.16
                                 (residue)
O.Od-0.18
(residue)
                                                                                                    sane as above
                                                                                                    sane  as  above
                                                                                                      Rlsebrouqh,
                                                                                                       et  il
                                                                                                    sale  as  above
                                                                                                                                        AHIC-3M.I*
                                                                     Rlsebrough,
                                                                     et al
                                                                     (196SI,
                                                                     AMIC-38I.^
Rlsebrouqh,
et al
(!<»**),
tMTC-38l»l>
                                                                                                                                        Rlscbrough,
-------
                             peregrlnus
                             (Immature)
        Oleldrln
>      Oleldrln
        Oleldrln
        Oleldrln
                    U.S..
                    Pacific
                    Ocean ,
                    Panama.Mexlc
                    o. and
                    Antarctic
              (flesh
              residue)
                             Chlamydotheca BSCH  —
                             arcuata       and
Chlamydotheca a Hh)
                                                              0.021.5 (Tl)
0.00001-0.001
(1.9-126 ppb
residue 33-*8
HK)

0.39 (A3
oercentKZ)
                                                                      et  al
                                                                      (1968)
                                                                      381.".
                                                                     KaHatskl.  et
                                                                     al  (14711.
                                                                     *NIC-550S
                                                The organisms «er» exposed  to
                                        O.ni and O.J  oob  of  the toxicants  for
                                        Hecks after which  time the amounts
                                        each tueeK H*»re  Increased  ten-fold  over
                                        the Initial amounts.  Ulothrlx occurred
                                        spontaneously  In  the test tanks.   The
                                        results shOH  that  chronic accumulations
                                        In Chiamyrtotheca  exceeded levels which
                                        were toxic In acute  tests.  Residues In
                                        Chtanydotheca ranged fro* 12.000 to
                                        260.000 tines greater than the
                                        theoretical concentrations in the  Materi
                                        those in Ulothrlx  Mere 7^^-3,000 tlaes
                                        exposure levels.

                                               same as  above
                                                                                                save as above
        The response of                   Naavl. et al-
pesticide-resistant aquatic organises to  (1969).
various pesticides was compared  to  the    «HIC-5979
resoonse of non-resistant species.
Pesticide-resistant species Here
collected at Relzonl and non-resistant
species at State College.  Copepods.
clams, snails, and sludge worms  from
Belzonl Here considerably more tolerant
to Pesticides  than  the non-resistant
organisms.  The  authors  note  that  the
effect  of Increased  tolerance in the
organisms Is  an  Increase in the  aaount of
pesticide residues  available  to  animals
of higher trophic  levels.
                                                                                  KanatsVcI, et
                                                                                  al(l«7l),
                                                                                  «MIC-550(>

                                                                                  KawatsKl, at
                                                                                  a I  (19711,
-------
Compound
•Oleldrln


Oleldrln


Oleldrin


Oleldrln











Oieldrln










Oleldrln


Organise
Tublfex
tublfex

Pnysa qyrlna


Physa qyrlna


Copepo«1s
(Cyclops
bicusoldus.
Cvclons
varicans.
Cyclop-;
vernal I«s,
Eucyctoos
sgllls.
albMus,
Orthoeyel ops
•odes tut)
Coo»po
B5A AHIC-5979









FL Belzonl, 0.40 (39 -- saae as above Naavl, et
and Hiss percent K2> al(1969),
BSA *t1IC-5979








L — ».&<» (T2) — The effect of 52 pesticides on Davis, et a
embryonic development of clams and
oysters t»as reported. Synerqlstlc (1969), AMIC
effects Hitn solvents Here also reported.
 Most of the compounds affected
develornent «ore than survival.  Soae,
however, drastically reduced larval
qroxth.  The authors point out the
necessity of evaluating the effects of
pesticides on all life stages of an
organise and not* the possibility of
                                          5990
-------
Dleldrln
Dleldrln
Oleldrln
Dleldrln
Oleldrln
Dleldrln
Oleldrln
Oleldrln
                      CP assostrea
                      vlrqinlca
                      (larvae)
Ganbusla
•f finis
(foal*.
cut 1.9

                                    8SA
                                  greater  than
                                  10.0
                                                       0.031 ITI>)
                               *.3
                                    BSA
                                   BSA
                      Lehlst«
                      reticulatus
                      (male,  l.a
                      cm, 0.7 g)
                     TMaoia
                     •ossanblea
                     (3.1. cm, 1.3
                     9>
Kuhlla        BSA
sandvlcensls
(«».3 cm, 1.9
9>

Stolephorus   BSA
purpurea 13.6
cm, 0.* g>

Agonus        BSA
cataohractus
                                                       0.007 (Tl>)
                                                       0.010 (T«.l
                                                       0.002 (T<>)
O.D05 (T 12
HR)
                                                       3.3  IT2)
                     Carelnus
                                   BSA   —
                                                       0.01-0.03  (TZ>
                                                                                  selecting ehcmlcats for pest control that
                                                                                  Mould not have serious effect on
                                                                                  shellfish.

                                                                                         same as above
                                                                      Davis,  etal
                                                                      (1969),
                a,c,d,e.           The  five  fish  species  are
                •ff»l»     commonly  found  In streams and  estuaries    al  (1970).
                (Honolulu  In seml-troolcal  areas.  C.  affinis  Has
                tap        the most  tolerant.  Varied sensitivity to
                wator)     the toxicants Mere  found.  K.
                           sandvicensls Mas  the most sensitive  fish
                           studied.  The standard method  procedure
                           Has folloned.
                                                                                                                                      et
                a,c,d,
                e.JT.i.
                (Honolulu
                tap
                water]

                a,c,d,

                (Honolulu
                tap
                water)
                a.Cid.e,ft
                l.salt
                Hater
a>c,d,e,f ,
1, salt
Hater

a«(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                                                         same as above
                                                 a«( contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and
                                                 daily
                                   One hundred-forty surface active
                           agentst solvent enulsIfters« oestlctdeSt
                           polychtorlnated blohenyls, pure
                           Inorqanlc* and organic chenicals Mere
                           evaluated against as  many as ten irarlne
                           organisms.  The authors noted that most
                           published data of this type deal with
                           toxlclty of chemicals to freshHater
                           organisms.

                                  same as above
                                                                                                       NunoaiHa,  et
                                                                                                       al  (1970),
                                                                                                       AHTC-SSS7
                                                                                                       NunooaMS,  et
                                                                                                       al  (1970).
                                                                                                       ANIC-6567
                                                                                                                            Nunoqanai et
                                                                                                                            al (1979),
                                                                                                                            AHIC-65&7
Nunogawa, et
al (1970).
AXIC-6567

Portrann, et
al (1971),
»«C-7701
                                                     Portmann, et
                                                     al  (1971),
                                                     AHIC-7701
-------
  CoHOound
            Field  Field
Organism    Study Location
Toxiclty,
Active
Ingredient,
  Ppm
Experimental
Variables,
Controlled
or Noted
                                                                                                  Comments
                                                                                                                           Reference
                                                                       solution
                                                                       renewal )
Oleldrln
                      Cardlum edule BS»    •—
                                                       areater  than
                                                                       a*(contin-
                                                                       uoug aer-
                                                                       ation,  sea-
                                                                       vator,  and
                                                                       daily
                                                                       solution
                                                                       renewal )
                                                                                         same  as above
                                                                                                    Portfann, «t
                                                                                                    al  11971),
                                                                                                    •HIC-7701
Oleldrln
                      Crangon
                      eranqon
                                    BS»
                                                       0.01-0.03  (T?)
                                               •«(contin-
                                               uous aer-
                                               ation,  sea-
                                               wator,  and
                                               daily
                                               solution
                                               renewal)
                                                                                         same  as  above
                                                                     Portmann,  et
                                                                     al  (1971),
                                                                     4HIC-7701
Oleldrln
                      Freshwater
                      drum
                                   FL
 Oleldrln
                      Aleutf*
                                   FL
                  Great Lakes
                  (Ontario,
                  Huron,
                  Erie,
                  Superior,
                  Michigan)
D.0<» (whole
body residue)
                  Or eat Lakes-  0.09-0.97
                  (Ontario,    (Hhote body
                  Huron,       residue)
                  Erie,
                  Superior,
                                          dupanor,
                                          Michigan)
                   Fish  from  Lahe  Mlchlqan  contained Pelnert
           2  to  7  times  more  DOT  (and  DDT analogs)    (1970),AHIC-
           and (Heldrln  residues  than  fish  from the   196
           other Great Lakes.  Fish  from Lake
           Suoerlor Invariably had the lowest
           accumulations of both  chemicals. The
           compounds tended to concentrate  In  fat
           (oils).   Considerable  additional data are
           presented.  The author noted the need to
           reduce  pesticide usage to a minimum and
           to replace  these Insecticides Mlth  less
           persistent  materials.
                                                                                        same  as  above
                                                                                                                            Reinert
                                                                                                                            <1970>,»tIC-
                                                                                                                            196
 Oleldrln
                      American
                      smelt
                                   FL
                  Great Lakea
                  (Ontario,
o.oz-o.io
(MhoI* body
                                                                                         same  as above
                                                     Relnerr
                                                     (1970),
-------
                                                  Huron,
                                                  Erie,
                                                  Superior,
                                                  Michigan)
                                 residue)
                                                                                                      196
         Oleldrln
Bloater       FL    Great Lakes  D.03-1.07
                    (Ontario,    (whole body
                    Huron,       residue)
                    Brie,
                    Superior,
                    Michigan)
                                                                                                  sane as above
                                                                                                                                    Relnert
                                                                                                                                    (1970),»NIC-
                                                                                                                                    196
         Oleldrln
r
ro
Broxn         FL    Great Lakes  0.00 (Hholebody
bullhead            (Ontario,    residue)
                    Huron,
                    Erie,
                    Superior,
                                                                                                 San* as above
                                                                                                                                    Relnert
                                                                                                                                    (1970).AMIC-
                                                                                                                                    196
                                                   OUpfJX*J.OZ*e
                                                   Michigan)
         Oleldrln
                              Channel       FL    Great Lakes  0.07  (whole
                              catfish             (Ontario,    body residue)
                                                  Huron,
                                                  Erie,
                                                  Superior,
                                                  Michigan)
                                                                                                 same  as above
                                                                                                      Relnert
                                                                                                      (1970),»MIC-
                                                                                                      196
         Oleldrln
                              Coho salnon
                              (flesh)
                                            FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Erie,
                    Superior,
                    Michigan)
O.OKxhole body
residue)
                                                                                                 sane as above
Reinert
(1970),»HIC-
196
         Oleldrln
                              Coho salnen
                              (eqqs)
                                            FL
                    Great Lakes
                    (Ontario,
0.0<» (whole
body residue)
                                                                                                 sane as above
Reinert
(1970),AMIC-
196
-------
  COHDOUIV)
            Field  Field
Organise    Study Location
                                                      Toxiclty,
                                                      Active
                                                      Ingredient,
                                                        Pom
                             Exoerlmental
                             Variables,
                             Control led
                             or Noted
                                                                                                 Comments
                                                                                                                           Reference
                                         Huron,
                                         Erie*
                                         Superior,
                                         Michigan)
Oleldrln
                     Gizzard shad  FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
                                                      o.o<»-o.09
                                                      (whole body
                                                      residue)
                                                                                        sane as above
                                                                                                   Reinert
                                                                                                   (1970),
                                                                                                   196
Oleldrin
                     Klyl
            FL     Great Lakes  0.28  (whole
                  (Ontario,    body  residue)
                  Huron,
                  Erie,
                  Superior,
                                                                                        same as above
                                                                                                                           Reinert
                                                                                                                           (1970),»HIC-
                                                                                                                           196
                                         dupanoz",
                                         Michigan)
Oleldrin
                     Lake herring  FL
                  Great Lakes  0.02-0.07
                  (Ontario,    (whole body
                  Huron,       residue)
                  Erie, .
                  Superior,
                  Michigan)
                                                                                        same as above
                                                                                  Reinert
                                                                                  11970),»WIC-
                                                                                  1S6
Oleldrin
                     Lake trout
                                   FL
                  Great Lakes
                  (Ontario,
                  Huron,
                  Erie,
                  Superior.
                  Michigan)
                                                      0.05-1.13
                                                      (whole body
                                                      residue)
                                                                                        same as above
                                                                                  Reinert
                                                                                  (1970),«HIC-
                                                                                  196
-------
          Oleldrln
Lake          Ft    Great Lakes  O.oz-o.W
whltetlsh           (Ontario,    (Hhott body
                    Huron,       residue)
                    Brie,
                    Superior,
                    Michigan)
                                                                                                  saae as above
                                                                                  Relnert
                                                                                  11970),*MIC-
                                                                                  196
          Dleldrln
Rock bass     FL    Great Lakes  o.oz (whole
                    (Ontario,    body residual
                    Huron,
                    Brie.
                    Superior,
                    Michigan)
                                                                                                  saae as above
                                                                                  Relnert
                                                                                  (1970),AMIC-
                                                                                  196
r
10
8
          Dleldrln
Round
whiterIsh
                                             FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.03 (whole
body residue)
                                                                                                  saae as above
Relnert
t!970»,»HIC-
196
          Dleldrln
                               Sea tanprey
                                             FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior,
                    Michigan)
             0.02 (whole
             body residue)
                                                                                                  saae as above
                                                                     Reinert
                                                                     .At1IC-
                                                                     196
          Oletdrln
                               SI lay sculaln FL
                    Great Lakes
                    (Ontario,
                    Huron,
                    Brie,
                    Superior,
                    Michigan)
             0.0* (whole
             body residue)
                                                                                                  sane as above
                                                                     Relnert
                                                                     (1970),»MIC-
                                                                     196
          Dleldrln
Nlne-splned
stickleback
Great Lakes
(Ontario,
O.OZlHhole body
residue!
                                                                                                  saae as above
Relnert
(1970),AHIC-
-------
Compound

Field Field
Orqinls* Study Location
Huron,
Brie,
Superior.
Michigan)
Toxlelty.
Active
Ingredient,
PD»

Exoerlnental
Variables,
Control led
or Noted Comments

Reference
196
         Oieldrln
f
g
                               ualley*        FL     Great Lakes  0.08-0.13
                                                   (Ontario,    (whole body
                                                   Huron,       residue)
                                                   Erie,
                                                   Superior,
                                                   Michigan)
                                                                                                 sane as above
                                                                                 Relnert
                                                                                 (1970),»MIC-
                                                                                 196
          Oieldrln
                              ~MtrtT«  bass    FL     Great Lakes  O.Oit-0.10
                                                   (Ontario,     (whole body
                                                   Huron,       residua)
                                                   Brie,
                                                   Superior.
                                                   Michigan)
                                                                                                 sane as above
                                                                                 Relnert
                                                                                 (19701,AMIC-
                                                                                 196
          Oieldrln
                               White perch   FL
Great Lakea
(Ontario,
Huron,
Brie,
Superior.
Michigan)
0.10 (whole
body residue)
                                                                                                 save as above
Relnert
(19TO),*nIC-
19*
          Oieldrln
                               White sucker  FL
Great Lakes
(Ontario,
Huron,
Brie,
Superior.
Michigan)
                                                                0.02  (whole
                                                                body  residue)
                                                                                                 sane as above
                                                                    Relnert
                                                                    (1970),»MIC-
                                                                    196
-------
Oletdrln
Vet I OH perch  FL
      Michigan!

      Greet Lakes
      (Lake
      Ontario,
      LaKeHuron,
      LakeErle.
      Lake
      Superior,
      Lake
      Michigan)
0.03-0.07
(Hhole body
residua)
Dleldrln
Wolffla
papullfera.
Olethyl-OL-tartarate Plnephales    8S»   —
                     proaelas
Olethyl fumarate



Olethvl fumarate


Olethyl aaleate



Olethyl succlnate


Olfolatan
Pimephales
proar I as
Plaephales
proaelas

Plmephales
proaelas
Plmephales
proaelas
Dlfolatan
                                                      100 (K)
                                                      650.0  CTI.)
                                   Hunter's
                                   medium
                                   diluted
                                   1:5
                                                 a*,d,e,o,
                                                 and Fe
                                   BS»   —
              8CFA
BSA
              BSA
                     Brachydanlo   L
                     rerlo
                     (larvae)
"..5



Z.S (Til.)


18.0 (Ti>)



1VO.O (Td)


1.0 (T 30 aln)
                                   and Fe
                                   and F«
                                   and Fe
                                   a*,d.«,o.
                                   •nd Fe
Rasbora       8CF»
hetereaerpha  and
              BSA
                                                      0.032 (Tl)
                                                                      a'.c.e.f,
                                                                      hard (HH>
                                                                      or
                                                                      SOFT(SH)
                                                                      synthetic
                                                                      dilution
                                                                                        saae as above
                                          Relnert
                                          tt970)t*HIC-
                                          196
         All compounds were harmful to    tforthley, et
duckweed to sone degroe.  Decreased       al (1971),
populations were noted at non-lethal      AKIC-3233
concentrations and some compounds
(Malathlon and 2,li-D) caused teratogenlc
effects at concentrations as low as 1 ppm,
        Malathlon and Its hydrolysis      Mender
products Here evaluated with the finding  (19.69) ,AHIC-
that one such product (diethyl fuaarete)  3787
Mas more toxic than Malathlon to fathead
•Innows.  Synrrqlsm occurred between
Malathlon and two products of hydrolysis.
 Continuous exposure resulted In
Increased toxiclty.

       sane as above                      Render
                                          (1969),*MIC-
                                          3/8T

       sane as above                      Bender (19*>9),
                                                             above
                                                                   sax* as abov»
                                          Bender
                                          (14I>9)
                                          3787
                                          Bender(iq«q)
                                          *HIC-37«7
                                                                    Folpet, OHolatan, and Captan     Abedi. et
                                                            Mere found  to be  toxic to zebraflsh       altl'Jf.B).
                                                            larvae xithln 90  nln.  Dlfolatan Mas aost AHIC-3717
                                                            toxic while Raptan was least  toxic.
                                                            Effects observed  Here cessation of
                                                            heartbeat and loss of plqment at Ion.  The
                                                            authors recommended this as a sensitive,
                                                            raolr) bloassay for these and  related
                                                            coapounds.
                                   One hundred sixty-four
                           pesticides, wetting agents, and
                           alscel laneous Hater pollutants showed a
                           Hide ranqe of toxlcity spanning 12 orders
                           of aagnltude.  Knowing the toxlcity and
                           percentage of all components of a
                                                                                        Alabaster
                                                                                        (19S3),
                                                                      Hater, or  formulation did not result  In easy
-------
  Coaoound
                        Organise
Flald  Field
Study Loot Ion
                                                      Toxlclty,
                                                      Active
                                                      Ingredient,
                                                        Pp«
Experimental
Variables,
Controlled
or Noted
                                                                                                 Comments
                                                                                                                           Reference
Olfolatan
                     Rasbora       BCFA
                     heteromorpha  and
                                   BS«
                                                      0.017 CT2)
Oloanln
                     Rasbora       BCFA
                     n«feromorpha  and
                                   BSA
                                                      3.3 (T2)
Dlmecron
                     Puntlus tleto —
                                                      0.1.1  (TV)
Olaethoate
                     Fish  (not
                     specified)
                   greater than
                   10-100 
-------
OlawTheat*
                      Sal mo
                      galrdnerl
              dCF*
              and
              BSA
                                                       9 I TZI
Olm*thoate
                      Carclnus
                      aaenas
                                   BSA    —
                                 greater  Than
                                 3.3  CTZI
OlMthoat*
                      Car ill urn edule BS*    —
                                                       H.3 (TZI
*«,C,e,f,
hard (HW)
or soft
(StfJ
thatle
water, or
•••water
for aomo
•pacles
a«(centln-
uoua cer-
ation, sea-
water, and
daily
solution
renewal)
                                                  a«(contin-
                                                  uous aer-
                                                  ation, sea-
                                                  water, and
                                                  dally
                                                  solution
                                                  renewal)
        One hundred sixty-four             Alabaster
pesticides, wetting agents, and            (1969),
miscellaneous water pollutants showed  a    ANIC-^*?5
wide range of toxlclty spanning 1? orders
of mannltude.  Knowing the toxlclty  and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty ot a
mixture of materials.  Sometines
pesticides were most toxic In hard water
and sometimes the opposite was true.
Testing The actual material as sold  was
found to be essential.

        One hundred-forty surface active   Portmann,
agents, solvent emulslflers, pesticides,   81(1971),
polychlorlnated blphenyls, nure            ANIC-7701
Inorganic, and organic chenlcals were
evaluated against as many as ten marine
organisms.  The authors noted that most
published data ot This type deal with
toxlclty of chemicals To freshwater
organisms.

       same as above
                                                                                                                            Portmann, «
                                                                                                                            al (1071),
                                                                                                                            ANIC-7701
OlMthoaTe
                     Crangon
                     crmngon
                                   BSA    —
                                 0.0003-D.
                                 (TZI
                                                                001
««(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                         saae as above
                                          Portaann, et
                                          al (1971),
                                          AN.IC-7701
OlMtttoate
Panda I us
aontaqul
                                   BSA    —
                                                       greater Than
                                                       0.03 (TZI
a»( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
                                                                                         same as above
                                          PorTmann,
                                          etal (19711,
                                          AH1C-7701
-------
ro
Toxiclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Ppm or Noted Comments
Dlmethy lailne Crangon BSA —
crangon
greater than a*(cor.tln-
100 (T2I uous aer-
Cne hundred-forty surface active
aqents, solvent emulslfiers, pesticides.
at ion, aea-ool ychlorinated blphenyls, pure





Olnethylphosphorodlt PImephales BSA
hole acid oromelas






Dloethy 1 phosohorodlt Plmephales BCFA --
hole acid oromelas

OlmethylohosDhorothl Plmephales BSA
onic acid prooelas

Dimethyl formamlde Cranqon BSA —
crangon
water, and
«4n 4 1 XT
OAixy
solution
renewal)


23.5 (Ti») a*,d,e,o,
and Fe






21.0 (Tli>) a»,d,o,o.
and Fe

«»2.5 (T4) a»,d,e,o.
and Fe

greater than a»(contin-
100 (T2> uous aer-
inorganic, and organic chevicals were
organisms. The authors noted that most
published data of this type deal with
toxlcity of chemicals to freshwater
organisms.
Malathion and its hydrolysis
products were evaluated with the finding
that one such product (dlethyl fumarate)
was more toxic than Malathion to fathead
minnows. Synergism occurred between
Malathion and txo products of hydrolysis.
Continuous exposure resulted in
Increased toxlcity.
same as above


same as above


One hundred-forty surface active
agents, solvent emulslfiers, pesticides.
ation, sea-ool ych lorlnitcrt blohenyls, Dure






water, and
daily
solution
renewal)


Inorganic, and organic chemicals were
evaluated against ns many as ten marine
organisms. The authors noted that most
published data of this type deal with
toxicity of chemicals to freshwater
organisms.
Reference
Portmsnn, «t
al (1971),
AMIC-77D1





Pender
(1959) ,
AMIC-37B7





Bender
(1969) ,
&MIC-3787
Render
(1969),
AHIC-3787
Portmann,et
al (1971),
AMTC-7701






          OlMthyl phosohate
                               Plmephales
                               prone I as
                                             BSA
                                                                11.0 (T<>)
a*,d,e,o,
and Fe
        Halathlon and Its hydrolysis
products were evaluated with the finding
that one such product (dlethyl funarate)
was more toxic than Malathion to fathead
minnows.  Svnerglsm occurred between
Malathion and two products of hydrolysis.
 Continuous exposure resulted In
Increased toxlcity.
8ender(1969>,
AHIC-37ST
-------
         01•*thy I ohosohlte
                              Plmephales
                              croneI as
         Dimethyl             Phormldlum
         ?»J.6-tefrachlorot«r aiblguum
         eohth«t*te
                                            BSA
                                            L     —
                                                                235.0  «T«.)
                                 o.5-in.o
                                 (33p»rcent
                                 growth
                                 Inhibited l
                                                                                and  F«
to
         Dlmlt*
                              Tublfex
                              tublfex
              Ft
              and
              8SA
Belzonlt
Hiss.
                                                                0.90  (NT?)
         OInltrobutyl phenol
                              Ganmarus
                              fasclatus
                                            BSA
                                                               1.8  (T*>
         Olnltroohenylether
Phorcldlum
amblquu*
                                            L     —
             0.9-10.0 (66
             percent growth
             Inhibited 1I>1
                                                                                                  same as above
        Of 7i»  chemicals  evaluated  as
alqlcldest only  9  Here more  toxic  than
CuSO<«.  None  inhibited qrowth of
mat-forming algae  lor more than 2  weeKs.
CuSO*»  formulated with certain Hettinq
agents was more  toxic than CuSDi. alone.
Cooner chloramlne  was also found to be
more toxic thar  CuSO^.   No wettlnn aqents
Here found to  be inhibitory  at trie
concentrations Investigated  (P»05  and
0.005  Bom).   Also  reoorted are factors
affecting qroith of alqae in canals to
determine Mhether  there  were leads to
controlling »ln»p  by environmental
managetrent.   No  practical environmental
means  were found.

        The response of
pesticide-resistant ^nuatic  organist's to
various pesticides vos comoared to the
re^non^e of non-re<:I*; tant species.
Pesticide-resistant species  xere
collected at  Oelzonl and non-resistant
species at State College.  Copepods<
CMmst snallSt and sludqe Morms Irom
Belronl Mere  considerably more tolerant
to oesticldes  than the non-resistant
orqanisms.  The  authors  note that  the
effect of Increased tolerance in the
organisms Is  an  Increase in  the amount of
pesticide residues available to animals
of higher trophic  levels.

        Of the aquatic Heed  herbicides
evaluated. Dlclone xas the most toxic,
Oaohnla Mas generally the most sensitive
orqanlsm.  All of  the Crustacea Mere
affected by much lower concentration
levels of herbicides than Indicated by
the TL sub SO  values.  All of the  animals
represent important food chain links.

        Of 7<>  chemicals  evaluated  as
alqlcidest only  9  Here more  toxic  than
CuSO"..  None  Inhibited gronth of
mat-forming algae  for more than ?  MeeKs.
CuSOit  formulated with certain netting
agents MBS more  toxic than CuSO". alone.
Copoer chloraolne  was also found to be
                                                                                   B«nder(1969><
                                                                                   AHIC-V8T

                                                                                   Otto  11970).
                                                                                   &MTOS92
Naavl, et
at USf>t),
AHIC-5979
                                                                                                      Sanders
                                                                                                      11978),
Otto (1978) i
AHIC-89Z
-------
          Compound
                                Organism-
                                            Field  Field
                                            Study Location
Toxiclty,
Active
Ingredient,
  f»r>«
Fxoerlmental
Variables.
Control led
or Noted
                                                                                                          Comments
                                                     Reference
                                                                                          •ore  toxic  than CuSOfc.   No  wetting  agents
                                                                                          •ere  found  to  be Inhibitory at  the
                                                                                          concentrations Investigated (0.05 and
                                                                                          0.005  com).  Also reported  are  factors
                                                                                          affecting arowth of  a Icae  In ctnals to
                                                                                          determine whether th«re  were leads  to
                                                                                          controlling  algae by environmental
                                                                                          Management.  No practical environmental
                                                                                          means  were  found.
3-
        Olnocao
         OInoevo
                              Fish  (not
                              seed fled)
                              R»shor»        RCFA
                              heteromorpha   and
                                            RSA
greater than
0.01-0.1 (K>
                                                               0.11  ITZt
         Olnocao
                              Rasbora        BCFA
                              heteromorpha   and
                                            BSA
                                                               0.07  (TZJ
                »•»«»•.t,
                hard (HW)
                or «oft
                (WJ «yn-
                tbatle
                uatar, or
                •eavater
                Tor aoma
                •paola*
                «»,c.e,.
                hard (HW)
                or soft
                {») syn-
                thetic
                dilution
                watar, or
                ••awater
                for some
                •paclaa
                   Anproxiniit* toxlcltles of         Hawdeslev-
           nuwerous pesticides connonly used In      Tnonas
           Britain wpre summsr 1 i»
-------
Olphen»id
Olphenaaid
Olohenavld
                      Gaimarirs
                      fasclatus
                                    BSA    —
                     Paleomontes   8S»
                     KadlaKensls
                      Asellus       BSA
                      brevlcaudus
                    greater  than
                    100.0  (T2t
                                                       98.0  (T2)
                    greater  than
                    100.0  (T?)
                   Of  the  aquatic  H«*d herbicides
           evaluatedt  Olelone  «as  the most  toxlcf
           Daohnla Has generally the most sensitive
           orqanlsn.   All  or  the Crustacea  xere
           affected by much  lower  concentration
           levels of herbicides than Indicated by
           the TL sub  SO values.   All of the  animals
           represent Important food chain linHs.

                  sane as  above
                                                                                         sane as above
Sanders
(1970).
AHIC-WS
                                                     Sanders
                                                     11970) «
                                                     ANIC-
                                                       80.0  (TZ)
                                                       1.0  (Tll>)
                                                                       a»
                                                                                         sa*e  as above
                                                                                         same  as above
                                                                                         sane as above
                                                                                         sane  as above
                                                     San-lers
                                                     (Iflroi.
                                                     (.55

                                                     Sanders
                                                                                                                           Sanders
                                                                                         AHIC-l.53

                                                                                         Sanders
                                                                                         (J<)70) ,
                                                                                         A'HC-'.SJ
                                                      70 CTZJ
~                 The effect of 52 pesticides on    Davis* et at
           embryonic development of clans and
           oysters Has reported.  Synerqistlc        C1969).AMIC-
           effects Hlth solvents Mere also reported. 5990
            Most of the compounds affected
           develocment more than survival.  So«e,
           hOMevPrv drastically reduced  larval
           qronth.  The authors point out the
           necessity of evaluating the effects of
           pesticides on all life staqes of an
           orqanlsn and note the possibility of
           selecting chemicals  for oest control that
           Mould not have serious effect on
           shell fish.

a*tc
-------
>
I
Toxlcity, Experimental
Active Variables,
Field Field Ingredient. Controlled
Compound Organism Study Location Pom or Noted Comments Reference
SOFTCSWJ
synthetic
dilution
Hater, or
seanater
for some
species



Olouat Caltibactls BSA — 16.* (T») •*•&»»«»*,
SP. {nymoh, 1,1, and
9-12 mm) silica,
calcium.
magnesium,
sodium.
potassium.
bicarbon-
ate,
carbonate,
sulfate,
iron,
dissolved
solids.
conduc-
tance
Dlouat Ena Magma so. BSA — greater than a»,b»,C,f,
(naiad. 16-2* 100 IT*) 1,1, «"»
mm) silica.
calcium,
magnesium.
sodium.
potassium,
bicarbon-
ate.
carbonate.
solfate,
iron,
dissolved
solids,
conduc-
tance
Hide range of toxlcity spanning 12 orders
of magnitude. KnoHlnq the toxlcity and
percentage of all components of a
formulation did not result In easy
predictability of the toxlcity of a
mixture of materials. Sometimes
pesticides Here most toxic in hard Rater
and sometimes the oooosite Has true.
Testing the actual material as sold Has
found to be essential.
The toxlcity of herbicides Olquat Wilson, et
and Oichlobenll to aquatic Invertebrates al f 19%9> ,
and fish Has determined In aquaria AHTC— SV5?
containing substrates natural to each
soecies. 01 qua I Has quite toxic to H.
az«teca but not as toxic to other
organisms. Dlchlohenil Has less toxic to
H. azrtecus but considerably more toxic
to the remaining organism than Oiauat
Hud lessened the toxicltv of both, but
more so for Diquat. Oichlobenll had a
sublethal narcotizing effect on the
organisms that resulted In
Immobilization. It Has concluded that
both herbicides could adversely affect
certain fish food organisms.
same as above Wilson, et
al (1969),
AMIC-SfcS?













-------
           Olouat
                     Hyal«l 1»
                     azteea
                     (adult, <»-8
                                              8S»    —
                                                                  o.os m>
                                                  a*,b*,c,f,
                                                  1,1, and
                                                  silica,
                                                  calcium,
                                                  magnesium,
                                                  sodium,
                                                  potassium,
                                                  blcarbon-
                                                  ate.
                                                  carbonate,
                                                  sulfate,
                                                  iron,
                                                  dissolved
                                                  solids,
                                                  conduc-
                                                  tance
                                                                                                     saae as above
                                                                      Wilson, et
                                                                      at (19691.
                                                                      • MIC-5W2
I
Otouat
Libellula sp. BSA
(naiad, 16-?".
greater than
100 (Tl»t
a«.b»,c,f,
1,1, and
silica,
calcium,
magnesium,
•odium,
potassium,
bicarbon-
ate.
carbonate,
sulfate.
Iron.
dissolved
solids,
conduc-
tance
                                                                                          sane as above
Wilson, et
at (19691.
           Olouat
                      LleneoMlus
                      so.  (larva.
                      1S-70 ••)
                                               as*   —
                                                                   33  (TV)
                                                  «*,b«,c,f,
                                                  1,1, and
                                                  silica,
                                                  calcium,
                                                  magnesium,
                                                  sodium,
                                                  potassium,
                                                  bicarbon-
                                                  ate,
                                                  carbonate,
                                                  sulfate,
                                                  iron,
                                                                                                     sane as above
                                                                       Wilson,  et
                                                                       al  (1969).
                                                                       AMIC-51.5?
-------
Toxlelty,
Active
Field Field Ingredient.
Compound Organise Study Location Ppn

Experimental
Variables.
Controlled
or Noted Consents
dissolved
solids,
conduc-
tance
Reference

Olouat
Tendluedldae  BSA   —
(larvae. 7-10
                                                      greater  than
                                                      100  (T4»>
                             a*,b»,c,f,
                             1,1, and
                             silica,
                             calcium,
                             magnesium,
                             sodium,
                             potassium,
                             bicarbon-
                             ate,
                             carbonate,
                             sulfate.
                             Iron,
                             dissolved
                             solids,
                             conduc-
                             tance
                                                                                        same  as  above
Wilson,et al
(19491,
Oiquat
Oiouat
                     Roccus        BSA   —
                     saxatitls
                     (fIngerlInqs)
                     Hya arenaria  f     Nomlnl
                                         CreeK, Va.
                                                      80
                                                      0.35  (SB)
                             a«,c,d,e,          Striped bass f Inqerl Inqs Here     Wellborn
                             f,p, and   aooarently nuch more sensitive to         (1969).
                             Iron       therapeutic and herblcldal compounds than AMIC-5723
                                        many freshwater fish.
                                                Consistent absence of Diauat  In   Haven
                                        edible Parts of clans and oysters Mas     11959) ,
                                        recorded.  Residues In Intequnent of clam S97g
                                        siphons MBS believed to be due to soil
                                        particles trapped In folds of tissue.  No
                                        Dlauat Mas found in water due probably to
                                        rapid adsorption by silt and bottom mud.
                                        Residues persisted for nearly one year In
                                        bottom mud.
Olouat
                     Crassostrea
                     vlrglnlca
Nonlnl
Creek. Va.
                                                      O.J5  (SB)
                                                                                        same  as  above
Haven
(1969).AHIC-
-------
         Olouat
         DIguat
                              Myrloohlllum
                              splcatu*
No«lnl
Creek, Va.
0.35 (1.0-70
percent K36)
same as above
                              Card turn «dule BS»    —
             greater than 10 a«(contin-         One hundred-forty surface  active
             IT?)            uous aer-  agents, solvent emulsl'lers, pesticides,
                             atlon, ssa-polychlorlnated blohenyls, pure
                             water, and inorganic, and organic eheirlcals were
                             dally      evaluated against as many as ten marine
                             solution   organisms.  The authors noted that most
                             renewal)   published data of this type deal with
                                        toxlclty of chemicals to freshwater
                                        organisms.
         Olouat
                              Crangon
                              crangon
                                            BS»   —
f
e
             greater than 10 a«(eontin-
                             uous aer-
                             ation, sea-
                             water, and
                             daily
                             solution
                             renewal]
         Olsoersol SO
                              Aqonus
                              cataohractus
                                            8S»   ~
                                                                100-330  (TV)
                             a«(contin-
                             uous aer-
                             ation, sea-
                             water, and
                             daily
                             solution
                             renewal)
                                                                                                  sa»e as above
                                                                                                  sane as above
                                   Haven
                                   (I«f69» .
                                   AMIC-5978

                                   Portnann, et
                                   al
                                                                     Portwann, et
                                                                     al (1971),
                                                                     AMIC-7701
                                                                     Portnann. et
                                                                     al 11971),
                                                                     AH1C-7701
         Dispersal SO
                              Crangon
                              erangon
                                            BS»   —
             3300-10(000
             ITZ)
                a*tcontin-
                uous aer-
                ation,  sea-
                water,  and
                dally
                solution
                renewal)
                                                                                                  sane  as above
                                   Portnann, et
                                   al (1971),
         Olsulfoton
         Oluron
                              Fish Inot
                              sptclf1*4>
                              Hercenarla
                              •ercenarla
             greater than
             1.0-10.0 IK)
                                                               2.5  (TZ)
                                   Approximate toxlcltles of         Haiidesley-
                           nu«i>rous pesticides commonly used In      Thomas(1971l
                           Britalr Mere summarized. An excellent     AMTC-I056
                           brief,  general discussion of toxlclty
                           testing Is also present.

                                   The effect of 52 pesticides on    Oavls, et al
                           embryonic development of clams and
                           oysters Has reported.  Synerglstlc        11969),AHIC-
                           effects with solvents Mere also reported. 5990
                            Host of the compounds affected
-------
  Compound
                       Organism
                                   Field  Field
                                   Study Location
                                 Toxlclty.
                                 Active
                                 Ingredient,
                                   Ppm
                Experimental
                Variables,
                Control led
                or Noted
                                                                                                 Comments
                                                                                                                           Reference
Oluren
Oluron
Mercenerla
•ercenarla
(larvae)

Cammarus
fasclatus

                                   BSA
                                                      greater than
                                                      9.0 IT12)
                                                      0.70 «T<»>
01-lsobutyl
ohenoxyethoxyethyl
dimethyl benzyl
aaeonlu* chloride
Phormldlum
emb i guum
0.5-10.0 (16
percent growth
inhibited l«t)
OI-ft-butyl tin oxide Creoidostomua L
                     terlonls
                                 150 {oral dose, ~
                                 Kl)
                                                                                 development more than survival.  Some,
                                                                                 however, drastically reduced larval
                                                                                 growth.  The authors point out the
                                                                                 necessity of evaluating the effects  of
                                                                                 pesticides on all life stages of an
                                                                                 organism and note the possibility of
                                                                                 selecting chemicals for pest control that
                                                                                 would not have serious effect on
                                                                                 shell fish.

                                                                                        same as above                      Davis, et
        Of the aauittc weed herbicides
evaluated, Dlclone was the most toxic,
Daohnia was generally the most sensitive
orqanlsm.  Alt of the Crustacea were
affected by much lower concentration
levels of herbicides than indicated by
the TL sub 50 values.  All of the animals
represent imoortant food chain links.

        Of 71, chemicals evaluated as
alglcldes, only 9 were more toxic than
CuSOi*.  None  Inhibited growth of
mat-forming aloae for more than ? weeks.
CuSO"t formulated with certain wetting
agents was more toxic than CuSO.it alone.
Copper chloraiMne was also found to be
more toxic than CuSO<>.  No wettlno. agents
were found to be inhibitory at the
concentrations Investigated (0.05 and
O.OOS ppm)«   Also reported are factors
affecting growth of algae in canals to
determine whether there were leads to
controlling algae by environmental
management.   No practical environmental
means were found.
                                   Capsules containing the tin       HItchua, et
                           compound were administered to the trout   al (19691,
                           by force feeding.  The tin comoound was   AHIC-5730
                           effective against the Intestinal  fluke
                           but erytnromycin was not.   Residue
                           analyses indicated tin was not readily
                                                                                                                           Sanders
                                                                                                                           (19701.
                                                                                                                           AMIC-*53
Otto (1970),
AMIC-89Z
-------
         Dl-n-butyl tin oilde Salmo
                              •quabonlta
fe
U)
         01-Systofl
         01-Syston
         01-Sy*ton
         OI-Sysfon
Mercenarla
•ercenarla
(eqqs)
Mercennrla
mereennrle
Itarvac)
Crassostrea
vlrqlnlca
(eqqs)
Crassostrea
vlrqlnlea
(larvae)
                                            L     —



                                            L     —
         01 IN. M d|*ethyl
         cocoa*Ine salt of
         •n do that I (ethyl
         bis) (?-ethylhexy«)
         phosphl na te7-oxabicy
         ele I?.?.II
         heptane-?,3-dlcarbo»
         yllc acid)
Phormldlum
amb1quua
                                 100-600  (oral   —
                                 dos«t NTC1
                                                               5.28  IT2)
                                                                1.39  
                                                               9.86  ITZ)
                                                                3.67  (TIV)
                                                               8.5-10.0  CNTE>  —
01 IN, N dimethyl    Phormldlua    L
trldecyl amlne) salt
of endothall
         ONOC
                              Fish  Cnot     —     ~
                                                                0.5-10.0  (0
                                                                percent growth
                                                                Inhibited 1<»)

                                                                       than
                                                                                          absorbed  by  tissue  outside  the  Intestinal
                                                                                          tract  and that  the  coaoound was raoldly
                                                                                          eliminated.   Tissue residue and retention
                                                                                          tine studies Here reeoaaended  for  drug
                                                                                          clearance purposes.

                                                                                                  save  as  above
                                                                                                  save  as above
                                                                                                  sane  as above
                                                                                                 saae  as above
                                                                                                  sane  as above
                                                                                          Of  7it  chemicals  evaluated  as
                                                                                 •Inlcldes.  only  9  »»re wore  toxic  than
                                                                                 CuSOit.   None  Inhibited growth  of
                                                                                 mat-formlnq algae  for nore  than  7  weeks.
                                                                                 CuSCKt  formulated with certain  wetting
                                                                                 aqpnts  was  nor*  toxic thin  CuSO". alone.
                                                                                 Conner  chlorarlne  was also  found to be
                                                                                 more toxic  than  CuSQ<»«   No  wetting agents
                                                                                 Mere found  to  be Inhibitory  at the
                                                                                 concentrations Investigated  (C.05  and
                                                                                 0.00"5 Dp«).   Also  reoorted  are factors
                                                                                 affecting growth of  algae  In canals to
                                                                                 determine whether  there  were leads to
                                                                                 controlling aloae  by environmental
                                                                                 •anaqevent.   No  practical environmental
                                                                                 •cans Here  found.

                                                                                         same as above
Hltchuo* et
al Cl-»69>,
•MIC-57S9

Oavls> et al

(19691.AHIC-
5998

Davis, et al

(1969).AHIC-
5993

Davis, et al

(1969>,A«»IO
5990

Davis, et al

(19691,AHIC-
5990

Otto  I19T9).
AHTC-89Z
                                                                                                      Otto  (1970).
                                                                                                      ftHIC-89?
                                                                                                   Approximate toxlcitles of
                                                                                                                                     Naitdesley-
-------
rv?
Comooun'l




Dobs JN








Dobs JN






Oobs JN






Dobs JN






Oobs 095





Toxicity,
Active
Field Field Ingredient,
Organism Study Location Pom
seed fled) 1.0-10.0 (K)



Carclnus BSA -- qreater than
•aenas 100 (T2>







Cardlum edule BSA — qreater than
100 





Cranqon BSA — qreater than
eranqon 100 





Pandalus BSA — qreater than
•ontaqul 100 (T2)





Csrclnus BSA -- qreater than
maenas 100 




Exoerl mental
Variables,
Control 1 ed
or Noted Comments
numerous pesticides commonly used in
Britain Here suinmar l?ed. An excellent
brief, general discussion of toxlcity
testing is also present.
a*(contin- One hundred- forty surface active
uous aer- aqents, solvent emulslf lers, pesticides.
ation, sea ool vch lorlnated blohenyls. cure
wato™, tmd Inorqanlc, and organic chemicals were
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
removal) published data of this type deal with
toxlcity of chemicals to «resh»ater
organisms.
a«*(contln- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal )
atCccntin- same as above
UCM3 aor-
etion, soa-
vc tor, and
drily
solution
renewal )
a*(contin- same as above
uous aer-
ation, 363-
water, and
daily
solution
renewal }
a*(contin- sarre as above
uous aer-
ation, sec.-
wntor, and
daily
solution
Reference
rco-os
(1171) ,S-I
10-^5

Por t r 3nnt
si (1971) ,
ATC-7701






Por t r.S'-n,
31 (1971),
AMIC-7701




Por t-iann.
al (I'i7!) ,
ANIC-7701




Por Tyann,
etsl ( ) t





er





-------
                                                                                 renewal)
         Dobs  »S5
                               Cardiua edul« BSA   —
                                                                     (TZ)
                                                                                o*(contin-
                                                                                uous aer-
                                                                                ation, sea-
                                                                                watcr, and
                                                                                daily
                                                                                solution
                                                                                renewal)
                                                                                          same  as above
                                                                                                                             Portmann, et
                                                                                                                             al U9M>,
                                                                                                                             AKTC-770-.
         Dobs
                               Crangon
                               crangon
                                             BSA   —
                                                       greater than
                                                       100 (TZ)
r
18
vn
Debs 055
                     Panda I us
                     •ont»qul
                                    BSA
greater man
100 (TZ)
                a«(contin-
                uous aer-
                ation, sea-
                water, and
                daily
                solution
                renewal)
a»(contin-
uous aer-
ation, aea-
water, and
daily
solution
renewal)
                                                                                         sane  as above
                                                                                               as above
                                                      Portnann,  et
                                                      at  (1971),
                                                      A1IC-77P1
Portnann, et
el (19M1,
         Debs OSS
                              Platlcthys
                              fIvsus
                                            BSA
                                                                10-30 ITZ)
                                                                       a*(contin-
                                                                       uous aer-
                                                                       ation, 3CC-
                                                                       wator, and
                                                                       daily
                                                                       solution
                                                                       renewal)
                                                                                                  same as above
                                                                      Portmanr,  et
                                                                      al  (1971),
                                                                      ANIC-7701
         Oodlne acetate
         Oonlclde A
                                    (not
                              so*clf le-1)
                              Mercenaria
                              •ercenwla
                              (eggs)

                                                       greater than
                                                       0.1-1.0 (K)
                                                       greater Than
                                                       10.0  (T2>
                                   Approximate toxiclties of         Nawl*sl«y-
                           nur»»rous pesticides commonly used  In      Tho»as(1371]
                           Britain were sumi"a>-izpa.  An excellent     AllC-lOS'i
                           brief, general discussion of toxicity
                           testing is also present.

                                   The effect oT 52  pesticides on    Davis,  etal
                           embryonic development pf  clap* and        tl9'i<»»,
                           oysters was reported.  Synerqistjc        AMIC-5993
                           effects with solvents were also reported.
                            Most of the compounds affected
                           development more than survival.  Sone,
                           however, drastically reduced larval
-------
COBDOurv)
Field Field
Organism Study Location
Toxicitv.
Active
Ingredient,
Pom
Experimental
Variables,
Control led
or Noted Comments
Peter ence
        Oonlelde *
        OOHlcide G
IU
CO
ON      Do»lcl<1e G
        Oo»pon
        OoKpon
                              Mercenarla
                              mercenaria
                              (Iarvae)
Mercenaria
nercenarla
(eqqs)

Mercenarla
merceoarla
(larvael

Rashora
heteroxoroha


                                           BCFA
                                           and
                                           as A
                                                              0.75  (TlZ)
                                                               less  than 0.25
                                                               (T?)
                                                               less  than
                                                               0.25CT1?)
                                                                   (TZ)
                             Sal no         SCFA  —
                             gairdnerl     and
                                           8SA
                                                               179  
                                                                                         growth.  The  authors  ooint  out  the
                                                                                         necessity ot  evaluating  the effects  ot
                                                                                         Desricldes  on all  life stages of  an
                                                                                         organism and  note  the possibility of
                                                                                         selecting chemicals  for  pest control  that
                                                                                         Hould not have serious effect on
                                                                                         she!If ish.

                                                                                                same as above
a*,c,o,r,
hard (KV)
or soft
(SW) syn-
thetic
dilution
water, or
seawotcr
for soaie
species
                                                                                                sane  as above
                                                                                                seme  as  above
                                                                                                      Davis, et a!

                                                                                                      < 1969! ,t«TC-
                                                                                                      SS?1

                                                                                                      Oavls, et
                                                     Dsuis, et
                                                     al I
                                                 bard (IIU)
                                                 or soft
                                                 {3W> syn-
                                                 thetic
                                                 water, or
                                                 soawater
                                                 for some
                                                 opeclea
        One hundred sixty-four
pesticides, wettinq agents, and
miscellaneous water oollutan»s showed  a
wide ranoe of toxicity snannlnq 12 orders
of magnitude.  Knowing the toxicity and
percentage of all conoonents of a
formulation did not result in easy
predictability of the toxicity of a
mixture of materials.  Sometimes
pesticides were most toxic in hard water
and soiretimes the opposite was true.
Testing the actual material as sold was
found to be essential.

       same as above
41abaster

AMIC-si?5
                                                                                                                                    Alabaster
                                                                                                                                    AMIC-5«.?5
-------
          DoxeMc fCIO?)
                               Carclnus
                               •aenas
                                             BSA
                                                                 500  (T2)
          OoxcMe  (CIO?)
                               CaPdlum edule BSA
                                                                
                a«(contir.-          One  hundpert-f opty surface activ*
                UOUs  aer-   aqents,  solvent emulsl f 1 eps, pesticides,
                ution,  sea-Potych lorlnated biohenyls, Pure
                water,  ar.ci  inopqanic, and orqanic chemicals »»pe
                daily      evaluated aqalnst ?s msny as ten mapine
                solution    opqanlsms.   The authors noted that nost
                1'enewal)    published data at this type deal Kith
                            toxlelty of  chemicals  to fpeshwater
                            opqanisms.
                                                                «t
                a«-(contln-
                uous aer-
                ation, sea-
                v.-atcr', and
                daily
                solution
                renev:al )
                                                                                                   sa"e
                                                                                                           above
                                                                                                                                       tMIC-7701
                                                                                                                                                 et
                                                                                                                                      al
                                                                                                                                      A1IC-/7C1
         Oexclde  fCIO?)
 I
ro
ro
-4
         Doxctd*  «:i^nated  as  CV, on,
           Cl, On, AQ, PC, MM, TN,  HP,  an1 NA with
           no fuPtnep descpjotion of theip chemical
           natuPe OP source.  Only  a few hioasssys
           wepe conducted with shPimo.  Molluscs and
           «chlnodepms wepe suggested as suitable
           test anlirals.  The authops stated that
           the method could be used to  test any
           ppoduct fop toxicity  in  seaxateP.
                                                                                                                                      al  (19711,
                                                                                                                                      AtIC-7731
                                                                               et
                                                                                                                                      al (1973)
-------
o
Compound
00
00
OSS
OTHC
Field Field
Organise Study Location
Fundulus BS* ~
heterocl 1 tus
N«r«ls vlrens BSA —
Nereis vlrens BS* — -
Palaemonetes BCF --
kadlaKensls
(adult)
Toxlclty,
Active
Inqredlent,
Pp«
0.0005 mi
O.OOOZ-0.001
mt
13.5 (T(.)
0.07 (residue)
Experimental
Variables.
Control led
or Noted Comments
a'.c.e, sane as above
and
synthetic
seaiiater
a*»c»e, same as above
and
synthetic
seaHater
8*.c,e, sane as above
and
synthetic
seawafer
a* Magnification ot POT aid Aldrln
taqqpd with C-l
-------
Oylox
0.8. Granular
                     Coccus
                     saxatills
                      tfingerlIngs)
                                   8SA    —
                     Sal no
                     galrdn«rl
              BCFA
              and
              BSA
Cconat 13046
                     Rasborn
                     n«teronorpha
              BCFA
              and
              BSA
                                                      0.19 CT2)
tC-9»
Rasbora
h«t«romorph»
                                   BCFA
                                   and
                                   BSA
                           Pesticide-resistant species  were
                           collected  at  Relzoni  and  non-resistant
                           species  at State  College.  Cooepods,
                           clans, snails,  and sludge  worirs Iron
                           Relzoni  were  consid»rinfv  more tolerant
                           to pesticides than tie  non-resistant
                           organisms.  The authors note that  the
                           effect of  Increased tolerance In  the
                           organisms  Is  an Increase  In  the amount of
                           pesticide  residues available to animals
                           of higher  troohic  levels.

S.2  (Tl»)        a«,c,d,e,f          Strloed bass  flnqerlinos  were     Hellborn
               ' ,p and     apoarently  much more sensitive to         (1969),
                Iron       therapeutic and herbicldat compounds than AMIC-57?!
                           many  freshwater fish.

2*050  (T2)      a*,c,e,f.           One hurdrert sixty-four            alabaster
                hard  (HH)  pesticides, Hettlnq agents, and
                or         miscellaneous «at«>r oollutants showed a
                SOFTtSM)   wide  range  of toxlclty spanning 12 orders
                synthetic  ot magnitude.  Knowing  the toxiclty and
                dilution   percentage  of all comconenfs of a
                water, or  formulation did not result in easy
                seawater   predictability of the toxlclty of a
                forsome    mixture  of  naferijis.   Sometimes
                species    pesticides  were most toxic In hard water
                           and sometimes the ooooslte «as true.
                           Testlnq  the actual material as sold Has
                           found to be essential.

                a*,c,e,f.           One hundred sixty-four            Alabaster
                hard  (HH)  pesticides, Hettino aoents, and           (1969),
                or         miscellaneous water oollutants showed a   AMIC-5U2S
                SOFT(SM)   Hide  range  of toxicity soanninq 1? orders
                synthetic  of itnqni tude.  Kno«lno  the toxlclfy and
                dilution   percentage  of all co^oonpnts of a
                water, or  formulation did not result in easy
                seawater   predictability of the toxlclty of a
                for some   mixture of materials.   Sometimes
                species    pesticides were most toxic in hard water
                           and soretires the opposite was true.
                           Testlnq  tne actual material as sold was
                           found to be essential.

l.Z IT2,        a*,c,e,f.          One hundred sixty-four            tlabast«r
h»rdwat«r>      hard  (HH)  pesticides, wetting agents, and           (1969),
                or so)t     miscellaneous water oollutants showed a   AMIC-5*t?5
                (SM)        wide range of toxicity spanning 12 orders
                synthetic  of magnitude.  Knowing the toxicity and
                dilution   percentage of all  comoonents of  a
                water, or  formulation did not result in easv
-------
  Compound
                       Orqanlsm
                                   Field  Field
                                   Study Location
                                 Toxlclty,
                                 Active
                                 Ingredient.
                                                 Exoerlnental
                                                 Variables,
                                                 Control led
                                                 or Noted
                                                                                                 Comments
                                                                                                                           Reference
EC-98
                     Rasbora       BCFA
                     heteromorpha  and
                                   BSA
                                 1.2 (T2,
                                 softMater)
E»col M-146 IS*
percent olvs Z>
percent F«col
N-9IIX)
Rasbora       BCFA
heteromorpha  and
              BSA
                                                      10 IT2>
Eacol 7«?
Rasbora       BCFA
heteromorpha  and
              BSA
                                                      6.0 c.e,ff
                                                                     .hard (HWJ
                                                                      or soft
                                                                      ISH) syn-
                                                                      thetic
                                                                      dilution
                                                                      water, or
                                                                      aaawater
                                                                      for aoaa
                                                                      apeolaa
                                                            predictability of  the toxlclfy of  a
                                                            mixture of  materials.  Sometimes
                                                            pesticides  Here mo^t toxic In hard Mater
                                                            and sometimes the  opposite Mas true.
                                                            Testlnq the actual material  as sold Mas
                                                            found to be essential.

                                                                   sane as above
                                          Alabaster
                                          11969),
                                          AMIC-5<,?5
        One hundred sixty—four
pesticides, HCttlnq agents, and
miscellaneous Mater pollutants showed a
Mlde range of toxlclty soanninq 12 orders
of maqnitude.  Knowinq the toxiclty and
percentage of at I eo*oon»nts of a
formulation did not result in easy
predictability of the toxicity of a
• Ixture of materials.  So-neti»cs
pesticides Mere most toxic in hard Mater
and sometimes the opposite Mas true.
Testing the actual material as sold was
found to be essential.

       sane a* above
Alabaster
•1969),
R1IC-5I.2S
                                                                                                      Alabaster
                                                                                                      (1969),
CHIO
                     Crassostrea
                     vlrglnlca
                                                      16.S IT?)
                                                                    The effect of 52 pesticides on
                                                            eabryonlc development of clans and
                                                                                                      Oavls, et at
                                                                                                      (1969).
-------
                      t»qo«>
EHTO
Cvpilan
                      Crassostrea
                      vlrolnlea
                      (larvae)
                      Cranqon
                      crangon
                                                       30.0 IT1U
iofl-330
take* «pi II'ussK
                                   USA
l.B-3.3 (T.
                                          mC-7701
Cndosultan
                     Fish  (not
                     soeclfled)
greater than
0.000001-0.0000
1 (K)
        Approximate toxicltles of         HaHdeslev-
numerous pesticides commonly  used  In      Thomas  (1971
Britain were summarized. An excellent     AMIC-1856
brief, general discussion of  toxlclty
testing Is also present.
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Comoound Organism Study Location Pom or Noted Comments Reference
Cndosutfan Rasbor» BCFA — 0.000003 tT2> a*,c,e,f,
heteromorpha and hard (HH)
BSA or soft
ISH)
synthetic
dilution
water, or
seawater
tor some
species
One hundred sixty-four Alabaster
pesticides, wettlna agents, afd (1969),
miscellaneous water oof lut^nrs showed a ANIC-S'i?':
wide ranqe of toxlcitv spmnin-j tires
pesticides were most toxic in nard water
and soffetlmes the ooooslte wai true.
Testlnq the actual material as sold was
found to be essential.
Cndosulfan
                      AgonuS
                      cataohractus
                                   BS»   —
                                                       0.03-1.0  (T2)
                                   a«(oontin- .        One hundred-forty surface  active  "or
                                   UOUs aer-  nqents, solvent euulsIflers, pestlcidss,  al
                                                                       ation,  sea-PO'vch'orlnated  biohpryts,  oure
                                                                       water   and  Inorqanlc,  and orqanic  cn^t^icals  wore
                                                                       ^ally       evaluated aqalnst  as  many  as  ten  marine
                                                                       solution    orqanisms.   The  authors noted that most
                                                                       renewal)    Published data of  this  tyoe deal  with
                                                                                  toxlelty ot chemicals to freshwater
                                                                                  orqanisms.
                                                                                                                            AMIC-7701.
Cndosulfan
                     CardIurn edul« BS»
                   greater than 10 ao(cor.tin-
                   IT2)            uoua aar-
                                   atlon, sea-
                                   water, and
                                   daily
                                   solution
                                   renewal)
                                                                                         same as above
Portmann. et
a I (19^:>,
»MIC-?7C1
Cndosulfan
                     Crangon
                     crangon
                                   BSA
                                                       0.01 (T2)
                                   a«-( contin-
                                   uous  aer-
                                   ation,  sea-
                                   water,  and
                                   dally
                                   solution
                                   renewal)
                                                                                         same as above
Portma^i, et
at (19?1),
Cndothall
                     Rasbora
                     heteromorpha
8CFA
and
BSA
(TZ1         •*»*»*t'»          One hundred sixty-four
            hard (HW)  pesticides, wettlnq aqents, and
            OF soft    miscellaneous water oollurants showed a
            (SW) »jn-  wide range of.toxiclty scanning iZ orders
Alabaster
(t969>.
-------
         Cndotnall
 >
 IU
u>
CJ
         Endofhall
         Cndothall
         Cndofhall
         Endothal
         Endrln
         Endrln
                                                                                tlMjttC
                                                                                dilution
                                                                                water, or
                                                                                seawater
                                                                                for soxe
                                                                                spa tiles
                              Hercenaria
                              •ercenarla
                              (eqqs)

                                                                51.0  (T2)
                              Hereen««rl8
                              •ercenarle
                              II arvne)
Crassostrea   L
vlrqlnlca
                                                                12.5  (T12)
                                                                28.2  CT2)
                              Crassostr«»   L
                              vlrqlnica
                              (larvae)
                              Fish (not
                              specified)
                              Fish (not
                              specified)
                              an»cystls
                              nlrtulans
                                 greater than
                                 10-100 (K)
                                 oreater than    —
                                 0.0001-0.001
                                 (K)

                                 0.5-1.0 (qroMth a*,c»ir
                                 inhibited)      SM
                                                             of  maqnltude.   Knowinq the toxicity and
                                                             o*rc»ntaoss ioi 11 ty of
                                                             selecting chemicals  for oest control that
                                                             would  not have serious  effect on
                                                             shell fish.
                                                                                                  sane as above
                                                                                                  same as above
                                                                                                  same  as above
        Approximate toxlcitles of
numerous pesticides commonly used in
Britain were summarized. An excellent
brief* general discussion of toxlclty
testing Is also present.

       same as above
        Metabolic products of Aldrln,
Oieldrin, and Endrln can be as toxic as
the parent compounds, as shown by  00
measurement.
                                                                                                       Davis,  et  al

                                                                                                       (1969), »Mi:-
                                                                                                                                     navis,  et al

                                                                                                                                     ( 19691.
Davis, et al

119*9) ,»1IC-
•5990

Mawdesley-
Thonas
(1971), AMIO
1056
                                          Hawdesley-
                                          ThOB«S(1971
                                          AHIC-1056
Batterton.et
al
-------
ro
Comnound
Ff\ttf I n
coor i n


Cndrln









Endrln






tnar In






Endrln






Endrln






Field Field
Organism Study Location

quadrup-
lleatun

Salvellnus BCFA —
fontlnalls
(1.15 q>







Salvellnus BCFA —
fontlnal Is
(2.01. q>




Salno clarkl BCFA —
(0.3? a)





Salno ctarfcl BCFA —
(1.30 q>





Sal no BCFA ~
qalrdn»rl
(!.?<> q»




Toxlcity. Cxoer I mental
Active Variables.
Ingredient t Controlled
Pom or Noted Comments

0.5*1.0 (growth a*»c*»r
Inhibited) SM


0.355 {TH a«,c,d.
s,r,i,o,
aulfate.
copper,
manganese,
Iron, and
chromium




0.59 (Ti.) a«,c,d.
e,r,l,o,
suirata,
copper,
nanemese.
iron, and
chronlum
0.00001 CK> *»,c,d,
e,r,l,o,
oulfate.
copper.
manganese.
iron, and
chromium
0.00002 (Tli> a«,c,d.
e.r.l.o.
aulfato,
copper,
manganese.
Iron, and
chromium
0.00 Of, (T«») *»,c,d.
e,r,l,o.
aulfate.
copper.
manganese,
Iron, and
chromium

sane as above


Four Insecticides Mere evaluated
on tour fish species at two body weights.
Standard method bloassay orocedures were
fol lowed. SyfflDtomotogy was also
recocted. Generally, toxlcity Mas
significantly different at the two body
weights. !.«.» more toxic at tne lower
body weight, exceot for Hatathlon.
Well-defined exoer inental conditions were
said to result In truer measurement of
toxlcity.
sane as above






sane as above






sane as above






sane as above






Reference
AMIC-K.71
Bat ter t on •
«t al
(19711.
AMIC-1«.M
Post, et al
(1971),
AHIC-1813







Post, et al
(1971) ,
A1IC-1812




Post, et al
(1971) ,
AMic-iai?




Post, ct al
(1971).
AHIC-181?




Post, et al
I197D ,
AMIC.-I*IZ




-------
          En*-in
                               llmneohllus
                               rhombIcus
                               (larvae)
.Knights      0.003 (whole
CRFEK,       body residue)
OunCounty,
Misc.
\J\
         Endrln
         Endrln
         Endrln
         Endrln
                               Slalls  so.     FS
                               (larvae)
                               Gannarus  so,   FS
                               Plmephales     BCFA
                               orone I as
                               Carass1us      BCF
                               auratus
Kniqhts      0.009
Creek, Dun   (wholebody
County,Wise, residue)
                                                   Knights
                                                   CreeKt Dun
                                                   County,
                                                   Misc.
             0.013-0.035
             (unoI(body
             residue)
                                                                0.25 DPb (U)
                                                                                a»,e
             0.00<»3 (oral     a*,c,q
             dose o«r day,S8
             i, mo)
         endrln
                               Oncorhynehus  BCF*
                               Klsulch  (1.50
                                                                0.76  IT*)
        Samoles  of  xater,  silt, bottom    Houbry, et
debris, bottom orqanlsus,  and  fish  Mere   a(  (1^68),
taken  In  1966  troi»  a  creek  adjacent to an SHIC-3753
orchard which had been  treated In
1«!<>3-1?SS with various  chlorinated
hydrocarbon  pesticides.  No residues Here
founr)  in  Hater samnles.  Silt  sanotes
contained 0.003-0.013 DDK  endrln and
0-0.01)5 cpm  dleldrln. Endrln residues of
0.011-0.025  oom  and 0.007-0.006 opn
diaMrln  Here  found In  debris  samples.
nesolte United  control data,  residue
analyses  Indicated  that contamination of
the environment  studied was United.
                                                                                                  sane as above
                                                                                                  sane as above
                                          Moutry, et
                                          a I
                                          Moubry, et
                                          al (14*8).
                                          SMIC-37S3
                             a«,e.d.
                             e,f,l.o,
                             aulfato,
                             copper,
                             nanconese.
                             Iron,  and
                             chromium
        ISS acted synerglstleally with    Solon, et al
parathlon to cause less survival of
fatheds but had an Indeterminate effect   (1969),AMIC-
nith ROT and no synerqlstic effect with    37<5
En»1rln.

        No effects Here noted at lower    Grant, et al
concentrations while higher doses caused  (1970),
some mortality, lowered growth rat?,      AH.IC-3S26
decreased thyroid cell height, decreased
qanetogenesls, lowered total body fat,
less vaeuot Izatlon of liver cells,
elevated serus Na concentrations,
osmo-regutatory disturbance, and other
effects.  The-authors note that sublethal

       sane as above
                                          Post, et al
                                          M971) ,
                                          4MIC-181?
-------
ro
LO
O\
Compound

Endr in












Endrln






Endrln






Endrln






Endrln


Toxicity, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppn or Noted Comments

Enrfomyc^ura F Western 0.17 (residue) — •
craverl U.S.,
(eqqs) Pacific
Ocean,
Panama,
Mexico, and
Antarctic







Pelecanus F Western 0.07-1.13
•occidental Is U.S.. , (residue)
(eggs) Pact f Ic
Ocean,
Panama,
Mexico, and
Antarctic
Sula F Western 0.01-0.06
leucoqrster U.S., f residue)
(eggs) Pad f ic
Oc»an,
Panama,
Mexico, and
Antarctic
Pandion F Western 0.?5 (residue)
hallaetus U.S..
(eqqs) Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Gaibusla L — 0.05-0.* (SB 3 —
• Minis hr)
(resistant)
effects could adversely affect fish
poou 1 at 1 ons.
d t" 1 * 1 1 t d
widely and analyzed tor HOT, DOE, PCB,
and a few other oestlcides to a lesser
degree. PC?) and DOT were found to be
widely dispersed globally. PCS was found
to be a powerful inducer of heoatic
enzymes that degrade oestradlol.
Reductions in thickness of eqg shells.
eggshell weight, and water retention
occurred. Alt affect hatching success.
The authors state that the peregrine nay
be the first species entlroated by global
contamination.
sa»e as above






sane as above






sane as above






Endrln resistant mosauitoTlsh
exhibited no consistent change in rate of
oxygen consumption. The susceptible
Reference


et al
(19SSJ ,
ANIC-38*i>










Rtsebrouqh,
et al
(1968),
AMIO38M»



Rlsebrougn,
et al
(1968),
»HIC-38<.«.



Rlsebrouqh,
et at
(1968),
AllC-JSkW



Mrlngvale.
et al
(1968),
-------
         EnrtrIn
         fnurln
Caxbusla      L

(susceptible)
                              Plueohales
                              proud as (3
                                            8SA
                                                               0.00001-0.
                                                               (SB 3 hr)
0.00077 IT2>
                                                 a«,c,e,f,
                                                 k,l,n,
                                                 and na(--
                                                 noslun,
                                                 sulfates,
                                                 iron,
                                                 calcium
IU
         Cntfrln
        Endrtn
                              Plmephales
                              crone I as H
                              en)
                              Pala«nonet«s
                              Hadlakensls
                              (resistant)
                                                               H.00057 (TZ>
                a*,e,e,f,
                lc,l,n,
                and nag-
                neslun,
                sulfates,
                Iron,
                calcium
                                            BS»   ~
                                                               0.0028-0.0137
                           at higher concentrations.  Some nortallty
                           occurred at .02-.075 oo» In susceptible
                           tlsh and at .Ml po« In the resistant
                           strain.

                                  saae as above
                                                                     Hclnqvatet
                                                                     et al
        Ploassays conducted
simultaneously  Indicated  that DDT was
conslri«>raMy  nore toxic to fatnead
minnows under static conditions than
under continuous «I on conditions.
Decreasing oxygen and increasing
metabolites may have enhanced DDT
toxic!ty.  An identical study «lth Endrln
resulted in only sllqhtty higher toxiclty
under continuous flow conditions.
Average pH, oxvqen, and anmonia nltroqen
were foil owed throuohout  the oxperlnents.
 The results nere conprehensl«ely
discussed taking into consideration »»ny
contributing factors.

       same as above
AMIC-5V75

Linear, et
al
                                                                                                                                    5S09
                                                                                                      Llncer,  et
                                                                                                      al  (1470),
                                  Bloassays  Her* conducted  Kith
                          shrlmo  fron  three  areas  of  intensive
                          pesticide  use  and  from an unexoosed area.
                           Previously  exoosed shrimp  Here from 1  to
                          ?5  times more  resistant  than unexposed
                          shrimp.  Both  types of shrlno Here also
                          exoosert in cages to waters  of the
                          contaminated areas.  Susceptible  shrimp
                          suffered fit  percent more mortality than
                          did resistant  shrlmo.  The  toxicity of
                          the Insecticides ranHed  in  descending
                          order xas  as follows:  nost toxic,
                          Endrln, DDT, Methyl paratnlon, Parathloni
                          medium  toxiclty, Cuthlon, Llndane,
                          Toxaohene, Strobanet lease  toxic
                          Chlordane, Sevln,  and Heptachlor.
                                                                                                      Naavl,  et
                                                                                                      (1970),
                                                                                                      AHIC-S519
                                                                              al
        Fndrin
                              Pala*«en»tes  USA   —
                                                               0.0009  (Tl)
                                                                                                 sane as abova
                                                                                                                                    Naovi.et  al
-------
Compound

Endrln
Field Field
Organise Study Location
kadlaKenvls
(non-
resistant)
Gambol 1 » U —
at finis
(resistant)
Toxlcity,
Active
Ingredient,
fom

D.5-? (SB6-9)
Experimental
Variables,
Control led
or Noted

Comments

~ Resistant nosqul t of ish Her*
exposed to Endrln for varyina periods of
time then fed to susceotible green
Reference
(1970),
ANIC-S519
Ferguson, et
al (1967),
ANIC-5976
ro
          Endrln
          Endrln
Gambusla
affinis
(resistant)

tenon i s
cyanellus
(susceptible)
                                             L      —
(whole body
residue)

greater than 1
(k
-------
          En*-In
r
NO
          Endrln
         Cndrln
         Endrln
         Endrln
         Endrin
         Cndrln
Cooroods
(Cvcl or>s
blcusoldus.
CycloDs
vaplc*ns«
Cyclons
vernal Is,
Eueyclops
aql Us,
Macro eyclops
albldus.
Opthoeycloos
modulus)
Tub If ex
tublfex

Physa gyPlna


Physa gyplna


Euoepa
slngieyl

Leoomls
•acPochlPus
FL
and
BSA










FL
and
BSA
FL
and
BSA
FL
and
BSA
FL
and
BSA
BSA

Belzonl, 0.08 (20
Hiss percent K2>











Belzonl, 6.D CNTE)
Miss.

State 0.55 

State 0.075 (K3)
Col lege.
MISS.
0.0001 
-------
Compound
Cndrln
Organise
Crassostrea
vlrglnlca
leqgs)
Field Field
Study Location
L —
Toxlcity,
Active
Ingredient,
Ppa
0.79 (T2)
Experimental
Variables,
Controlled
or Noted Coaaents
— - saae as above
Reference
Davis, et al
C19S9),A1IC-
Cndrln
Cndrln
Crassostrea
vlrqtnlca
(larvae)

Lepoals
aacrochlrus
                                   L     —
                                   8S»   —
                                                      greater than
                                                      1Q.O
                                                      0.001-0.002
                                                      (Kl
Cndrln
Cndrln
Cndrln
Cndrln
Cndrln
                     Leooals
                     alcroloohus
                     Leooals
                     •aerocMrus
                     Lepovls
                     •aeroehlrus
                     lepovls
                     aaeroehlrus
                     Leooals
                     •aeroehlrus
                                   BS«   —
                                   FP
                                   FP
                                   FP
                    Orlft wood
                    Far> Ponds,
                    Indiana

                    Orlftnood
                    Far* Ponds.
                    Indiana

                    OrlftHood
                    Fara Ponds*
                    Indiana
                                   8CF»  —
                                 1.001-0.002
                                 CKt
                                                      O.DO". (K2>
                                                      0.001 (K21)
                                                      0.046  (Kl)
                                                      0.002 (Tit
                                                                                        saae as above
                                                                                                                           Davlst et
                                                                                                                           • 110599!)
        Lab. tests Mere folloxed by tests He^eynolds
In oonds to eradicate fish.  Cndrln       (1969),»HIC-
toxlclty persisted In one oond study (W6  108
Dob) rven after the pond had been mptled
and refilled twice.  In oonds. Cndrln
tbxlclty varied widely.  The author
stated that this cheolcal MBS too
danqerous for use as a pesciclde except
In extrenely Isolated Instances.
                                                                                        saae as above
                                                                                        saae as above
                                                                                        sane as above
                                                                                        saae as above
                                                                    Cndrln absorbed by bluegllt In
                                                            lethal and sublethal exposures Has
                                                            deteralned by electron caoture gas
                                                            chro«*tograDhy.  Absorotlon Has Measured
                                                            at varying tlaes uo to 24 hr.  The
                                                            authors stated that a teaoorarv decrease
                                                            In absorption at the sublethat
                                                            concentration level suqoests the fish
                                                            •ere aetabolizlnq and excreting the
                                                            Endrln.
                                          McReynotds
                                          (I960),
                                          •HIC-1D8

                                          Hc9eynolds
                                          (11^91,
                                          •HIC-108

                                          HcRevnolds
                                          (19fi9),
                                          AMIC-1B8

                                          HcReynolds
                                          (1<>69) ,
                                          »HIC-1B8

                                          Bennett, et
                                          81(1970),
                                          AMIC-19S
-------
 Endrln
 Endrln
 Cndrln
Endrln
Cndrin
Endrln
eolchlorhydrln
                      Leoomls       BCFA
                      •acrochirus
                      Lepomis      BCFA
                      •acrochirus
                      Leoomls
                      •acrochlrus
                      Leoonls
                      •atrochlrus
                     lepomis
                     •acrochlrus
                     Cyorlnodon
                     varlegatus
                     (50-70 ••)
                                   BCFA   —
                                   BCFA  —
                                   BCFA  —
                                   BSA
Rasbora       BCFA
heteromorpha  and
              BSA
                                                       0.0002  (SSI)
                                  o.noo?
                                  10.04-0.13 DO*
                                  •uscle
                                  residue)

                                  0.0002
                                  (0.60-0.70 pp»
                                  qut residue)

                                  0.000?
                                  (0.80-1.0 DO*
                                  IIver residue)

                                  0.0002
                                  (0.80-0.30 OP"
                                  whole body
                                  residue)

                                  0.001 (K)
                                                                   sane as above
                                                                                        same  as above
                                                                                        sane as above
                                                                                        sane as above
                                                                                        same as above
Bennett,et
at
(1970),AMIC-
195

Bennett, et
al (1970),
AMIC-19S
Bennett, et
al  (1970),
AMTC-195

Bennett, et
al  (1970),
AMIC-195

Bennett, et
al  (1970),
AHIC-195
                                                      36 (T2)
 a",                Sensitivity of  threi- generations
 seaxater   of sheeosheacJ minnoMS to 03T and Fndrin
           Nas determined.  Sensitivity to ODT
           varl«d seasonally.  Fish were bred In
           ponds 15m X 5» X 1.25*  exposed to
           pesticides In aquaria,  and survivors used
           for breeding.  The results for DOT Here
           not entirely clear due  to the seasonal
           variability.  Increased and decreased
           sensitivity Mere recorded for the Fl
           generation at different times. Increased
           sensitivity for the F2, and decreased for
           the F3.  The authors stated that
           Incorporation of DDT in ova via lioids
           •ay have caused increased sensitivity.
           Endrin toxlcity Has decreased in the Fl
           and Increased in the F? qeneratlon.

a*,c,e,f.          One hundred sixty-four
hard   pesticides. Netting agents, and
or         miscellaneous Hater pollutants showed a
SOFT(SH)   Hide range of toxlcity scanning 1? orders
synthetic  of magnitude.  Knowing  the toxicity and
dilution   percentage of all components of a
Mater,  or  formulation did not result in easy
seanater   •predict jbl 1 1 ty of the toxlcity of a
for so«e   mixture of caterlals.  Some tines
species    pesticides were Most toxic In hard Mater
           and sometimes .the opposite Mas true.
                                                                                                      Holland, et
                                                                                                      al (197C),
                                                                                                      AMIC-726
Alabaster
(1969).
-------
Coeoound
Eotam
Eterlne fulfat*
Field Field
Organise Study Location
Gammarus BSA —
Negaorlon BSA
brevlrostrls
<1-I kg)
Toxiclty, Fxperlmentat
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
Testing the actual material as sold was
found to be essential.
23.0 (Ti.) a* Of the aquatic weed herbicides
Oaohnla Mas generally the most sensitive
organism. Ill of the Crustacea Mere
affected by much lover concentration
levels of herbicides than indicated by
the TL sub 50 values. All of the animals
reoresent Imoortant food chain links.
11 (NTE 3 hr) a,c,e Data from study of dru? effects
on young lemon sharks were treated
mathematically to demonstrate
Reference
Sanders
1 1070) •
AMIC-W3
<>aldrldge(19
69),
AM.IC-3832
Ctsolvene
                     Carclnus
                     •aenas
                                   9S»
                                                      10—33  (T2)
Csselvene
                     Cardlua «dule BS»   —
                                                       33-100  (T2>
           applicability  of  classical rat*  theory  to
           the study  of chemical  shark  deterrents.
           IncapacItatlon (narcosis) was  the  primary
           parameter  timed for  effectiveness.   This
           Mas usually guite raold  for  the  more
           effective  drugs.

a»(contin-          One hundred-forty surface  active   Portmann,  et
UOU3 nor-  agents,  solvent emulslflers,  pesticides,   al
ation,  sea-DOlychlorlnated biphenyls, oure            (1971),»MIC-
water,  and inorganic, and organic cherlcats Mere     7701
daily      evaluated  against as many as  ten marine
solution  organisms.  The authors  noted  that most-
renewal)  oublIshed  data of this type  deal with
           toxlclty of chemicals to freshwater
           organisms.

                  sane as above                      Portaann,  et
                                                      al
                                                      11971),»HIC-
                                                      7701
                                                                       uous  aer-
                                                                       ation,  soa-
                                                                       woter,  and
                                                                       daily
                                                                       solution
                                                                       renewal)
Csselvene
                     Crangon
                     cranqon
                                   BS»
                                                       10  (TZ)
a«(contin-
uous aer-
ation, sea-
water, and
                                                                                         sane  as  above
Portnann, et
al (197H,
•HIC-7701
-------
                                                                       daily
                                                                       solution
                                                                       renewal)
Essolvene
                      Ostrea edulls BSA    ~
                                                       33-100 (T2J
                 a»( contin-
                 uous aer-
                 ation, aea-
                 wcter, and
                                                                        solution
                                                                        rcne-.ral)
                                                                                         same as above
                                                      Portnann,  «t
                                                      al  (19711.
                                                      AMIC-7701
Cssolvene
                      Panda I us
                      •ontaqui
                                   BSA
                                                       10 (TZt
                 a»(contin-
                 uous  aer-
                 ation,  sea-
                 wa tqr,  and
                 dally
                 solution
                 renewal)
                                                                                         sane as above
                                                      Portrann,  et
                                                      al  (1971),
                                                      AMIC-7701
C**0 solvent FC-1S5
                     Cranqon
                     cranqon
                                   BS»
                                                       10-33 (T2>
Cthanedlol
                     Cranqon
                     cranqon
                                   BSA
qreater than
100 IT2>
Cthanolamlne
                     Cranqon
                     eranqon
                                   8S»    —
greater than
100 (T2>
                ac( contin-
                uous aer-
                ation, sea-
                water, end
                                                                       solution
                                                                       renewal )
a«(contin-
uous aer-
ation, sea
water, er.d
daily
solution
renewal)
a* (contin-
uous aer-
ation, S3Q-
water, and
daily
solution
renewal)
         One hundred-forty surface active
 aq«nts» solvent emulsIflers, pesticides,
 ooIvchI orInated blrh^nvls, pure
 Inorganic, and organic cnrfflcals were
 evaluated against PS many as ten marine
 organisms.  The authors noted that most
 published data of this type deal with
 toxlclty of chemicals to freshwater
 organisms.

         One hundred-forty surface active
 aq-nts, solvent emulslflers, pesticides,
.DOlychlorInated biohenylsi our*
 Inorganic, and organic chemicals w»re
 evaluated against as many as ten marine
 organisms.  The authors noted that Host
 published data of this tyce deal Hlth
 toxlclty of chemicals to freshwater
 organises.

        same as above
                                                      Portiann,  et
                                                      al  (1<>71>,
                                                      AHJC-7701
Portinann, et
al (1971),
AHIC-7701
                                           Portmann, et
                                           al (1971),
                                           AHIC-7701
-------
Conoound
Ethanol
.Organise,
Sett*
Field Field
Study Location
• m^
Toxlcity,
Active
Ingredient,
Ron
?8SO (SB 6 hrl
Experimental
Variables,
Controlled
or Noted Comments
a* The effects of ethanol and
Reference
Raynes. et
                     soIendens
tthlon
                     Pashora
                     heteromorpha
BCFA
and
BSA
                                                      0.53 (T2)
                                                                      OP soft
                                                                      ISM) a?a-
                                                                      tbetie
                                                                      dilution
                                                                      water, or
                                                                      •eawmter
                                                                      for '
Ethlon
                     Tublfex
                     tublfex
Ft
and
BSA
Belzonl,
Hiss.
                                                       1.50  tNTE)
Ethoeeen S-25
                     Pas bora
                     heferomorpha
                                   and
                   9.39  m,
                   hardxater)
                                                                      hard (HW;
                                                                      or soft
                                                                      (SH)  ayn-
bourbon en the aggressive response of     al
Siamese fighting fish were determined.    (1968), AHIC
Cthanol Increased all I snow               5712
(aggressiveness) and bourbon and bourbon
congeners decreased It.  The authors
tentatively concluded that the delayed
effect of the congener resulted fro<«
involvement of a different Dhyslological
mechanism and that this nay be related to
hangover effects in nan.

        One hundred sixty-four            Alabaster
pesticides, wetting agents, and           M96. AMT.C-
alscel laneous water pollutants showed •   5*25
wMe range of toxlclty spanning 1? orders
of  magnitude.  Knowing the toxlcitv and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of materials.  So«e times
pesticides Mere most toxic In hard water
and so»«tjmes the opposite was  true.
Testing the  actual  •af«rj«l •* sold «»»
found  to bt
-------
Cthoneen S-Z5
                      Rasbora
                      heteronorpha
<5CFA
and
as*
0.68 (TZ,
softxat«r)
Cthylene phosphite
                     Pineohales
                     crone fas
                                   BS«   —
                                                       34.0  (U)
Cthyl parathlon
                     Cardlum edule BS»   —•
                                                       3.3-10  
-------
Compound Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient,
PD«
Experimental
Variables,
Control led
or Noted Comments
Reference
         £-311.
         Fenac  (Ha salt)
>
Fenac (Na saltl


Fenac (Na salt)


Fenac (Na saltl



Fenac (Na salt)



Fenac (Na salt)
Coho salmon  BSA   Hood Canal,  0.01  (X)
(fingerlings) In    Hoodsport,
             situ  Wash.
                                                                                                                                     Tracy, et al
                                                                                                                                     (19t>9),
                              Gammarus
                              faselatu?
                                            OS*
Paleomontes
karl I ak»n% J^

As*11 US
brevlcaudus

Orconectes
nals
BSA


BSA


BSA
                              Daohnla aaqna BSA
                              Cyoridoosis
                              vidua
                                            BSA
                                 greater than
                                 100.0 CT2)
                                                               greater  than
                                                               tno.D  IT?)

                                                               greater  than
                                                               lOO.O(TZ)

                                                               greater  than
                                                               100.0  (T?)
                                                                greater  than
                                                                100.0  (T?>
                                 greater than
                                 100.0  (T7)
                                                                                 with  fair to  good oil dlsoerslon
                                                                                 caoabi lity.

                                                                                        sane as above
                                                                                         Of  the  aquatic Heed herbicides    Sanders
                                                                                 evaluated.  Old one  was the most  toxic,    (1471),
                                                                                 Daohnla Has generally the most sensitive  AHIC-WJ
                                                                                 organ l«mi.   All  of the crust.irea  Here
                                                                                 affected by much  lower concentration
                                                                                 levels of herbicides than Indicated by
                                                                                 the TL sub  50 values.  All of the  animals
                                                                                 reoresent important food chain links.

                                                                                        same as  above                      S;
                                                                   same as above
                                                                   same as above
                                                                                                  sane as above
                                                                   same as above
                                                                                                      Sand«--s(ig70),
                                                                                                      AHIC-1.53
                                                                                                       1.53

                                                                                                       Sanders
                                                                                                       (1970 1, •lic-
                                                                                                       it "53

                                                                                                       Ssnders
         Fenac  (Na salt)
         Fenoproo
                              Lenonls
                              •acrochlrus
                                            BSA
                              Rasbora       RCFA
                              heteroaorpha  and
                                            BSA
                                                                19.0  (T2)
                                                                37
                                                 a*                same  as  above                       Sanders
                                                                                                       (1970,
                                                                                                       AHIC-*53

                                                 a>,Cfe,ft          One  hundred sixty-four             Alabaster
                                                 bard (Htfj  pesticides,  netting aqents,  and            J19A9),
                                                 or soft    miscellaneous nater pollutants showed  a    A1IC-5<.?5
                                                 (SH) syn- • wide range of toxlclty  spanning  12  orders
                                                 thetic     of magnitude.   Knowing  the  toxlcity and
                                                 dilution   percentage of alt components of  a
                                                 water, or  formulation  did not result  in easy
                                                 seawater   predictability  of the toxlcity of a
-------
 Fcntln acetate
                      PandaI us
                      montaqul
                                    BSA   —
                                                  for  soMe   Mixture of  Materials.   Sometimes
                                                  species    pesticides  Mere most toxic In hard water
                                                             and sometimes the oooosite was true.
                                                             Testing the actual  Material  as sold Mas
                                                             found  to be essential.

                                  greater  than  33  a»(contin-         One hundred-torty surface active
                                  (T2)             UOU3 aer-  aqents, solvent enutslflers,  oestlcldes,
                                                  ation,  sea-Polychlorinated blohenyls, cure
                                                  water,  and Inorganic,  and organic  cheirlcals Mere
                                                  dally      evaluated against as many as  ten marine
                                                  solution   organ ISMS.   The authors noted that Most
                                                  renewal)   published data of this  type  deal xlth
                                                             toxlclty of  chemicals to freshwater
                                                             organ isms.
                                          Portaann, et
                                          at  (1971).
                                          ANIC-7701
Fenuron
                      Mercenarla
                      mercenarla
                      (eqqs)

                                  greater  than
                                  10.0  (T2)
        The effect of 52 pesticides on    Pavls> et
embryonic development of clans and        al(1969).
oysters Mas reported.  Synerglstlc        4NIC-5990
effects Mlth solvents Mere also reported.
 Most of the compounds affected
development more than survival.  Some,
hoNever, drastically reduced larval
qroMth.  The authors ooint out the
necessity of evaluating the effects of
pesticides on all life staoes of an
orqanlsir and note the oosslbillty of
selecting chemicals tor pest control that
Mould not have serious effect on
shell fish.
Fenuron
Ferrle eh I or I do
Ferric sulfate
Ferrous chloride
Mercenarla
Mercenarla
I larvae)

Carasslus
auratus
                     Carass1us
                     auratus
                     Carass1us
                     auratus
                                   |       ^^
Ferrous sultate las  »croneurla
Fel
              L


              BS»
                                                       greater  than
                                                       5.0  «T1?)
                                                       5-10
                                                       5-10  (KV)
                                                       5-10
                                                       16  (T9)
                                                                                              as above
                                          Davis, et
                                          al(19S9),
                                          AMIC-5990
                                                                                          Iron salts Merc most harmful       *shl*v
                                                                                  Immediately after dissolving,  resulting   (1978),»MIC-
                                                                                  In  gill  blockage (reversible), absorption 5<>36
                                                                                  In  digestive tract,  and Iron precipitates
                                                                                  In  epithelium' and renal  tubules.
                                                                       a*,c,d,e,f
                                                                                         same as above
                                                                                         same  as above
                                                                                          EpheMerelta (Mayfly)  Mas the most Warnlck,  et
                                                                                                      Ashley
                                                                                                      (1970),
                                                                                                      A1TC-5I.36

                                                                                                      *shley(1970).
                                                                                  sensitive  aquatic Insect  of  those         at(1969),
                                                                                  studied,  and copper the most broadly      ANIC-3767
                                                                                  toxic  metal.  The authors suggest that
-------
  Compound
            Field  Field
Organism    Study Location
Toxlclty,
Active
Ingredient,
  Pom
                                                 Experimental
                                                 Variables.
                                                 Controlled
                                                 or Noted
                                                                                                  Convents
                                                                                                                            Reference
Ferrous sulfate  las   Ephemera 11a   BSA
Ferrous sulfate  (as   Hydropsyche    BSA
Fe)
Ferrous sulfate       Carassluv      L
                      auratus
Flnavol FSK
Cr»n*ton       ASA
cranqon
                                                       0.32 ITM
                                                       16 (T7)
                               9-10 (1C.)
                                                       180-330 CT21
 Flnasol  0<5RZ
                      Cranqon
                      crangon
                                    BSA   —
                                                       3300 (T<»)
                                                                       a*«c,d,e«f
                                                 ,c,d,e,f
                                                          aquatic Insects nay not be as sensitive
                                                          to heavy netals as fish.

                                                                 sane as above
                                                                       a&tcontin-
                                                                       uous aer-
                                                                       ation  sea-
                                                                       water,  and
                                                                 sane as above
                                                                     MarnlcK,
                                                                     etal  11069).
                                                                     AMTC-3767

                                                                     Warnick,  et
                                                                     81(1969).
                                                                     ANIC-3767
                                                                  Iron salts  Here most harmful      Ashley
                                                          Immediately after dissolving, resulting   (1970).
                                                          In qill bloeKaa*  (reversible), absorotion
                                                          in dlqestlve tract, and Iron orecloltates
                                                          In eolthellum and renal tubules.
                                                                       solution
                                                                       renewal)
                                               ae(contln-
                                               uoua aer-
                                               ation, sea-
                                               water, and
                                               dally
                                               solution
                                               renewal )
                                                                  One hundred-forty surface active
                                                          agents, solvent eiuls i Tiers, oestlcides,
                                                          Dolvchlorinated blohenyls, oure
                                                          Inorganic, and organic chemicals were
                                                          evaluated against  as  nany as ten marine
                                                          organisms.  The authors noted that nost
                                                          published data of  this type deal with
                                                          toxlclty of chemicals  to  freshwater
                                                          organlsns.

                                                                 *»•• »* above
                                                                     Portmann, et
                                                                     at (1971),
                                                                     AHIC-7T01
                                                                     Portmann, at
                                                                     al (1971),
                                                                     AHIC-7701
Flnasol SC
                      Cranqon
                      crangon
                                    BSA   —
                                                       33-100 (T2>
                                               a*(contin-
                                               uous aer-
                                               ation, sea-
                                               water, and
                                               dally
                                               solution
                                               renewal)
                                                                                         sane as above
                                                                     Partmann, et
                                                                     al (1971).
                                                                     AMIC-7701
 Flack  o.p.  Fly  dip
                                    BCFA  —
                                                       0.73 (T2)
                                                                         ,c,e,f,
                                                                                          One hundred sixty-four
                                                                                                                            Alabaster,
-------
                      hetaroMorphe  and
                                    BS*
                                   hard       pesticides,  wetting  aqents.  and            (19S9),»MIC-
                                    (HM)or     Miscellaneous  Hater  ooltutants showed  a    5*25
                                   soft  (SN)  Hide ranqe of  toxlclty soannlnq tZ orders
                                   synthetic  of naqritude.  Knowing the  toxlclty  and
                                   dilution   percentage of  all  covoonents of a
                                   Hater,  or  foraulatlon  did  not  result  In easy
                                   seawater   predictability of  the toxlclty of a
                                   for SOMO   Mixture of Materials.  SonotlMes
                                   species   pesticides Here  Most toxic  in hard Hater
                                              and socetlMcs  the  opposite  Has true.
                                              Testlnq the  actual Material  as sold  Has
                                              found  to be  essential.
Fluoresceln sodlua    Sal MO
                      galrdncrl
                                   BS»   —
                   1.J7Z  (TV)
Fluorwsceln so<1IUM   Ictalurus
                     ounctatus
                                   BS*   ~
                                                      Z.Z67  «T*>
                   Th« dyes Rhodanlne B and
           Fluoresceln sodlu* Here found to be
           relatively non-toxic  in poa
           concentrations while  antlaycln Has toxic
           at pob levels.  The author states that
           neither dye at field  use concentrations
           should slqnlfIcantly  Influence the
           activity of *ntl*ycln « aqalnst fish.

                  sane as above
                                                                                        «arKIng
                                                                                        (1969),
                                                                                        HarKlnq
                                                                                        <19691,»HIC-
Fluorescein sodlt»   LepOMls       BS*
                     aacrochlrus
                                                                                        saae  as above
                                                                                        Marl, Ing
                                                                                        t19691,»"IC-
FluoroMIl
                     Rasbora       BCF*
                     heteroaorpha  and
                                   BS*
                                                      3,500  (TZI
                                   hard (HM)
                                   or
                                   SOFTtSU)
                                   synthetic
                                   dilution
                                   Hater, or
Fluoroklli
                     Salao
                     qairdnerl
BCF*
and
BS*
                                                      1.S90  (T2)
                                                                      for son*
                                                                      species
8*tCt«tft
hard (HHI
or
SOFT(SW)
synthetic
dilution
•»ter, or
seaitater
        One hundred sixty-four
pesticides, Hettlnq aqents, and
Miscellaneous Hater pollutants showed a
Hide ranqe of toxiclty spanning 12 orders
of Magnitude.  Knowing the toxicity and
percentage of all conoonents of a
formulation did not result In easy
predictability of the toxlclty of a
Mixture of Materials.  Sonetlnes
pesticides Here Most toxic In hard water
and sOMetlMes the opposite Has true.
Testing the actual Material as sold Has
found to be essential.

       save as above
                                                     Alabaster
                                                     (1969),
                                          Alabaster
                                          (1969),
-------
ro
VJI
o
Conoouni)


Fluorofcllt









Fellzoll

Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Orqanise Study Location Ppn or Noted Comments
for some
species
Platessa BCFA — 1,200 (TZ> a».c,e,f.
vulgar Is and hard   pesticides, wetting agents, and           (1969!,
or soft    miscellaneous water pollutants showed a   AHIC-S<>?S
-------
         Formaldehyde
                              Salvo trutta
                                            BCFA
                                            and
                                            BSA
                                                               90
ro
Ml
         Formaldehyde
                              Crangon
                              eranqon
                                            8SA   —
                                                               330-1000 (T2>
         Formaldehyde
                              Plstlcthys
                              f I esus
                                            BS»   —
                                                               100-330  (T2)
                 (SW)  ayn-  wide ranqe  of  toxlcltv spanning 12  orders
                 thetic     of  maorltude.  Knowing the  toxlclty  and
                 dilution  percentage  of  all  components  of a
                 water,  or  formulation  did not result  In easy
                 seawater  predictability of  the toxlclty of a
                 tor some  mixture of  materials.  Sometimes
                 speclea    pesticides  Mere most toxic  In hard  Mater
                           and sometimes  the  opposite  was true.
                           Testing the  actual material as sold  was
                           found  to be  essential.

                                  sane  as above
                a*,cte,f,
                hard  (HH)
                or soft
                (SH)synthe
                tic
                dilution
                water, or
                seawater
                for some
                species

                ai>(contln-         One hundred-forty surface active
                uous eer-  agents, solvent emulsltiers, pesticides,
                atlon, sea-DO'vch'orlnated blphenyls. Pure
                water, ftnd Inorqanlc. and organic chenlcals were
                dally      evaluated aqalnst as many as ten marine
                solution   organisms.  The authors noted that most
                renewal)    published data of this type deal with
                           toxlclty of chemicals to freshwater
                           organisms.
                a*(contin-
                uous aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)
                                                                                                 same as above
                                           Alabaster
                                           (1969).
                                           AHIC-51.25
                                          Portrann, et
                                          al  (1471),
                                          ANIC-7701
                                          Portaann, et
                                          al  (1971),
                                          AHIC-7701
         Formal In
                              Sal no
                              galrdnerl

200-1.00 (SB.
*-6 hr)
        Caudal arterial blood samples
were taken at selected time  Intervals
evaluated for acid-base balance and for
gill. Kidney, and  liver function by
measuring 0? consumption, total CO?,
HC03, Cl(minus), Ca(Z plus), blllrubln,
whole blood pH, and Vitamin C depletion.
Formal In treatments seemed to be a more
severe stress to rainbow gelscff ofele
data and discussion are presented.
    Hede»eyer
and (197l),AHIC-
    3287
-------
ro
\J1
IU
Toxlclty. Experimental
Active Variables,
Field Field Ingredient. Controlled
Compound Organise Study Location Ppm or Noted Comments
Formalin Oncorhynchus L —
klsutch
foff9l in Tracblnotus BSA —
enrol Inus
(Juvenile)








Fora* 1 In Roccus BSA —
saxatllls
(f Inqerl Ings)

Formic acid Care Inus BSA —
•aenas
200-400 (SB, f
4-6 hrl

and
•ul fate.
sodium,
calcium.
potassium.
Bagnesium,
carbonate.
bicarbon-
ate.
salinity
18 (T4I a»,e,dfa.
f,p, and
Iron

80-90 IT2I a*(contln-
uous aer-
same as above

In this study of pompano salinity
MBS controlled at 10, ?0, and 30 ppt and
investigated as a variable. Acrltlavln,
formalin, and potassium permanganate Mere
slightly more toxic at the highest
salinity, while copoer sulfate was
slightly less toxic. These compounds are
used as prophylactic bacterial
treatments. All appeared to he
reasonably safe to use excepte possibly
potassium permanganate.
Striped bass finger linos were
apparently much more sensitive to
therapeutic and herblcldal compounds than
•any freshwater fish.
Pne hundred-forty surface active
agents, solvent emulslfiers, pesticides.
atlon, aaa-oolychlorinated blphenyls, pure






wator, and
daily
solution
renewal )


Inorganic, and organic chewlcals Mere
evaluated against as many as ten marine
organisms. The authors noted that most *
published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
Reference
Wedemever
(1071), AMIC-
B l^dsonQf »jt
al (1971),
AMIC-5570








Mel Iborn
(1969),
AMIC-S7?3

Portmann, et
al (1971),
AMIC-7701






          Formothlon
                               Puntlus tlcto --
                                                                0.16S ITt)
          Fervothlon
                               Rasbora
                               heteromorph*
BCFA
and
BSA
                                                                l.Z (TZ)
a,c,d,e,f          Of the pesticides Investigated,   Bhatla
           the most toxic was Klofos followed in     11971),A1IC
           deereaslng order by Sumlthlon, Malathion, S*?J
           Formithion, Olmecron, Sevln, and BHC. The
           author cites the need for more selective
           pesticides nontoxic to fish or
           antagonistic agents for reducing fish
           toxlclty.

a*,Cte,f,          One hundred sixty-four            Alabaster
hard (HW)  pesticides, wetting agents, and           (1969),
or soft    miscellaneous Mater pollutants showed a   AMIC-5*?S
(SU) syn-  Hide range of toxlclty spanning iz orders
tfaotlc     of magnitude.•  Knowing the toxiclty and
-------
 Furfural
 •.asbora       BCFA  —
 heteromorpha  and
               8S»
                                                       23 (T2>
to
^jj       f»0m
                     Steel head
                     trout
                     (fingerlIngs)
                                   BS»
                                                       65.0  (T«O
F.O. 300-B
Camlen CM
Coho aalnon   B3A
(fingerllnga) in
              altu

Cardtun edule 8S»
Hood Canal,
Hoodaport,
                                                      fc.O (K)
                                                       33-100  (T2)
Cam! en CM
                     PandaI us
                     montagal
                                   BS»
                                                       10-33  IT2I
                                                                       dilution
                                                                       water, or
                                                                       seawater
                                                                       for some
                                                                       species
                              a.«,c,e,f,
                              hard (HW>
                              or soft
                              (SM) syn-
                              thetic
                              dilution
                              water, or
                              seawater
                              for aona
                              •peolea
                                                                                           percentage of all conoonents of a
                                                                                           formulation did not result In easy
                                                                                           predictability of the toxlclty of a
                                                                                           mixture of materials.  Sometimes
                                                                                           pesticides Here most toxic In hard Mater
                                                                                           an<1 sometimes the opposite Has true.
                                                                                           Testing the actual material as sold xas
                                                                                           found to be essential.

                                                                                                   One hundred sixty-four            Alabaster
                                                                                           pestlcidesi netting agents! and           (19691,
                                                                                           miscellaneous nater pollutants showed a   *niC-5l»25
                                                                                           Hide range of toxiclty spanning 1? orders
                                                                                           of magnitude.  Knowing the toxlclty and
                                                                                           percentage of all comoonents of a
                                                                                           formulation did not result In easy
                                                                                           predictability of the toxiclty of a
                                                                                           mixture of materials.  Sometimes
                                                                                           pesticides were most toxic In hard Hater
                                                                                           and soiretlmes the opposite H«S true.
                                                                                           Testing the actual material as sold was
                                                                                           found to be essential.
                                                                     Evaluation of  11  oil  dlsoersants
                                                             resulted In a ranKlng  for each and a
                                                             recommendation for use according to the
                                                             ranklnq.  Ranking Has  based on toxiclty
                                                             and  oil  dispersal effectiveness.  Corexlt
                                                             77fiit appeared to have  the least toxlclty
                                                             with fair to good oil  dispersion
                                                             capability.

                                                                   MM *• above
                                                                                   Tracy, et al
                                                                                   (19691,
                                                                                   »«.IC-383«.
                                                  •*(contln-          un*  hundred-forty surface active
                                                  uous eer-   agents,  solvent enulslfiers,  pesticides,
                                                  atlon,  sea-POlychlorlnated blphenyls,  pure
                                                  water,  and  Inorganic, and organic chemicals were
                                                  daily       evaluated against as many as  ten marine
                                                  solution    organisms.   The authors  noted that most
                                                  renewal)    published data of this type deal with
                                                             toxlclty of  chemicals to freshwater
                                                             organisms.

                                                  «»(contln-        s»»e  as above
                                                  uoua aer-
                                                  ation,  sea-
                                                  water,  and
                                                  daily
                                                  solution
                                                                                                                                     Trmcy, et al
                                                                                                                                     (1969J.
                                                                                                                                     AKIC-3&3U.

                                                                                                                                     Portmann, et
                                                                                                                                     al C1971>,
                                                                                                                                     AHIC-7701
                                                                                   Portmann,  et
                                                                                   al  (1971),
                                                                                   A1IC-7701
-------
£
Coaoound

Gael en 0




Gael en 0





Caelen 0






Gael en OVt






Caelen OS*




Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organise Study Location Pom or Noted Consents
renewal )
Cardlua edule BSA — 33 CTZ) a«(contin- sane as above
uous aer-
ation, sea-
water, and
doily
solution
renewal)
Cra no on BSA — 10 CT2I M.f „«•«.«„ *»•• »« above
cranqon * * contin-
uous aer-
ation, sea
water, and
daily
solution
renewal )
Panda 1 us BSA — 10 IT?) a*(contin- *»•* »« above
•ontaqul UOU3 aer_
ation, sea-
wcter, and
daily
solution
renewal )
Carclnus BSA — 10-33 IT?) a,«(contin- saae as above
ram as uous aer-
ation, soa-
wcter, and
daily
•olutlon
renewal)
Cardlu* edule BSA — 10-33 IT?) a«(contln- sa»e as above
uous a or-
ation, sea-
water, and
daily
Reference

Portnann, et
al (19711,
ANIC-7701




Port»ann, et
al (1971),
1MIC-7701




Port«ann, et
al
(197H,AHIC-
7701



Portnann, et
al (1971),
AHIC-7701




Portnann, et
al (1971),
AHIC-7701


-------
                                                                                solution
                                                                                renewal)
         Gaalcn OS*
                               Cranqon
                               cranqon
                                             BSA
                                                                10 (T2)
                                                  a»(contin-
                                                  uous aer-
                                                  ation, sea-
                                                  water, and
                                                  daily
                                                  solution
                                                  renewal}
                                   sane as above
                                                                      Portnann, et
                                                                      al (1971),
                                                                      ANIC-7701
         Gail en OS*
                              Ostrea edulls BSA    ~
                                                                15-55 (T2)
                                                  a*(contin-
                                                  uous aer-
                                                  ation,  s=a-
                                                  water,  arid
                                                  doily
                                                  solution
                                                  renewal)
                                                                                                  sa»e as abov«
                                                                                                                                     Portwann, et
                                                                                                                                     al  (1971),
                                                                                                                                     AMIC-T701
vn
vn
         Ganlen PRX
Cranqon
cranqon
                                            BSA
                                                                330-1000 (T<>>
                a«(contin-
                uous aer-
                ation, sea-
                wator, and
                daily
                solution
                renewal)
                                                                                                  same as abov«
Portnann, et
al (1971),
4MIC-7701
         Ganl«n
                              Crangon
                              crangon
                                            BSA
                                                                100-330  (Tit)
                                                 a*(con;in-
                                                 uous aar-
                                                 ation,  sea-
                                                 water,  and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                                  sa»e as above
                                                                     Port»arS IT2)      a*,c,e,f.          One hundred sixty-four
                hard (HH)  oestlcldrs, wettlnq agents, and
                or         iKlscel laneous Mater pollutants shooed a
                SOFT(SH)    Mlrle range of toxlclty soanolng 12 orders
                synthetic  of magnitude.  Knowing the toxlclty and
                dilution    percentage of all comoonents of a
                Hater,  or  formulation did not result In easy
                seaxater    predictability of the toxlclty of a
                tor some    mixture of materials.  Sometimes
                species    pesticides were most toxic in hard water
                           and sometimes the ooooslte xas true.
                           Testing the actual Material as sold was
Alabaster
(1969),
-------
Compound
Gesapax
Toxicity,
Active
Field Field Inqredient,
Orqanlsm Study Location Ppm
Pandalus BSA — 33 (T21
pontaqul
Experimental
Variables,
Control I ed
or Noted

a*( contin-
uous aer- agents,
ation, 3ea-polychl<


One


hundred- forty surface active
jrinated blohenyls, pur*>
Reference
Portwann, et
al (14711,
AMIC-7701
         Glob* terranycln pet Roecus
         tabs                 saxatllls
                               (f logerlInqs)
                                             BSA
O\
         GtoQuat C
                              Crangon
                              cranqon
                                            RSA
                                                                100-300  (T2)
         Cramoxone
         11J7)
                   H  (J.F.
Rasbora
heteromorpha
BCFA
and
BSA
17 UZ,
hardnater)
         Gra*oxon«
         11371
                   U  (J.F.
Rasbora       BCFA
heteromorpha  and
              BSA
                                 «>6 (TZ,
                                 softwater)
                                                 water, and Inorcjanic, and organic cheTlcals  xere
                                                 daily      evaluated aqalnst  as  many as  ten  marine
                                                 solution   organisms.  The authors noted  that nost
                                                 renewal)   published data of  this type deal  wltK
                                                            toxlcity of chemicals to  freshwater
                                                            orqanlsms.

                                                 a
                                                 or soft
                                                 (SW)
                                                 synthetic
                                                 dilution
                                                 Mater,  or
                                                 seaHater
                                                 for some
                                                 species
                                   a*,c,e,f,
                                   hard  (HH>
                                   or soft
                                   (SM)
                                   synthetic
                                   dilution
        One hundred-forty surface active
agents, solvent emulslflers, pesticides,
pelyehlorlnated biphenyls, cure
Inorganic, and organic cheirlcals Here
evaluated against as nany as ten marine
organisms.  The authors noted that most
published data of this type deal «ith
toxlcity of chemicals to freshxater
organisms.
        One hundred sixty-four
pesticides, wettinq agents, and
miscellaneous Kater pollutants showed a
wide ranqe of toxicity spanning 1? orders
o' maqnitude.  Knowinq the toxlcity and
percentage of all components of a
formulation did not result in easy
predictability of the toxicity of a
mixture of materials.  Sometimes
pesticides Mere most toxic in hard Hater
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.

       same as above
                                                                                        Portmann, et
                                                                                        al  M97D,
                                                                                        AMIOT701
                                                                                                                                     Alabaster
                                                                                                                                     AMIC-SI.2S
                                                                     Alabaster
                                                                     (196 <»»,
                                                                     AHIC-5VZ5
-------
         Granoxon* IJ.F.
         15*11
Rasbora
h«t»ro«ornha
BCFA
anil
8S»
570 «49>,
                                   ANIC-5U25
                                                                                                 same as above
                                                                     Alabaster
                                                                     (1969),
                                                                     AMIC-5U25
                                                      The effect of 5? pesticides on    Davis, et
                                              embryonic development of clams and        al(1969)»
                                              oysters Has reported.  Svnergistlc        A1IC-S990
                                              effects Hlth solvents Here also reported.
                                               Most of the compounds affected
                                              development more than survival.  Some,
                                              hoH»vpr, drastically reduced larval
                                              qronth.  The authors point out the
                                              necessity of evaluating the effects of
                                              pesticides on all life staoes of an
                                              organism and note the possibility of
                                              selecting chemicals for pest control that
                                              would not have serious effect on
                                              shell fish.
        Crlseofulvln
        Gulf agent 1009
Mercenaria
mercenaria
(larvae)

Crangon
cranqon
                                            BSA    —
                                                               less than 1.0
                                                               «T12I
                                                               330
                                                                                                 same as above
                                   a*(contin-         un* hundred-forty surface active
                                   uous aer-  agents, solvent efflulsiflers, pesticides,
                                   atIon,  sea-PO|vchlorlnated blphenyls, pure
                                   water,  and Inorganic, and organic chemicals Here
                                   daily      evaluated against as many as ten marine
                                   solution   organisms.  The authors noted that most
                                                                     Davis,  *t
                                                                     al(l969>,
                                                                     A1TC-S990

                                                                     Portnann, et
                                                                     al  H971),
                                                                     AMIC-7701
-------
            Coaoourxl
                                 Organism
                                              Field  Field
                                              Study  Location
Toxlclty.
Active
Ingredient,
  Ppm
ExoerlMental
Variables,
Control led
or Noted
                                                                                                            Comments
                                                                     Reference
          Guthlon
                                Ictalurus     BSA    —
                                Ounctatus
                                                                 3.29  (T<»1
ro
VJ1
CD
          Guthlon
          Cuthlon
          Cuthlon
          Guthlon
           Cuthlon
           Cuthlon
                               Ictalurus
                               •el as
                               Carass1us
                               auratus
                                CynrInus
                                carplo
                                             BSA
                                             BS*    —
                                              RSA    —
                                Plmeohales     BSA
                                promelas
                                Lttnomls       BSA
                                maerochlrus
                                leoonls       BSA
                                •Icrolophus
                                                                 3.50
                                                                 *.27
                                                                 8.695 (Tl>)
                                                                 0.295 tT<>)
                                                                 0.022 |T<»>
                                                                 0.052 (T<>)
                renewal)   published data of this type deal tilth
                           toxlclty of chemicals to freshwater
                           organisms.

                a,                 OrganochlorIne Insecticides were  HaceK, et
                synthetic  the most toxic conpounds,                 aU1970)»
                Testwater  organochosphates Intermediate, carbamates AtlIC-5510
                           the least toxic.  Brown trout Has the
                           species most susceptible to
                           orqanochlorlnest coho salmon the most
                           susceptible to carbamates, and goldfish
                           were the least susceotible of all
                           species.  Sate concentrations established
                           by bloassays with salmonids or
                           centrarchlds MOUM imely be safe for
                           cyorlnids and Ictalurids.  Sate levels
                           for Ictalurids or eyorlnlds would
                           probably be hazardous for centrarchids
                           and salmonids.  The use of goldfish In
                           bioassays was discouraged.
                                                                                 synthetic
                                                                                 test Mater
                                                                                 synthetic
                                                                                 test Mater
                 a,
                 synthetic
                 test  water

                 a,
                 synthetic
                 test  water

                 a,
                 synthetic
                 test  water

                 a,
                 synthetic
                 test  water
                                                                                                   same  as  above
                                                                                                   same as above
                                                                                                   same as above
                                                                                                   same as above
                                                                                                   same as above
                                                                                                   same as above
                                                     HaceK, et
                                                     al (19T0),
                                                     AHIC-5510

                                                     Hacek, et al

                                                     (19701, AHIC-
                                                     5510

                                                     Macek, et
                                                     al (19731.
                                                     Hacek,  et
                                                     al (1970),
                                                     Hacek,  et
                                                     aUl<>70>,
                                                      Hacek,  et
                                                      at (19701.
                                                      AM.IC-5510
-------
Cuthlon
 Guthlon
 Cuthlon
 Cuthlon
Cuthlon
Cuthlon
                      Mlcropterus    BSA
                      salnolife*
Cuthlon
Cuthlon
                      S»l«o
                      qalrdnerl
                                    8SA
                      Saleo trutta   BS»   ~
                      Oneorhvnchus   BSA
                      klsutch
Perca         8SA
ftavescens

Palaemonetes  BSA
kadiakensis
freslstantl
                                                       0.009 )
                                                       O.D17 IT*I
                                                       0.013 CT«.J
                                    a.
                                    synthetic
                                    test  water

                                    at
                                    synthetic
                                    test  Hater
                                    synthetic
                                    test  water

                                    a,
                                    synthetic
                                    test  Hater
                                                                       synthetic
                                                                       test Hater
                                                                                         sane as above
                                                                                         same as above
                                                                                         sane as above
                                                                                         sane as above
                                                                                         sane as above
                                                                                                      MaeeK,  et
                                                                                                      altl«70),
                                                                                                       Macek,  et
                                                                                                       at (1970),
                                                                                                       4MIC-5513

                                                                                                       MacrV.  *t
                                                                                                       at 119TO)t
                                                                                                       ftKTC-5510

                                                                                                       Mscek,  et
                                                                                                       81(1970),
                                                                                         Macek.  et
                                                                                         a1(l970),
                                                       (Tl)
                                                      Bioassays  were conducted with     Naovl* et a!
                                              shrlno  tron  three  areas  of  Intensive      (1970),
                                              pesticide use  and  from an unexoosed area. AMIC-5519
                                               Previously  exposed shrimp  Here fro" 1  to
                                              26  tines more  resistant  than  unexposed
                                              shrimp.  Both  types of shrimp were also
                                              exposed In caqes to naters  of the
                                              contaminated areas.  Susceptible shrimp
                                              suffered 66  percent more mortality than
                                              did resistant  shrimp.  The  toxiclty of
                                              the Insecticides ranked  In  descendlnq
                                              order Has as foil oust  nost toxic,
                                              Endrin, DOT, Methyl parathlon, Parathlonl
                                              medium toxiclty, Cuthlon, Lindane,
                                              Toxaphene, Strobanei lease  toxic
                                              Chtordane, Sevin,  and Heptachlor.
                     Palaevonetes  BSA    —
                     kadlakvnsls
                     (non-
                     r« olatant)
                     TubIfex
                     tublfex
Ft
and
BSA
                    Belzonl,
                    Hiss.
                                                       0.0089  (Tl)
                                                       1.00  (NTE)
                                                                                         same  as above
        The response of
pesticide-resistant aauatlc orqanlsos to
various Pesticides Mas compared to the
response of non-resistant soecles.
Pesticide-resistant soecles were
collected at Belzonl and non-resistant
species at State College.  Copepods,
clans, snails, and sludge worms from
Belzonl Here considerably more tolerant
to pesticides-than the non-resistant
                                                                                        NaavU et
                                                                                        11970).
                                                                                        AMIC-5519
                                                                                                                                      • I
Naavl, etal
11969),
AMIC-5979
-------
  Compound
                       Organism
                                   Field  Field
                                   Study Location
                   Toxlclty,
                   Active
                   Ingredient,
                     Ppm
Experimental
Variables,
Control led
or Noted
                                                                                                 Comments
                                                                                                                           Reference
CutMon
Cuthlon
CutMon
                     Horcenarla
                     mercenarla
                     (eggs)
                                                      0.86 (T2)
                     Mercenarla
                     •ereeniirla
                     (larvae)
                     Crassostrea   L
                     vlrqlnlea
                     (eggs)
                                                       0.86  (TtZ)
                                                       0.62  (T21
Heptachlor eooxlde   Brown
                     bullhead
FRL   Misc. states 0.3<. residue
                   (SB)
Heptachlor eooxlde   Caro
Heptachlor eooxide   Channel
                     catfish
                                   FRL    Misc.  states  0.0<>  residue
                                                       (SB)
FRL   Misc. states 0.03 residue
                   (SB)
                                              orqanlsns.  The authors note that the
                                              effect of Increased tolerance in the
                                              organisms Is an Increase In th« amount ot
                                              pesticide residues available to animals
                                              of higher trophic levels.

                                                      The effect of 52 pesticides on    Oavls, et al
                                              embryonic development of clans and
                                              oysters was reported.  Syneralstlc        (1969)
                                              effects with solvents were also reported. S990
                                               Most of the compounds affected
                                              develocment more than survival.  Some,
                                              however, drastically reduced larval
                                              growth.  The authors oolnt out the
                                              necessity of evaluating the effects of
                                              pesticides on all life stages ol an
                                              organism and note the possibility of
                                              selecting, chemicals for oest control  that
                                              would not have serious effect on
                                              shellf ish.
                                                                                         same  as above
                                                                                         sane  as above
                                                      The  Bureau of Sport Fisheries
                                              continued  its  fish moni tor Inq  oroqra""  by
                                              collecting H»7 composite  fish  samples
                                              from 50 nationwide monitoring  stations
                                              during  the fall  of 1969.  Fish were
                                              analyzed for residues of  11
                                              orqanochlorlne Insecticides, liplds, and
                                              PCB-s.

                                                     sane  as above
                                                                                         same as above
                                                                                                                            Davis,  et al
                                                     S990

                                                     Davis, et al

                                                     U9«.9I.»MIC-
                                                     S990

                                                     Henderson,
                                                     et al
                                                     (1971),
                                                     Henderson,et
                                                     al  (1971),
                                                     AMIC-li.07

                                                     Henderson,
                                                     • t  al
-------
                                                                                                                            (19*1).
 HeotaeMor eooxlde
HcBtacMor epoxld*
                      Small mouth
                      buffalo
                     Fa I co
                     oei-»grlnus
                     (Immature)
                                   PRL
HIsc. states 0.16 residue
             (SB)
Western
D.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
0.09 (Mhole
body residue!
Meotachlor eooxlde
Heotaehlor
                     Fa I co
                     oeregrlnus
                     (adult)
                     Gizzard shad  FRL
Western      0.18-1.0 (whole
U.S.,        body residue)
Pacific
Ocean.
Panamai
Mexico,and
Antarctic

Misc. states fl.i»5 residue
             (SB)
He»taehlor
Heotacnlor
                     Blue catfish  FRL
                     Rasbora       BCF*
                     heteromoroha  and
                                   BS*
                                         disc, states 0.22 residue
                                                      (SB)
                                                      0.05 (TZ)
       same as above                      Henderson,
                                          et al
                                          (1971I.
                                          *HIC-1<,97

        Peregrine falcons, falcon crey,   Rlsebrough,
and other predator soecies Here collected et al
Hldely and analyzed lor DOT, ODE, PCS.    (1968), AMIC-
and a few other pesticides to a lesser    38<»I>
deqree.  PCR and DOT Mere found to be
widely dispersed globally.  PCB was found
to be 9 powerful inducer of hepatic
enzynes that deqrade oestradiol.
Reductions in thickness of egq shells,
eggshell weight, and water retention
occurred.  All affect hatching success.
The authors state that the per*qrine may
be the first species entlrpated by global
contamination.
                                                                                        s*«e  as  above
                                                                     Rlsebrougn,
                                                                     et al
                                                                     (1968),
                                                                                         The Bureau of Sport Fisheries
                                                                                 eontinuod  its  fish monitoring proqran by
                                                                                 collecting li>7 composite  fish samples
                                                                                 from 5Q nationwide monitoring stations
                                                                                 during the fall of 196g.  Fish were
                                                                                 analyzed for r»sldues of  11
                                                                                 orqanochtorlne insecticides,  llplds? and
                                                                                 PCS-s.

                                                                                        sane as above
                                                                     Henderson,
                                                                     eta I
                                                                                  Henderson,
                                                                                  etal (1971),
                                                                                  AMIC-H.97
                             a*,c,e,f.          One hundred sixty-four            Alabaster
                             b*rd (HW)  pesticides, wetting agents, and           (1969),
                             or soft    miscellaneous wafer pollutants showed a   AMIC-5b?5
                             (S4) syn-  wide range of toxiclty spanning 12 orders
                             thetlc     of magnitude.  Knowing the toxiclty and
                             dilution   percentage of all components of a
                             water, or  formulation did not result In easy
                             •eaumter   predictability of the toxiclty of a
-------
Covoound

Field Field
Organism Study Location

Toxlclty,
Active
Ingredient,
Pp»

Experimental
Variables,
Control led
or Noted
for some mixture of
species pesticides
Consents Reference
Materials. Sometimes
were most toxic In hard water
Heotachlor
Heotachlor
                     Lepomls
                     cyan*11 us
                     (Resistant)
                                   BS»
                                  1.96  (T2>
                     Leoomls
                     cyanellus
                     (Susceptible)
              BS»
                                 0.07 (T21
 and sometimes  the  ooooslte Has true.
 Testlnq  the  actual  material as sold was
 found  to  be  essential.

         Green  sunflsh  from BelzonI, Miss. Ninchew, et
 were resistant to  Chlordane, Heptachtor,  al(197»),
 Llndanp,  and Strobane, but not to         *MIC-5«t71
 Parathlon.   Golden shiners fro™  the same
 location  were  resistant  to Llndane and
 Strobane,  tolerant to  Chlordane  and
 Heptachlor,  and susceptible to Parathlon.
 Lack  cf  resistance to Parathlon
 indicated lack of  agricultural usaoe of
 orqanochosphates in that area.   Resistant
 fish were compared to  susceptible ones
 collected at Starkvllle.
                                                                   sane as above
                                                                                                      Hlnchew, et
                                                                                                      al (10701,
Heptachlor
Heotachlor
Notemlgonus
crysoleucas
(Resistant)

Noteilgonus
crvsoleucas
(Susceptible)
                                   BS»
                                   BSA
                                                           (T3)
                                                      0.
-------
         Hepfachlor
         Keptachi or
         Heptachlor
u>
         Heptachlor
Palae*onet«s
KadlakensJs
(non-
real slant)

Het«ropneU3-
tos fossills
A*phlpnous
cuchta
                                            BSA
                                                               0.01.06  (Til
1.0 (S3 2 hr,K  —
<•«. hr)
                                                                                          Medium  toxlcity,  Guthlon, Llndane,
                                                                                          Toxaph«ne« StrobaneJ  lease  toxic
                                                                                          Chlordane, Sevln,  and Heptachlor.

                                                                                                  same  as above
                                                                                                  Epldernal  lesions of catfish
                                                                                          barbels were moderate to severe after
                                                                                          exposure noted.  Barbel curllnq and
                                                                                          Inactlvatlon were  associated effects.
                                                                                                                                    Naavi,  «t 81
                                                                                                                                    Konar
                                            BSA
                                                               2.0 (K31
                                                                                »,c,dte,f
                                                                                                                                    Konar
                                   All bloassar animals xere
                           collected  locally sooarently near
                           Muzaffarpur. Bihar, India.  The bloassay  «MIC-i.<.»
                           consisted of a simple | ar (8-llter) with
                           dally solution renexal (except for
                           plankton studies In xhlch solutions «*re
                           not renewed).  A safe apallcatlon rate of
                           0.813 Ib/acre was suggested for survival
                           of Host aquatic species.
                              Anabus
                              trstudlncus
                                            BSA
                                                               0.5 (K3>
                                                                                a.e.d.e, f
                                                                                                 sane  as above
                                                                                                      Konar
                                                                                                      I19TO) .
         Heptachlor
         Heptachlor
         H«pt»cMor
Channa
ounctatus
(frvl

Channa
punctitus
(adult)

Esenius
danrlca
                                            BSA
                                            BSA   —
                                            BSA
                                                               0.001 (Kilt
                                                               Z.O (K2I
                                                               0.2 (Kt)
                                                                               a.ctd,e,f
                                                                                                 same as above
                                                                                                 sane  as above
                                                                                                 sane as above
                                                                     Konar
                                                                     (19701 .
                                                                     AMIC-M.8

                                                                     Konar
                                                                     I197P) ,
         Heotachlor
         Heptachlor
Heteropnoua-
tea foasllis
Mry)
                                            BSA
                                                               0.016 (K2>      a,c,d,*,f
H«t*ropnau«- BSA
tes  fossllis
(adultt
                                                               1.0 (K2>
                                                                               a,c.d,e,f
                                                                                                 sane as above
                                                                                                 sane as above
                                                                     Konar
                                                                     (19ro),AMIC-
                                                                     Konar (1970) ,
                                                                     AM!C-i>ii8
-------




s







Coapound
Heptachlor
Heptachlor
Heptachlor
Heptachlor
Heptachlor

Heptaehlor
Heptachlor
Heptachlor
Heptachlor
Heptachlor
Heptachlor
Field Field
TJrqanlsa Study Location
Oaphnla BS A
Oiaptoeus BSA — —
Gastrotrlcha BSA —
Naupl lus RSA
Pandorlna BSA — -

Volvox BSA —
Anlsoptera BSA --
(nynphs)
Belostoaa BSA —
Indlca
Cybister SB. BSA —
Oytlscus sp. BSA
(larvae)
Oytlscus SB. BSA —
(adult)
Toxiclty,
Active
Ingredient.
Poa
0.1 (K)
0.1 IK)
0.1 (NT)
0.1 (K)
0.001 (K)

O.OD1 (K)
0.01 (K5)
2.0 (K3)
0.1 (K3)
0.05 (K2)
0.1 (K3)
Experimental
Variables.
Control led
or Noted
a.c.d.e.t
a.c,d,e, t
a.c.d.e.f
a,c.d,e, t
a,c,d.e,f

a.c,d,e,f
,,c.d...r
a.c.d.e.f
a.c.d.e, f
a.c.d.e.f
a.c.d.e.t
Comments
save as above
saae as above
sane as above
sane as above
saae as above

saae as above
saae as above
sane as above
saae as above
saae as above
saae as above
Reference
Konar
(1970). AHIO
ttft
Konar
Konar
(1970) .
Konar
(1970),
Konar
AMIC-«i<.S
Konar
(197(1) ,
AHIC-H8
Konar
(19711).
Konar
(1970),
Konar
(1970).
A1TC-H8
Konar
(1970), »HIC-
Konar
(1970).
-------
k
vn
Hepfechlor


Heotachlor



HeptaeMor



Heptachtor



Meotacnlor



Heotachlor



Hepfaehlor



Heotachlor



HepfaeMor



Heptacntor



HeptacMor



Heotachlor



Heptachtor



HeotacMor



Heptaehlor
                                Hydroohllus   BSA   -r
                                sp.

                                Neoa so.       BSA
                                Notonecta so. BSA   —
                                Ranatra       BS»
                                fillfornls
                                              BSA
                                annulatun
                                Hystus      -  BSA
                                vlttatus
                                Nsndus nandus BSA   ~
Puntlus       BSA
                                Trlcho       a,c,d,*,t



                                 0.007  (K3)       a.c.d.e.f
                                                                 0.5 (Kit
                                  0.1  (ICH
                                  0.3  (K3I
                                                                 0.1 (K)
                                Cyorls
                                              BSA
                                                                 0.1 (K)
                                                                 0.1   (Kl)       a.c.d.c.r
                                                  a.c.d.e.f
                                 0.1  (NTEi        a.c.d.e.r
                                                                                 a.c.d.e,f
                                                                 0.001 (K)       a.c.d.e.f
                                                                                 a.c.d.e.f
                                                                                 a.c.d.c.f
sane as above


sane as above



sane as above



same as above



sane as above



sane as above



sane as above



sane as above



sane as above



sane as above



sane as above



sane as above



same as above



sane as above



sane as above
Konar(1970J,
A*1IC-8

Konar
(1970»,
41IC-UI.8

Konar
(19701,
AMIC-lt8

Konar
11973),
                                                                                                       Konar
                                                                                                       (1970) ,A«IC-
Konar
(1970),AHIC-
Konsr
(1970) ,
                                                                                                       Konsr
                                                                                                       (1970) ,
                                                                                                       AMIC-«.l(8

                                                                                                       Konar
                                                                                                       (1970) ,
                                                                                                       Konar
                                                                                                       (1970),
                                                                                                       f.1.8

                                                                                                       Konar
                                                                                                       (1970).
-------
f
&
Compound
Meptachlor
Meotachlor
Hexachl orobenzene
Hexacnl orobenzene
Hexach 1 orobenzene
Hexachl orobenzene
Hexachl orobenzene
H« xach f or odl me thy 1
cut Ton*
Toxlclty, Experimental
Active Variables.
Field Field Ingredient, Controlled
Organism Study Location Ppm or Noted Comments
Labeo rohlta BSA — 0.0? (Kl> a,c,d,e»f same as above
(early
f inserting)
Labeo rohlta BSA ~ 0.20 (K2) a,c,d,e,f same as above
(late
f Inqer ling)
Anqullla FRL St. John, 0.01 (residue) —
rostrata N.R., Can.
Esox nlqer FRL St. John, 0.03 (residue! --
N.B., Can.
Salmo salar FRL St. John, 0.002
N.B., Can. (residue)
Cluoea FRL St. John, 0.003-0.006
harenqus N.B., Can. (residue)
Scomber FRL St. John, B.001
scombrus N.B., Can. (residue)
Phormldlum L — 0.5-10.0 (NTE) —
ambiquum
PCB""s were found In higher
concentrations than organochl or ine
pesticides In all fish analyzed. The
authors point out that PCB is less toxic
In an acute sense than orqanochl orines,
that little Is Known of sublethal PCB
distribution and effects is needed.
same as above
same as above
same as above
same as above
Of 7i» chemicals evaluated as
alqlcides, only 9 Here more toxic than
Reference
Konar
(197B»,»MIC-
U<.B
Konar
(1970), AHIC-
<>t8
Zltko
(1971),
AMIC-S71S
ZltHo(197U,
AMIC-371S
ZltKo(1971),
AMIC-371«:
Zltko
(1971),
AMIC-3715
ZltKo
(1971),
AfIC-3715
Otto<1978) ,
AHIC-89Z
                                                                                           CuSO<>.  None  Inhibited growth of
                                                                                           mat-forminq algae for more than ? weeks.
                                                                                           CuSOi. formulated xlth certain netting
                                                                                           agents Has more toxic than CuSOl> alone.
                                                                                           Cooper chloramne Has also found to be
                                                                                           more toxic than CuSnit.  No netting agents
                                                                                           Here found to be Inhibitory at the
                                                                                           concentrations investigated (H.05 and
                                                                                           0.005 ppm).   Also reported are factors
                                                                                           affecting growth of algae in canals to
                                                                                           determine Hhether there Here leads to
                                                                                           controlling alga* by environmental
-------
Hexedecanol
(Preoarat »lfol HV
IB)
                     Copeoods
                                   8SA
                                                       (NTE)
         Hexadecanol
         (Praparat Alfol  HV
         10)

         Mexadecanof
         (Praparat Alfol  HV
>       10)

TO       Hexad»eanol
Cr»       (Praparat Alfol  HV
-1       10)

         Hexadecanol
         (Praparat Alfol  HV
         101

         Hexadecanol
         (Praparat Atfol  HV
         10)

         Hlllvale  Fly  dip
                     Oaohnla
                                   BSA   —
                     TublMclds    BSA   —
                     LeblstM      BSA
                     retlcutatus
                     Salmo         9SA
                     qalrdnerl
                     Gerrls
                                   BSA   —
                     Rasbora       BCFA
                     heteromorpha  and
                                   BSA
                                                       (NTE)
                                                       INTO
                                                       (NTE)
                                                       (NTE)
                                                      (Suffocation)
                                                      2.1 (Tl)
                *»,c,e,f.
                bard (HV)
                or aoft
                {«) ayn-
                thetio
                water, or
                aeawater
                for >on«
                •peclai
Hlstaalnc phosphat*
                     Ncqaorlon
                     brevlrostrls
                     (1-3 ko)
                                   BSA
kt (NTE 2 nr)    a,c,«
                           •anageeent.  No practical environmental
                           means were found.

                                   The formulation was applied to    fann
                           the Hater surface at concentration levels (1971),AMIC-
                           to yield a more or less continuous        3079
                           •onomolecutar layer.  Gerrls and other
                           surface-oriented aauatlc Insects as Hell
                           •s Insect larvae that surface to breathe
                           and hatch could not maintain themselves
                           at the surface and therefore sank and
                           suffocated.

                                  same as above                      "ann
                                                                                        same as above
                                                                                        same as above
                                                                                        sane as above
                                                                                        same as above
                                                                     3079

                                                                     Hann
                                                                     (1971
                                                                     3079
                                                                                                                                 ,AHIC-
                                                                     Mann(1971)
                                                                     AMIC-3079
                                          Hann
                                          I1S71),AMIC-
                                          3079

                                          Mann
                                          tl«71),AMIC-
                                          3079

                                          Alabaster,
                                          11969),A1IC-
        One hundred sixty-four
pesticides, wetting aqents, and
miscellaneous water pollutants shotted a
wide ranae of toxlclty spanning 12 orders
of magnitude.  Knotting the toxicity and
percentage of all components of a
formulation did not result In easy
predictability of th« toxlclty of a
mixture of materials.  Sometimes
pesticides xere most toxic In hard water
an-1 sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
        Data from study of drug effects   Batdrldqe
on youncj lemon sharK% wore treated        fl*lft^l,
mathematically to demonstrate             AMIC-3132
applicability of classical rate theory to
the study of chemical shark deterrents.
-------
  Conoound
              Field  Field
  Organism    Study Location
             Toxlclty,
             Active
             Ingredient,
               PDH
                                                                       Experimental
                                                                       Variables.
                                                                       Control led
                                                                       or  Noted
                                                                                                  Comments
                                                                                                                           Reference
Hobstone OSD
                     Crangon
                     cr angon
                                   BSA
                                                       1.0-3.3  (T2>
Hoc SC 178D
                     Cranqon
                     cranqon
                                   BSA
                                                       330-1000  (T2>
Holl-Cne» 622
                     Steethead
                     trout
                     (tInqerlInqs)
                                   BS*   —
                                                       3.2  (W
Boll-Chen 622
Houqhtosolv*
Coho salmon   BSA
(ringerllngs) In
              altu
Hood Canal,
Hoodsport,
Wash.
                     Cranqon
                     crangon
                                   BSA   —
                                                      0.1 (K)
                                                       10-33  (T2>
           Tncaoacltatlon (narcosis)  Has the primary
           parameter timed for effectiveness.  This
           nas usually qulta rapid for the more
           effective drugs.

ac(contin-         One hundred-forty surface active  Portmann, et
uous aer-  agents, solvent emulslflers, pesticides,  al (1971).
ation, sea. poI yenlorlnated blohenyls. oure           AMIC-7781
water, and inorganic, and organic cheolcals Here
dally      evaluated against as many as ten marine
solution   organisms.  The authors noted that most
renewal)   oubllshed data of this tyoe deal Hith
           toxlclty of chemicals to freshwater
           organ Isms.

a*-(contin-         One hundred-forty surface active  Portmann, «t
uous aer-  agents, solvent emulslflers, pesticides,  al (1971),
ation, sea-oolych lorlnated biphpnyls, oure           ANIC-7701
water, and Inorganic, and organic chemicals Here
daily      evaluated against as many as ten marine
solution   organisms.  The authors noted that most
renewal)   oubltshed data of this type deal with
           toxlclty of chemicals to freshwater
           organisms.

--                 Fvatuatlon of 11 oil dlsoersants  Tracy, et
           resulted In a ranking for each and a      alfl969).
           recommendation for use according to the   ANIC-383<>
           ranKina.  Ranting Has based on toxiclty
           and oil dispersal effectiveness.  Corexlt
           776". appeared to have the least toxlclty
           with fair to good oil dispersion
           capabl 11 ty.

                 same as above                       Tracy, et al
                                                     (1969),
                                                  a«{contin-         One hundred-forty surface  active
                                                  uous aer-  agents* solvent emulslflers, pesticides,
                                                  ation, sea-Polychlorlnated blphenyls, pure
                                                  water, and Inorganic, and organic chenlcals Here
                                                  daily      evaluated against as many as ten marine
                                                  solution   organisms.  The authors noted that most
                                                  renewal)   published data of this type deal Kith
                                                            toxlcity of chemicals to freshwater
                                                                                  Portmann, et
                                                                                  al  (1971).
                                                                                  AHIC-7701
-------
                                                                                           organisms.
         Hydrochloric acid
                              Brook  trout
                                                                OH  3.5  (SBlt)
         Hydrochloric acid
r
VO
         Hydrochloric acid
         Hydrochloric acid
         Hydrochloric acid
         Hydrochloric acid
         Hydrochloric acid
         Hydrochloric acid
         Hydrochloric acid
Br»chycentrus 8CFA
americanus
(larva* and
nymphs)
                                            BCF»  —
                                            BCFA  —
Cohemerella
suhvar la
(larvae and
nymphs)

Hydropsyche
bettenl
(larva* and
nymphs)
                              Taenlopteryx  BCFA
                              maura (larvaa
                              and nymphs)
Boreria
vlnosa
(larva** and
nymphs)

Acroneurla
lycorlas
(larva* and
nymphs)

Stenonema
rubrum
(larvae and
nymphs)
Ophlogomphus  BCFA
ruplnsulensls
                                            BCFA  —
                                            BCFA  —
                                            BCFA  —
                                                                     Excessive  mucin  accumulated in     Vaala.  et  al
                                                             the  gill  region  of exposed  trout.   No
                                                             evidence of  enhanced  hemoooiesis  or       (1969)*AMTC*
                                                             Increased red  cell destruction  Mas  found.  5709
                                                              The authors concluded  that  one of  the
                                                             reasons  for  trout  deaths In  acid  water  is
                                                             that  compensatory  erythrooolesis  does not
                                                             occur or  Is  not  rapidly  Initiated.
                                                                pH  1.21-1.8      a.c.d.e
                                                               PH              a«c,d,e
                                                               •».35-5.05>8    a,c,d,»
                                 (T
                                                               pH Z.90-3.7<»    a.c.d.e
                                   tauatlc Insects generally Here
                           tolerant of acid conditions for at least
                           one weeK.  Th* organisms died .at pH
                           values be I ox those normally found In
                           streams.  The authors point out that
                           ecological factors In streams may cause
                           different results.  Research on long-term
                           effects on nolrtng, growth, reproduction,
                           and survival Mas recommended.

                                  seme as above
                                                               pH 3.15-3.1.1    a.c.d.e
                                                               PH 3.31-3.71    a.c.d.e
                                                                                                 same  as above
                                                                                                 same  as above
                                                                                                 same  as above
                                                                                                 same  as above
                                                                                                 same  as above
                                                                                                 same  as above
                                                                                                                                     8*11,  et  al
                                                                                                                                     »>1IC-5988
                                                                                                                                              al
                                                                     Bel I, et
                                                                     (1969),
                                                                     AKIC-5988
                                                                     Bel 1 , et al
                                                                     (19S9I,
Bell, et al
(1969).
AHIC-5988

Bel I, et al
(1969),
AMIC-5988
                                                                     Bel I, et «
                                                                     (1969),
                                                                     A1IC-5988
                                                                     Bel I, et al
                                                                     (1969),
                                                                     AMIC-5988
                                                                     Bel I, et al
                                                                     (1969).
-------
Compound


Hydrochloric acid



Hydrochloric acid



Hydrochloric acid

Toxiclty, Experimental
Active Variables,
Flold Flald Ingredient, Controlled
Organism Study Location Poa or Noted Comments
(larvae and
nymphs)
Isogenus BCFA —
frontal is
1 larva* and
nymphs)
Pteronarcys BCF» — •
dorsata
(l*rvae and
nymphs)
Carclnus BSA ~
maenas


PH 3.20-<».0                       to test the effect of hydrogen sutflde on al  (1970),
                                                                                 Pike eggs and sac fry and the effect of   AMIC-5516
                                                                                 oxygen concentrations on hydrogen sulfide
                                                                                 toxlclty.  Eggs subjected to hydrogen
                                                                                 sulflde produced a higher oercentaae of
                                                                                 sac fry with anatomical sailor-nations.
                                                                                 Sac fry hatched from eggs held at the
                                                                                 higher hydrogen sulfide concentrations
                                                                                 were smaller than the controls.  Sac fry
                                                                                 subjected to hydrogen sulflde showed
                                                                                 decreased gronth rates at the higher
                                                                                 concentrations.  The level of dissolved
                                                                                 oxygen was significant only in relation
-------
Hydrogen sulfl,
   Daphnla  was generally the  most sensitive   AMIC-<>53
   organism.   All  of  the Crustacea  were
   affected by much  tower  concentration
   levels of herbicides than  indicated  by
   the  TL Sub  50 values.   All of  the animals
   represent Important  food chain links.

           Of  71. chemicals evaluated as      Otto (1970)*
   alglcldes,  only 9  were more toxic than     AMIC-892
   CuSOi>.   None inhibited growth  of
   mat-forming aloae  for more than  2 weeks.
   CuSOfc  formulated  with certain  wetting
   agents was  more toxic than CuSO
-------
          Coaoound
        HZS1F6  (as
        FLUOPIOE*
         ZAA
         latin* brushneed
         killer
10
         lallne  orast  gronth
         regulator  (Regulox)
         latine  verqlclde
         •eedklller D
Toxicity, Experimental
Active Variables,
Field Field Ingredient. Controlled
Organism: Study Location Pp* or Noted Comments
Plmephates BCF —
promelas

woirria i>
papullfara



Sal mo BCF* ~
galrdnerl and
USA










Sal mo BCF* —
galrdnerl and
as*







Sal mo BCF* —
galrdnerl and
as*







0.8-0.13 (NT) a*,c,d,e,f
,r»,s

100 (X) Hunter's
medium
diluted
1:5


27 CTZ) a*,c,e,f.
hard
tHil) or
soft (SVO
synthetic
dilution
Hater, or
seaHater
for some
species



56 IT21 a»,c,*,T,
hard (HH)
or soft
(SH)
synthetic
dilution
water, or
aeawater
tor some
spades
3.3 (TZI a'.c.e.f.
hard(HH)
or soft
ISMI
synthetic
dilution
Hater, or
seauater
for some
soec las
same as above


All compounds were harnful to
duckweed to aorae decree. Decreased
populations were noted at non-lethal
concentrations and some compounds
(Kalathlon and 2A-D) caused teratogenlc
affaeta at concentrations aa low aa 1 ppm,
One hundred sixty-four
pesticides, netting aqents,_and
miscellaneous Hater pollutants showed a
Hide range of toxicity spanning 12 orders
of magnitude. Knowing the toxicity and
percentage of all comoonents of a
formulation did not result in easy
predictability of the toxicity of a
mixture of materials. Sometimes
pesticides Here most toxic in hard Hater
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
same as above









same as above









Reference
Arthuret al
U971),
ANIC-3290
Worthley, at
al (1971),
WUC-3233


a
Alabaster
(196g> ,AMIC—
5*iZ5










alabaster
(1969),
*HIC-5<.?5







Alabaster
tl9S9).AMIC-
51.25







-------
lodoacetic add
Phormldlum
•e-blquum
                                   L     —
O.f-10.0 (100
percent growth
Inhibited 1O
Toxynll Na
Basher*       BCFA
heteromorpha  and
              BSA
                                 68 (TZ,
                                 hard-water)
loxynll Na
Rasbora       BCFA
heteromorpha  and
              BSA
                                 3.3 (T2,
                                 softwater)
                                                                      hard
                                                                      (HM)or
                                                                      soft (SHI
                                                                      synthetic
                                                                      dilution
                                                                      water, or
                                                                      seaiiater
                                                                      for son*
                                                                      species
                a*tcte,f.
                hard
                (HM)or
                soft tsu)
                synthetic
                dilution
                Hater, or
                seatiater
                for son*
                species
                     Gammarus
                     faiclatus
                                   BS»   —
                                                      19.0
        Of 7it chemicals evaluated as
alqlcides, only 9 Mere mart toxic than
Cu<>0<>.  None  inhibited qrowth of
mat-forming algae for more than ? HeeHs.
CuSO
-------
Compound
Field Field
•Organism Study Location
Toxlclty,
Active
Ingredient,
Ppm
Experimental
Variables.
Controlled
or Noted Comments Reference '
         Iron
I
          Iron
          Iron
         Iron
          Iron
         Iron
         Iron
                               Paralafarax
                               clathratus
                                             FH
                               Paralabrax
                               elathratus
                               Paral abrax
                               elathratus
                               Paratabrax
                               clathratus
                               Par at abrax
                               clathratus
                               Paralabrax
                               clathratus
                               Paralabrax
                               elathratus
                               (gravid
                                             FH
                                             FM
                                             FH
                                             FH
                                             FH
                                             FN
Scatterqood  <>>> (dorsal
Steam PI ant i Muscle
Los Angeles, residue)
Cat.
Catallna     3? (dorsal
Island, Cat. muscle
             residue*

Scatterqood  
-------
                              females!
ro
-a
vn
         Iron
         Iron
        Iron
        Iron
        Iron
        Iron
        Iron
        Iron
                              Paralsbrax
                              clathratus
                              Paralabrax
                              clathratus
                              Paralabrax
                              clathratus
                              Paralabrax
                              clathratus
                              Paratabrax
                              clathratus
                             Paralabrax
                             clathratus
                             Paralabrax
                             elathratus
                             Paralahrax
                             clathratus
        Iso-oroovl           Rasbora
        Z,«»» dlnI tro-6-sec-bu heteromorpha
        tylphenyl carbonate
                                            FH
                                            FM
                                            FH
                                            FH
                                           FH
                                           FH
                                           FM
BCFA
and
BSA
       Scattergood   160  (liver
       Steam  Plant,  residue)
       Los  Angeles,
       Cal.

       ratalIna      205  (liver
       Island, Cal.  residue)
      Scatterqood  72  (Integument
      5t«am Plant, residue)
      Los Angeles«
      Cal.

      Catallna     77  I Integument
      Island, Cal. residue)
      Scatterqood  <> 80  (heart
      Steam Plant, residue)
      Los Angeles,
      Pal.

      Catallna     6
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                      Staoleton
                                                      (1968),
                                                      AMIC-S980
                                                                                                                                    S tao I « ton
a*,c,e,t.          One hundred sixty-four
hard (HH)  pesticides, wetting agents, and
or soft    miscellaneous xater ool lutants shotted a
(SVO       wide range of toxlclty scanning 12 orders
synthetic  of magnitude.  Knotting the toxlclty and
dilution   percentage of all comoonents of a
Hater,  or  formulation did not result In easy
seawater   predictability of the toxlclty of a
forsoma    mixture of materials.  Sometimes
species    pesticides Here most toxic In hard Mater
           and sometimes the oooosite Has true.
           Testing the actual material as sold Has
           found to be essential.
                                                     Staole.ton
                                                     (196S1 ,
                                                     AHIC-59SQ
                                                     Staoleton
                                                     (l^sa),
                                                     AMIC-5990

                                                     Staot eton
                                                     (1968),
                                                     AHIC-5980
                                                     Staol eton
                                                     (196M,
                                                                                                                                    Staoteton
                                                                                                                                    AMIC-5980
Staoleton
(19f>8) ,
AMIC-5980

Alabaster
(1969),
AHIC-5%25
-------
I
Ori
Comoound
I.C. I. Summer sheep
dip










Jansol v-60






Jansol v-60


Jansol v-60


Jan-Sol v-60







Jan-Sol v-60
Toxlclty.
Active
Field Field Inqredlent,
Organism Study Location Pom
Rasbora «CF* — I..1 (T2I
heteromorpha and
BS*









Pimephales BS* -- aporox. 56.0
promelas (Ti»)





Pimephales BSA — approx. 7.5
promelas (HSCI

Biochemical L — 350.000
oxygen
demand
Steel head BS* — 35.5 CT*1
trout
(f Inqerl Inqs)





Coho salmon BSA Hood Canal, 0.8 (K)
( f 1 nqer 1 1 nqs ) In Hoodsport,
situ Wash.
Exoerlmental
Variables,
Control led
or Noted Comments
a'.c.e.f.
hard
)
                                                                                                   Bioassays  Here conducted  at  12  C.  Harking
                                                                                            The toxlclty of Juqlone  to rainbow  trout  (1970),A*1IC-
                                                                                           and blueglI Is .Mas  not altered              5517
-------
 5-
a
         Juglone
         Juqlon*
Juglone
         Ju9lon*
                               Esox  luclus   BSA
                               auratus
Cyorlnus
cvolo
                              Catostomus
                              co»i»»rsonl
                                            BSA   —
                                   BS*
                                            BSA
                                                                0.0271 ITVI
                                                                0.080  (T
                                                                                           significantly In Maters of different
                                                                                           tenoerature or hardness.  Standard (oH
                                                                                           7.1.)  and buffered (DH 9.0) solutions of
                                                                                           Juglone aaed for one Meek effectively
                                                                                           killed ralnbOH trout although
                                                                                           acoroxlmately three tines as much Jug I one
                                                                                           Has r'-julred at the hlqher oH.  Juqlon*
                                                                                           Is ea;Ily reduced to less toxic
                                                                                           components by factors In  the natural
                                                                                           environment.  However, Juqlone Is
                                                                                           sufficiently persistent to eltnlnat*
                                                                                           target fish.

                                                                                                  sa«e as above
                                                                                                  sane as above
                                                                                         same as above
                                                                                                  save as above
                                          Marking
                                          (1975) ,
                                          AfIC-5517

                                          Marking
                                          (19701 ,
                                          AMIC-5517

                                          Harking
                                          11070).
                                          SMIC-5S17

                                          Marking
         Juglone
         Jugfone
         Juglone
         Jug) on*
                     Ictaluru*
                     ••las
                     Ictalurus
                     punctatus
                              l«oo*ls
                              cyan«!I us
                                            BSA   —
                                            BSA   —
                                            BSA
                     lepoitls       BSA
                     •aerochlrus
                                                                0.0757
                                                                0.0367  (TV)
                                                                0.01.69  (T«l
                                                                0.01.29  (TV)
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                       Harking
                                                                                                       (1970) ,
                                                                                                       AMIC-SS17

                                                                                                       Marking
                                                                                                       (19701 ,
                                                                                                       AMIC-5517

                                                                                                       Marking
                                                                                                       (197D).
                                                                                                       AHIC-S517

                                                                                                       Marking
                                                                                                       (197C) ,
         Kartex
         Kelth«ni>
                               eoccus
                               saxatilis
                               (finq»rlIngs)
                     Tublfex
                     tublfex
                                            BSA
              FL    Relzonl,
              and   Hiss.
                                                                3.0  (Ti,)
                                                                0.50  (NTC1
                                                                      a*,ctd,e,f          Strioed bass ftnqerllngs ner*     He)(born
                                                                      ,D and      apparently much nore sensitive to         (1969).
                                                                      iron        therapeutic and herbicldal compounds than AHIC-5723
                                                                                  •any  freshwater fish.
        The response of
pesticide-resistant aquatic organisms to
Naqvl. »t at
(1969).
-------
  Compound
                       Organise)
Field  Field
Study Location
Toxlcity,
Active
Ingredient*
  PD»
Experimental
Variables,
Controlled
or Noted
                                                                                                 Comments
                                                                                                                           Reference
                                   8SA
Ketoendrln
Ketoendrln
Kief es
                     Anaeystls     L
                     nl <1u I ans
                     Agmenellum    L     —
                     qimdrup.
                     lleatwT

                     Puntlus tlcto —    —
                   0.5-1.0 (growth a*»c*»r
                   Inhibited)      SH
                                                      NTt
                                                      0.00017  m>
                                   a».c»,r
                                   SH
                                                                      a.c,d,e,f
                           various pesticides was compared to the
                           resoonse of non-resistant species.
                           Pesticide-resistant species were
                           collected at Rplzonl and non-resistant
                           species at State College.  Cooepods,
                           clams,  snails, and sludge worms from
                           Belzonl were considerably more tolerant
                           to pesticides than the non-resistant
                           organisms.  The authors note that the
                           effect  of Increased tolerance In the
                           organisms Is an Increase In the amount of
                           pesticide residues available to animals
                           of hlaher trophic levels*

                                   Metabolic products of Aldrln,
                           Oleldrln, and Endrln can be as toxic  as
                           the oarent compounds, as shown by  00
                           measurement.

                                  same as above
                                                                                                                           AHIC-5979
                                                     Batterton,
                                                     al (1971),
                                                     AHIC-1%71
                                                                     Batterton,
                                                                     et al(1971)
                                                                     AMIC-1J.71
                                                                                          Of  the  pesticides  Investigated,    Bhatia
                                                                                  the most  toxic  Has  Klofos  followed  in      (1971),IHIC-
                                                                                  decreaslnq  order  by Sunlthion,  Nalathlon,  5*23
                                                                                  Formlthlon,  Olnecron, Sevln,  and BHC. The
                                                                                  author  cites the  need  for  more  selective
                                                                                  pesticides  nontoxlc to  fish or
                                                                                  antagonistic agents for reducing fish
                                                                                  toxlclty.
LAS
                     Plmeohalos    BCFA
                     promelas
Lauryl ether sulfate Cardlurn edule 8SA
(plus ethylene
oxide)
                                                       3.5  CTi.)
                                                          (T2)
                                                                       a».e
                                                                                                                                      al
                                                      L»S  acted synerqjstleal I/ with    Solon, «t
                                              parathlon to cause  less survival of       (1969),
                                              fatheris but had an  Indeterminate effect   »MJC-37S5
                                              with DDT and no synerglstlc effect with
                                              Endrln.

                                   at-(contin-         One hundred-forty surface active  Portmann, et
                                   uous aer-  aqents, solvent emutslflers, pesticides,  al
                                   aticn, aea-POlychlorlnated blphenyls, pure           (1971),AMIC-
                                   water, and Inorganic, and organic chemicals Here     7701
                                   dally      evaluated against as many as ten marine
                                   solution   organisms.  The authors noted that most
                                   renewal)   published data of this type deal with
                                              toxiclty of chemicals to freshwater
-------
                                                                                  organism.
 Lauryt  ether  sulfate Cranqon
 (plus ethylene       erangon
 oxide)
                                    BS»   —
                   qreater  thanlOO  a«(contin-
                    (T2>             uous aer-
                                    ation,  sea-
                                    water,  and
                                    dully
                                    solution
                                    renewal)
                   same  as  above
                                                      Portn>ann,et
                                                      •I  (1971),
                                                      »NIC-7701
Leuryl ether  sulfate Carelnus
(elus ethylene        vaenas
OK loci
                                    BS»   —•
                   greater  thanlOO a«(contln-
                   CTJI            uoua aer-
                                   ation, sea-
                                   water, and
                                   daily
                                   solution
                                   renewal)
                                                      same  as above
                                                      Portmann.et
                                                      el  11=171),
                                                      AKTC-7701
Lauryl ether sulfate  Panda I us
lotus ethylene        nontagul
oxide)
BS*   —
                   greater thanlOO. a«(contln-
                   (TZ>            uous aer-
                                   ation, sea-
                                   water, and
                                   dally
                                   solution
                                   renewal)
                  sane as above
                                                     Port»ann,eT
                                                     al  (1471),
                                                     AHIC-77B1
Lead arsenate
Lead carbonate
                     Fish  Inot
                     specif led)
                     Carass1us
                     auratus
                   greater than
                   10-100 (K)
                                                       110  IT7)
Lead nitrate  (as
lead)
                     Cardluei edule 8S»    —
                   greater than
                   500 (T2)
                   Aporoxlmat* toxlcltles of
           nunerous oestlcldes cownonly used In
           Britain ir«r« sum«arl2*
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Organism Study Location Ppm



Lead nitrate (as Pandalus BSA — 375 CT2)
leadl tiontaqul





Experimental
Variables,
Controlled
or Noted Comments Reference
renewal) published data of this type deal with
Toxlclty of chemicals to freshwater
organisms.
e*(contin- same as above Portmann, et
UOU3 aer- at (1971).
ation, sea- HHT.C-7701
water, and
daily
solution
renewal)
lead nitrate
Car ass 1 us     L     —
auratus
                                                      6.6 (T7I
                                                                      a,c
Lead sulfate (as
Pbl
Lend sulfate (as
Pbl
Lead sulfate (as
Pbl
Lead
                     Acroneurla    BSA
                     Ephemerella   BSA   —
                     Hydroosyche   BSA   —
                                                         (T1U)
                                                      16 (T7I
                                                       3?  (T7>
a*,c«d«e« f
                   In addition to toxlclty data.      Heir,  et  al
           conditioned avoidance response was        (1970),
           studied at sublethal concentrations.  The AMIC-739
           lowest concentration of  metal  resulting
           In significant impairment was!  arsenic,
           O.int  lead, 0.071 mercury, 0.0031  and
           selenium, 0.2*5.  Deleterious effects
           occurred at metal concentrations
           approximately similar to potable water
           standards.

                   Ephemerella (mayfly) was the most HarnleK,  et
           sensitive aguatic Insect of those
           studied, and copper the most broadly
           toxic metal.  The authors suggest that
           aquatic Insects may not be as sensitive
           to heavy metals as fish.

a*,c,d,e,f        sane as above
a»,c,d,e,t
                  same as above
                                                                                                                           al(1969>,
                                                                                                                           •MIC-3767
                                                                                                      Varnlck, et
                                                                                                      al(1969),
                                                                                                      AHIC-3767

                                                                                                      HarnicK, et
                                                                                                      al 11969),
                                                                                                      ANIC-3767
                     Coregonus     FL    Moose Lake,  0.5  (residue)
                     cluoeaformis        Can.
                   Concentrations of 13 toxic
           elements in dressed fish from heavily
           industrialized and non-industrialized
           areas were determined.  Only mercury
           exceeded regulatory Halts, and
           concentrations of most elements Mere
           essentially the same in fish from both
                                                                                                      Uthe, et
                                                                                                      (1971),
                                                                                                      AHIC-3819
                                                                                                                                    al
-------
                                                                                  artas.
Lead
Lead
                     Coregonus     FL
                     clupeaformls
                     Esox  luclus   FL
Lake
Ontario*
Can.

Moose Lake,
Can.
                                                       0.9  (rasI due I
                                                       0.5  (residue)
                                               same as above
                                                                                         sane  as  above
                                                                     Uthe. et al
                                                                     (1971),
                                                                                                                            Uthe,  et  al
Lead
                     Esox  luclus   FL
                                          Lake  St.
                                          Pierre, Can.
                                                       0.5  (residue!
                                                                                         sine  as  above
                                                                                                                           Uthe.  et
Lead
Lead
Lead
Lead
                     Esox luclus   FL
                     Osnerus
                     •ordax
                     Perca
                     flavescens
                     Paralabrax
                     clathratus
                                   FL
                                   FL
                                   FH
                                         Lake  Erie,
                                         Can.
Lake Erie,
Can.
Lake Erie,
Can.
Seattergood
Steam Plant,
Los Angelas,
Cal.
                                                        .9  (reslduel
                                                       0.5  (residue)
                                                       0.5  (residue)
2.1 dorsal
muscle
residue)
Lead
Lead
                     Paralabrax
                     clathratus
                     Paralabrax
                     clathratus
                                   FM
                                   FH
CatalIna     1.3 (dorsal
Island, Cal. muscle
             residue)

Scattergood  1.1 (ventral
Steam Plant, muscle
Los Angeles, residue)
Cal.
                                                                                         sane  as  above
                                                                                         sane  as above
                                                                                        sane  as above
                                                                                        same as above
        Fish collected front en effluent
ploe of a steam plant and from offshore
Maters of Catallna Island were analyzed
for trace element content.  Trace element
content of the effluent xater Mas at
least 5 times greater than that of normal
sea water for cadmium, coooer, nickel,
Zinc, and chromium.  Livers of fish trow
the effluent Mere nearly twice the size
of those from the ocean.  Greatest
differences In concentration occurred
Hlth aluminum, cadmium, and nickel.
Sliver, barium, lithium, and lead showed
the least differences.  The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on marine organisms.

       sane as above
Uthe, et al
(1971), »MIC-
3819

Uthe, et al
«1971),A1IC-
3819

Uthe, et al
(1971) ,»MIC-
7S19

Staoleton
(1968),
«MIC-S9M>
                                                                     Staol eton
                                                                     (196S),
                                                                     S tao I eton
                                                                     (196S),
                                                                     AMIC-S980
-------
Conoound
Lead
Ltad
Lead
Lead
Lead
Lead
Lead
Lead
Lead
Lead
Orqanlsn
Paratahrax
cl athratus
Paralabrax
cl athratus
Paral abrax
cl athratus
Paral ibrax
cl athratus
(qravl
-------
         Lead
         Llndane (aa»»
         Llndane
UI
         Llndane
                              Paralabrax
                              clathratus
      Paralabrax
      el*thr*tus
HHCI  Fish (not
      specified)
                              Lepoals
                              cyan*Ilus
                              (Resistant)
              FH    Scattergood  2.2  (eyeball
                    Stea* Plant, residue)
                    Los Anqeles,
                    Cal.

              FH    Catallna     3.<>  (eyeball
                    Island* Cal. residue)
                                                               greater than
                                                               0.01-1.0  (K)
                                                               1.93 (TZ>
                              Leoowls
                              cy ane11us
                              (Susceptible)
                                            BS»   —
                                                               0.05 (T2)
                                                                         save as above
                                                                                                 saae as above
                                                                    Approximate toxleltles of
                                                            nuwerous pesticides commonly used  In
                                                            Britain H*re suntrnarized. An excellent
                                                            brlelt qenvral discussion of toxlclty
                                                            testing is also present.
                                                                                                            Stapleton
                                                                                                            (196B).
                                                                                                            4MIC-5990
                                                                                                                                    Stapl»ton
Haxdesley-Th
  omas 11971
AMIC-1056
                                                                          Green sunfish from Belzonl, Hiss. Hinchex, et
                                                                  nere resistant to Chlor^ane, Heptachlor,  al(1970)>
                                                                  Llndane, and Strobane, but not to
                                                                  Parathi on.  Golden shiners froi the same
                                                                  location Here resistant to Llndane and
                                                                  Strobane, tolerant to Chtordane and
                                                                  HeotacMor, and susceptible to Parathlon.
                                                                   Lack of resistance to Parathlon
                                                                  Indicated lack of agricultural usaoe of
                                                                  orqanochosphates In that area.  Resistant
                                                                  fish were compared to susceptible ones
                                                                  collected at Starkvllle.
                                                                                                 sane as above
                                                                                                                                    Mlnche», et
         Llndane
         Llndene
Notenlgonus
erysoleucas
(Resistant)

Notealgonus
crysoleucas
(Susceptible)
                                            BSA   ~
                                            BS«   —
                                                               3.K, (TZ)
                                                               0.19 (TZ)
                                                                                                 sane as above
                                                                                                 sane as above
                                                                                                            Hlnchew, et
                                                                                                            alJ1979),
                                                                                                            AMIC-51.71

                                                                                                            Ninclex, et
                                                                                                            al(1970),
                                                                                                            A1IC-5fc71
        'Llndane
      Ictaturus
      punctatus
                                            BS»   •—
                                                                     (TO      at                 Orqanochlorlne Insecticides Here  Haeek, tt
                                                                               synthetic  the most toxic compoundst                 al (1
-------
Compound

Llndane
Llndane
r
(O Llndane
L 1 n4an»
L 1 ndane
Llndane
Llndane
Llndane
Li Man*
llndtne
Field Field
Orqanlsa Study Location

Ictalurus BSA —
ire las
Carassius BSA ~
auratu^
Cyorinus USA —
carplo
PMephales ASA
prone las
Leponis BSA
•acrochlrus
Leoonis BSA —
•icrolophus
NIcrooterus 6SA —
salaoldes
Salno BSA —
9alrdnerl
Salao trutta BSA
Oncorhynenus BSA —
klsutch
• Toxiclty,
Active
Inqredlent,
PPM

0.064 (T
0.131 (T
0.090 (Tit)
O.OH7 ITI.)
0.06(1 (Tit)
0.083 (Tl.)
0.032 (Tit)
0.0?7 ITIt)
0.002 (TV)
0.01.1 (Tit)
Experimental
Variables,
Controlled
or Noted Conments

a,
synthetic
test nater
a,
synthet Ic
test Mater
a.
synthetic
test water
a,
synthetic
test Mater
a,
synthetic
test Hater
a,
synthetic
test Mater
a,
synthetic
test Hater
a,
synthetic
test Hater
a(
synthetic
test Hater
synthetic
test Hater
centrarchlds Hould IlKely be safe for
cyorinlds and Ictalurlds. Sate levels
for Ictalurlds or cyorinlds would
and satnonlds. The use of goldfish In
bioassays Mas discouraqed.
sane as above
sane as above
same as above
saoe •« above
sane as above
sane as above
sa«e as above
sane as above
sane as above
saae as above
Reference

MacrK, etal
AMIC-5510
MaccK, etal
(1970) ,
Macefct et
»l (1970).
MaceK, etal
(1970,
AHIC-5510
Mac«k, etal
(1970) ,
HaceK, etal
(1970),
HaceK.et al
(1070) ,
• M.IOS510
Hacek, etal
(1970) ,
AMIC-5513
Macek, et
al (197C),
ANIC-S510
(1970) ,
•HIC-5510
-------
         llndane
vn
         Llndane
         Llndane
         Llndanc
                              Perea
                              ftaveseens
Pataewonetes   3S»
kadlaken>>
                                                                0.01I.-D.0373
                                                                (TH
at                same as above                      "acek.  et»l
synthetic                                            (19701,
test water                                           Aiic-5510

a*                 Rioassays were conducted with     Naqvi,  et al
           shrimp from three areas of  intensive      (1970),
           pesticide use and from an unexoosed area. AHIC-5519
            Previously exposed shrimp  Here from i to
           2^ tlires wore resistant than unexoosed
           shrimp.  Both types of shrimp were also
           exposed in cages to Haters  of the
           contaminated areas.  Susceptible shrimp
           suffered 66 percent more mortality than
           did resistant shrimp.  The  toxlclty of
           the insecticides ranked in  descending
           ord-r Has as follows:  most toxic,
           Endrin, COT, Methyl parathlon, Parafhiont
           medium toxlclty, Guthlon,  Llndane,
           Toxanhene, Strobanoj lease  toxic
           Chlordane, Sevln, and Heotachlor.
Pa Iaemone tes
k»<11alnsl«
(non-
resistant)

Moron*
saxatllls
(finger IInqs)
                                            BS»   —
                                            BS»
                                                               O.OOS1  (Tl)
                                                               0.
-------
,._
Llndane












Llndane


Llndane

Organism
Coo»oi'1s
(Cycl oos
bieusoldus.
Cyetoos
var leans.
Cycl oos
vernal is.
Eucycloos
aql 1 is.
Macro cyclops
al bidus,
Orthocycloos
modestus)
Tubif ex
tublfex

Mercenaria
mercenarla
(eqqs)
Field Field
Study Location
FL flelzonl.
and Miss
BSA










FL Relzonl,
and Miss.
BSA
L --

Toxlclty,
Active
Ingredient,
Ppm
0.60 (87
percent KZJ











<..« (NTE)


greater than
10.0 (TZt
Experimental
Variables,
Control led
or Noted Comments Reference
-- • same as above Naovi, et al
( 1°69) ,
AMIC-5979










same as above Naavi, et
al (19f>9) ,
ANIO59T9
~ The effect of *2 nestlcides on Davis, et
embryonic develooment of clams and al(l°69).
                                                                                 effects xlth solvents xere also reported.
                                                                                  Host cf the co^Dounds affected
                                                                                 develocwent more  than survival.  Some,
                                                                                 however, drastically reduced  larval
                                                                                 grOHth.  The authors oolnt out the
                                                                                 necessity of evaluating the effects of
                                                                                 pesticides on all  life staqes of an
                                                                                 orqanism and note  the oossiblllty of
                                                                                 selecting chemicals for pest control  that
                                                                                 would not have serious effect on
                                                                                 shell fish.
Llndan*
LIndane
Llndane
Mercenarla
oercenaria
(larvae)

Crassosfrea
vlrqinlca
(eqqs)
                     Gamhusla
                     affinis
                     {female, 4.3

                                   BSA
                                                       greater  than
                                                       10.0  (T12)
                                                      9.1  (TZ)
                                                      0.13 (T<»)
                                                                                                                           Oavls,  et
                                                                                        same  as above
—                sane as above                      Davis, et al

                                                     <19S9).A1IC-
                                                     5990

a,c,d,             The five fish species are         Nunoqana, et
8,f,l,     commonly found In streams and estuaries   at (1970),
(Honolulu  in semi- trooical  areas.   G.  afflnls Has   AMIC-6567
-------
f
         Llndane
         Lind&ne
        Lindajie
        Lindana
        Linear  alxytate
        sulfonate
        Linear  alkylate
        sulfonat*
                              C«l,  1.9 ql
                              Lehlstes
                              retIculatus
                              (male, 1.8
                              cm, 0.2 ql
Tllapla
nos salable*
(3.^ cm,
1.3 0)

Kuhlia        BSA
aandvlcensla
(U.3 em.
1.5 a)

otolephorus   BSA
purpurea (3*6
en, O.It- G)
                                            8SA
                                            BSA
                                                               0.05 (T<0
                                                              0.06
0.00^
(T 12 hr)
Pimeohales
crone I a?
                                            BCFA
                                            BCFCH —
                                                               0.63 (NTE)
                              prooel »s
                                                  tap        the most tolerant.   Varied sensitivity to
                                                  water)      the toxicants were  found.   K.
                                                             sandvicensis was the most  sensitive fish
                                                             studied.  The standard nethod procedure
                                                             Has foiloHed*

                                                                    same as above
                 *,c,d.
                 »,t,i,
                 (Honolulu
                 tap
                 water)

                 ft,c,d,e,f,l
                 (Honolulu
                 tap water)

                 a,c,d,e,f,l,
                 salt water
                                                                               a,c,d,e;f,i,
                                                                               salt water
                                                                                                       al  (197C),
                                                                                                sane as above
                                                                                                same as above
                                                                                                same as above
                                                                               I.I .n,
                                                                               calc lum,
                                                                               maqnes lum«
                                                                               sol lum,
                                                  sul fate,
                                                  beryl I lum,
                                                  strontium,
                                                  Iron,
                                                  boron,
                                                  barium,
                                                  a lum 1 num,
                                                  zinc,
                                                  CODDPr,
                                                  cadm 1 um

                                                  a»,c,d,f ',
                                                  1.) in,
                                                  calcium,
                                                  maqnesiun,
                                                  sodium,
                                                  cotasslun,
                                                  sul fate,
                                                  beryl I lun,
                                                  strontlu»»
                                                  Iron,
                                                  boron,
                                                  barium,
                                                  aluminum,
                                                  zinc,
                                    tcute and chronic  toxlclty
                            studies resulted in  a  laboratory fish
                            production Index for fathead minnow.
                            Lethality of  LAS to  nenly  hatched  fry  was
                            the most critical  factor  Hlth no effect
                            at  0.* pom on soawnlno eqq oronuctlon,  or
                            hatchabillty  at  this concentration.   A
                            funqus infection of  mature wales occurred
                            and was controlled by  means of
                            antibiotics.   No accumulative mortality
                            occurred.  The application factor  was
                            calculated to be between  14 and  25
                            percent.  The concentration of 0.63 pom
                            was determined to be the  maxinum
                            acceptable concentration  of LAS  for
                            fatheads.

                                   sane as above
Kunopawa, et
al (1970),
AKIC-6567

Jiunogava, et
al (197C),
AKIC-65o7

Nunogawa, et
al (1970),
AKIC-6567
Plckerinq,
et al (1
-------


Comoound


Llnuron




Llrostanol











LIssaool IPA






Lltsaool 1"






Toxlcity, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organise Study Location Ppm or Noted Comments
copper.
cadmium
Fish Inet -- — greater than — Approximate toxlclties of
spec if led) 10-100  numerous Pesticides commonly used In
Britain Here summarized. An excellent
brief, general discussion of toxlcity
testing is *tso present.
Rasbera BCFA — 0.04t ITZ1 a»,c,e,f, One hundred sixty-four
heteromorpha and hard (HH) pesticides, wettlno anont^. anri
BSA or miscellaneous Hater ootlutants showed e
SOFTI1W) Hide range of toxlcity spanning 12 orders
synthetic of magnitude. Knowing the toxlcity and
dilution percentage of all components of a
Hater, or formulation did not result in easy
seawater predictability of the toxlcity of a
species pesticides Here most toxic in hard Hater
and sometimes the opposite Has true.
Testing the actual material as sold Has
tound to be essential.
Crangon BSA — 1080-3300 IT2) a«(ecatln- same as above
crangon uous aer-
ation, sea-
water, and
daily
solution
renewal)
Crangon BSA — 330-1000 CT2I a»(contin- *••• »s «bove
crangon uous aer—
•tion, sea-
vcter, and
daily
solution
renewal)


Reference


MaHdesley-
Tho»as<1171)
AMIC-1056


Alabaster
(146QI ,
AM.IC-542S









Portaann, et
al (1971).
AMIC-7701




Portmann, et
al 11971),
AHIC-77J1




Llssaool NX
Rasbora       BCFA
heteromorpha  and
              B3»
                                                      3.S ITZt
a*,c,e,t.          One hundred sixty-four            Alabaster
hard {HH>  pesticides, wetting agents, and           119691,
or         miscellaneous Hater pollutants shoHed a   AMIC-912S
SOFTfSM)   Hide range of toxlcity spanning 1? order*
synthetic  ef magnitude..  Knonlng the toxlcity and
-------
Ll**a0ol  NX
                      Crangon
                      eranqon
                                   BSA    —
                                                       1010-3300  IT?)
Lithium
                     Paratabrax
                     el athratus
                                   FH
Seatterqood  6.9 {dorsal
Steaa Plantt muscle
Los Angeles.
Cal.
Llthiue
                     Paratabrax
                     ctathratus
                                   FH
Catallna     6.2 (dorsal
Island, Cal. muscle
             residual
                                   dilution   oereentage  of all components of a
                                   Mater, or  formulation did not result  In easy
                                   seaNater   Dredictabllity of the  toxiclty of a
                                   for some   alxture of  materials.  Sometimes
                                   soecles    pesticides  Mere most toxic  In hard Mater
                                              and soiretlmes the ooooslte  MBS true.
                                              Testing the actual material as sold Mas
                                              found to be essential.

                                   a»(contln-         One hundred-forty surface active
                                   UOU9 aer-  aqents, solvent emuls1fiers, pesticides,
                                   ation, aea-Oolychlorlnated blphenyls,  oure
                                   water, and Inorqanic,  and organic chemicals were
                                   daily      evaluated against as many as ten marine
                                   solution   orianlsms.  The authors noted that nost
                                   renewal}   published data of this type deal with
                                              toxiclty of chemicals to freshwater
                                              organisms.

                                   —                 Fish collected from an effluent
                                              Dloc of a steam plant and fro« offshore
                                              waters of Catallna Island Mere analyzed
                                              for trace element content.  Trace element
                                              content of  th* effluent Mater Mas at
                                              least 5 tines greater than  that of normal
                                              sea Mater for cadmium, coooer,  nlcKel,
                                              7lnc, and chromium.  Livers of  fish from
                                              the effluent were nearly tMlce the size
                                              of those from the ocean.  Greatest
                                              differences In concentration occurred
                                              ulth alurlnum, cadmium, and nickel.
                                              Silver, barium, lithium, and lead shoMed
                                              the leist differences.  The author
                                              concluded that trace element analysis of
                                              tissues could be used to determine the
                                              effect of pollutants on earine organises.

                                                     sane as above
                                                                                  Portn.ann, et
                                                                                  al  (l^Tll,
                                                                                  AMIC-7701
Staoleton
(1968), &MIC-
5980
                                                                                                                           Staoleton
                                                                                                                           *NIC-59»0
Llthlua
Llthlun
lltMua
                     Paralabrax
                     elathratus
                     Paralabrax
                     cIathratus
                     Paral abrax
                     cIathratus
FH    Scatterqood  6.7 (ventral
      Steaa Plant, muscle
      Los Angeles, residual
      Cal.
                                   FN
Catallna
Island, Cal,
Scatterqood
SteM Plant,
                   5.6 (ventral
                   •use Ie
                   RESIDUE!

                   0.6 (qonads
                   residual
                                                                                        saae as above
                                                                                        saee as above
                                                                                        save as above
                                                                                  Staoleton
                                                                                  119(8),
                                                                                  41IC-S9SO
Staoleton
(1«6B>,
AHIC-«i980

Staoleton
(1968),
-------
Comountf

Llthlu*
Lithium
LithluB
Llthlu*
LIthlua
Llthlu-
UthlUB
Llthlu*
Llthlua
Lithlua
Orqanls*

Paratabrax
clathratus
Paralabrax
el athratus
(qravld
females)
Parat abr^x
cl athratus
Paral abraic
el athratus
Paral abrax
clathratus
Paralabrax
el athratus
Paralabrax
ct athratus
Paralabrax
el athratus
Paralabrax
el athratus
Paralabrax
clathratus
Field
Study

FN
FN
FN
FN
FN
FN
FN
FN
FN
FH
Fl*ld
Location
Los Ang«l«s<
Cat.
Carat Ina
Tstandt Cat.
Catal ina
Island, Cal.
Scatterqood
Ste»» Plant,
Los Anqeles,
Cal.
Catal Ina
Island, Cal.
Scatterqood
Strain Plant,
Los Angeles,
Cat.
Catat Ina
Island, Cal.
Scatterqood
Stean Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Scattergood
St«aa Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Toxicity, Cxeerlaentat
Active Variables,
Ingredient, Controlled
PPH or Noted

8.* (gonads --
residue)
7.7
(gonads
residue)
5.8 (liver
residue)
7.J (liver
residue)
6.8 (Intequnent --
residue)
7.7 (Integuaent ~
resldue)
7.6 (heart
residue)
8.5 (heart
residue)
580 (eyeball
residue)
l?fc (eyeball —
residue)
Comments

sane as above
sane as above
same as above
saae as above
sa«e as above
sane as above
saae as above
sane as above
sa*e as above
sa»e as above
Reference
AMIC-Sq&O
Staoleton
(19M) ,
A1IC-*q
-------
                                                                                                                            AKIC-5980
Lubrol  APNS
                      Car dl urn edule BSA   —
Lubrot »PNS
                      Cr*nqon
                      crangon
                                    BSA    —
10-33  IT2)      a«lcontin-         One hundred-forty surface active
                UOU5 acr-  aqents, solvent emulslflers, pesticides,
                ation, sea-polychlorlnated biohenyls. Pure
                water, and Inorganic, and organic cherlcals were
                daily      evaluated aqalnst as many as ten marine
                solution   orqanlsms.  The authors noted that most
                renewal)   published data of this type deal with
                           toxlclty of chemicals to freshwater
                           organisms.

33-100 (T2>     *«(eontln-        same as above
                uous aor-
                ation, sea-
                wator, and
                dally
                solution
                renewal)
                                                                                                                            Portmann,  et
                                                                                                                            al  J1971),
                                                                                                                            AHIC-7701
                                                                                                      Portmann, et
                                                                                                      al  (1971),
                                                                                                      AHIC-7701
Lubrel L
                     Ravbora
                     heteroeoroha
              OCFA
              and
              BSA
16 CT2,
hardwater)
Lubrel L
                     Pasbora
                     heteromorpha
              BCFA
              and
              BSA
1Z.5 tlZ,
softwater)
Naqle Power
Plmeohales
orone I a*
                                   BSA
                                                      H..O (T<»>
                                                                       hard  (HM)
                                                                       or soft
                                                                       (SH>
                                                                       synthetic
                                                                       dilution
                                                                       Mater, or
                                                                       seaitater
                                                                       for some
                                                                       species
s*,c,e,f,
hard (HHI
or soft
(SH)
synthetic
dilution
water, or
seawater
for some
species

c,d,e,f
        One hundred sixty-four
pesticides, wettlno aqents, and
miscellaneous water pollutants showed a
wide rarqe of toxlclty spanning 12 orders
of magnitude.  Knowing the toxlcity and
percentaqe of all components of a
formulation did not result in easy
predictability of the toxicity of a
mixture of materials.  Sometimes
pesticides were most toxic in hard water
and sometimes the ooposlte was true.
Testinq the actual material as sold was
found to be essential.

       same as above
                                                     Alabaster
                                                     «1969),
                                                     AHIC-6U2?
                                   Toxlclty of six oil spill
                           dlsoersants was determined alonq with
                           800 values.  Pond water was used as
                           diluent and oil was Included in the
                           experiment.  Oil markedly reduced
                           toxlclty of all dlsoersants.  Data are
                                          Alabaster
                                          (1969),
                                          AMIC-54Z5
                                          Zilllch
                                          (1969),AMIC
                                          ?909
-------
  Compound
            Field  Field
Oroanlsm    Study Location
                                                      Toxlclty,
                                                      Active
                                                      Ingredient,
                                                        Pom
                                                                      Experimental
                                                                      Variables,
                                                                      Control led
                                                                      or Noted
                                                                                                 Comments
                                                                                                                           Reference
Magic Power
      Poner
Hegneslum
Magnesium
Magnesium
Hagnesluf
                     Plmeohnles
                     prone las
                                   BSA   —           2.7 (MSC)
                     Biochemical   L
                     oxygen deeand
                     Paral abrax
                     clathratus
                     ParaIabrax
                     clathpafus
                     P»ra1abrax
                     clathratus
                     Paralabrax
                     el atnratus
                     ParaIabrax
                     ctethratus
                                                       880,000
                                                          given as "«ost probable** 96-hr TL  sub

                                               c,d,e,f           sane as above



                                               e,d,e,f           same as above
            FM    Scatterqood  1670 (dorsal
                  Steam Plant, muscle
                  Los Angeles, residue)
                  Cal.
            FH    Catallna     ?190(dorsal
                  Island, Cal. muscle
                               residue)

            FH    Scattergood  1BZO (ventral
                  Steam Plant, muscle
                  Los Angeles, residue!
                  Cal.

            FH    Catallna     ?190(ventral
                  Island, Cal. muscle
                               residue!

            FH    Scattergood  1010 (gonads
                  Steam Plant, residue)
                  Los Angeles,
                  Cal.
        Fish collected from an effluent
pipe of a steam plant and from offshore
Haters of Catallna Island Here analyzed
for trace element content.  Trace element
Content of the effluent Hater was at
least 5 times en-eater than that of normal
sea Hater for cadmium, cooper, nickel,
zinc, and chromium.  Livers of fish from
the effluent Here nearly twice the size
of those from the ocean.  Greatest
differences In concentration occurred
Hlth aluminum, cadmium, and nlcKel.
Silver, barium, lithium, and lead showed
the least differences.  The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on marine organises.

       sane as above
711 IIch
(19
-------
•Ugneslun



Hagneslun




Hagneslu*




Nagneslua
Paralabrax
Clathrafus
Paralabrax
clatnratus
(gravid
feiales)

Paralabmx
elathratus
                                   FH
              FH
              FH
Paralabrax    FH
elathratus
                    Catal Ina     ?<.?(! (gonads
                    Island, Cal. residua)
                     Catal Ina      l«tZO
                     Island, Cal.  taonads
                                  P«sldU«»
                     Seiittergood  690  (liver
                     Stea* Plant, residue)
                     Los Angeles,
                     Cal.

                     Catal Ina     10*0 ( liver
                     Island, Cal. residue)
                                                                                         sane as above
                                                                    saae  as  above
                                                                    same  as  above
                                                                    sane  as above
                                                                     Staoleton
                                                                     (1968).
                                                                     AMIC-5980
                                                                                                       AMIC-S98C


                                                                                                       Staoleton
                                                                     Slacleton
                                                                     6S).
Naqnesiu"
Haqneslu*
Hagneslu*
Paralabrax    FH     Scattergood  730  (Intequaent
elathratus           St»a» Plant, residue)
                     Los Angeles,
                     Cal.

Pamlabrax    FH     Catal Inn     840  (Integunent
clathratus           Inland, Cal. residue)
Par at abrax    FH    Scattergood  1Z80  (heart
elathratus          Steam Plant, residue)
                    Los Angeles,
                    Cal.

Paralabrax    FH    Catal Ina     9<>0 (heart
elathratus          Island, Cal. residue)
                                                                                         sane as above
                                                                                         sane as above
                                                                                         save as above
                                                                                         same  as  above
                                                                                                      S t a o I e t o>\

                                                                                                      aiIC-5980


                                                                                                      Staoleton
                                                                                                      Staoleton
                                                                                                       I19SM ,
                                                                                                      Stsoleton
                                                                                                      (t9SS) ,
Naqneslua
Hagneslua
Halachlte qreen
Par at abrax
elathratus
Paralabrax
elathratus
                                   FH
                                   FH
Rasbora       BCFA
heteronorpha  and
              BSt
                    Scattergood  10SO (eyeball
                    Stea» Plant, residue)
                    Los Angeles,
                    Cat.

                    Catal Ina     1<»70 (eyebal I
                    Island, Cal. residue!
O.fcfe (Tl,
nardNater)
                                                                                         saae  as  above
                                                                                         same  as  above
                                                 a*,c,e,t.          One hundred sixtv-'our
                                                 hard  I!*H)  pesticides, netting agents,  and
                                                 or soft    Miscellaneous water oollutants showed a
                                                 (SW)       wide range of toxlclty scanning 12 orders
                                                 synthetic  of  magnitude.  Knowing the toxlclty and
                                                 dilution   percentage of all comoonents of a
                                                 Hater,     f emulation did not result In easy
                                                                     Staoleton
                                                                     (196*),
                                                                     •MIC-59S9
Staoleton

AHIC-5980

Alabaster(19
69).
-------
  CoMoound
                       nrqanisa
                                   Field  Field
                                   Study Location
                   Toxlcitvt
                   Active
                   Ingredient,
                     PPM
                ExperI mental
                Variables,
                Control led
                or  Noted
                                                                                                 Comments
                                                                                                                           Reference
Malachite areen
Pasbora       BCFA
heteromorpha  and
              BSA
                   0.0« (Tl,
                   sottnater)
Malachite areen
                     Sal no
                     qalrdnvrl
flCFA
anr,
                                                 hardlHW)
                                                 or soft
                                                 (SHI
                                                 synthetic
                                                 dilution
                                                 Hater,
                                                 or seawater
                                                 for some
                                                 species
                                                                                        same as above
                                                                                                                            alabaster
                                                                                                                            (1959).A*IC-
                                                                                                                            51,25
                                                                                        sa«e as above
                                                                                                       Alabaster
                                                                                                       
                synthetic
                dilution
                                                                                         same as above
                                                                                                       Alabaster
                                                                                                       (1969),AHIC-
                                                                                                       5*25
-------
         Malachite green
fU
         Malathion
         Malathion
         Halafhlon
                              Morone
                              saxatllls
                              
-------
Coeoound

Halatnion






Malathlon






Halathlon






Halatrtlon






Malathlon






Field Field
Orqnnls* Study Location

Salvellnus BCF* —
f ontlnal Is
(2.13 g)




Sal«o elarKl BCF* ~
(0.33 q>





Sal»o elarkl BCF* —
(1.25 q)





Sal»o BCF* —
qairdnerl
(0.1.1 q)




Oncorhynchus BCF* —
Kisutch (1.70
q)




Toxlclty, Fxoerimental
Active Variables,
Ingredient, Controlled
Pom or Noted Convents
toxlclty.
120.0 (T<>> a«,c,d, sane as above
e.r.l.o,
aulfat*.
copper.
annconase.
iron, and
chromium
0.15 (Ti>) a»,c,d, same as above
•,f,i,o.
auirate,
copper,
manganaia,
iron, and
chromium
0.20 (TO a«,c,d, saae as above
e,r,l,o,
aulfate,
copper.
manganese.
iron, and
chromium
0.12 (TO a»,o,d, sane as above
e,f,i,o,
auirate,
coppor.
manganese.
iron, and
chromium
0.269 (Tit) a«,e,d, sane as above
e,r,i,o,
aulfat*.
copper.
nangoneaa.
iron, and
chromium
Reference

Post, et
4LI1971),
4MIC-181?




Post, et
(1971),
4HIC-1S1?




Post, et
(19711,
*MIC-1»12




Post, «t
(197H,
•MIC-1812




Post, et
<1971! ,
»MIC-1812













al






al






al






al






Malathlon
                     Cyorlnus      L
                     carplo
                                                      0.010 (SB)
        This study «as conducted to
determine whether comoonents ot tissues
fron various fish would Interfere xlth
CLC determinations for Malathlon.   Good
                                                                                                                           *NIC-37?8
-------
 He lathIon
RalatMon
Halathlon
                      Catostomuv
                      cOMcrsonl
                      P*rca
                      Esox  nlq«r


                                    L      —
                                                       0.010 (SB)
                                                       0.010 (SB)
                                                       0.010 (SB)
                                                                                  recovery (80-96 percent) Mas obtained
                                                                                  Mlth best recovery from shin. flesh, and
                                                                                  gills.  Recovery Has less successful In
                                                                                  liver, brain, and blood.  The author
                                                                                  recommends the GLC orocedure as simoler
                                                                                  than the us* of activated charcoal.

                                                                                         San* as above
                                                                                         same as above
                                                                                         sa«e as above
                                                                                                       ffaoab
                                                                                                       (19SS)t
                                                                                                       •HIC-3728

                                                                                                       Raoab
                                                                                                       (1"6!» ,
                                                                                                       • "IC-372IJ

                                                                                                       Raaab
                                                                                                       (I960),
Helatnlon
Halath| on
                      Note*lionus   L
                      crysoleucas
                      Piaephalas
                      promelas
                                                       0.010 (SB)
                                                       16.0 CTI.)
                                                                                         sane as above
                                                                                                      Raasb
                                                                                                      (1968)
a.»,d,e,o,          Halathlon and Its hydrolysis
and Pa     products were evaluated with the finding
           that one such oroduct (dlethyl  tumarate)
           Has more toxic than Halathlon to fathead
           minnows.  Syrterqls** occurred between
           Halathlon and two products of hydrolysis.
            Continuous exposure resulted in
           Increased toxiclty.
Ha lath ion
Ha lathIon
                     Pimephales
                     prone I as
                                   BCF»   —
                     Punt Ius  tieto —     —
                                                       11.0  (Tl
                                                 a*,d,e,o,
                                                 and Ft
                                                                       a.c,d,e,f
                                                                                         sane as above
                                                                                                      Bender
                                                                                                      (1969>>*HIC-
                                                                                                      3787
                                                     Bender
                                                     (1919.)
                                                     3787
                                                                    Of the pesticides investigated,
                                                            the most toxic was Klofos fol loved in
                                                            decreaslnq order by SUB it hi on, Halathlon,
                                                            Formlthlon, Oimecron, Sevln,  and PMC. The
                                                            »uthor cites the need for more selective
                                                            pesticides nontoxic to  fish or
                                                            antaqonistic agents for reducing fish
                                                            toxiclty.
                                                                                                                            Bhatla
                                                                                                                            (1971) , A>1IC-
Ha lath Ion
Rasbora       BCFA
heteroaorpha  and
              BS»
                                                       8 (T2>
l.«,C,a,f,          One hundred sixty-four
hard (Htf)  pesticides, nettlna agents, and
or soft    miscellaneous water ooltutants showed a
tSW) syn-  Hide range of toxiclty scanning 12 orders
thetic     of magnitude.  Knowlnq the toxtclty and
dilution   percentage of all components of a
water, or  formulation did not result In easy
                                                     Alabaster
                                                     (1969),
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Orqanlsm Study Location Pom

Experimental
Variables,
Control led
or Noted
seawater
species
prertlctabll 1 ty
pesticides
were
Comments
of the
most
toxlcity
toxic
In
ot a
es
hard water
Reference

         Ha lath Ion
Ictalurus
punctatus
                                            BSA
                                                                6.97 (T<>)
ro
          Matathlon
         Halathlon
         Malathion
Ictalurus
vet as
                               Carasslus
                               auratus
                               Cyorlnus
                               carpio
                                             BSA
                                             8SA
                                             BSA
                                                                1Z.90 (T4)
                                                                10.70 CU)
                                                                6.59 CT<»)
           and sometimes the opposite Has true*
           Testing the actual material as sold was
           found to be essential*

a,                 Orqanochlorlne Insecticides were  MaceK,et al
synthetic  th« most toxic compounds,                 (1970),
test water orqanochosrhates  Intermediatet carbamates 4MIC-5510
           the least toxic.  Brown  trout Has  the
           species most susceptible to
           orqanochlorInes,  echo salmon the most
           susceptible to carbamates* and qoMfish
           Mere the least susceotlbte of all
           species.  Safe concentrations established
           by bloassays ulth salmonids or
           centrarchlds would  lih<-ly be safe  for
           cyorinlds and  Ictalurids.  Safe  levels
           for Ictalurids or cyorlnlds Hould
           probably be hazardous for centrarchids
           and salmonids.  The use  of goldfish In
           bloassays was discouraged.
                                                                                a,
                                                                                synthetic
                                                                                testnater
                                                 synthetic
                                                 test  water

                                                 a,
                                                 synthetic
                                                 test  water
                                                                                                  same as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                      HaceH,  et
                                                      81 C197PI,
                                                      4MIC-5510

                                                      NaceK.et al
                                                      Mace*,  et
                                                      al (197C),
                                                      tMIC-5510
         Halathlon
                               Pl«ieohales    BSft
                               promelas
                                                                8.65 (T<>)
                                                 a,
                                                 synthetic
                                                 test  water
                                                                                                  same as above
                                                      "acen.et  al
                                                      <19T0) .
          Malathlon
          M»lath Ion
                               Leoomls
                               macrochlrus
                                             BSA   —
Leoomls       BSA
•icroloohus
                                                                0.103 (Ti.)
                                                                0.170
                                                                                synthetic
                                                                                test water
                                                                                a,
                                                                                synthetic
                                                                                                  same as above
                                                                                                  same as above
                                                      *aceK,et  al
                                                      (iq70),
                                                      •HIC-SS10

                                                      HaceK.et  al
                                                      (1970>,
-------
                                                                       test water
                                                                                                                            ANIC-5519
 Halathlon
 Hatathlon
 Halathlon
 Halathlon
Halathlon
Halathlon
Halathlon
Halathlon


Nalathlon
                      HlcroPterus   3SA
                      salnoldes
                      Salmo
                      galrdneri
                                    8SA   ~
                      Salmo trutta  BSA
                      Oncorhynchus  BSA
                      klsutch
                      Perca
                      IIaveseens
                                    BSA   —
                                                       O.ZB5 (Ti.)
                                                       0.170 IT4)
                                                       0.300 (Tit)
                                                       0.101 (Ti.)
                                                       0.263 (T«.)
                                                  at                 same as above                      MaceK.et si
                                                  synthetic                                             (1970),
                                                  test  water
                 a,
                 synthetic
                 test Hater

                 a,
                 synthetic
                 test Mater
                                                                       synthetic
                                                                       test water
                                                                                         sane as above
                                                                                         same as above
                                                                                         sane as above
                                                                                                       NsceH, etal
                                                                                                       (1973),
                                                                                                                            HaceK, et
                                                                                                                            al(197Q),
                                                                                                       Haeek.et
                                                                                                       (197T),
                                                                                                       AMIC-5510
                                                                                                                al
                      Morons
                      saxatlIIs
                      (f InqerlInqs)
                                    BSA
                     Cyprlnus
                     carplo

                                                       5  (S8«t)
                                                  a,                 same as above                      KaceH,  etal
                                                  synthetic                                             (1970),
                                                  test Hater                                            AMIC-SSIO

                                                  a,c,d,e,f.          All  ccmoourHs  were Invest iqated   Wellborn
                                                  p          because ot  their  orobsble  ussq*  In        (1971),
                                                            hatchery oroductlon  of Hhlte  Ba^s.        AHTC-S571
                                                            Conmounds that can be  used at recommended
                                                            concffn tra t I ons Here  Aquathol, Casaron,
                                                            Llndane,  and Terranycln concentrate.
                                                            Those  That  should not  be used Here
                                                            Acrlflavlne, Raylusclde, Malachite qreen
                                                            oxaltte,  and Malathlon.

                                                  ~                  Malathlon residues In carp        Bender (1969) »
                                                            occurred primarily in  the  liver  and flesh ANIC-5731
                                                            Hlth lesser  amounts  In the brain,  blood,
                                                            and qills.   Retention  tine Has relatively
                                                            brief Hlth  most of the residue passing  on
                                                            or belnq metabolized within 1-2  days.
                                                            Metabolism  In  the fish foreaut,
                                                            degradation  biochemically,  and lack of
                                                            uptake  due  to  ION permeability Here cited
                                                            as possible  explanations lor  the results
                                                            obtained.  Lack of persistence in  fish
                                                            couoled Hith slOH hydrolysis  In  the
                                                            environment  seem  to  Indicate  that  this
                                                            compound has desirable characteristics
                                                            regarding safety  to  humans.
Cyprlnus
carplo

Copeoods
                                   FL
                                          State
J.6-66.6
(residua)

0.025 (K3)
                                                                                         sane as above
                                                                                          The response of
Pender(l<»69),
AMIC-5731

Naavl, et al
-------
Compound














Halethlon












Hetathlon


Hatatnlon


Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Org»nls« Study Location Ppm or Noted Comments Reference
(Cyclops and College,
blcusoldus, 8SA Hiss.
Cvcloos
var leans.
Cyclons
vernal is.
Fucycloo*
aqllls,
Hacrocyclops
albldus.
Orthocyclops
modes tusl


Conenods FL Relzonl, 0.025 (13 —
(Cyclops and Miss percent KZ1
blcuspldus, RSI
Cycloos
var leans.
Cyelons
vernal Is,
Fucyeloos
aqilis.
Kacro cyolops
albldus.
Or t hoc vetoes
•odestusl
Tublfex FL Relzonl, 3.0 (NTE)
tunlfex and Hiss.
BSA
Crassostrea L — 9.07 CTZ) —
vlrqlnlea
IC99SI
oestlclde-reslstant aquatic orqanisus to (1969),
various pesticides Mas compared to the «MIC-S979
r»soonse ot non-resistant species.
Pesticide-resistant species were
collected at Pelzoni and non-resistant
species at State College. Copepods,
clnms* snails, and sluHae Morn« froi*
Belzoni Here considerably nore tolerant
to pesticides than the nan-resistant
organisms. The authors note that the
effect of Increased tolerance In the
organisms Is an Increase In the amount of
pesticide residues available to animals
of higher trophic levels.
same as above Naavl, et al
(1969),
•HIC-5979










same as above Nsavl, et
al (1969),
AMIC-59r
-------
M»lathi on
 Malathlon
                      Crsssostrea
                      vlrqlnlca
                      (larva*)
                      Cardlu* edule 8S»   —
                                                       2.66 ITU.)
                                                       3.J-10 «T2>
 Nalatnlon
                      Crangon
                      crangen
                                    BS»   —
                                                       0.33-1.0 (TZ)
                                                                                  shellfish.

                                                                                         same as above
                                                  a*(contln-          One hunrtred-forty surface active
                                                  uoua,  aer-  agents,  solvent vmulslflers.  pesticides.
                                                  atlon,  soa-polychlorinatea blphenyls. cure
                                                  water,  and  Inorqanlc,  and organic chemicals Mere
                                                  dally       evaluated against as many as  ten marine
                                                  solution   organisms.   The authors noted that most
                                                  renewal)    published data of this type deal Kith
                                                             toxicity of chemicals  To freshwater
                                                             organisms.

                                                  a»(contln-        same as above
                                                  uoua,  aer-
                                                  ation,  sea-
                                                  water,  and
                                                  dally
                                                  solution
                                                  renewal)
                                                                                                                            Davis, et al
                                                                                                                            Portmann, et
                                                                                                                            al U971),
                                                                                                                            AMIC-7701
                                                     Portmann,  et
                                                     al  (1971),
                                                     AMIC-7701
Kalathlon
Halelc >eM
Wolffia
papullfera
                     Plnephnles
                     prometas
                                   BS»
Manazon
Hancozeb
                     Fish  (not
                     specified)
                      Fish  (not
                     SD'Cifled)
                                                      100  (K)
                                                       5.0
                                 greater than
                                 100-1000  (K)
                                 greater than
                                 1.0-10.0 (K)
Hunter*a            All  compounds were hnrmful  to    Worthier,  et
medium     duckweed to some degree.  Cecressed       61  (1971),
diluted    populations were noted at non-lethal     AMIC-3233
1:5        concentrations  and  some compounds
           (Halathlon and  2,L|.-D) caused  teratogenlc
           effects at concentrations as  low as  1 ppn.

a*,d,e,o»           HalatMon ana It;  hydrolysis      Bender
and Fe     products were  evaluated iiith  the finding  (1969) .tire-
           that one such  product (diethyl fumarate)  3787
           was more toxic than Nalathion to fathead
           minnows.  Synerglsn occurred between
           Malathlon and  two oroducts of hydrolysis.
            Continuous exposure resulted in
           Increased toxlclty.
                   Approximate toxlcltles of
           numerous pesticides commonly used in
           Britain were summarized. *n excellent
           brief, general discussion of toxiclty
           testing is also present.

                  sane as above
Hawdesley-
Thomasm
A1IC-1056
                                                     Haw-lesley-
                                                     Tho*as(197l>
Naneb
                     Fish  (not
                     specified)
                                 greater than
                                 0.1-1.0 (K)
                   Approximate toxlcitles of         Mawdeslev-
           numerous Destlcldos commonly used In      Thomas
           Britain were summarized. An excellent     (1971) ,AMIO
           brlef.  general discussion of toxlclty     1056
           testing Is also present.
Haneb
                      Agonus
                                   BSA    —
                                                       0.33-1.0  (T?)
                                                                                          One  hundred-forty  surface active   Portaann,  et
-------
Toxiclty, Experimental
Active Variables,
Field Field Ingredient. Controlled
Compound Organism Study Location Ppm or Noted Comments
eataohractus (contln- aoents, solvent emulslflers, pesticides.
uous, aer- pol ychlerlnated biohenyls, pure
atlon, sea Inorganic, and organic chenlcals were
water, and evaluated against as many as ten marine
dally organisms. The authors noted that most
solution published data of this type deal with
renewal) toxiclty of chemicals to freshwater
organises.
•neb Asterlas BSA — 33-100 (TZ) *•( contln- same as above
rubens uoua, aer-
ation, sea
water, and
dally
solution
renewal)
aneb Cardlum edule BSA — 100-330 (TZ) a»(eontln- sane as above
uoua aer-
ation, sea-
water, and
dally
solution
renewal)
•»>«b Crangon BSA — 3.3-10  a«(contln- same as above
crangon uoua aer-
ation, sea-
water, and
daily
solution
renewal)
angaries* Coreqonus fl Hoose Lake, 0.7 (residua) — Concentrations of 13 toxic
cluoeaformls Can. elements In dressed fish fro« heavily
Industrialized and non-Industrial Ized
Deference
al 11971),
AMIC-7701






Portmanr, et
al (1971),
AHIC-7701




Portwann, et
al ll^T-u,
AMIC-7701




Portmann, et
al (1971),
AMIC-7701




Uthe, et
AL(1971),
A1IC-S819
                                                                                 areas Here determined.  Only mercury
                                                                                 exceeded regulatory Units, and
                                                                                 concentrations of most elements were
                                                                                 essentially the save in fish from both
                                                                                 areas.
Manganese
                     Coreqonus
                                         Lake
                                                      0.7 (residue)
                                                                                        same as above
                                                                                                                           Uthe.  etal
-------
Manganese
Manganese
Manganese
Manganese
cluoeaforals


fsox luclus   FL



Fsox luclus   FL



Esox luclus   FL
Os«erus
•ord»x
                                   FL
Ontario,
Can.

Moos* Lake.  3.0  (residue)
Can.
Lake St.     3.2 (residue!
Pierre, Can.
                    Lake Erie,   0.9 (residue)
                    Can.
Lake Erie,   0.02 (residue)
Can.
                                                                                        saoe as above
                                                                                        sane as above
                                                                                        saae as above
                                                                                        sane as above
                                          4HIC-3B19

                                          Uthe, et al
                                          (1971), »MIC-
                                          3S19,

                                          Uthe, et
                                          • HI9M),
                                          »1IC-3819

                                          Uthe, et al
                                                                                                                           Uthe, et al
Manganese
Manganese
Manganese
Manganese
Manganese
Perca         FL
flavescens
Paralabrnx    FH
cl athratus
Lnk* Erie,   0.21 (residue)
Can.
Scatterqood  0.9 (dorsal
Steam Plant, nuscle
Los Angelas, residua)
Cal.
                                                                                        same as above
Paralabrax    FH    Catallna     0.6 (dorsal
clathratus          Island, Cal. muscle
                                 residue)

Paralabrax    FM    Scattargood  0.9 (ventral
clathratus          Steam Plant, muscle
                    Los Angeles, residue)
                    Cal.

Paralabrax    FM    Catatlna     0.5 (ventral
clathratus          Island, Cal. Muscle
        Fish collected from an effluent
oloe ot a stea™ olant and from offshore
Haters of Catalina Island nerp analyzed
lor trace element content.  Trace element
content of the effluent Hater was at
te*st 5 times ore^ter than that of normal
sea Hater for caditlum, coooer, nicKel,
zinc, and chrowlu".  Livers of fls* fro*
the effluent were nearly twice the size
of those from the ocean.  Greatest
differences In concentration occurred
Hlth alurlnum, cadmium, and nickel.
Sliver, barium, llthlu*, and lead showed
the least differences.  The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on narine organises*

       sane as above
Uthe, et al
(1971), »KIC
3819

Staoleton
(1968) ,
•MIC-5980
                                                                                        sane as above
                                                                                        sane as above
                                                                                  Staoleton
                                                                                  I196M ,
                                                                                  4MIC-S9SO

                                                                                  S t a o I e t on
                                                                                  (1"68),
                                                                                  AMIC-598Q
                                                                                  Staoletor>
                                                                                  (1968) .
-------
Comoound

Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Organism

Paral ahrax
cl athratus
Paralabrax
clathratus
Paral afcrax
cl athratus
(qravid
f ema 1 es)
Paral ahrax
el athratus
Paral ahrax
cl athratus
Paral ahrax
cl athratus
Paral ahrax
cl athratus
Paral abrax
ct athratus
Paral abrax
clathratus
Paralabrax
clathratus
Field
Study

FM
FM
FM
FM
FM
FM
FM
FM
FM
FM
Toxlclty, Experimental
Active Variables,
Field Ingredient, Controlled
Locat Ion Pern or Noted
residue)
Scattergood 1.1 (gonads — -
Steam Plant, residue)
Los Angeles,
Cal.
Catallna 1.7 (gonads
Island, Cal. residue)
Catalina 3.3
Island, Cal. (gonads
residue)
Scattergood 3.<» (liver
Steao Plant, residue)
Lois Angeles,
Cal.
Catalina <>.3 (liver
Island, Cal. residue)
Scatterqoort 0.7 (Integument —
Steam Plant, residue)
Los Angeles,
Cal.
Catallna 0.8 (Integument -• -
Island, Cal. residue)
Scattergood 1.6 (heart --
Steam Plant, residue)
Los Angeles,
Cal.
Catallna !.<• (heart
Island, Cal. residue)
Scattergood 1.6 (eyeball
Steam Plant, residue)
Los Angeles,
Comments

same as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
Pef erence
AMIC-S910
StaD I eton
(1968) ,
AMIC-5981
Staoleton
(1968) ,
AMic-sgan
Staoleton
(1968) ,
AHIC-^980
Staoleton
(19&SI ,
AMIC-59SO
Staol eton
(19^8) ,
AMic-sgso
Stjioleton
(1968).
AMIC-5980
Staol eton
I19SM ,
ATC-5980
Staoletcn
(1968).
AMIC-5980
Staoleton
11968).
AMIC-5988
Staoleton
(19681.
AMIC-59JO
-------
                                                   Cat.
          Manoaoese
                               Paralabrax
                               clathratus
                                             FH
                    Catatlna     2.6 (eyeball
                    Island, Cat. residue)
                                                                                                  sane as above
                                                                     Staoleton
                                                                     (196*1,
          Hanoxol
                               Pasbora
                               heteromorpha
                                                                16 (T2>
                                             and
                                             BSA
r
vn
          NCPA
                               Fish (not
                               soeclfl»d>
                               Crassostrea
                               vlrqlnlca
                               (egqs)
                                 greater than
                                 10-100 (K)
                                                                19.6 (T2)
          HCPA
                               Crassostrea
                               vlrqlnlca
                               (larvae)
                                                                31.3 (Til.)
                a*,c,e,f.          One hundred sixty-four            Alabaster
                hard (HH)  pesticides, Mettlnq agents, and
                or soft    miscellaneous Mater pollutants shOMed a
                (SHIsynthe Mine range ot toxlclty soainlno 12 orders
                tic        of magnitude.  KnOMlnq the toxlclty and
                dilution   percentage of all comoonents of a
                Mater, or  formulation did not result In easy
                seaMater   predictability of the toxlcity of a
                for sone   mixture of materials.  Sometimes
                species    pesticides Mere most toxic in hard Mater
                           and sometimes the opposite Mas true.
                           Testing the actual material as sold Mas
                           found to be essential.

                                   Approximate toxlclties of         "aMdesley
                           numerous pesticides commonly used In      Thomas
                           Britain Mere summarized. An excellent     (19M1
                           brief, general discussion of toxlclty     1056
                           testing Is also present.

                                   The effect of «!2 pesticides on    Davis, et
                           embryonic development of clams and        (1969),
                           oysters Mas reported.  Synerglstlc        ANIC-5990
                           effects Mith solvents »ere also reported.
                            Most of the compounds affected
                           development more than survival.  Some,
                           however, drastically reduced larval
                           growth.  The authors oolnt out the
                           necessity of evaluating the effects of
                           pesticides on all  life sfaaes of an
                           organism and note the oossiblllty ot
                           selecting chemicals for pest control that
                           would not have serious effect on
                           she!I fish.

                                  sane as above                      Davis, et al

                                                                     (1969),AMIC-
                                                                     5990
                                                                                                                                               al
          Mecarb»«
Fish (not
specified)
greater than
0.001-0.01 (K)
        Approximate toxlclties of         MaMdesley-
numerous pesticides commonly used in      Thonast1971)
Britain Mere summarized. An excellent     AHIC-10S6
brief, general discussion of toxlclty
testlnq Is also present.
-------
10


Conoouni
Menazon









Toxlcity, Experimental
Active Variables,
Field Field Ingredient, Controlled
Orqanlsm Study Location Ppm or Noted Comments
RasborK BCFA — 151, 
                               Acroneurla    BSA
                              Cohemere11 *   BSA
                              Hyrtroosych*   BSA
Uatersloora   L
cucul1sta
(larvae)
Buqula
neritina
(larvae)

Solrorbls
lanellosa
(larvae)

C.aleolarla
caesolrosa
                                                                ? (Tit)
                                                                z mi
                                                                2 (Tit)
0.10 (T 2hr)

                                  0.20  CT  2 hr)
                                                                O.H (T Z hr)
                                                                0.12  (T  2  hrl
                                                         t,t         Fohemerella  (mayfly)  was  the  most  War-nick,  et
                                                            sensitive  aquatic  Insect  of  those          al(1969>,
                                                            studied, and  coooer  the most  broadly       »1I!
                                                            toxic  metal.   The  authors suqaest  that
                                                            aouatlc Insects  mav  not be as sensitive
                                                            to heavy metals  as fish.
                                                    ,c,d,e,f
                                                  a»,c,d,e,t
                a,c,l, and
                salinity
                                                                                                  same as above
                                                                    same  as above
                                                                     HarnlcK. et
                                                                     al (19*9),
                                                                     ANTC-J767

                                                                     HarnlcK, et
                                                                     al
        This study was conducted To
determine snecles ot marine larvae
suitable tor use In test screeninq
antlfoullnq chemicals.  A. sallna (brine
shrino) appeared to have the best
potential tor this ouroose.  A. sallna
larvae sensitivity xas qreatest starting
at age 20-AO hr, and tolerated relatively
I ox oH (5.0).

       same as above
Wisely, «T
al (11S7I,
AMIC-S70S
                salinity

                a,c,l, and
                salinity
                a.c.lt  and
                salinity
                                                                     Wisely, et
                                                                     al
                                                                                                  sane as above
                                                                                                  sa«e as above
                                          Wisely, et
                                          a I II 967) ,
                                          AMIC-S73*

                                          Wisely, et
                                          a I (1967),
-------
                      (larva*)
                                                                                                                             »MIC-1>70S
 Mercuric  chloride
 (as Hq)
 Mercuric  chloride
 las Hq)
Mercuric  chloride
las  MI)
Mercuric  chloride
las  »ercury)
Mercuric chloride
las •«rcuryl
Hytllus
eluli?
nlonulatus
(larvae)

Crassostrea
comnerclalls
(I arvae)

Arteula
salIna
(larvae)

Carclnus
•aenas
                                    L     —

                                    BS»   —
                                                       13.1 (T 2 hr)
                                                       180.9 (T 2 hr)
                                                       1809 (T 2 hr)
                                                       1.2 (TZ)
                      Cardlum edule 8S»   —
                                                       9.0 (T3>
and
sailnlty
a.CiI, and
salinity
•.,0.1,
and
salinity

a»(eontin-
uoua, aer-
ation, soa
water, and
dally
•olutlon
renewal)
                                                                                         sane as above
                                                                                         saee as above
                                                                                         sane as above
                                                      Wisely, et
                                                      al  11967).
                                                  a»(contln-
                                                  uoua aer-
                                                  ation,  aea-
                                                  water,  and
                                                  dally
                                                  solution
                                                  renewal)
        One hundred-forty surface  active
aqents, solvent e»ul51 tiers,  pesticides,
polychlorinated biphenyls, cure
Inorqanlc, and organic cheirlcals Mere
evaluated aqalnst as many as  ten marine
organisms.  The authors noted that nost
published data of this type deal oltn
toxlclty of chenlcals to freshwater
orqanlsns.

       saae as above
                                           Wisely,  et
                                           al
                                           Wisely,  et
                                           al  (1967),
Port*anr», et
al (1971),
• •1IC-77D1
                                                     Port»ann, et
                                                     al (1971).
                                                     •1IC-7701
Mercuric chloride
(as a>ercury>
Mercuric chloride
las aercury)
Crangon
cranqon
                                   BS*    —
                                                       0.10-0.33(11.)
                     Ostrea edulls  USA    —
                                                       t.2 (T2>
a«( contin-
uous aer-
ation, sea*
water, and
dally
solution
renewal)

a»(contin-
uous, aer-
ation, sea.
water, and
dally
solution
renewal)
                                                                                         sane as above
                                                                                                                                      et
                                                                                         saae as above
                                          a) (1971),
                                          »MIC-770t
                                                                                                      Portwann,  et
                                                                                                      a I  (1971),
                                                                                                      AMIC-7701
Mercuric chloride
                      Pandalus
                                   BS»   —
                                                       0.08 (T2)
                                                                                         same as above
                                                                                                                            Portaann, et
-------
Comnound
fas mercury!




Hereurlc chloride
(as mercury)





Hereurlc chloride







Mercuric chloride


Mercuric chloride


Field Field
Organism Study Location
•ontaqul




Platlethys BSA
flesus





Carasslus BSA --
auratus






Carasslus BSA —
auratus

Carasslus BSA —
auratus

Toxicity,
Active
Ingredient,
POD





3.3 (TZ>






0.25 (S81)







0.25 (15 ppm
tissue residue
1 d)
0.25 C.O-SO pom
tissue
residua 100 hr)
Variables,
Control 1 ed
or Noted
(continuous
aeration.
and dally
solution
renewal >
a»
(continuous
aeration.
seaxater.
and dally
solution
renewal)
a»,e







a»,e


a'.e


1
Comments





save as above






Mercury accumulated rapidly in
qoldflsh. The higher the concentration
UP to 1.0 pom, the more rapid MBS the
accumulation. At higher concentrations.
of the mercury beinq found in the mucus.
The authors noted that bacterial
mefhytatlon occurs In dead fish but only
If muchus is present.
same as above


same as above


Reference
al (197U,
ANIC-7701



Portuann, et
al (197U,
A*IC-77gl




HcKone, et
al (l°7i».
AMIC-1*1*?





McKoie, et
al (11711,
AMIC-l«.S?
PcKone, et
al (10711.
ANIC-li.9?
Hereurlc chloride    Anbassis      BSA
                     safgha
                                                           (Tl)
a».                Measurement of residual dissolved Pal lard,et
seaxater   oxyqen during exposure of fish to         al (1969),
           toxlcarts resulted In data similar to     AHIC-300
           that obtained froi Z<>- and *8-hr
           bloassays by the standard vethod.  The
           residual  oxyqen method required only S hr
           to conduct.   Variables studied included
           density per  unit votuve,  temperature, and
           fish size.   The authors conclude that the
           residual  oxygen method is a quick and
           reliable  procedure for routine monitoring
           work.
-------
 Mercuric chloride
                      Carats Ius
                      auratus
                                                       O.S? IT7)
>
I
Mercury  (total)
Mercury  (total)
Mercury  (total)
Mercury  (Total)
Mercury (Total)
Mercury (Total)
Mercury (total)
Mercury (total)
Mercury (Total)
Mercury  (total)
                                Salvellnus    Fl    Cayuqa LaKet 6.2Mresidue)
                                namaycush (1        Ithaca, N.Y.
                                yr)
Salvellnus
namaycush (11
yr)
Salve) Inus
namaycush (12
yr)
Salvel Inus
na»ayeush (?
yr)
Salvel Inus
nanaycush (3
yr)
Salvel inus
namayeush (w
yr)
Salvellnus
namaycush (5
vr)
Salvel Inus
namaycush (6
yr)
Salvel Inus
ramaycush (7
yr)
Salvellnus
FL
FL
FL
FL
FL
FL
FL
FL
FL
Cayuga Lake,
Ithaca, N.Y.
Cayuqa Lake,
Ithaca, N.Y.
Cavuqa Lake,
Ithaca, N.Y.
Cavuga Lake,
Ithaca, N.Y.
Cayuqa Lake,
Ithaca, N.Y.
Cayuqa Lake,
Ithaca. N.Y.
Cayuqa LaKe,
Ithaca, N.Y.
Cayuqa Lake,
Ithaca. N.Y.
Cayuga Lake.
0.58 (residue)
0.57 (residue)
0.27 (residue)
0.37 (residue)
d.i.3 (residue)
0.
-------
Coaooun4

Mercury (total)
Mercury
Mercury
Mercury
Mercury
Mercury
Mercury
Mercury
Metasystox
Organls*
pamaycush (6
yr)
Sal vet Inus
namayeush (9
yr)
Copegonus
clupeaf or«ls
CoPegonus
cluneafopHls
Esox lueius
Esox luclus
Esox lueius
Osmepus
•opdax
PePca
f lavescens
Rasbora
heteromopDha
Toxlclty,
Active
Field Field Ingredient,
Study Location Ron
Ithaca, N.Y.
FL Cayuga Lake, 0.53 (residue)
Ithaca, N.Y.
FL Hoose Lake, 0.07 (residue)
Can.
PI 1 aW A fl IT ff»A«l/4iiAl
r i_ Lane u.if iresiouei
Ontario,
Can.
FL Hoose Lake, 0.11 (residue)
Can.
FL Lake St. 0.70 (residue)
Pierre, Can.
FL Lake Erie, 0.49 (residue)
Can.
FL Lake Erie, 0.05 (residue)
Can.
FL Lake Erie, 0.22 (residue)
Can.
BCFA — 6.5 (T2>
and
BSA
Exoerlnental
Variables,
Control led
or Noted Comments

— - sane as above
Concentrations of 13 toxic
>l«ments In dressed t Ish from heavily
Industrialized and non-industrialized
areas were determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements were
essentially the same In fish Iron both
areas.

-- same as above
-- same as above
•— - same as above
-- same as above
-- same as above
a*,c,e,f. One hundred sixty— four
hard (HH) Destlcldes, wetting agents, and
or miscellaneous Hater oollutants showed a
SOFT(SH) Hide range of toxlcity scanning 12 orders
synthetic of magnitude. Knowing the toxlcity and
dilution percentage of. all components of a
Reference
(1971) ,
»»ic-m»
Bache, et al
(1971) ,
AMIC-3S18
Uthe, etal
(1971) ,
AMIC-3819
U t ^ ft « c t^ t
(19T1) .
AMIC-3S19
Uth«, et al
(1971) ,4MIC-
3S19
Uthe, et
ALI1971),
SMIC-3519
Uth*. et al
(1971),&Mic-
3U9
Uthe, et al
(1971), A«IC-
3319
Uthe, et at
(1971), SMIC-
7819
Alabaster
(1969),
AMIC-SfcZS
-------
Hethanol
                      Agonus
                      eataohractus
                                    8SA
                                                       10,000-33,000
                                                       IT2»
M«thanol
                     Cardlurn edule flSA
                                                       3300-10,000
                                                       (T2)
                                    water,  or  formulation did not result In easy
                                    seawater   predictability of the toxlclty of a
                                    for  sone   mixture of materials.  Sometimes
                                    species    pesticides Here most toxic in hard Hater
                                               and soiretlmes the ooooslte Mas true.
                                               Testing the actual  material  as sold Has
                                               found to be essential.

                                    a*(contln-         One hundred-Tor TV  surface active
                                    uous, aer- agents, solvent emuls1fiers,  cestlcides,
                                    ation,  aea-polvchlorlnated biohenyls, bure
                                    water,  and inorqanic, and organic chenicats Here
                                    dally       evaluated aqalnst as many  as  ten marine
                                    solution   organisms.  The authors noted that most
                                    renewal)    published data of this type  deal  with
                                               toxiclty of chemicals to freshwater
                                               orqanisms.

                                                      saute as above
                                                                       «*{ contin-
                                                                       uous aer-
                                                                       ation, sea-
                                                                       water, and
                                                                       dally
                                                                       solution
                                                                       renewal)
 Portmann,  et
 al  »1971>,
 Anic-7701
                                                                                         Portaann,  et
                                                                                         al  (1971),
                                                                                         AMIC-7701
dethanol
                     Crangon
                     erangon
                                   BS»    —
                                                       1700  (Ti«>
                                                                       a«(contin-
                                                                       uous aer-
                                                                       ation, sea-
                                                                       water, and
                                                                       dally
                                                                       solution
                                                                       renewal)
                                                                                         same as above
                                                                                        Portiann,  et
                                                                                        al  I19T1I,
                                                                                        AMIC-701
Hethoxycnl or
•tritium  labelled)
                     Sorghum
                     halpense
U
(node
I
ecosy
stem)
1 Ib per A      atc,q.             This small laboratory model
(NTE)           standard   ecosystem orocedur<> was dpvelooed to
                reference  study pesticide blodeqradabl I i ty and
                Hater and  ecological magnification.  The food-chain
                sand       pathways In this system Here;  (i)
                           sorghum - caterpillar (larva), (2)
                           caterolller (excreta) - Oedooonium, (3)
                           OffdOTonium - snail, (it)  Estiqmene
                           (excreta) - diatoms,  (5)  Diatoms -
                           plsnktcn, (6)  Plankton — Culex (larvae),
                           (7)  Culex - Gambusia.  The fish is  the
                           too  of the food chain.  Using
                           Isotoolcally labeled  oestlclrtos (1
                           Ib/acre application rate), residues Here
                           determined for only selected organisms
                           (snail, mosquito,  and fish)  and Hater,
fetcalf, et
al (19711,
-------
            Compound
                                 Orgtnlsm
                                             Fluid  Field
                                             Study Location
                                                      Toxlclty,
                                                      Active
                                                      Tnqredlent,
                                                                      Experimental
                                                                      Variables,
                                                                      Control led
                                                                      or Noted
                                                                                                           Comments
                                                                                                                                    Reference
Hethoxychlor         Cstlqmene
(tritium labelled)   acrea
                                             L
                                             (Hod.
                                             •1
                                                      1 Ib per A
                                                      (K-NTE)
                                                                      a,c,q,
                                                                      standard
                                                                      reference
                                                                      Mater and
                                                                      sand
                                                                                 Reorodueibl11ty appeared to be qood.   The
                                                                                 authors state that the method qlves a
                                                                                 good estimation of the potential  toxlclty
                                                                                 of pesticides and their breakdown
                                                                                 products to a variety of orqanlsus and Is
                                                                                 suitable for  computer modeling.

                                                                                        same as above
                                                                                                                           Netcalf. et
                                                                                                                           al
to
          Hethoxychlor
          (tritium labelled)
                               Physa sop
                                   (Mod.
                                   .•1
                                   •COST
                                                                15.7 (residue)
                                                                      a,c,g,
                                                                      standaro
                                                                      reference
                                                                      Mater and
                                                                      sand
                                                                                                  same as above
                                                                                                                           Hetcalf,  et
                                                                                                                           al  (1971),
          Hethoxychlor
          (tritium labelled!
                               Oaphnla maqna
                                             (Mod-
                                             •1
                                             «oorr
                                             at«n)
                                                      1 Ib per
                                                      (K-NTE)
                                                                      a,e.g.
                                                                      standard
                                                                      reference
                                                                      Mater and
                                                                      sand
                                                                                                  same as above
                                                                                                                           netcatr,  et
                                                                                                                           al  (19711.
Hethoxychlor         Culex plplens L
ftritium labelled)   mtlaqua-      (mode
                     fMO&to*     i
                                   ecosy
                                   stem)
                                                                O.VS(residue)
                                                                                                  same as above
                                                                                standard
                                                                                reference
                                                                                Mater and
                                                                                sand
                                                                                                                                     Hetcalf,  et
                                                                                                                                     al  (1171).
Hethoxychlor         Oedogonlum    L
(tritium labelled)   cardlacua     (mode
                                   I
                                   •cosy
                                   stem)
                                                                1 Ib per
                                                                A(NTE)
                                                                      a,c,q,
                                                                      standard
                                                                      reference
                                                                      mater and
                                                                      sand
                                                                                                  same as above
                                                                                                                           Hetcalf,  et
                                                                                                                           al  (1971),
Hethoxychlor         Gambusla      L
(tritium labelled)    affinis       (mode
                                   I
                                   •co*y
                                                                0.33 (residue)
                                                                                a,e.g.
                                                                                standard
                                                                                reference
                                                                                Mater and
                                                                                                  same as above
                                                                                                                           Netcalf, et
                                                                                                                           al  (19711,
                                                                                                                           »MIC-Hi95
-------
                                            ste«O
                                                                                sand
         ".•thoxychlor
         (tritium label 1*4)
U)
         (tritluei lab*I lad)
         He thoxychlor
         (tritium labell«4>
         HethoxycMor
         (trltlun  labelled)
 Diatoms       L
 (Kavleula.,     (node
 Cosclnodia-   I
 cua.  Dip-     ecosy
 loneaa, and   st*«)
 MatooallA)

 Protozoa       L
 (Nuclearia.    (node
 Coleps,        I
 Vortlcellat    ecosy
 and            stem)
 Paraoeciua)

 Rotifera       LInod
 (Aaplanebnop- el
 us, Hotoaat-   ecosy
 ta., Euelaria,  steel
 Seardium)
                              Hater
                                            L
                                            ecosy
                                            stenl
1 Ib oer A
(NTEJ
                                                               1  Ib per A
                                                               (NTE)
1 Ib per A
(NTE1
                                  0.0016
                                  (residue)
 a.c,q,
 standard
 reference
 Mater and
 sand
                otc,g,
                standard
                reference
                Mater and
                sand
a.c.g,
standard
reference
Mater and
sand

a.c.q,
standard
reference
Mater and
sand
                                                                                                  saee  as above
                                                                                                  sane  as above
                                                                                                  saae  as  above
                                                                                                 sane  as  above
                                                                                                                                     Wetcalf.  et
                                                      Metcalf,
                                                      etal  (19711.
Hetcalt,
etal (1971),
                                                                     Hetcalf, et
                                                                     al (19711.
         Nethoxyenior
        Methoxychlor
        Methoxychlor
                              Chlronoiius
                              tentans
                              llnstar)
                                            BSACF —
                                                               5.5 (T*l
Stenonema
candirtui*
linstar)
                                            BSACF —
Taenloptervx  BSACF
nival Is
(Instar)
                                                               2.1 (Tit)
                                                               0.98 (TU
c.d.e              This chemical Mas evaluated
           primarily because  It  is on* of the
           principal substitutes for DOT.  Raoid
           breaKdcnn of the chemical occurred Mhen
           llvlnq orqanlsirs Here present.  The
           half-life of methoxychlor Has 7 days in
           Ann Arbor city nater* but Has fpuch nore
           raold (less than 1 day) In local creeK
           Mater and si OH (approximately 200 days)
           in distilled nater.  These studies Mere
           to be continued to determine long term
           effects but no data are presented.

c.d.e             sane as above
                                                                               c.d.e.             same as above
                                                                                                       lender.et al
                                                                                                       (1971).
                                                                                                       AMIC-JZ79
                                                                     Bender,  et
                                                                     al(1971),
                                                                     AMIC-3279

                                                                     Sender.et  al
                                                                     (1971),
                                                                     AMIC-J779
        He thyIen*  bis
                              Phoraldiua
                                            L      —
                                                               0.5-10.0 (16    —
                                                                                                  01 7k chemicals evaluated as
                                                                                                                                    Otto (1970).
-------
Compound
thloeyanate
Field Field
'Organism Study Location
aablguum
Toxlclty,
Active
Ingredient,
Ppm
percent
Experimental
Variables.
Control led
or Noted Comments
alqlcides, only 9 Her* nor* toxic than
Reference
AMIC-M?
O)
         Hethylmercury
         Hethylmercury
         Hethy I Mercury
         Nethylmercury
         MethyI acreury
         HethyI mercury
         Hethylmercury
                                                                qrowth Inhibited
                                                                HO
                              Salvelinus     FL     Cayuqa Lake, 0.07 (residue)
                              n««iaycush  (1         Ithaca, N.Y.
                              yr»
Salvelinus    FL
namaycush  (2
yrl

Salvellnus    FL
namaycush  (3
yr)
                               Satvelinus
                               namavcush (
                               yr)
                                             FL
                                                   Cayuqa Lake, 0.11
                                                   Ithaca, N.Y.
                                                   Cayuqa Lake, 0.21
                                                   Ithaca, N.y.
                     Cayuqa LaKe,  0.3<>
                     Ithaca, N.Y.
                                                                     (residue)  --
                                                                     (residue)
                                                                     (residue)  --
Salvelinus    FL
namaycusn  (5
yr)

Salvelinus    FL
.nanaycush  (6
yr)

Salvelinus    FL
navaycush (7
yr)
                                                   Cayuqa LaKe, 0.35 (residue)
                                                   Ithaca, N.Y.
                                                   Cayuqa Lak*,
                                                   Ithaca, N.Y.
Cayuqa Lake, 0.31
Ithaca, N.Y.
                                                                     (residue)
                                                                     (residue)
Cu<:oii.  None Inhibited oronth of
mat-formlnq alqae for more than 2 weeks.
CuSOI. formulated nlth certain Hettinq
aqents Has more toxic than CuSOl> alone.
Cooper chloramlne HAS also found to he
more toxic than Cu30<>.  No netting aqents
Here found to be Inhibitory at the
concentrations investigated (0.05 and
0.105 ppir) .  Also reported are factors
affectlnq qroHth of alqne In canals to
determine nhether there were leads to
controllinq algae by environmental
management.  No practical environmental
means Here found.

        LaKe trout stocKed annually as    Bache, et al
taqqed finoerllngs Here netted and        (1971),
analyzed  for mercury and methyImercury.   A1IC-SS1H
Total mercury and the proportion of
methy lirercury to mercury Increased Mlth
aqe but not sex.

       same as above                      Cache, et al
                                          (19711,
                                          AMIC-3818

                                          Bache, et al
                                          (1971),
                                          AMIC-SS18

                                          Bache, et al

                                          A««IC-381»

                                          Bache. et al
                                          (1971),
                                          AH.IC-1818

                                          Cachet et al
                                          (19711,
                                          AN.TC-3818

                                          Bache, et al
                                          (1971),
                                          AHIC-3818
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
-------
 f
8
          Hethylm*rcury
         Methylmwreury
         Hethyl mercury
         Methyl mercury
         Me thylo»ntynol
         Nethyloentynol
Salv*lInus    FL    Cayuga  Lake,  I).SI  (residue)
namayrush (8        Ithaca,  N.Y.
yr)

Sal vel Inus    FL    Cayuqa  Lake,  0.1.3  (residue)
                                         (9
                                                   Ithaca, N.Y.
                               vr>
                               Sal vet Inus    FL    Cayuqa Lake, 0.1.1 (residue)
                                         (11
                                                   Ithaca, N.Y.
                               yr)
Salvel Inus    FL    Cayuqa  Lake,  0.47  (residue)
nawaycush (12       Ithaca, N.Y.
vr)
                               Sal mo
                               galrdnerl
                                             BSA
                              Salno  trutta  BSA
Methyloentynol
Methyloentynol
Methyl pent ynol
Methylpentynol
Methylpentynol
Sal vel Inus
fontlnal is
Sal vel Inus
namaycush
Esox lucius
Ictalurus
punetatus
Leoomts
•acrochlrus
BSA
BSA
BSA
BSA
BSA
                                                                870-1260 (Tt>)   a*,c,f
                                 680-1100 (Tit)   a*tCtf



                                 1100-1200 (TV)  a»,C,f


                                 660-1160    »*,c,l
                                                                less than 900   a*»c,f
                                                                IT*)
                                                                1700-1890 CTJ.)  a»,cff


                                                                l?60-13dO (T«.)  a*,c.f
                                                                                                   same  as  above
                                                                                                  sane  as  above
                                                                                                  same  as above
                                                                                                  same  as  above
                                                                     MethyIoentynol  was tested in
                                                             9fi-hour bioassays for Its toxicity to
                                                             rainbow trout,  brown trout,  brook trout.
                                                             laKe  trout,  northern olke. channel
                                                             catfish,  blueqitlsi  MrqemouTh bass, and
                                                             walleyes*   Channel  cattish were the most
                                                             resistant  and lake  trout  the *ost
                                                             sensitive.   Two-inch rainbow trout, brown
                                                             trout,  and  lake trout were more sensitive
                                                             to methyloentynol  than  larqer ones in the
                                                             96-hour exposures.   The druq was more
                                                             toxic  to  blueqills  and  rainbow trout with
                                                             elevated  temperatures.  Toxiclty was
                                                             barely  Influenced by changes In Mater
                                                             hardness.

                                                                    sane  as  above
                                    Pac*>e,  et  al

                                    AMIC-38H

                                    Pache,  et  al
                                                                                                                                      Bache.  et al
                                                                                                                                      I19M) ,
                                    Pache, 'et  al
                                    (1171),
                                    aiic-ms

                                    Markinq(19S9> ,
                                    4MIC-S«>77
same as above


same as above


same as above



same as above


saa* as above
                                   "arking
                                   (1969),
                                   51.77
                                                                                                                                     Marklnqtl9S9|
Harking(19S9) .
AMIC-5I»77

f arking
(19S9J.AHIC-
5*77

»«arklnq(1959) .
»«IC-5<»77

Harkinq(1969>,
»MIC-5l»77
-------
Conoound
M«thyloentynol
M«thyloentynol
Organism
Mlcrooterus
salnoldes
St Izostedlon
vl treun
Field Field
Study Location
BSA
BSA
Toxicltyt
Active
Ingredient,
Pom
1100-1350 (T<.)
11*0 (T<>)
Experimental
Variablest
Controlled
or Noted Comments
a*,c,f sane as above
a*,c,f sane as above
Reference
:fIC-5<.77
Marking
119*9) ,»MIC-
SI.77
         Hethyl parathlon
CO
t->
ON
         Methyl  oarathion
Leoonls       8SA   —
cyanelI us
(Resistant)
                              Leoomis
                              cvanellus
                              (Susceptible)
                                            BSA
                                                               greater than
                                                               5000 (T2)
                                 greaterthan
                                 •5000 (T2)
        Green sunflsh Iron Helionl, Hiss. Hinchew, et
were resistant to Chlordane, Heotachlor,  al (19TO)«
Llndane, and Strobanet but not to
Par^thion,  Golden shiners fron the sa»e
location were resistant to Llmlane and
Strohane, tolerant to Thlordane and
Heotachlor, and suseeotltle to Parathlon.
 Lack ct resistance to Parathion
indicated lack of agricultural usage of
organochosohates In that area.  Resistant
fish Here comoared to susceotible ones
collected at Starkvltle.
                                                                                                 sane as above
                                          Hl
                                          al
         Methyl  oarathion
         Methyl oarathion
Notem1nonus
crysoleucas
(Resistant)

Notemlaonus
crysoleucas
(Susceotlble)
                                            aSA
                                            BSA
                                                               greater than
                                                               6000  (T2)
                                                               greater
                                                               thanSOOO ITZ)
                                                                                                 sane as above
                                                                                                 sane as above
                                          Hlnchex. et
                                          al  lig7C),
                                                                                                                                    al
         Methyl oarathion
                              tctalurus
                              ounctatus
                                            BSA   —
                                 5.71 (T4)       at                 Oroanochlorlne insecticides were  Hacek, «t al
                                                 synthetic  the most toxic cowoounrts,                 (1970),
                                                 test water organochesohates Intermediate, carbaiates AMIC-S510
                                                            the least toxic.  Prown trout Has the
                                                            soecies most susceptible to
                                                            organochlorlnes, coho salmon the »ost
                                                            susceptible to carba*ates, and goldfish
                                                            Here the least susceotible of all
                                                            soecles.  Safe concentrations established
                                                            by bloassays with saltonlds or
                                                            centrarchlds would likely be safe for
-------
 Methyl  oarathion
 Hefhyl  oarathion
 Methyl  oarathion
Methyl  oarathion
Methyl oarathion
Methyl oaratnion
Methyl oarathion
Methyl oarathion
Methyl oarathlon
Methyl oarathion
Methyl oarathion
Methyl oaratnlon
let alur us BSA
•el as
Carasslus BSA —
auratus
Cyorlous BSA —
carolo
Plmeohales BSA —
prone las
Lenoml*; ' BSA --
macrochlrus
Leoonls BSA --
nlcroloohus
Microoterus BSA —
sal moliles
Salno BSA —
galrdnerl
Salno trutta BSA —
Oncorhynchus BSA -—
Kisutch
Perca 8SA —
f lavescens
Pataenonetes BSA
kadiakensis
6.6". (T<>)
99.00 (TM
7.13 (T«.)
8.90 (T<>)
5.72 (T
5.17 (Tl.)
5.22 (Tl.)
2.75 (Tl.)
*.7* (Tit)
5.30 (T".)
3.06 (Tit)
0.0025-0.0233
(Tl)
a,
synthetic
test Hater
a,
synthetic
test water
a.
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
a.
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
synthetic
test water
a*
                                                                                  cyorlnlds and Ictalurlds.  Safe levels
                                                                                  for ictalurids or cyprlnlds would
                                                                                  probably be hazardous for centrarchlds
                                                                                  and salnonlds.  The use of goldfish In
                                                                                  bloassays was discouraged.

                                                                                         sane as above
                                                                                         same as above
                                                                                         sane as above
                                                                                         sane as above
                                                                                         same as above
                                                                                         sane as above
                                                                                         sane  as  above
                                                                                         sane  as  above
                                                                                         sane  as  above
                                                                                         same  as  above
                                                                                        same  as  above
        Bloassays were conducted with
shrlmo from three areas of Intensive
                                           Pacek.et  al
                                           (19701,
                                           SMIC-5510

                                           Maeek. et at

                                           •MTC-5S1C

                                           MaceX, et at
                                           (1970 .
                                           AMIC-5510

                                           Hacett. et al

                                           AMTC-S510

                                           HaceK, et al

                                           AMIC-5510

                                           K^cek* et al
                                          Macek, et at
                                          (1970) .
                                          Hacek, et al
                                          (1970) .
                                                                                                                                     al
                                                                                                                            (1970),
Maeek, et al
(1973»,
AMIC-55H

Macex. et al
(1970),
AHIC-5510

Naovl, et al
(1970),
-------
  Compound
                       Organism


                     (resistant)
                                   Field  Field
                                   Study Location
                                 Toxlelty.
                                 Active
                                 Ingredient,
                                   Pp«
                                                                              Experimental
                                                                              Variables,
                                                                              Control led
                                                                              or Noted
                                                                                                 Comments
                                                                                                                           Reference
 >
U)
Methyl parathlon
Methyl paratnion
Palaemonetes  BSA
kadlakensls
(non-
resistant)
Tunlf»x
tunlfex
                                            Ft
                                            ant
                                            BSA
RelzonI,
HISS.
                                                      0.0037 (Tl)
                                                      6.00 (NTF)
                                                            pesticide  us*  and from  an  unexoosed area.  AMIC-5519
                                                            Previously  exposed  shrimp were from 1 to
                                                            25  times more  resistant  than  unexoosed
                                                            shrimp.  Roth  typos  of  shrimp Mere  also
                                                            exposed  In cages  to  Maters of the
                                                            contaminated areas.   Susceptible shrimp
                                                            suffered f*>  percent  more mortality  than
                                                            did resistant  shrimp.   The Toxlelty of
                                                            the Insecticides  ranked  in descending
                                                            order  was  as foil CMS;   mast toxic,
                                                            Fndrln,  DOT, Methyl  parathion, Parathlonl
                                                            medium toxlclty,  Guthlon,  Lindane,
                                                            Toxaohene, Strobanet lease toxic
                                                            Chtordane, Sevln, and Heotachlor.
Hevlnfos
                     Basbora
                     heteromorpha
              BCFA  —
              and
              BSA
                                                      11.9 tTZ)
                                                                               a*.c,e,f,
                                                                               hard (HW)
                                                                               or
                                                                               SOFT(SH)
                                                                               synthetic
                                                                               dilution
                                                                               water, or
                                                                               seawater
                                                                               for
                                                                               son*
                                                                                        sane as above
                                                                                                                           Naavl, et al
        The response of
pesticide-resistant aauatlc organisms to
various pesticides Mas compared to the
response ot non-resistant soecies.
Pest Ic Ide— r es Is t ant species Mere
collected at Pelzonl and non-resistant
species at State College.  Copepods,
clams, snails, and sludQ" Morms from
Relzonl Mere considerably morA tolerant
to pesticides than the non-resistant
organisms.  The authors note that the
effect of Increased tolerance In the
organisms Is an Increase in the amount of
pesticide residues available to animals
of hloher trophic  levels.

        One hundred sixty-four
pesticides, Netting agents, and
miscellaneous Mater Pollutants shoMed a
Hide range of toxiclty spanning 1? orders
of magnitude.  KnoMlng the toxlcity and
percentage ef all comoonents of a
formulation did not result In easy
predictability of the toxlclty of •
•Ixture of materials.  Sometimes
pesticides Here most toxic in hard Mater
Nadvi, et
IJ9S9I,
AHIC-5979
                                                                                  Alabaster
                                                                                  (19691,
                                                                                  AHIC-5i»?5
-------
         Ml Ibex
                              ffasbora
                              heteroMorpha
              BCFA
              and
              BSA
                                                                3.5  (T2)
r
UJ
         WoaSPlM
Fundulus      BSA
heteroelItus
                              Nereis vlrens BSA   —
                              Crangon       RSA
                              crangon
D.0003-0.0006
CT*>
                                                                                spades
                *».c,e,f.
                hard (HW)
                or soft
                (SV) syn-
                thetic
                dilution
                Miter, or
                saa.va.ter
                for-aooe
                apecies
a*,c,e,
and
synthetic
seawater
           and sometimes the ooooslte was true.
           Testing the actual material as sold was
           found to be essential.

                   fine hundred sixty-four
           pesticides, wetting agents, and
           miscellaneous water pollutants showed a
           wide ranqe of toxicity scanning 12 orders
           of magnitude.  Knowing the toxiclty and
           oereentaoe of alI components of a
           formulation did not result In easy
           predictability of the toxlclty of a
           mixture of materials.  Sometimes
           pesticides were most toxic in hard water
           and sometimes the opposite was true.
           Testing the actual material as sold was
           found to be essential.

                  same as above
                                                                                                                                     alabaster
                                                                                                                                             et
                                                                                                      al
                                                               0.00006-0.floods a'.cte,
                                                               (Tit)            and
                                                                               synthetic
                                                                               seawater
                                                                                                 same as above
                                                                                                      LaRorhe.et
                                                                                                      al J197C),
                                                               1000-3300  (T<»)
                                                                                                      Portmann, et
                                                                                                      al (1971),
                                                                                                      •MIC-7701
         Mobllsol
                              Crsngon
                              crangon
                                            BS»
                                                               10-33 
                a«(contln-         One hundred-forty surface active
                uous, aer- aq^nts,  solvent enulslf lers.  oesticldeSi
                atlon, aea>polychlorlnated blphenyls,  pure
                water, and Inoroanlc,  and organic chemicals were
                dally      evaluated against as itany as  ten marine
                solution   organisms.   The authors  noted that most
                renewal)   oubflshed data of this type rteal with
                           toxlcity of chemicals to freshwater
                           organisms.

                a«(contin-         °ne hundred-forty surface active
                uoua, aer- agentst  solvent emulslf iers,  pesticides,
                ation, aoa-polychlorlnated blohenyls,  pure
                wnter, and Inorganic,  and organic cheiricals w,*re
                daily      evaluated against as many as  ten marine
                solution   organisms.   The authors  noted that most
                renewal)    published data of this type deal with
                           toxiclty of chemicals to freshwater
                           organisms.

                                   Of  the aauatlc weed herbicides   Sanders
                           evaluated.  Oiclone was the  eost toxic,   (19>OI,
                           Oaohnla  was generally the most sensitive »MIC-»53
                           organise.  All of the Crustacea were
                                                                                                      Port«»nn, et
                                                                                                      al (1971),
                                                                                                      AMIC-7701
-------
           Comoound
                                            Field  Field
                                Organism    Study Location
                                                      Toxiclty,
                                                      Active
                                                      Ingredient,
                                                        Ppm
Experimental
Variables,
Control led
or Noted
                                                                                                          Comments
                                                                                                                                    Reference
         Notinate
                     Paleomontes   BSA   —
                     kadlahensls
                                                               1.0U2)
           aTfected by much loner concentration
           levels of herbicides than Indicated by
           the TL sub SO values.  Alt of the animals
           represent Important food chain links.

                  same as above
                                                                                                                                    Sanders
                                                                                                                                    (19731 ,
                                                                                                                                    AMIC-<.53
r
8
         Hoi mate
Nollnate
         Hollnate
         Nollnate
         Nollnate
         No Iybdenum
                              Aseltus       BSA
                              brevicaudus
                     Orconectes    BSA
                     nals
                              Oaphnla maqna BSA
                              Cyprldopsls   BSA
                              virtus
                              Lepomls       BSA
                              macrochlrus
                                                               D.<»0 (TZ)
                                                       5.6  (TZI
                                                               0.60 (T?)
                                                               0.18 (T3)
                                                               0.1.8 (T2I
                              Paralabrax    FN    -Scatterqood  0.1  (dorsal
                              elatnratus          Steam Plant, muscle
                                                  Los An9eles,
                                                  Cal.
                                                                                                 same as above
                                                                                        same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                 same as above
                                                                                                                           Sanders
                                                                                                                           (1970) ,
                                                                                                                           AMIC-1.53

                                                                                                                           Sanders
                                                                                                                                    Sanders
                                                                                                                                    (i°ro) ,
                                                                                                                                    • HTC-fcSS

                                                                                                                                    Sanders
                                                                                         Fish  collected  from  an  effluent
                                                                                  pioe  ol a  stea1"  plant and  troii  offshore
                                                                                  Haters of  Catallna  Island  «ere  analyzed
                                                                                  for trace  element content.   Trace  element
                                                                                  content of  the effluent  water Has  at
                                                                                  least 5 times greater than that  of  normal
                                                                                  sea Hater  for cadmium,  copper,  nickel,
                                                                                  zinc, and  chromium.  Livers  of  fish from
                                                                                  the effluent  were nearly tuice  the  size
                                                                                  of those from the ocean. Greatest
                                                                                  differences in concentration occurred
                                                                                  with  aluminum, cadmium,  and  nickel.
                                                                                  Silver, barium,  I ithiun, and lead shotted
                                                                                  the least  differences.   The  author
                                                                                  concluded  that trace element analysis  of
                                                                                  tissues could be used to determine  the
                                                     AMIC-4S7

                                                     Sand«>-s
                                                     (19731 ,
                                                     AMIC-i.53

                                                     Stanleton
                                                     (196SI,
                                                     AMIC-5980
-------
 N«lyb4«iHM
 Holyttdenu*
Molyb4*nw*
Purnlahrax    FH    Cstallna     0.3(dorsal
clathratus          Island,  Cat.  Muscle
                                  residue)

Paralabrax    FH    Scatterqood  0.2  (ventral
clathratus          Stean  Plant,  Muscle
                    Los  Angeles,  residue)
                    Cal.

Paralabrax    FH    Catallna     0.2tventral
elathratus          Island.  Cal.  ousel*
                                  residue!
                                         effect  of  pollutants on Marine organises.

                                                saae as above



                                                sane as above



                                                sane as above
                                                                      Staoleton
                                                                      (1968).
                                                                      Alloys')

                                                                      Staoleton
                                                                      (146(1).
                                                                      »MIC-'i980


                                                                      Stsoleton
                                                                      (IORI>),
                                                                      AHIC-S9S1
NolyMenu*
Nolybdenu*
Nolybdenm
Nolvbdenue
Paralabrax
clathratus
                                    Fn
Paralabrax    FM
clathratus
Paralabrax    FH
clathratus
IqravM
feaalei:!

Paralabrax    FH
elathratus
                     Paralabrax
                     Clathratus
                                   FH
Scatteraood  0.7  (gonads
Steaa Plant, residue)
Los Angeles,
Cal.

Catallna     O.Stqonads
Island, Cal. residue)
                                          Catallnalsla 0.6
                                          nd,  Cal.      (qonads
                                                       residue)
Scatterqood  0.2 (liver
Steam Plant, residue)
Los Angeles,
Cat.
                    CatalIna
                    Island, Ca
             0.
-------
Comoound Organism
Molybdenum Paml*hrax
clathratus

Molybdenum Paralabrax
clathratus


Holybdenua Paralabrax
clathratus

Honoxone Sal mo
galrdnerl










Hono (N, N dliethyl Phormldlum
alkyl amine) salt of amblquum
Toxielty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Study Location Ppm or Noted Comments
FH Catallna 0.
-------
         Honuron
                              Hercenaria
                              •ercenarla
                              feggs)

                                  greater than
                                  6.0 9>«
                              Cardlu* edule 9S4
CO
10
                                 greater  than  10 a»(contln-          one  hunrtr<«d-forty surface  active
                                 IT3)            UOUs  aer-   agents,  solvent  emulslflers,  pestlci9),
                                                     AMIC-SS^O

                                                     Portmann, et
                                                     a I  (1971),
                                                     Portmann, et
                                                     al J19711,
                                                     »MIC-77D1
        F«s-^^^
Negaorlon
brevlrostrls
(1-3 Kq)
                                            BSA
Z0.9 (SB ID     »,c,e              Data from study of drug effects
•in)                       on younq lemon sharks were treated
                           mathematically to demonstrate
                           aoplIcabl11ty of classical rate theory to
                           the study of chemical shark deterrents.
                           Incaoacltat Ion tnarcosls)  was the orimary
                           parameter timed for effectiveness.  This
                           was usually Quite raold for the more
                           effective drugs.
                                                     Psldrldge
                                                     J1969),
-------
Compound
5-2 2Z
Organism
L«oomls
•acroehlrus
Field Field
Study Location
8SA —
Toxlclty,
Active
Ingredient,
Pom
30 (S81»
Experimental
Variables,
Controlled
or Noted Comments
a.* Little difference In nitrogen
excretion rate Has found between treated
and control fish. Anaesthesia should
Reference
Savltx
(1969) ,AMIC-
5838
Mystox LSC-P
Pasbora       HCFA  ~
heteromorpha  and
              8SA
                   18 (T2.
                   hardwater)
Hystox LSC-l>
Pasbora
heteroworpha
8CFA
•nd
BSA
5.6 (T2,
sortwater)
Nystox LSE-L
                     Sal mo
                     qalrdnerl
              BCFA
              and
              BSA
                                                       36  (T2>
Nystox LSE-P
                     Sal»o
                     ^alrdnerl
              8CFA
              •nd
              BSA
                                                         (TZ)
                           have reduced nltroqen excretion but did
                           not.  The author believed that Increased
                           •ucus secretion was a possible
                           explanation for the results obtained.

                a*,Ct«,ft          One hundred sixty-four            Alabaster
                hiird(NW)    pesticides, netting aqents. and           11969) .AMIC-
                or soft    nlscel laneous water pollutants shotted a   S
-------
         Nystox CSL-L
                               Sal «o
                               qairdnerl
               BCFA
               and
               BSA
                                                                180 (T2I
         Hystox LSL-P
                              Salao
                              galrdnerl
              BCFA
              and
              BSA
                                                                68  (T?)
vn
         NystOX LSL
                              Rasbora
                              heteromoroha
              BCFA
              and
              BSA
8.Z (T2,
hardHater)
         Nystex ISL
                              Rasbora
              BCFA
              and
              BSA
J.5 
-------
  Compound
            Field  Field
Organism    Study Location
Toxielty,
Active
Ingredient,
  Pp«
Experimental
Variables.
Control led
or Noted
                                                                                                  Contents
                                                                                                                           Reference
Nabaei
Nabae>
Naleo
                     Mercenaria
                     mercenarla
                     (larvae)
                     Crassostraa
                     virqlnlca
                     (eqgs)


                     Pasbora       BCFA
                     heteromorpha  and
                                   BS*
                                                       1.75  CT12)
less than 0.5
(T2J
                                                       0.76  ITZI
                bard IHH)
                or sort
Nalce ?«.0
                     Rasbora       BCF»
                     heteromorpha  and
                                   B5A
                                                           (TZ)
                                                                       thotle
                                                                       dilution
                                                                       *imt«r, or
                                                                       flea.ua ter
                                                                       Cor aoiaa
                                                                       ipaolaa
                a*,e,e,r.
                hard (HW)
                or soft
                           development more than  survival.  Some,
                           however,  drastically reduced  larval
                           groxth.   The authors oolnt  out  the
                           necessity of evaluating the effects  of
                           oestlcldes on all  lire stages of an
                           organism  and note the  possibility of
                           selecting chemicals for oest  control  that
                           HOuld not have serious effect on
                           shellfish.

                                 sane as above
                                                                    Oavls. ct al
                                  saae as above
                                                     5930

                                                     Davis,  et  al
                                                                  One hundred sixty—four
                                                          pesticides, wetting agents, and
                                                          miscellaneous water oollutants showed a
                                                          wide range of toxlclfy soannlnq 12 orders
                                                          of magnitude.  Knowing the toxiclty and
                                                          percentage of all components of a
                                                          formulation did not result in easy
                                                          predictability of the toxlcity of a
                                                          mixture of materials.  Sometimes
                                                          pesticides were most toxic in hard water
                                                          and sometimes the opposite was true.
                                                          Testing the actual material as sold was
                                                          found to be essential.

                                                                 same as above
                                                     5990

                                                     Alabaster
                                                     (1969),
                                                     ANIC-5WZ?
                                                     Alabaster
                                                     11969),
                                                                       thatlc
                                                                       dilution
                                                                       «tt«r, or
-------
 N»ICO ?*J
 Ratbora       BCFk
 heteromoroha   and
 Haohthenlc acids     Leoomls       8SA,
                      •i}crochlrus   L
0.28 (T2)       a».c,e,f.
                hard  (HH)
                or
                SOFT(SW)
                synthetic
                dilution
                Mater, or
                seaMater
                for son*
                species

5.6 (T<>>        a«,e, and.
                synthetic
                dilution
                miter
                                                                                         same as abova
                                                                                                                            Alabaster
                                                                                                                            (1969),
Naohthenlc  acids
                      Mltzschla     8SA,
                      linear!*-      L
                                                                     This study Has conducted to
                                                             determine the relative toxlcltles of ?0
                                                             eonaon constituents of Industrial xastes
                                                             to a fish, an alqa, and an Invertebrate.
                                                             The exoerlnents Mere conducted over a
                                                             10-y«ar period for varied purposes.  The
                                                             authors recommend bioassays Mlth at least
                                                             three components of the food Meb.

                                                                    sane as above
Patrick, et
al MQ6*>,
*«C-57?0
Naohthenlc  acMs      Physa         BSA,
                      heterostrapha  L
                                                                                         same as above
N*
                      Fundulus       BSA
                      heteroclItus
»3.1 mi       a»,e, and
                synthetic
                dilution
                water

7.1 ITI>)        *»,e, and
                synthetic
                dilution
                water

D.00018-0.OOOSi, a*.c.e.and         A  laboratory procedure based on
                synthetic  Standard Methods tor 96-hr toxlcity
                seaxater   determinations of  crude oil  and
                           oll-dlspers^nt mixtures Mas  described.
                           The  dlspersants varied  considerably in
                           toxlclfy,  ranqlng  from  0.01  to 7.1  ml/I,
                           TL50 for 96  hr.  These  did not differ
                           Significantly from 2iiO  hr  values.   The
                           dlspersants  Mere deslqnated  as C*«  no,
                           Cl,  00,  AO,  PC,' HM,  TN,  BP.  and NA  with
                           no further description  of  their chemical
                           nature or  source.   Only  a  feM  hloassays
                           Mere conducted xlth  shrimp.  HollusHs and
                           echlnoderms  Mere suqqested as  suitable
                           test animals.  The authors stated that
                           the  method could be  used to  test any
                           product  for  toxlcity in  seaMater.
                                                                                                       Patrick,  et
                                                                                                       a I  <146 ft).
                                                                                                       ANIC-5720
                                                                                                       Patrick
                                                                                                       al  flif.M
                                                                                                       A*IIC-S7?0
                                                                                                                                     et
                                                                                                       La"?oche,  et
                                                                                                       al  (1970),
N*
Hebur on
                     Nereis vlrens BSA
Hercenarla    L
•ercenarla
(e99S)
                                                       0.000007-0.0000  a*,c,e,
                                                       6 (Tl>>           and
                                                                       synthetic
                                                                       seaMater
                                                       less  than  2,
                                                       m»
                                                                                                      la*oche,et
                                                                                                      al  U970),
                                                                                         sane as above
                                   The effect  of  5?  pesticides on    Davis,  et
                           embryonic rfeveIoonent  of  clams and        81(1969),
                           oysters  Mas reported.   Synerqlstlc        AMIC-5990
                           effects  with solvents  were also reported.
                            Most  of the compounds affected
                           development more  than  survival.  Some,
-------
           Compound
              Field  Field
              Study Location
                                                                Toxlclty,
                                                                Active
                                                                Ingredient,
Experimental
Variables,
Control led
or Noted
                                                                                                           Comments
                                                                                                                                    Reference
         Neburon
         Memagon
Mereenarla
•ercenarla
(larvae!

Hercenarla
•ercenarla
(eggs)
                                            L     —
                                                                less  than
                                                                (T12I
                                                                10.0  (T2I
UJ
ro
OO
         Ne>ag<>n
         Meoaycln sul.  None  Inhibited growth of
           •at-forming algae  for more than 2 weeks.
           Cu^Ot*  formulated Hlth certain wetting
           agents was more  toxic than CuSO
-------
 Nlcl<*l sulfate las
 nickel>
 Carclnus
 aaenas
                                    BSA   —
                                                       ?55  CT2I
 Nickel  sulfate (as
 nickel)
Nickel  sulfate (as
nick* I)
                      Cardlua edule BSA   —>
Crsnqon
cranqon
                                    BS*
                                  greater than
                                  $00  (T2J
                                                           (T2I
 water,  and Inorganic,  and organic clericals Mere
 dally      evaluated aqainst  as Many  as  ten varlne
 aolutlon   organisms.   The authors noted that most
 renewal)   Dubtlshed data of  this type deal with
            toxlclty  of chemicals to freshwater
            orqanls*s«

 a«(contln-        One hundred-forty  surface active
 Uoua, aer- aijents, solvent emulsl t l*rs.  oestlcldes<
 atlon,  sea-oolychlorlnated blohenyls,  cure
 water,  and Inorganic,  and orqanlc cheflcals were
 dully      evaluated aqalnst  as many  as  ten ear In*
 solution   organisms.   The authors noted that Most
 renewal)   oubllshed data of  this tyoe deal with
            toxlclty  of chemicals to freshwater
            organisms.

                  saae as above
 *»( contin-
 uous, aer-
 ation,  soa-
 water,  and
 daily
 solution
 renewal)

a»(contin-
uous aer-
ation,  aaa-
water,  and
daily
aolutlon
renewal)
                                                                                         saa* as above
                                                      Portnann, at
                                                      al  Cl<)71>,
                                                      •Mic-rm
                                                      Port»ann,  et
                                                      al  (1S71I,
                                                      AHIC-7701
                                                     Portaann,  et
                                                     al  «1<»71I,
                                                     AMIC-7701
Nickel sulfat*  (as
nickel!
                      Ostrea edulls BS»
                                                       100-150
                                                 •.•(contin-
                                                 uous aer-
                                                 ation, aaa-
                                                 wa.ter, and
                                                 daily
                                                 aolutlon
                                                 renewal)
                                                                                         saa* as above
                                                     Porteann, et
                                                     al  (1971),
                                                     •NIC-7701
Nickel sulfate  (as
nickel)
PandaI us
•ontagul
                                    BSA
                                                       13.9 (T2)
a*( contin-
uous aer-
ation, sea-
water, and
dally
aolutlon
renewal)
                                                                                         saae as above
                                                     Port«ann, et
                                                     al  (14711,
                                                     AMIC-7701
-------
           Compound
            Field  Field
Orqanlsm    Study Location
                                                               Toxlclty,
                                                               Active
                                                               Ingredient,
                                                                 Ppm
                Experimental
                Variables,
                Control led
                or Noted
                                                                                                          Comments
                                                                                                                                    Reference
         Nickel  sulfate (as   Salmo
         NIZ »»us»             qalrdnerl
                              (eqqs and
                              sperm)
                                            BSA
                                                               1.0 (NTE)
                a,c,f              Data were given in mq/l which Has Shan, et at
                           taken to be the equivalent of op*.        (1971),
                           Fertilization rates Here statistically    AMIC-im.1.
                           similar In both test (Cu and Nil and
                           control waters.  The rat* of hatching N»S
                           slqnl f leant I v different for eoqs exposed
                           to Cu and the rate of devel ooi*ent was
                           Increased.  The authors concluded that In
                   ,       hard waters neither Cu nor Nl Is likely
                           to Impair fertilization In rainbow trout.
U)
         Nickel  tulfate (as   Acroneurla    BSA
         Nickel  sultate las   Cphemerella   BSA
         Nil
         Nickel  sulfata  (as   Hydroosyche   BSA
         Nil
         Nickel  suitate (as   Phormldlum    L
         Nil                   amblquum
                                                               33.5 (T*>
                                                               6d (TIM
0.5-10.0 (16
percent growth
lnhlbltedl<»>
                                                                               a*tc,d,eif
                a*tCtdt*tf
                a*tC(d,ef1
         Nickel  (Plus coooer.  Sal BO
         lineI                 galrdnerl
                                            BSA   —
0.5-1.4 (T2)
                                   Ephemerella (mayfly) was the most Warnlck
                           sensitive aquatic Insect of those
                           Studied, and cooper the cno chemicals evaluated as
atqlcldes, only q xere more toxic than
CuSOU.  None Inhibited qrooth of
•at-formlnq alqae for nore than 2 necks.
CuSOU formulated Hlth certain netting
aqcnts Has nor* toxic than CuSO<> alone.
Coooer chlorairlne Has also found to be
• ore toxic than CuSOii.  No nettlnq aqents
were found to be Inhibitory at the
concentrations Investlqated (D.05 and
0.005 oonl.  Also reported are factors
affectlnq qronth of alqae In canals to
determine whether there Her* leads to
controlling alqae by environmental
•anaqenent.  No practical environmental
means were found.
                                   RalnbOH trout Here exposed to     8ro»n,»t al
                           copper, phenol, zinc, or nickel solutions (1970),
                           to determine 1.8-hour LCSO values for      ANIC-S99*
-------
 Nickel
                      Coreqonus     FL    Moos* Lake,  0.2 (residue)
                      elupeaforals        Can.
£
u>
 Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
                      Fsox  luclus    FL
                      Esox  fuclus   FL
                      Esox  luclus   FL
                     Osaerus       FL
                     aordax
                     Perca         FL
                     flavescens
                     Coreqonus     FL
                     cluoeaformls
                              Paralabrax    FH
                              clathratus
                                          Moose Lake,   0.2 (residue)
                                          Can.
                                          Lake  St.      0.2  (residue)
                                          Pierre, Can.
                                          Lake  Erie.    0.2  (residue)
                                          Can.
Lake Erie.   O.Z (residue)
Can.
                                                  Lake  Erie.   0.2  (residue)
                                                  Can.
Lake         0.? (residue)
Ontario,
Can.

Scattergood  5 (dorsal
Steam Plant, Muscle
LosAnqeles,  residue)
Cat.
                                                                                           Mixtures of  copper and phenol 1  copper,
                                                                                           zinc?  and phenol I  and copper• zinc,  and
                                                                                           nickel.   It  was concluded that  acute
                                                                                           lethal  toxlclties  of  the elxtures could
                                                                                           be adeauately described by summations of
                                                                                           the fractional toxlclties.

                                                                                                   Concentrations of 13  toxic
                                                                                           elements In  dressed fish from heavily
                                                                                           Industrialized and non-Industrialized
                                                                                           ureas  were determined.  Only  mercury
                                                                                           exceeded regulatory limits, and
                                                                                           concentrations of  most elements were
                                                                                           essentially  the same  in fish  froa both
                                                                                           areas.

                                                                                                  saae  as above
                                                                                         same  as  above
                                                                                         saae  as  above
                                                                                        same  as above
                                                                                        same as above
                                                                                        same as above
                                                Fish collected from an effluent
                                        pioe of a steam plant and from offshore
                                        Haters of Catatlna Island Here analyzed
                                        for trace element content.   Trace element
                                        content of the effluent water Has at
                                        least 5 times greater than  that of normal
                                        sea Hater for cadmium, coooer, nickel,
                                        zinc, and chromium.   Livers of fish froa
                                        the effluent Here nearly twice the size
                                        of those fro* the ocean. Greatest
                                        differences In concentration occurred
                                        Kith atunlnum, cadalua, and nickel.
                                                                                  Othe.et at
                                                                                  (1971).
                                                                                  AMIC-3819
 Uthe, et  al
 (1971),AMIC-
 3819

 Uthe, et
 • LU971I,
 4HIC-3I19

 Uthe, et al

 3819

 Uthe, et al
 (1971),AHIC-
 3819

Uthe. et al
 C1971),AMIC-
 3819

Uthe.et al
 (19711,
AMIC-3819

Staoleton
 (1968),
AMIC-5980
-------
Cecoound

Mich*!
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Organise

Pars! »t>rax
elathratus
Paratabrax
clathratus
Paratabrax
elathratus
Paralnbrax
el athratus
Paralatirax
clnthratus
Paralahrax
cl athratus
(gravid
females)
Paralabrax
cl athratus
Paralabrax
cl athratus
Paralabrax
el athratus
Field
Study

FH
FM
FM
FM
FN
FM
FN
FN
FH
Field
Locat Ion

Catal Ina
Island. Cat.
Scatter qood
Steam, Plant,
Los Angeles,
Cal.
Catal Ina
Island> Cal*
Seatterqood
Steam Plant,
LosAngeles,
Cal.
Catal Ina
Island, Cal.
Catal Ina
Island, Cal.
Scatterqood
St«an Plant,
LosAngeles,
Cal.
Catal Ina
Island, Cal.
Scatterqood
Steal* Plant,
LosAnqelcs,
Toxlcity,
Active
Ingredient,
Pp»

6.. 7 (gonads
residue)
72.2 (gonads
residue)
8.6
(gonads
residue)
3.9 (liver
residue)
7.6 (liver
residue)
9 (Integuaent
residue)
Experimental
Variables,
Controlled
or Noted Comments
Silver, barlue, lithium, and lead shooed
the least differences. The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on narlne organisms.
sane as above
~ sane as above
~ sane as above
~ sane as above
-- saae as above
— sane as above
-- same as above
same as above
— sa«e as above
Pelerence

Staoleton
IIS^I,
AMIC-5980
Staoleton
<19<-!O,
MIC-5983
Staoleton
<1<>6M,
»MIC-S9SO
Staoleton
(1968),
ANIC-«;980
Staoleton
I1»6M ,
AHIC-5980
Stapleton
(19681 .
AHIC-5980
Staol eton
(I960.
AMIC-S980
Staoleton
(196d).
ANIC-5980
Staoleton
(1968) .
AHIC-5980
-------
U)
U>
         Nickel
         Nickel
         Nickel
         MICH*I
         Nickel
         Nickel
                               Rural ahrax
                               clathratus
                               Paralabmx
                               clathratus
                               Paralabrax
                               clathratus
                               Paratabrax
                               clathratus
                              Paralabrax
                              elathratus
                              Sal no
                              qalrdnerl
                                             FM
                                             FH
                                            FN
                                            FH
CatalInn
Tsland> Ce
in.2
I Integument
residua)
Stuoleton
(1968),
Scatterqood  A.I  fheart
Steae Plant, residual
LosAngeles,
Cat.

Cat a Una     10.8  (heart
Island. Cat. residue)
Scatter good  6.<> (eyeball
Steam Plant, residue)
LosAngeles,
Cal.
CatalIna
Island, Cal.
                                            BS»
33.? (eyeball
residue)
                                                                3?.0
         Nicotine
                              Negaorlon
                              brevlrostrls
                              (1-3 kg.)
                                            BSA   ~
                                                               31.  (SB)
         Nicotine
                              Labeo rohlta  L     —
                                                               1.0  (SB7)
                                                                     Stsoleton
                                                                     (1968),
                                                                     •MIC-59SO
                                                                     Staolcton
                                                                     (1<9S8) ,
                                                                     AMIC-5980

                                                                     Staoleton
                                                                     (19^8),
                                                                     AHIC-59SO
Staoleton
(1968).
                                                                                                  saae as above
                                                                                                  same as above
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                  same  as above
                             a,c,e              RalnboM trout Mere exposed to     Broun, et al
                                        eoooer, phenol, zinc, or nickel solutions (1970),
                                        to doternilne fc«-hour LCSO values for      AHIC-599«>
                                        mixtures of cocoer an4 Dhenoti copoer,
                                        zinc, and ohenoli an.4 cooper, zinc, and
                                        nlcKel.  It Mas concluded that acute
                                        lethal toxlclties of the mixtures could
                                        be arteauately described by summations of
                                        the fractional toxlclties.

                             a,c,e              Data from stud/ of drug effects   Baldrldge
                                        on younq tenon sharks Nere treated        (1959),
                                        mathematically to demonstrate             3S3?
                                        aoollcahlllty of classical rate theory to
                                        the study of chemical shark deterrents.
                                        Incanacltat Ion (narcosis)  MAS the primary
                                        parameter timed for effectiveness.  This
                                        was usually quite rapid for the more
                                        effective drugs.

                             a.d.e.t            This experiment showed that       Konar
                                        nicotine could be successfully used to    (1970),
                                        llve-esotur* fish from reservoirs.  Fish  »MIC-S">35
                                        surfaced and recovered rapidly when
                                        placed In freshwater.  Fish remaining In
                                        test solutions above <» pom did not
                                        recover.  This chemical  Has considerably
                                        less toxic to the aquatic  Insects
                                        studied.
-------
CO
Comoound
Nicotine

Nlcotln*

Nicotine


Nicotine



Nitric acid








Nitric acid






Nitric acid






Field Field
Organism Study Location
Punt 1 us L —
soohore
Panatra L — -
fltlformls
Dytlscus so. L


Hataropnaus- L
tea rossllls


Agonus BSA ~
cataohractus







Asterlas BSA —
rubens





jCarcinus BSA —
•aenas





Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
1.0 (SB7) a,d,e,f same as above

tO (NTE7) a.d.e.f same a* above

<>00 (NTE7I a,d,e, f same as above


3.2 (SB 5 hr>, — . epidermal lesions of catfish
K in hrl barbels Here moderate to s»v»re after
exoosure noted. Rarbel curling and
Inactlvatlon Here associated effects.
100-330 (T2) a*(eontln- "ne hundred-forty surface active
uoua aar- agents, solvent emutslfiers, oestlcldes.
atlon, sea- POlych lorinated blohenyls, pure
water, and Inorqanlc, and organic chemicals Here
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) oubllshed data of this tyoe deal xith
toxlclty of chemicals to freshwater
organisms.
100-330 (T2> a»(contln- same as above
uous aer-
ation, sea-
water, and
dally
solution
renewal)
180 (T2I a»(contln- sa.e as above
uoua aer-
ation, sea-
water, and
dally
solution
renewal)
Reference
Konar
i«c-Usn
Konar
(19701,
Konsr
(1970) ,
AMIC-5U35
Konar (1969),
AMIC-57?f,


Portmann, et
al (1971).
AMIC-7701






Portmann, et
el (1971),
AMIC-7701




Portmann, et
al
(1971), AMIC-
7701



         Nitric acid
                              Cardlum edule BSA
                                                               330-1000 (T2)   «*
-------
i>9
ErlcKson, et
al (197(1),
ErlcKson, et
al (1970),
FrlcKson, et
al (1970),
*MIC-i.<.9
Nltrllotrlae
etlc acid
Erlckson, et
al (1970),
ErlcVson, et
al (1970),
Erlckson, et
al (1970),
Srlckson, et
al (1970),
-------
Field Field
Compound Organism Study Location
Ml trofurazone Hercenarla L —
•ercenarla
(egqs)
Toxlclty,
»ctlv«
Ingredient,
Pom
greater than
100.8 CTZ)
Experimental
Variables,
Control l*d
or Noted
Consents
— The effect of
embryonic development
oysters was reported.
52 pesticides on
of clans and
Synerqistle
Reference
Davis, et i
(1969),
4MIC-5990
>
         Ml trofurazone
         Nltroqen
         (dissolved)
Nercenarla
•ercenarla
(larvae)

Oneorhynchus
tshauytscha
(Juveniles)

              FR.BS Priest
              CH    Rapids Dam,
                    Mash.
                                                                greater  than
                                                                100.D  (T12>
             Super
             saturation
         HI tro?en
         Cdltsolved)
         Nitrogen
         (dissolved)
Salmo
qalrHnerl
(adults)

Oneorhynchus
klsuteh
<|uvenlles)
F«,
BSCN
                    HcNary Oaa,
                    Hash.
Priest
RapldsDae,
Mash.
             Supersaturatlon
             (NTE 35»
                                 Super
                                 saturation
                                 16-16 percent
                                        effects with solvents were also reoorted.
                                         Host of the compounds affected
                                        develoceent more than survival.  Soae,
                                        however, drastically reduced larval
                                        qrowth.  The authors point out the
                                        necessity of evaluatlnq the effects of
                                        pesticides on all  life staoes of an
                                        oraanlsK and note  the oossibllity of
                                        selecting chemicals for oast control that
                                        MOuM not have serious effect on
                                        shellfish.

                                               same as above
                                                      The nltroq»n qas regime In the
                                              Colunbla River Mas studied  in 1966 In
                                              order to determine whether  hlqh levels of
                                              dissolved nltroqen nlqht be responsible
                                              for losses of adult salaon  and poor
                                              production of young fish at spawning
                                              channels,  examinations of  dead (uvenlla
                                              salmon revealed that most fish had
                                              symntoms of "qas bubble disease".
                                              Juvenile saloon Keot at sufficient depth
                                              to compensate for the Supersaturatlon of
                                              dissolved nitrogen were free of symptoms
                                              of qas bubble disease.  Fish under stress
                                              fro* the Supersaturatlon of dissolved
                                              nltroqen were very Intolerant to
                                              temperature Increases.

                                                     saae as -above
Davis, et al
(1969).
•HIC-599D

Ebel (1969
AHIC-6198
                                                                   sa*e as above
                                                                                        Ebel  (1969).
                                                                                        •NIC-6198
Ebel (1969)t
•NIC-6198
-------
U)
co
-j
          Nitrogen
          (dissolved)
          HI,  Cu,  Cr,  CN,
          Zn (••stenater)
                      Oneorhynchus
                      nerka
                      (adults)

                      Pln«>ohales
                      prone I as
                                             FR
                     McNary  Oam,
                     Hash.
              BSACF Grand  River
              (ML)  at Wyoming,
                    Michigan
Nl, Cu, Cr, CM. and  CatostomuS
Zn IwasteMater)      commersonl
Nonyl phenol 1?
(olus ethylene
oxide)
         Nonyl ohenol 12
         (Dlus ethylene
         oxide)
Carclnus
•aenas
                                             BSACF Grand River
                                             (HL)   atiiyoalng,
                                                   Michigan
                                   BS»   —
                                                       Suoersaturatlon
                                                       (SB35)
                                                                                                  same as above
                                                       •oprox.  1.67
                                                       percent  (T3)
                                                       between
                                                       1.35-3.75
                                                       percent (T3)
                                                      greater than
                                                      100JT2)
                              Cardlua edule 8S»
                                                                92.6  CT2)
                                                      fbel
                                                      AMIC-619S
a,c,e, con-         A  mobile  bloassay  unit  was
ductlvity, utilized to  conduct  this study  or
NifCUfCr,  municipal  Mastmater containing the
CN, and Zn indicated  toxicants. River  Mater «»i
           used as  diluent.  The conclusion Mas
           reached  that synerglstlc or  additive
           toxic effects occurred since toxlelty  was
           greater  than that of any of  the Ions
           singly.
71IIIch
(1969),
                                                 a,cte,  con-
                                                 ductivity,
                                                 Hl.Cu.Cr,
                                                 CH, and Zn
                                                                                                  save as above
a*(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
                                                                       a«(contin-
                                                                       uous aer-
                                                                       ation,  aea.
                                                                       water,  and
                                                                       daily
                                                                       •olution
                                                                       renewal)
        One hundred-forty surface active
agents, solvent enulsifiers, pesticides,
polychlorlnated blphenyls. Pure
Inorganic, and organic chenlcals were
evaluated against as many as ten marine
organisms.  The authors noted that most
published data of this type deal with
toxlelty of chemicals to freshwater
organisms.
       saee as above
                                                                                                                            <1969>,
                                                                                                                            1NIC-2906
Portpsni.et
al
                                                                                                      Portmann. et
                                                                                                      al
                                                                                                      (1971),AMIC-
                                                                                                      7701
         Monyl phenol 12
         (plus ethylene
         exlde)
                     Crangon
                     crangon
                                            8S»
                                                               89.5  (T2)
                                                 a»(eontin-
                                                 uoui, aer-
                                                 ation, aea-
                                                 wator, and
                                                 dally
                                                 •olution
                                                                                                  ••••  as  Move
                                                                                                                           Portnann. et
                                                                                                                           al
                                                                                                                           (1971),MIC-
                                                                                                                           7701
         Nonyl  phenol 12
         (plus  ethylene
         exide)
                     PandaIus
                     •ontagul
                                            BS«   —
                                                               19.3  (T2)
                                                 at (contin-
                                                 uous, aer-
                                                 ation, a«a-
                                                                                                 se»e as above
                                                                                                                           Pertnann, et
                                                                                                                           al
                                                                                                                           (19711.AHIC-
-------
            COB-pound
                                 Orqanlsa
Field  Field
Study location
Toxlcity,
Active
Ingredient,
Experimental
Variables,
Controlled
or Noted
Comments
                                                                                                                                     Reference
                                                                                water, and
                                                                                daily
                                                                                solution
                                                                                renewal)
                                                                                        7781
          More*
                               Gammarus
                               faselatus
                                             BSA   —
                                                                1.* mi
U)
          Norseman
                               Cranqon
                               crangon
                                             BS*   —
                                                                3.3-10 (TO
                               Pasbora       BCFA  —
                               hateroaorpha  and
                                             BSA
                                                                     ITZ)
          N*H 1113
                               Rasbora       BCFA  —
                               heteroaorpha  and
                                             BSA
                                                                11 U2I
                                   a*(contin-
                                   uous aer-
                                   ation, sea-
                                   water, and
                                   dally
                                   solution
                                   renewal)
                                   a»,c,e,f,
                                   hard (HH1
                                   or
                                   SOFTCSHI
                                   synthetic
                                   dilution
                                   •ater, or
                                   seaiiater
                                   for
                                   SOBC
                                   spec 1e s
                                   a*,c,e,f,
                                   hard (HM)
                                   or soft
        Of  the aquatic urns herbicides    Sanders
evaluated,  Olclone  was the most toxic,      (1970),
Daphnta was generally the most sensitive  »HIC-*55
orqanisn.   All of the Crustacea Here
affected by much  loner concentration
levels of herbicides than indicated by
the TL sub  50 values.  All of the aniaals
represent important lood chain links.

        One hundred-forty surface active  Portaann, et
aqents, solvent enulslflers,  pesticides,  al  (1971).
•polychlorInated blph*nyls» pure           ANIC-7701
Inorqanlc,  and organic cheaicals Here
evaluated against as many as  ten narlne
ornanisms.   The authors noted that Most
published data of this type deal with
toxlcity  of chenicals to  freshwater
orqanlsns.

        One hundred sixty-four            Alabaster
pesticides, Hettlnq agents, and           (19591,
•iscellaneous Hater pollutants showed a   AMIC-51Z5
• He ranqe  of toxlcity soanninq 12 orders
of  aaqnltude.  Knowing the toxicltr and
percentage  of alI components  of a
fomulatlon did not result in easy
predictability of the toxlcity of a
mixture of  Materials.  Sometimes
pesticides  Mere most toxic in hard nater
and sometimes the opposite was true.
Testing the actual  aaterlal as sold «as
found to be essential.
                                                                                    _
                                                                                synthetic
                                                                                dilution
                                                                                •afar,  or
                                                     sane as above
                                           Alabaster
                                           (19691,
-------
              1313
Rasbora       BCFA
heteromorpha  and
              BSA
                                                                5.0 ITZI
          HueIdol  dlazlnon
          she«p dip
Rasbora       BCFA
heteromorpha  and
              BSA
                                 l.M ITU
NO
                                                  seawater
                                                  for  some
                                                  species

                                                  «*,C,e,f.
                                                  hard (H¥)
                                                  or soft
                                                  (SU)
                                                  thetlc
                                                  dilution
                                                  Mater, or
                                                  ••mutter
                                                • for'aome
                                                  •peelea

                                                  *«,c,8,r,
                                                  h»rd (HW)
                                                  or aoft
                                                  ISUJ
                                                  thatle
                                                  dilution
                                                  water, or
                                                  seawator
                                                  for  aome
                                                  apoelaa
         Hystatln
                                            I     —
                                                                B.5-10.0  (NTE>   —
                               aablquua
         N-»«thvt carbaaata
         darlvltlva
Rasbora       BCFA
heteromorpha  and
              BSA
                                                                0.58  (TZ>
                                                                                hard  (HHt
                                                                                or  soft
                                                                                (SW)
                                                                                synthetic
                                                                                dilution
                                                                                •at*r,or
                                                                                •aaHatar
                                                                               .for tea*
                                                                                                  saaa as above
                                                                                                                                     Alabaster
                                                                                                                                     (1969).
                                                                   saaa as above
                                                                                                      Alabaster,
                                                                                                      (19691,AMIC
                                                                    Of  Tit  chenlcals  evaluated  as     Otto
                                                            alqleld*s<  only  9 Here more  toxic  then   AHIC-892
                                                            CuSOd.   Non«  Inhlbltel qroMth  of
                                                            mat-fornlnq algae for more  than ?  necks.
                                                            CuSOU  formulated Mlth certain  wetting
                                                            aqents  Has  more  toxic than CuSOlt alone.
                                                            Conner  chloranine Mat also  found to  be
                                                            • ore  toxic  than  CuSO<>.   No netting aqents
                                                            Mere  found  to  be Inhibitory  at the
                                                            concentrations Investigated  (0.05  and
                                                            O.nns ppnl.  Also reported are factors
                                                            affecting growth of  alqae In canals  to
                                                            detemlne Mhether there  Mere leads to
                                                            Controlling algae by environmental
                                                            aanaqenent.  No  practical environmental
                                                            •eans Here  found.

                                                                    One hundred  sixty-four            Alabaster
                                                            Pesticides, wetting  agents,  and           (1969),
                                                            •iscellaneous  Mater  pollutants showed  a   AHIC-5«2S
                                                            Mlde range  of  toxlclty spanning 12 orders
                                                            Of aaqnltude.  Knowing the toxiclty  and
                                                            percentage  of  all  components of a
                                                            formulation did  not  result In easy
                                                            predictability of  the toxlclty of  •
                                                            •ixtura of  materials.  Sometimes
-------
  Compound
                       Organls*
                                   Field  Field
                                   Study Location
                                 Toxlclty,
                                 Active
                                 Ingredient,
                                   PPM
                Experimental
                Variables.
                Control led
                or Noted
                                                                                                  Consents
                                                                                                                            Reference
H-351V
                     Crassostrea
                     vlrglnlca
                     feqqsl

Crassostrea
vlrglnlca
(larvae)

Mercenarla
mercenarla
(eggs)
                                 less than 0.5
                                 IT2)

                                                       less than 0,9
                                                       • Tli.)
                                                       less than l.D
                                                       ITZ)
                species    pesticides w<>re most toxic In hard Hater
                           and sometimes the ooooslte Mas true.
                           Testing the actual material  as sold xas
                           round to b<> essential.

                -—                 The effect of "!Z pesticides on
                           embryonic development of clans and
                           oysters was reported.  Synerqlstlc
                           effects with solvents were also reported.
                            Most of the comoounds affected
                           development more than survival.  Some,
                           hoxever, drastically reduced larval
                           growth.  The authors point out the
                           necessity of evaluating the effects ot
                           pesticides on all life stages of an
                           organism and note the oosslblllty of
                           selecting chemicals for pest control that
                           would not have serious effect on
                           shellfish.

                                  same as above
                                                                                         same as above
Davis, et al

<1969),A1IC-
5998
                                                                     Davis, et
                                                                     al 11969),
                                                                     AMIC-5990

                                                                     Davis, et al

                                                                     (19691 .AHIC-
                                                                     5990
M-J5I*
Oetyl phenol 11
lotus ethylene
oxide)
Nercenarla
•ercenarla
IIarvael

Crassostrea
vlrglnlca
(eggs)

Crassostrea
vlrglnlca
(larvaet

Caretnut
•aenM
                                   L     —
                                   BSA   —
                                                       less than 1.0
                                                       (Tl?)
                                                       less than l.D
                                                       IT2I
                                                       less than  1.0
                                                       (Til.)
                                                                                         sane as above
                                                                                         same as above
                                                                                         same as above
greater thanlOO a*                 One hundred-forty surface active
(TZI            (eontlnuou agents, solvent emulslflers, pesticides,
                %          polychlorlnated blphenyls, pure
                aeration.  Inorganic, and organic cheelcals were
                seawater,  evaluated against as many as ten marine
Davis, et
al(l969),
AMIC-59°5

Davis, et
81(1969),
AHIC-599B

Davis, et
8111969).
AMIC-5990

Portmann,et
al  (1971),
AHIC-7701
-------
         Oetyl phenol 11
         (plus ethylene
         exldel
                              Card I urn edule 85*   —
                                  19.6ITZ)
                                                                                and  dally   organisms.   The authors  noted that most
                                                                                solution    published  date of  this type  deal  Kith
                                                                                renewal)    toxlelty of  chealcals to freshwater
                                                                                           organism*.
 a,* (contin-
 uous aer-
 ation,  sea-
 water,  and
 daily
 solution
 renewal)
                                                                    same as above
                                                                                                       Portnann, et
                                                                                                       al(1971l,
                                                                                                       ANIC-7701
         Oetyl phenol 11
         (plus ethylene
         oxld*)
Crangon
erangon
                                            BSA   —
                                  63(Tt)
f
a«( contin-
uous, aer-
ation, sea-
water, and
dally
solution
renewal)
same as above
                                   Porteann, et
                                   al(1971),
                                   AMIC-7701
         Octvl  phenol  11
         (plus  ethylene
         oxldet
Pandatun
•ontagul
                                            BSA   —
                                                               10.B (TZI
a«( contin-
uous, aer-
ation, sea-
water, and
dally
solution
renewal)
                                                                                                 same as above
                                   Portwann, et
                                   al«t971),
                                   AMIC-7701
         Oetyl  phenol  11
         (plus  ethylene
         exldel
Platlethys
flesus
              BSA   —
                                 33-100 (T2I
a»(contin-
uous, aer-
ation, sea-
water, and
dally
solution
renewal)
                                                                   same  as above
                                   Portmann,  et
                                   at
                                   C1971)tA«IC-
                                   7701
        00
                              Fundulus
                              heteroelItus
                                            BSA   —
                                 0.0005 ITfcl     a*,Cte,             A  laboratory  procedure  based  on
                                                 and         Standard Methods  for  9S-hr  toxlelty
                                                 synthetic   determinations of  crudp  oil  and
                                                 seaHater    oll-dlspersint mixtures  was  described.
                                                             The  dlspersants varied considerably  In
                                                             toxlcityt  ranging  from 0.01  to  7.1 ml/I,
                                                             TL50 for 96  hr.  These did not  differ
                                                             significantly  from ?i»0 hr values.  The
                                                             dlsoersants  Here  designated  as  CX, 00,
                                                             Cl,  00,  AO,  PC, MM, TN,  BP,  and NA with
                                                             no further description of their chrnlcat
                                                             nature or  source.   Only  a Tex bloassays
                                                             were conducted Mlth shrimp.  HollusKs and
                                                             echlnoderms  Ner* suggested as suitable
                                                             test animals.   The authors stated that
                                                             the  method could  be used to  test any
                                                             product  for  toxlelty  In  seaxater.
                                                     LsRoche.et
                                                     al (1970),
                                                     AHIC-H5
-------




Comoound
00



Oil herder









Toxlclty,
Active
Field Field Ingredient,
Organism Study Location Ppa
Nereis vlrens 8SA — 0.0001^-0.0009*
(T*>


Cranqon BSA — 3300-10,000
cranqon (T»)








Experimental
Variables,
Control ltd
or Noted Comments
a*,c,e, same as above
and
synthetic
seanater
*»(eontin- one hundred-forty surface active
UOUS aer- aa»nts, solvent emulslf lers, pesticides.
atlon, aoa-pol ychlorlnated blohenyls, pure
vater, and inorganic, and organic chevlcals w«re
daily evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms.




Reference
LaRoche,et
al (1970),
ANtC-»«.S

Portmann, at
al (1971),
AMIC-7701






         Oil (crude)
                              Palaemonetes  BSA   —
                              vulgarls
                                  greater  than
                                  1.0  (TM
a*,c,e,
and
synthetic
seaiiater
ru
         Oil Icruda oil Bl    Fundulus      BS»
                              heteroelltus
         Oil (crude oil 81    Nereis vlrens BS»
         Oil fr •fined)
        0«az«ne
                              Pataeeonetes  8S»
                              vulgar Is
Hercenarla
•ercenarla
                                  0.0083 (T4>
                                                               0.0061 (TV)
                                                               0.00005 IT*)
                                                  a*,c,e,
                                                  and
                                                  synthetic
                                                  seawafer

                                                  a*,c,e,
                                                  and
                                                  synthetic
                                                  seaMater

                                                  a*,c,e,
                                                  and
                                                  synthetic
                                                  seaitater
        A laboratory procedure based on
Standard Hethods for 96-hr toxlclty
determinations of erule oil an
-------
U)
         Oaazene
         Omazene
         Oaazene
Mercenarle,
aereenarla
(larvae)
Crassostrea
vlrglnlea
(eggs)
Crassostrea
vlrqlnlca
(Inrva*)


         Orthodlehlorobenten* Her can aria
                              aercenarla
                              (egos)
                                                                0.3*  (T1Z)
                                                                0.07S  (T2>
                                                               0.3*  (Tilt)
                                 greater titan
                                 100.D IT2)
         Orthodlchlorobentene Hercenarla
                              aercenarla,
                              (larvae)
         0>lne-cop»er
Sal BO
galrdnerl
                                            L     —
• CM
and
65*
                                 greater than
                                 100.0 (Tit)
                                                               0.1* (Til
                                                                                            Most  of  the compounds  affected
                                                                                          devetocaent  nor*  than survival.   Some.
                                                                                          however,  drastically reduced  larval
                                                                                          growth.   The authors oolnt  out  the
                                                                                          necessity of evaluating the effects  of
                                                                                          pesticides on all  life  stapes of  an
                                                                                          organ Is*  and note the possibility of
                                                                                          selecting cheelcals for pest  control  that
                                                                                          would  not have serious  effect on
                                                                                          shellfish.

                                                                                                 saae  as above
                                                                                                                                    Oavlst  et  al
                                                                                                  saae  as  above
                                                                                                 sane  as ahove
                                                                                        5990

                                                                                        Davis, et al

                                                                                        C1969),»1IC-
                                                                                        5990

                                                                                        Oavlst et al

                                                                                        (1069). »MIC-
                                                                                        5990
                                                                                        Davis, et
                                                                                        (1969),
                                                                                        »HIC-599D
                                                                                                                                              al
                   The effect of 52 pesticides on
           embryonic development of clams and
           oysters Mas reported.  Synerqlstlc
           effects with solvents were also reported.
            Host of the compounds affected
           develocaent more than survival.  Some.
           however, drastically reduced larval
           growth.  The authors point out the
           necessity of evaluating the effects of
           pesticides on all life stages of an
           organism and note the possibility of
           selecting chemicals for pest control that
           Mould not have serious effect on
           shell fish.

                  saee as above                      0«vls, et al
                                                     (1969)t
                                                     ANIC-5990

a*,c,e,f.          One hundred sixty—four            Alabaster
hard CHM)  pesticides. Netting agents, and           (1969),
or soft    miscellaneous Mater oollutants showed a   AMIC-S»?S
(SMIsynthe wide range of toxtclty spanning 12 orders
tic        of magnitude.  Knomlng the toxlcitv and
dilution   percentage of all component* of a
Hater, or  formulation did not result In easy
-------
  Compound
                       Organise
              Field
              Study Location
                   Toxiclty,
                   Active
                   Ingredient,
                     Pom
                                                                      Experimental
                                                                      variables.
                                                                      Cantrolled
                                                                      or Noted
                                                                                                 Comments
                                                                                                                          Reference
                                                                      seawater
                                                                      for some
                                                                      species
Oxygen
Leooals
eacrochlrus
              BCF   —
                   0 to saturation  »«••
                   (S8«>
o-dlchlorobenzene
(58 oereent plus ?0
percent crescyllc
acid)
Aasbora
heteromorpha
BCF*
and
8SA
                                 9.1  ITZ)
o.o-dlethyl o-?
pyrazinyl
pnosPhorothlate
Rasbora       BCF*
neteroeorpha  and
              BS*
                                                 hard (HH)
                                                 or
                                                 SOFTJSH)
                                                 synthetic
                                                 dilution
                                                 water,
                                                 orseawater
                                                 lor son*
                                                 species
                                                 a*«c,e,t,
                                                 hard (HH)
                                                 or soft
                                                 (SHI
                                                 synthetic
                                                 di lution
                                                 Hater,  or
                                                 seanater
                                                 for so»e
                                                 specie*
                                                            predictability of  the  toxlclty of a
                                                            mixture  of  materials.   Sometimes
                                                            pesticides  Mere most toxic  in hard Mater
                                                            and soaetlmes  the  opposite  was true.
                                                            Testing  the actual  material  as sold was
                                                            found  to be essential.

                                                                    Fish 15-29 c«  long  Mere exposed   Burton
                                                            to  gradual  hypoxla stress to determine    (1970),
                                                            the effect  on  skeletal  muscle and  liver   AMIC-63«5
                                                            lactate  and oyruvate.   Tests were
                                                            conducted at S and 20  C with DO reduced
                                                            froa saturation to zero over an 8-hour
                                                            period.  Low DO Increased lactic acid
                                                            concentrations in  muscle and liver at
                                                            both temperatures! pyruvlc  acid  levels
                                                            remained constant. Lactic  acid  levels
                                                            Mere higher at 5 C than at  to C, and  fish
                                                            Mere better able to tolerate low oxygen
                                                            levels at the  lower temperature.

                                                                    One hundred sixty-four            Alabaster
                                                            pesticides, wettlnq aqents, and           (1969).
                                                            miscellaneous water pollutants showed *   AMIC-5W5
                                                            Mlde ranqe of toxlclty spanning 12 orders
                                                            of  magnitude.   Knowing the toxlcity  and
                                                            percentage of all  components of  a
                                                            formulation did not result  in  easy
                                                            predictability of  the  toxlcity of  a
                                                            mixture of  materials.   Soaetlnes
                                                            pesticides Mere most toxic  in  hard water
                                                            and sometimes the  opposite was true.
                                                            Testing the actual material as sold mas
                                                            found  to be essential.
                                                                                        same as above
                                                                                        Alabaster
                                                                                        (1969),
-------
          Paraouat-di
          (eethyi)  chloride
Ratbora       BCF*  —v
heteroaorpha  and
              US*
         Paraauat
                               Chara sp
                                                   Jeffarson
                                                   Count»•»
                                                   Colo.
                                                                32 «T2»
                                                 •*,c,e,f,h
                                                 ard  (HM>
                                                 or soft
                                                                                                  saae as abova
                                                                1.1MK16I
                                                 synthetic
                                                 dilution
                                                 Mater, or
                                                 seanater
                                                 for soaa
                                                 species

                                                 a,c,d,e,g,
                                                 and Hater
                                                 stage
                                                                     Alabaster
                                                                     tl969»,»1IC-
                                                                     5*25
                                                                    Paraauat almost eliminated Chara
                                                            sp. In 16 days and gave Initial control
                                                            of Solroqyra so.  The latter recovered
                                                            Hi thin 3 aos.  Fish deaths  and other
                                                            effects occurred within 1.6 Kr.  Paraquat
                                                            Mas recovered froe aud 99 days after
                                                            application* Indlcatlna that this
                                                            herbicide can be very persistent.  This
                                                            study xas conducted In 196%.  Llvecar
                                                            exposure of some fish Has one technique
                                                            employed.
                                                                     Earnest
                                                                     (1971),
                                                                     4M.IC-5S6*
\JI
         Pareauat
         Paraauat
         Paraouat
         Paraauat
         Paraauat
                               Mater          FL
                               (botteal
                               Mud
                                             FL
                               Splroqyra  sp   FL
                               Chara  sp      FL
                               Splroqyra  sp  FL
                    Jefferson
                    County.,
                    Colo.

                    Jeffarson
                    County.,
                    Colo.

                    Jefferson
                    County.,
                    Colp.

                    Jefferson
                    County.t
                    Colo.

                    Jefferson
                    County.,
                    Colo.
1.1% (1.5 ppn   •,c,d,e,9,
aax residue!    and Hater
hrl             stage
                                                                1.14 115.9 ppa
                                                                •axresldue 16
                                                                residua 164)
                a,c,d,e,q,
                and Hater
                stage

                a.c.d.e.g.
                and Hater
                stage

                a,c,d,e,g,
                and Hater
                                                                l.l«i  (2300 ppa
                                                                aax tissue
                                                                raaldua 8d)
     (1300 ppa  a,c,d,e,g,
    tiaau*      and Hater
realdn* lul)   » stage
                                                                                                  sane as above
                                                                                                  saae as abova
                                                                                                  sane as above
                                                                                                  sa*e as abova
                                                                                                  saae as abova
                                                                                                      Earnest
                                                                                                      tl971),»MIC-
                                                                                                      556%

                                                                                                      Earnest
                                                                                                      (19T1J,
                                                                                                      •KIC-556%

                                                                                                      Earnest
                                                                                                      (19TU,
                                                                                                      •HIC-S56*

                                                                                                      Earnest
                                                                                                      (197H,
                                                                                                      •HIC-556*

                                                                                                      Earnest
                                                                                                      (19711,
                                                                                                      AHIC-55M
         Paraquat
         Paraauat
                               KaInbox trout  FL
Channel       FL
catfish
Jefferson
County.,
Colo.
Jefferson
County.i
Colo.
1.1 (1.9ppa Max a,c,d,e,g(
tlaaue 1 . and Hater
raaldua Id) stage
1.1 (1.3 ppa a,c,d,a,gt
•ax and Hater
tlaaue 1 stage
                                                                                                  saae as abova
                                                                                                  saae as abova
                                                                reeidue Id)
                                                                     Earnest
                                                                     (19711,»MIC-
                                                                     5561,

                                                                     Earnest
                                                                     (19711,
                                                                     *MIC-556%
-------
Compound Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient,
Pom
Experimental
Variables,
Control led
or Noted Comments
Reference
>
         Paraquat
         Paraquat
         Paraquat
         Paraquat
Green sun fish FL    Jefferson
                    County.,
                    Colo.

Blueqllls     FL    Jefferson
                    County.,
                    Colo.

Mater (top)   FL    Jefferson
                    County.,
                    Colo.

Cardlun edule USA   —
         Paraquat
Crangon       BSA
crangon
1.1 (Z.lppm max a,c,d,e,gf
t Issueresidue   and Hater
16 d>            stage

1.1 (1.6 ppmmax a,c,d,e,g,
t Issueresidue 8 and Mater
d>              staqe

1.1U (0.6 pp»   a,c,d,e(g,
nax residues    and Mater
hr-l dl         stage
                                                                                                 sane as above
                                                                                                 sane  as above
                                                                                                 sane  as above
greater than 10 a»(contin-         One hundred-forty surface active
(T2)            uous aer-  agents, solvent emuls1flers, oestlcides,
                atlon, sea-oolvchlorlnated blohenyls, pure
                water, and inorganic, and organic chemicals Mere
                dally      evaluated against  as many as ten marine
                solution   organisms.  The authors noted that most
                renewal)   published data of  this type deal Mith
                           toxlclty of chemicals to freshwater
                           organisms.
                                 greater than 10 a»(contin-
                                 CT2)            nous aer-
                                                 ation, sea-
                                                 water, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                                  sane  as  above
                                                                                                      Earnest
                                                                                                      (1971),
                                                                                                      AMIOS56*

                                                                                                     • Earnest
                                                                                                      (1971*,
                                                                                                      AMIC-S56I.

                                                                                                      Earnest
                                                                                                      (1971),
                                                                                                      AMIC-55M.

                                                                                                      Portmann, et
                                                                                                      al (1971),
                                                                     Porfmann, et
                                                                     al  (1971),
                                                                     AHIC-7701
         Paratnlon (plus 0.75 Plnephsles    BCFA
         ppn LAS)             prone I as
         Parathlon (plus 0.5  Plneohales    8CF»
         ppn LAS)             oromelas


         Parathlon (plus t    Plnephales    BCFA
         ppn LAS)             proneI as
                                 0.8 (Z.5        a»,e               LAS acted synergistlcally Mith    Solon, et al
                                 percent K)                 parathlon to cause  less survival of       (1969),
                                                            fatheds but had an  indeterminate effect   AMIC-3785
                                                            Mith DDT and no synerglstlc effect Mith
                                                            Endrln.
                                 O.S (61.5       a»,e
                                 percent K)
                                 0.1 (95 percent a*,a
                                 K)
                                                                                                  sane  as  above
                                                                   sane as above
                                                                     Solon, et al
                                                                     (1969),
                                                                     AH.IC-37S5

                                                                     Solon, et al
                                                                     (1969),
-------
         Parathlon  (Sesavcx
         pretreatnent  at  t
         ppn)
         Parathlon  (Sesanex
         pretreatnent  at  2
         PP«>

         Parathlon  (Sesanex
         ppetreatnent  at  Z
         Oo • I
Notenlgonus
chrysoleueas
Leoonls
cyan*II us
Leoomis
nacrochlrus
                                             t      —
0.20 CtSpercent --
AChE
Inhibition)
O.?0 (UO
percentAChE
Inhibition)

0.20 (Wpercent
AChE
Inhibition)
        Fish brain AChE activity Has not
affected by Sesamex alone but Has
significantly Inhibited by parathton.
Pretreatirent with Sesamex at 2 ppn
resulted In decreased Inhibition of AChe
activity by parathlon.

       sane as above
                                                                    sane  as  above
Gibson, et
al (1971).
AMIC-3799
                                          Gibson* et
                                          al <197U ,
                                          AMIO3T99

                                          Gibson, et
                                          a I (1P7D,
         Parathlon
 r
u>
         Parathlon
         Parathlon
         Parathlon
         Parathlon
         Para th Ion
leoonl*
•acrochlrus
(brain
tissue)
                                                                0.7?  (SB  30
                                                                nln,  invltro)
                              Plnephales    BCFA  —
                              pronelas
                              Plxephales    BCFA  ~
                              oronelas
                              Notenlqonus   L     ~
                              chrysolcucas
                              Leponls
                              cyan*11us

Leoomls       L
•aerochlrus
                                                                    (T<»t
                                 0.6 (5 percent
                                 K)
                                 0.20 (67
                                 percent
                                 AChE
                                 inhibition)
O.?0 (71.
percent AChE
Inhibition)

O.ZO (68
percent AChC
Inhibition)
                                   This study Has conducted to       Gibson, et
                           determine whether brain tissue and        al (1969) »
                           handllnq variables ( f reez loq- than Inq)     AHIC-378'5
                           affected AChE assays.  AChE Inhibition of
                           ?5 oercent occurred at 750 pnb*
                           Considerable variation occurred, i.e., no
                           symotoms Here evident and fish recovered
                           after experiencing 9B oercent AChF
                           Inhibition.  The authors reconwend
                           standardization of handling procedures
                           and fish strain.

                                   LAS acted synerqistleally Hith    Solon, et
                           parathlon to cause less survival of       al(1969),
                           fatheds but had an Indeterminate effect   ANIC-3785
                           tilth DDT and no synerqlstlc effect xlth
                           Endrin.
                                                                                                  sane  as  above
                                   Fish brain AChE activity Has not
                           affected by Sesanex alone but Has
                           significantly inhibited by parathion.
                           Pretreatnent with Sesanex at 2 ppn
                           resulted in decreased Inhibition of AChe
                           activity by parathlon.

                                  San* as above
                                                                                                  sane  as above
                                          Solon,  et
                                          al (1969).
                                          AHIC-3785

                                          Gibson,  et
                                          al  (19M).
                                          AHIC-3799
                                          Gibson,  et
                                          al  (1971),
                                          •HIC-3799

                                          Gibson,  et
                                          •1(1971),
                                          AN.IC-3799
-------
Co* pound
Parathlon
Organise
Lepomls
cyan*! lus
IP<>sI«tantl
Field Field
Study Location
BSA —
Toxlelty,
Active
Ingredient,
Pp.
0.38 CTZ)
Experimental
Variables,
Control ted
or Noted
a»
Comments



Green sunflsh from Belzonl, Hiss.
Mere resistant to Chlorrtanw, Heotachlor,
LIndane, and Strobune, hut not to
Reference
MincheN, •
al 119701,
ANIC-5*71
Parathion
                     cyanellus
                     fSu«e»ptIbla>
                                   BSA
                                                      0.31  (T2)
                                                                                 Parathion.  Golden shiners fron the sa*e
                                                                                 location Mere resistant to LIndane and
                                                                                 Strobane, tolerant to Chlordane and
                                                                                 Heotachlor, and susc«otlble to Parathlon.
                                                                                  LaeK of resistance to Parathlon
                                                                                 Indicated lacK of agricultural usaae of
                                                                                 organochosphates In that area.  Resistant
                                                                                 fish Mere compared to susceptible ones
                                                                                 collected at Starkvllle.

                                                                                        sa»e as above
                                                                                                      NlncheM, et
                                                                                                      at(1970),
                                                                                                      AHIC-«!«.7l
Parathlon
Parathlon
Notemlqonus   BSA
cry-:
Notemlqonus   BSA
crvsoleucas
(Susceptible)
                                                      Z.SO  IT2)
                                                       1.90  (T2)
                                                                                        sa»e as above
                                                                                        saa* as above
                                                                                                      HlncheM, et
                                                                                                      al(1970),
                                                                                                      AHIC-5U71

                                                                                                      HlncheM,
                                                                                                      etal (1970),
                                                                                                      AHIC-5*71
Parathlon
Parathlon
                     Pa I aeiaone tes
                     kadiakensls
raslatant)

Pataevonetes
KadlaKensls
(resistant)
                                   BSA   —
                                   BSA   —
                                                       0.0071  (Tl)
                                                      0.0066-0.0116
                                                      (Tl)
                                                                                        sane as above
                                                                                                      Naovl. et al
                                                                                                      (1970),
                                                                                                      AHIC-5519
                                                                    Ploassays were conducted with     Naavi, et al
                                                            shriip fron three areas of Intensive      (1970),
                                                            pesticide use and fro* an unexoosed area. AHIC-S519
                                                             Previously exposed shrimp Mere fron 1 to
                                                            ?5 times more resistant than unexoosed
                                                            shrimn.  Both types of shrine were also
                                                            exposed In cages to Maters of the
                                                            contaminated ureas.  Susceptible shrlnp
                                                            suffered 66 percent more mortality than
                                                            did resistant shrlmo.  The toxlclty of
                                                            the insecticides ranked in descending
                                                            order Mas as follows!  most toxic,
                                                            Endrln, DOT, Methyl  paratnion. Parathlont
                                                            medium toxlclty, Guthion,  LIndane.
-------
          •••rath I on
                               Notemlgonus
                               crysoleucas
                                             •      ^^
          •arathlon
                               Tub Hex
                               tub Ifex
              FL
              and
              BS*
Belzonl,
Miss.
r
VO
         Parathlon
                               Cardlurn edule BS*   —
                           Toxaohene. Strobanet lease toxic
                           Chtordane. Sevln, and Heotachlor.

0.5  (SB 1-Z)    —                 Fish exposed as Indicated had     Butler, et
                           significant or highly significant changes al (1969).
                           In hematocrlt, leucocytes, lymphocytes,   ANIC-5977
                           heteroohlls. and  In body Height.  No
                           significant changes were noted In body
                           length, or erythrocyte total and
                           fragility.  The authors state that
                           effects on hemopoelsls and cell membranes
                           could produce the results reported.

Z.OO (NTEt      —                 The response of                   Naovl, etal
                           pesticide-resistant aquatic organisms to  (1969),
                           various pesticides was compared to the    »MIC-5979
                           response of non-resistant species.
                           Pesticide-resistant species Here
                           collected at Belzonl and non-resistant
                           soecles at State College.  Cooeoods.
                           clams, snails, and sludge Norms from
                           Belzonl were considerably more tolerant
                           to pesticides than the non-resistant
                           organisms.  The authors note that the
                           effect of Increased tolerance In the
                           organisms Is an Increase In the amount of
                           pesticide residues available to animals
                           of higher trophic levels.

3.3-10 (T2I     a*(eontin-         One hundred-forty surface active  Portmann, et
                uous aer-  agents, solvent emulslflers. pesticides,  al (1971).
                atlon, sea.polychlorinated blphenyls.  pure           AHIC—7701
                water, and Inorganic, and organic chemicals were
                daily      evaluated against as many as ten marine
                solution   organisms.  The authors noted that aost
                renewal)   published data of this type deal nlth
                           Toxlcity of chemicals to freshwater
                           organisms.
         Par*thI on
                               Cranqon
                               crangon
                                            BS»    ~
                                 I.003-0.01
                                 mi
                            *«( contin-
                            uous aer-
                            ation, sea-
                            water, and
                            dally
                            solution
                            renewal)
                                                                                                 saae as above
                                                                     Portmann,  et
                                                                     al  (1971).
                                                                     »MIC-7701
         •erethlon
PI eur onec tes
platessa
                                            BS*
                                                               B.03-0.10  (T2t
                            a»(contin-
                            uous aer-
                            ation, soo,-
                            watar, and
                                                                                                 same as above
                                                                     Portmann.  et
                                                                     al  (1971),
                                                                     »HIC-7701
-------
Toxiclty,
Active
Field Field Ingredient,
Cmoound Organism Study Location Ppa

irafhlon Ictalurus 8CF* — 0.8-3.8 (K up
nebulosus to 30 dt
Experimental
Variables,
Controlled
or Noted Comments Reference
daily
solution
renewal)
a*,c,d,e, r Catfish blood content of Mount, et al
,9 parathlon Has shown to be directly (19%9),
u»
         ParathIon
         •CB
                              Ictalurus
                              nehulosus
                                            BCF»
                                 10-SO Ibtood
                                 residue)
                                                            corre!atable Mlth Hater content,          AHIC-11
                                                            lethality, and sublethal symptoms.
                                                            Freeze-thaning of blood five times
                                                            resulted In disruption or blood cells and
                                                            release of unaltered parathlon thus
                                                            Indicating that this pesticide Is not
                                                            readily and completely metabolized In
                                                            fish.

                                                   ,c»d,e,f        same as above
                              Unite sucker  FRL    Hlsc.  states D.27-lt.8
                                                                residue (SB)
         •CB
         •CB
                              YelloH perch  FRL    Hlsc.  states 0.28-12.6
                                                                residue (SB!
                              Chain
                              pickerel
              FRL   Hlsc. states d.%9 residue
                                 (SB)
                                                                    The Bureau  of Sport Fisheries
                                                            continued  Its  fish  monitoring  program  by
                                                            collecting 11.7 composite  fish  samples
                                                            from 50 nationwide  monitoring  stations
                                                            during the tall  of  1969.  Fish were
                                                            analyzed for residues of  11
                                                            organochlorlne Insecticides, Holds, and
                                                            PCB-s.

                                                                   sane as above
                                                                                                  same as above
Mount,et al
(1969) •
•MIC-11

Henderson,
et al(197t),
»t1IC-H.07
Henderson,
et alftqril,
»MIC-1«.97

Henderson,
etal (1971),
• HIC-11.07
         PCS
         PC*
                              White cattish FRL   Hlse.  states  less  than
                                                                0.10-2.16
                                                                residue  (SB)
White perch   FRL   Hlsc. states less than
                                 •.10-7.68
                                 residua ISB)
                                                                                                  sane as above
                                                                                                  saae as above
Henderson,
et al
(19711.
AMIC-1V07

Henderson.et
al (1971),
«HXC-1«07
-------
                               Goldfish
              FRL    HlSC.  states 9.50  residua
                                  (SRI
                                                                                                   saae  as above
                                                                                         Henderson,
                                                                                         • t »1
                                                                                                                                      i«>o7
                               PuaoMnseed   FRL
                                                   Hisc. states 2.68 residua
                                                                (SB)
                                                                                                   saae as ibov*
                                                                                                       Henderson,
                                                                                                       • t si (14711,
                                                                                                       *Mic-i*07
                               Larqeaouth    FRL   Misc. states  less  than
                               bats                              0.10-8.07
                                                                 residue  (SB)
                                                                                                   saae as above
                                                                                                       Henderson,
                                                                                                       • t al
                                                                                                       (1971),
                                                                                                       »MIC-1MI7
          KB
                               Brawn
                               bullhead
                                             FRL
                     Misc.  states 0.3<.-<..00
                                  residue (SB>
                                                                                                   saae as above
                                                                                         Henderson,«T
                                                                                         al (1971),
         PCS
Ul
VM
Carp          FRL    Misc.  states less  than
                                  o.10-11.r
                                  residue (SB)

Channel       FRL    Misc.  states less  than
catfish                           0.10-6.77
                                  residue (SB)
                                                                                                   save  as  above
                                                                                                   saae  as  above
                                                                                         Henderson, et
                                                                                         al (1471),
                                                                                         »MIC-1«.07

                                                                                         Henderson,
                                                                                         et «l
                                                                                                                                      AMTOl«i07
                               Redhorso      FRL   Misc. states less than
                               sucker                           0.10-0.2?
                                                                residua (SB)
                                                                                                  saaa  as  above
                                                                                                       Henderson,
                                                                                                       et al
                                                                                                       (19711 ,
                                                                                                       »MIC-1«.07
         KB
Gizzard shad  FRL   Misc. states  0.22-0.86
                                  residua  (SB)
                                                                                                  saaa as above
                                                                                         Hend*rson,et
                                                                                         al
         KB
                               Sootted
                               sucker
              FRL   Misc. states  less  than  0.10
                                  residua  (SB)
                                                                                                  same  as  above
                                                                                         Henderson,et
                                                                                         at  (1971),
                                                                                         *MIC-l«i07
         KB
                               BlueqlllS
              FRL   Misc. states  0.39-1.19
                                  residue  (SB)
                                                                                                  same  as above
                                                                                         Henderson,
                                                                                         et al
                                                                                         (1971),»HIC-
                                                                                         I«i07
         KB
Redbreast
sunfish
FRL   Hlse. states 0.19 residue
                   (SB)
                                                                                                  saae  as above
Henderson,
et at(1971),
»HIC-1«>07
                               Strlpad       FRL   Hlse. states less than
                               aullet                           0.10-1.39
                                                                residua  (SB)
                                                                                                  saae as above
                                                                                                       Henderson,
                                                                                                       et al
                                                                                                       (1971),
-------


u>
VJ1
ru







Coapound
PCB
PCB
PCB
PCB
PCB
PCB
pcb
PCB
PCB
PCB
PCB
Orqanlsa
Blue catfish
Rock bass
Freshnater
drua
Bloater
LaKe
Mhltef Ish
LaKe trout
Hhlte craoole
Blqaouth
buffalo
Saallaouth
buffalo
Flathead
catfish
Col day*
Field
Study
FRl
FRL
F*L
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FIH.
Field
Location
Misc.
Misc.
MlSC.
MlSC.
N1SC.
MlSC.
MlSC.
MlSC.
Nlse.
MlSC.
H|SC.
states
states
states
states
states
states
states
states
states
states
states
Toxlclty, Exoerlaental
Active Variables,
Inqredlent, Controlled
Poa or Noted
less than 0.10
residue (SB)
0.39-l>.10
residue (SB)
1.9d residue
(SB)
residue (SB)
1.96 residue
(SB)
residue (SB)
0.83-1.79
residue (SB)
less than
0.10-1.21
resldue(SB)
2.66 residue —
(SB)
3.»8 residue —
(SB)
I.1S-Z.35 —
residue (SB)
Comments
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
Deference
Henderson,
etal (19M),
AMIC -1*07
Henderson,
et al (1971),
AMIC-1«.07
Henderson,
et al 11171),
AHIC-H07
Henderson,
et al
(1971). SMIC-
11.07
Henderson,
et aid1"!),
AHIC-11.07
Henderson,
et al (1971),
AMTC-1U07
Henderson,
et al (1971),
AMIC-1U07
Henderson,
et at
(1971),
AMIC-11.07
Henderson,
et 81 (l?7l>,
AMIC-1«.07
Henderson,
ANIC-l«i07
Henderson,
•t al(197t>.
-------
          PCB
                               Hal lay*       FRL   Hlsc.  states O.ZZ residue
                                                                (SB)
Sauqer        FRL   Misc. states  1.09 residue
                                  (SB)
                                                                                                  saae as »bow«
                                                                                                  saae as above
                                                                                                       »MIC-1«.07

                                                                                                       Henderson,
                                                                                                       et al
                                                                                         11.07

                                                                                         Henderson.et
                                                                                         at
                                                                                         <197l>,
         •CB
Flunnelaouth   FRL  Misc. states  2.1H residue
sucker                            (SB)
                                                                                                  saae as above
                                                                                         Henderson t
                                                                                         et
U>
vn
         •CB
         •CB
         PCB
         PC8
Black
bulI head
FRL   Hlsc. States 0.15-0.21
                   residue  (SB)
MMte bass    FRL   Misc. states  LOW residue
                                  (5B»
                               Black  crapele  FRL
Lerqescale    FRL
sucHer
      Misc. states less than
                   0.10-1.83
                   residue  (SB)

      Hlsc. states less than
                   0.10-1.16
                   residue  (SB)
                                                                                                  saae as above
                                                                                                  sane as above
                                                                                                  sane as above
                                                                                                  saae as above
Henderson,
et »l(l«71>,
• HIC-1I.B7

Henderson,
*f at
(1971), »HIC-
1<,07

Henderson, et
al (1471),
Henderson,
et al
(1971),
• NIC-l«t07
         tt*
Seallaouth    FRL
bass
      Misc. states less than 0.10
                   residue (SB)
                                                                                                  sane as above
Henderson, et
at (1971),
         PCB
Northern
sauaHfIsh
                                             FRL
      Hlsc. states 0.58-1.19
                   residue  (SB)
                                                                                                  sane as above
Henderson, et
at (1971),
4MIC-H.07
         •C8
                               Chlselnouth    FRL
                    Hlsc. states 0.71-0.98
                                 residue  (SB)
                                                                                                  saae as above
                                                                                        Henderson,
                                                                                        et al(1971),
                                                                                        «HIC-1«.07
         •CB
         •CB
Klaaath
sucker
                                             FRL
                               Rainbow trout  FRL
      Hlse. states 0.13 residua
                   fSBI
                    Hlsc. states  B.ZT-*.k8
                                  residua  (SB)
                                                                                                  saae as above
                                                                                                  saae as above
Henderson,
et al(197i),
• MIC-11.07

Henderson,
et •1(1971),
-------
Coetoound

PCB
PCB
PCB
i
V»»
Org»f»is«

qrldqellp
sucker
Arctic
grayling
Pound
•hltef Isn
Longnose
sucker
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Study Location Pen or Noted Consents

FRL Misc. states 2.75 residue — sane as above
(SB)
FRL Misc. states !."»? residue ~ sae,e as above
(SB)
FRL Hlsc. states 2.62 residue ~ same as above
(SB)
FRL Hlsc. states 1.53-3.87 — same as above
residue (SB)
Pet erenee
AMIC-1V07
Henderson,
et SH19M),
ANIC-t«.fl7
Henderson,
AHIC-1U07
Henderson,
et al (1971),
A1IC-1I.07
Henderson,
etal (1971),
AHIC-1<.07
PCB
KB


PCS


KB


PCB



PCS



PCB
                     Sebastodes    FO
                     so.
Pacific      1.0 t liver-
Ocean, Cal.  residue)
        Sanotes of narlne anlnals Here    Hunson
collected from three locations off the    (1972),»MIC-
coast of Southern California and analyzed 3096
for residues of chlorinated hydrocarbons.
 The data suggest that Kellefs whelk
Mould be a good indicator organism for
studying the regional distribution of
chlorinated hydrocarbons.
Parat ahrix
nebul 1 f er
Anlsotrenus
davldsonl
Pixel onetaoon
pulehru*
Hal lot Is
puf esc ens
Stronqylocent
rot us
franc Iscanus
Hlnnltes
•ul tlrueosls

FO
FO
FO
FO
FO
FO

Pacific
Ocean, Cal.
Pacific
Ocean, Cal.
Pacific
Ocean, Cal.
Pacific
Ocean, Cal.
Pacific
Ocean, Cal.
Pacific
Ocean, Cal.

0.2% (liver
residue)
0.51 (liver
residue)
0.?9 (liver
residue)
less than 2.0
(qonad
residua)
0.12-0.21
fgonad
residue)
0.9
(gonad
residue)
                                                                                         sane  as  above
                                               sa*e as above
                                               same as above
                                               sa«e as above
                                               sane as above
                                                                                        saae as above
                                          Munson(1972>,
                                          AMIC-3096

                                          Hunson(1973),
                                          AMIC-3096

                                          Munson(197Z).
                                          Hunson
                                          «197?»,
                                          AMIC-30<»6

                                          Hunson
                                          (1972),
                                          AMIC-3096

                                          Hunson (197?),
                                          AHIC-3096
-------
PCB
PCB
PCB
PCB
U)
VI
vn
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
Hal lot 1«
corrugata
Kelletla
fcelletll
Penul Irua
InterrupTus
Anqultla
' rostraTa
S«b»atode8
•arlnus
fsoie nlger
Salao salar
Cluoea
harengus
Scoaber
seoabrus
rlytllus
edulls
Cadus aorhue
Uroohyels
tenuls
FO
FO
FO
FRl
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
Pacific
Ocean. Cal.
Pacific
Ocean. Cal.
Pacific
Ocean. Cal.
ST. John,
N.B., Can.
ST. John,
N.B., Can.
ST. John,
N.P-. , Can.
ST. John,
N.B., Can.
ST. John,
N.B., Can.
ST. John,
N.B., Can.
ST. John,
N.B., Can.
ST. John,
N.B.. Can.
ST. John,
N.B.t Can.
O.OOS (gonad
residue)
0.?3 (residue) —
0.16 (auscle
residue)
0.71 (residue) —
Trace
(residue)
0.33 (residue) —
0.<»S (residue) ~
(residue)
0.35 (residue) ~
0.1* (residue) --
0.03 (residue) ~
O.OZ (residue) —
saae as above
saae as above
saee as above
PCB"*s were found In higher
concentrations than orgarochlor Ine
.pesticides In alt fish analyzed. The
authors point out that PCB is less toxic
In an acute sense than organochtorlnes,
that little is known of sublethal PCD
effects, and that aore knowledge of PCB
distribution and effects is needed.
same as above
saae as above
saae as above
saae as above
sane as above
saae as above
same as above
saae as above
Munson
3096
Hunson
3(96
Wunson(197?|«
Zltko
(1971) i
•NIC-3715
Zltko
3715
ZltKo
( 19711. •HIC-
3715
Zltko
(1971),V»IC-
3715
Zltko(1971),
»«C-3715
Zltko
(1971),MIC-
3715
Zltko
(1971), »MIC-
3715
Zltko
<1971),»MIC-
3715
ZltKo
(19711,»HtC-
3715
-------
>
vn
Coeoound
»»C«

•C8












»cs






•CB






PC8






res


Toxiclty, Experimental
Active Variables.
Field Field Ingredient, Controlled
Organise Study Location Pp« or Noted Comments
Hippo- FRL
glossoides
plataasoldes
F»lco F
peregrimis
(eggs)










Falco F
o*r»gr inus
•Immature)




Falco F
peregrlnus
(immature)




Falco F
oeregr Inus
(adult)




Falco F
oeregrlnus
(adult)
St. John, 0.03 (residue)
N.B., Can.
Western 10.2 (residue) —
O.S.,
Pacific
Ooaan,
Panama,
Mexico, and
An tare tic






Western 0. 16-81. (flesh —
U.S., residue)
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western 3.3-l,<.20 «»at —
U.S., residue)
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western 19.7-%1.5
U.S., (flesh
Pacific residue)
Ocean,
Panama,
Mexico, and
Antarctic
Western 3.2-1,980 (fat —
U.S., residue)
Pacific
sane as above

Peregrine falcons, falcon prey.
an>1 other predator «oecles Mere collected
widely and analyzed tor DOT, HOE, PCS,
and a tew other oestlcldes to a lesser
degree. PCR and DDT Here found to be
widely dispersed globally. PCP was found
enzymes that degrade oestradiol.
Reductions In thickness of egq shells.
eggshell weight, and water retention
occurred. Ill affect hatching success.
The authors state that the peregrine "ay
be the first species entlroated by global
contamination.
saoe as above






same as above






sane as above






sane as above


Reference
Zltko
(1«71»,
AMIC-ST1S
Risebrougn,
et al
(1968).
4HIC-38M.









Rtsebrough,
et al
(1968), AMIC-
3»<.i.



Rtsebrough,
et al
(19S8),
AMIC-38k«



Risebrough,
et al
(1968),
AHTC-38
-------
         PCS
         PCS
U)
vn
         PCS
         PCS
         PCS
         PCS
                              looaelanla
                              •elanla
                              Haloeyptena
                              •Icrosoaa
Plronyx
vlvesl
Erxlonychura
cravert
leqgs)
Thalasseus
efeqans
(eqqsl
Larus
heeraanl
(cqqs)
Ocean,
Panama,
Mexico,and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Oc**n,
Panama,
Mexico, and
Antarctic

western
U.S.,
ParIfic
Ocean,
                                 1.0  (Hhole body
                                 residual
                                 0.35 (whole
                                 body residue)
0.02 (Mnole
body residua)
                                                                                                  save as above
                                                                                                  saae  as above
                                                                                                  saae  as above
Mexico, and
Antarctic

western
U.S.,
Pacific
Ocean,
Panama,
Mexico,and
Antarctic

Western
U.S.,
Paclf Ic
Ocean,
Panama,
Haxleo, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama.
Mexico, and
Antarctic
                                                                    (residual
                                                                                                 saae  as  above
                                                                1.5  (residua)
                                                                                                 saae  as  above
                                                                8.1  (residua)
                                                                                                 saaa  as above
                                                                                                                                     4HIC-38W.
                                                                     Rlsebrouqn,
                                                                     et al
                                                                     I19K8I,
                                                                     INIC-S8S*
                                                                     HI safer oug ti*
                                                                     et al
                                                                     (1468),
                                                                     AHIC-38**
                                                                                  Rlsebrouqh.
                                                                                  et al
                                                                                                                                     AHIC-38**
                                                                     Rlsebrou<]h,e
                                                                     t al  (19«8I.
                                                                     AMIC-3SHU
                                                                     Risebrouqn,
                                                                     et al
                                                                     (1968),
                                                                     AMIC-38V".
                                                                     Rlsebrouan,
                                                                     etal  (19681,
                                                                     AHIC-38M,
-------
OJ
\J\
 CD
Comoound
PCS






PCB






PCB






PCS






PCB






PCB




Orqanlsn
Pomoxls
annular Is





Pomoxls
nlgro-
naculatus




Leoomls
•acrochlrus





Pyqoseel Is
advllae
(eqqs)




Futmanus
glaclalls





Put f Inus
creatoous



Field Field
Study Location
F Western
U.S.,
Pacific
Ocean t
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Paclt Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Hestern
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Hrstern
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
F Hestern
U.S.,
Pacific
Ocean,
Panama,
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
O.OOt (whole -- same as above
body residue)





0.003 (whole — same as above
body residue)





0.005 (whole -- same as above
body residue)





0.0di» — - same as above
(residue)





0.08-6.5 (whole — sane as above
body residue)





O.it? (whole — same as above
body residue)



Reference
Rlsebrouqh.e
t al (1968),
AMIC-Sm




Plsebrouqh,
et al
(iqfiM ,
AMIC-38<>«



Rls»brouqh,
et al
(1968),
AHIC-3Sk*



Rlsebrovign,
et al
(1968),
ANTC-38H,



Rlsebrouqh,
et al
(1968),
Amc-38*<>



Rlsebrough,e
t al (1968),
ANIC-38
-------
         PCB
         pee
U)
vn
NO
         PCS
         PCS
                               Pu Minus
                               qrlseus
                              PuffInus
                              tenulrostrls
                              Oceanodroma
                              homocnroa
                              Peleeanus     F
                              occidental Is
                              (eqqs)
Freqata
•aqnlfIcens
(egqst
Sula
leucoqaster
                    HexIco( and
                    Antarctic

                    Western
                    U.S.,
                    Pacific
                    Ocean*
                    Panama,
                    Mexico, and
                    Antarctic

                    Western
                    U.S.,
                    Pacific
                    Ocean,
                    Panana,
                    Mexico, and
                    Antarctic
                    Western
                    U.S.,
                    Pacific
                    Ocean,
                    Panama,
                    Mexico,
                                                           and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico,and
Antarctic

Western
U.S.,
Pacific
Oce an,
Panama,
Mexico, and
Antarctic

Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
             0.9-1.2 iMhole
             body residue)
             Z.I (whole body
             residual
             9.8 (whole body
             residual
                                 0.010^-0.0231
                                 (residue)
0.0057-0.084
(residue)
0.00<,»
(residue)
                                                                                                  saae as above
                                                                                                  same as above
                                                                                                  sane as above
                                                                                                  same as above
                                                                                                  sane as above
                                                                                                  same as above
                                                                     Risebrou9h,
                                                                     et al
                                                                     (1968),
                                                                     »MIC-S8«.<>
                                                                     Rlsebrougn,
                                                                     et al
                                                                     (1966),
                                                                     AMIC-38M
                                                                     PIsebrouqh,
                                                                     et al
                                                                     (1968),
                                                                     Rlsebrouqh,
                                                                     • t al
                                                                     (1968),
Rlsebrough,
et al
(1968),
Rlsebrou9nt
et al
(1968).
AMIC-mit
         pea
                              Phalacrocorax F
                                                   Western
                                                                0.113
                                                                                                  same as above
                                                                                                                                     Rlsebrough,
-------
Compound Organism
penlclllatus
(eagst




IB Phalacroeorax
pelaglcus
(eggst




!• Anas
cyanoptera





:B El anus
tcucurus
feggs)




:B Ace loiter
cooper 11





!• Aoulla
chrysaetos
(•99*)




Field Field
Study Location
U.S..
Pacific
Ocean t
Panama!
Mexico, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Hexlco,and
Antarctic
F Western
U.S.,
Pacific
Ocenn,
Panama,
Hexlco, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Hexlco, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama*
Mexico, and
Antarctic
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppn or Noted Comments
(residue)





0.062 — same as above
(residue)





0.91 (whole — same as above
body rest duet





0.00as<»-0.006<> — same as above
(residue)





6.3 (Dhole body — same as above
residue)





0.23 (Mhole — same as above
body residue)





Reference
et al
(1968),
AHIC-38**



Rlsebrough,
et al
(1968).
AMIC-SSMi



RIsebrouqt,
etal (1968),
AHIC-38tt




Rlsebrouqh,
et al
(1968).
ANIC-38«.»



Rlsebrou9n,
et al
(1968).
AKIC-381*



R isebrouqn.
et al
(1968),
AHXC-38«t



-------
MB
MB
MB
MB
MB
MB
                      Pandlon
                      ha IIartus
                     Fa I eo
                     coluabarlus
                     Falco
                     soarverlus
                     Faleo
                     soarverlus
                     (e<*os>
Nyctlcorax
nyctleorax
(eggs)
Larus         F
occidental Is
leq9S>
Sterna
torsterl
(eons)
                    Western
                    U.S.,
                    Pacific
                    Ocean,
                    Panana,
                    Mexico, and
                    Antarctic

                    Western
                    U.S.,
                    Pacific
                    Ocean,
                    Panana,
                    Mexico, and
                    Antarctic
                    Western
                    U.S.,
                    Paclf 1C
                    Ocean,
                    Panana
                    Mexico
                                                  and
             0.003^-0.103
             (whole body
             residue)
             0.39 (Hhole
             body residue)
             0.31 (whole
             body residue)
                                                       0.09  (residue)   —
                                                                                         sane as above
                                                                                         sane as above
                                                                                         sane as above
                    Antarctic

                    Western
                    U.S.,
                    Pacific
                    Ocean,
                    Panama,
                    Mexico, and
                    Antarctic
Western      D.023-0.33
U.S.,        (resldut)
Pacific
Ocean,
Panama,
Mexico,  and
Antarctic
Western      0.023-1.31
U.S.,        (residue)
Pacific
Ocean,
Panana,
Mexico, and
Antarctic
                                                                                         saa* as above
                                                                                         same as above
                                                                                         saae as above
Western
U.S.,
Pacific
Ocean,
                                 0.11*
                                 (residue)
                                                                                         saae as above
                                                                                                      Rlsebrougn,
                                                                                                      et  al
                                                                                                      (1968),
                                                                                                      AHIC-38«t
                                                                                                      P.Isebrou9h,
                                                                                                      et  al
                                                                                                      (1968),
                                                                                                      ANIC-3S«<>
                                                                                                      PIsebrough.
                                                                                                      et al
                                                                                                      (1961),
                                                                                  et al
                                                                                                      Plsebrouqh,
                                                                                                      et al
                                                                                                      (1968),
                                                                                                      ANIC-3««i>
                                                                                                      Rlsebrough,
                                                                                                      et al
                                                                                                      (1968),
                                                                                                      AHIC-3«
-------
Coaoound Organise



!8 Hydrooroqne
caspla
(•qgs)




!B Phalaropus
lul learlus





:• Urla aalqe
(eqast





IB Ptyehoraaphus
aleutlcua





JB SyntMlboraap
hus antlauua





!• Cerorhlnca
aenocarata





Field Field
Study locution
Parian a •
Hvxlco. and
Antarctic
F Western
U.S.,
Pacific
Ocean ,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pftelf Ic
Ocean ,
Panama,
H»xlco« and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pacific
Ocean ,
Panama,
Mexico, and
Antarctic
F Western
U.S..
Pacific
Ocean,
Panama,
Haxlco, and
Antarctic
F Western
U.S..
Pacific
Oe»*n.
Panama,
Mexico, and
Antarctic
Toxlclty, Experimental
Active Variables.
Ingredient. Controlled
Pea or Noted Coaaents



0.11V-1.01 — saae as above
(residue!





D.10 (whole ~ saae as above
body rest duel





*5 (residue) ~ sane as above






(.16 (whole ~ saae as above
body residual





D.1S (whole ~ saae as above
body residue)





0.16 (whole ~ saae as above
body residue!





Reference



Rlsebrouqh.
et al
(1968),
AMIC-38W



Rlsebrougri,
et al
(1468).
AM.IC.-3AM>



Risebrough.
et al
« 11681 ,
AMIC-38M.



RIsebrouqh,
et al
(1968) ,
*NIC-J8«,V



Rlsebrough,
et al-
(19681.
AMIC-38IA



Rlsebrough.
• t al
(1468).
ANIC-S8»%



-------
         PCB
         PCS
         PCB
         ft
                               ZenalduTa
                               •acroura
                              Tyto alba
                              leqqs)
                              Sturnella
                              neqleeta
                              Fundulus
                              heteroclltus
CO
                     Western
                     U.S.,
                     Pacific
                     Ocean,
                     Pane*a,
                     Mexico, and
                     Antarctic

                     Western
                     U.S.,
                     Pacific
                     Ocean,
                     Panama,
                     Mexico, and
                     Antarctic

                     Western
                     U.S.,
                     Pacific
                     Ocean,
                     Pan ana,
                     Mexico, and
                     Antarctic
                                  Mo residua      —
                                   saaa a* above
              BSA   —
 0.<>7-0.66
 (residue)
O.OOZS-0.0261
(residual
                                 0.0003H-O.OOOI.
                                 (TV)
                8»,e,e,
                and
                synthetic
                seaxater
        Pebulete
                              Nereis vlrtns BSA   —
Gammarus      BSA
fasclatus
                                                               0.00068-0.00079 a»,C,e,
                                                               (T«            and
                                                                               synthetic
                                                                               seanater
       sa«a as above
                                                                      Rlsebrouqh,
                                                                      et  at
                                                                      (196$),
                                                                      AHIC-3RI.V
                                          Rlsebrouqh,
                                          etal  (19«S),
       sane as above
                                          Rlsebrouqn,
                                          et »l
                                          (196S),
                                          AMIC-JKM.
        A  laboratory procedure based on
•Standard Methods  for qK-hr toxlclty
deternlnat Ions of crurl* oil and
olt-dlspers*nt mixtures «as described.
The dlsoersants varied considerably in
toxlclty, ranqlng fro* 0.01 to 7.1 •!/!,
TLSO for 96 hr.   These did not differ
slinl f Icantl y fro* ?
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredient. Controlled
Compound Organism Study Location Poa 9r Noted Comments Reference
water, and
dally
solution
renewal)
Pentachloroohenol Crassostrea L — less then 0.25 ~
vlrglnlca (T2I
teggsl
Inorganic. >nd organic chemicals »ere
evaluated against as many as ten Marine
organisms. The authors noted that most
published data of this tyoe deal with
toxlclfy of chemicals to freshHater
organises.
The effect of 52 pesticides on OavlStet el
embryonic development of clams and (19691 t
oysters was reported. Synerglstle AHIC-5990
*
         PentacMoroDhenot
         Penfechloroohenyl
         •cetate
         PentacM or ooheny I
         •cetate
         •erolln No. 9
Crassostrea
vlrqlnlea
(larvael

Crassosfrea
vlrglnlca
Crassostrea
vlrglnlca
flarvael

Crangon
cranqon
                                            L     —
                                            •      M_^
              t     —
                                            8S«   —
                                                                O.BT1
less than 0.25  —
                                  less than 0.025 —
                           effects  with  solvents  Here  also reported.
                            Host  of  the  compounds affected
                           develocment more  than  survival.  Some.
                           however,  drastically reduced  larval
                           growth.   The  authors point  out  the
                           necessity of  evaluating the effects ot
                           pesticides on all life stages of  an
                           organls* and  note the  possibility  of
                           selecting chemicals for pest  control that
                           •oufd  not have serious effect on
                           Shellfish.

                                 sane  as above                      Davit;,  et
                                  same as above
                                  same as above
                                                      4NIC-5990

                                                       Oavls*  et
                                                      a I  (1969).
                                                                3.3-10  (T2)
                                                                     Davis,  et  al
                                                                     (1969).
                                                                     •NIC-S990

                                                                     Portmann.  et
                                                                     al  (19711.
                                                                     •Mic-rroi
         •erthane
                              TubI few
                              tubIfex
              rt
              and
                                                               •.*• (MTf»
                                                  Miss.
a*(contln-         One hundred-forty surface active
uous aer-  agents, solvent eaulslflers. pesticides.
atlon, aea-pol vchlorlnatod blphenyls. pure
Water, and Inorganic, and organic chemicals were
dally      evaluated against as many as ten marine
•olutlon   organisms.  The authors noted that aost
renewal)   published data of this type deal with
           toxlclty of chemicals to freshwater
           organisms.

— -                 The response of                   Naovl. etal
           pesticide-resistant aquatic organisms to  (19691*
-------
                                    BS»
 Petrol It*  W-1HVJ
Patrollte W-1U39
Phenkapton
Phenoberbltal
Phenobarltal
Phenolic*
                      Steel heal
                      trout
                      I f Ingerllnq*)
                                    BSA   —
                                                       35.5 (T
Coho salmon   BSA   Rood Canal,  1.5 (K)
(flngerllnga) In    Hoodaport,
              •Itu  Hash.
                     Fish  Inot
                     specified)
                     Neqaprlon     BSA   —
                     brevlrostrls
                     (1-3 kq>
                                 greater than
                                 1.0-10.0  
                                  300  (NTE3.Z5
                                  hr>
                     Carasslus
                     auratus
Fish (not
specifled)

                                                      75  (MTE)
greater than
0.1-1.0 (Kl
                           various pesticides Mas compared  to  the    AHIC-S979
                           resoonse of non-resistant species.
                           Pesticide-resistant soecles were
                           collected  at  Belzonl  and non-resistant
                           species at State  College.  Cooepodst
                           claws, snallst and sludoe norms  from
                           Belzonl Here  considerably more tolerant
                           to pesticides than the non-re-sl stant
                           orqanlsns.  The authors note that the
                           effect of  Increased tolerance In the
                           orqanlsns  Is  an Increase In the amount of
                           pesticide residues available to animals
                           of higher trophic levels.

                                   Evaluation of 11 oil dlspersants  Tracy, etal
                           resulted In a ranfelnq for each and a      (1969).
                           recommendation for use according to the   AHIC-383*
                           ranKlnq.  Ranking MBS based on toxlclty
                           and oil dlsoersal effectiveness.  Corexlt
                           776
-------
Comoound
Phenols (plus
•••on I a and zlnel
Toxicity,
Active
Field Field Ingredient,
Organism Study Location Pom
Sal mo 8SA — 0.5-2.51, (T2>
ga 1 rdner 1
Experimental
Variables,
Controlled
or Noted Comments
Britain were summarized. An excellent
brief, general discussion of toxicltv
testing Is also present.
a,e*,d,e*t Rainbow trout were exposed to
f»» concentrations of fluctuating levels of
Reference
(1«7H, AMI
1056
Brown, et
11969),

• 1
>
         Phenols leius
         coooerl
Sal mo
qalrdnerl
                                            BS»
                                 0.5-1.75 IT2I   a.c,e
         Phenols lolus
         cooper, ilnet
         Phenols
Salao
galrdnerl
                                            BS»
                                 0.6-2.1,0 (T2)   a.c.e
Rashora       BCFA
heteromoroha  and
              BSA
                                                               6.2 CT2,
                                                               hardwater)
                                                 a*,c,e,f,
                                                 hard (HW>
                                                 orsoft
                                                 (SH)
                                                 synthetic
                                                 dilution
                                                 water, or
                                                 seawater
                                                 tor soae
                                                 seeeles
                                                            ammonia, phenol, and zinc and to constant
                                                            mixtures ol the tv~»e.  Tests Mlth
                                                            fluctuating levels of toxicants showed
                                                            that LC50 values Here similar to those
                                                            for constant concentrations as long as
                                                            the oerlodiclty of the fluctuation did
                                                            not exceed the resistance tine for the
                                                            poison.  Except when zinc predominated In
                                                            th« mixtures, the fractional toxlcltles
                                                            could be summed to give the toxicity of
                                                            the mixture.

                                                                    Rainbow trout were exposed to     Brown, et
                                                            cooper, phenol, zinc, or nlcKel solutions al(19701,
                                                            to determine  and cooper, zinc, and
                                                            nickel.  It was concluded that acute
                                                            lethal  toxlcltles of  the mixtures could
                                                            be adequately described by summations of
                                                            the fractional  tnxlcltles.
                                                                                                      Brown,et al
                                                                                                      (1970).
                                                                   same as above
        One hundred slxtr-four            Alabaster
oestlcldes, wetting agents, and           (1969),
miscellaneous water pollutants showed a   ANIC-5*25
wide range of toxicity scanning 12 orders
of magnitude.  Knowing the toxicity and
percentage of all components of a
formulation did not result In easy
predictability of the toxicity of a
mixture of materials.  Sometimes
pesticides were most toxic in hard water
and sometimes the opposite was true*
Testing the actual material as sold Has
found to be essential.
-------
 Ptienols
 Rasbora
 heteromorpha
                                    BCF*
                                    and
                                    BS»
7.1. IT2,
softwater)
 Phenols
                      Leooals
                      macrochlrus
              BS»,
              L
                                                       13.9 I TO
Phenols
Phenol*
Phenols
                      Nltzschla
                      linear is'
              BS«,
              L
                     Physa         BS«»
                     haterastrooha L
                     Hercenarla
                     •ercenarla

                                                       258  (TSI
                                                       9*  (Ttl
                                                      5Z.6  UZ)
ft»,e,e,f,
bard (HW)
or 30ft
(SW)
synthetic
dilution
water or
sotwater
for some
species

a*»e» and
synthetic
dilution
water
                a*tCt  and
                synthetic
                dilution
                •ater

                a*«e,  and
                synthetic
                dilution
                water
saae as above
Phenols
Phenols
Hercenarla
•ercenarla
IIarvae)
                     Crasiostraa
                     vlrqlnica
                                   L     —
                                   t     —
                                                      99 (T12t
                                                      98.3 ITZI
                                   Alabaster
                                   (1959),
                                   *NIC-5*Z9
                                   This study HSS conducted to       Patrick*  et
                           d«ternlne  the relative toxicltles or  It    al  (196a).
                           coimon  constituents of industrial  wastes   »NIC-57?0
                           to  a  Msh,  an alga* and  an  Invertebrate.
                           The experiments Here conducted  over a
                           10-year period for varied purposes.  The
                           authors recoavend  bloassays Hlth at least
                           three components of the  food web.
                                                                                        saae  as above
                                                                                        same as above
                                                     Patrick,  et
                                                     al  (1968),
                                                     »nIC-97ZB
                                                                                                      Patrick, et
                                                                                                      al (1468),
                                                                                                      AMIC-5720
                                                                    The effect of 92 pesticides on    Davis, et al
                                                            embryonic development of elans and
                                                            oysters Mas reported.  Synerqlstlc        (1989),»MIC-
                                                            effects with solvents Mere also reported. 9990
                                                             Host of the compounds affected
                                                            develocaent acre than survival.  Some.
                                                            however, drastically reduced larval
                                                            growth.  The authors Point out the
                                                            necessity of evaluating The effects of
                                                            pesticides on all life stages of an
                                                            organism and note the possibility of
                                                            selecting chemicals for pest control that
                                                            would not have serious effect on
                                                            shellfish.
                                                                                        saae as above
                                                                                        same as abeve
                                                                    Davis, et al

                                                                    «t969».*t«C-
                                                                    9990

                                                                    Davis, et at
-------
  Cemeund
                        Organise
                                   Field  FUld
                                   Study Locatla
Toxlclty.
Active
Ingredient,
  Ppm
                                                 Experimental
                                                 Variables,
                                                 Control led
                                                 or Noted
                                                                                                 Convents
                                                                                                      R«l«r«nc«
•nenols
                      (eqqsl
                     Sal BO
                     qalrdnwl
                                   BS»
                                                      9.* IT2I
Phenol*
                                   BS»
Phenols
Phenols
Phenols
Phenols
Phenols
                     Ganbusla
                     af finis
                     (female.  t.3
                     cm,  1.9 ql
                     Leblstes
                     retleulatus
                     (•ale. l.t
                     e«, a.? qi
                     Tllapla
                     aossaoblca
                     (T.I. c», 1.3
                     qi
Kuhlla        BS»
sandvtcensls
«i.3 c«, 1.5
9>

Stoteohorus   BS»
purourva 13.6
ca, I.* gl
                                                       26  ITdl
                                                 •..o.d.
                                                 •,r»i,
                                                 (Honolulu
                                                 tap
                                   BSA   —
              BS»
                     Carclnus
                                   BSA   —
                                  si
                                 19  IT*)
                                                      11  ITVI
                                                      8.91 IT12 hr)
                                                      96 IT?)
                »,c,d,e,
                e.f.l,
                (Honolulu
                tap
                water
                a,c,d,e,f,
                1,
                sal tnater
                                                                      a,c,d,e,f,
                                                                      I, salt
                                                                      «ater
                                                                                                      9990

                                                                    RalnboH trout Here exposed to     Broun, et al
                                                            coooer, phenol, zinc, or nickel solutions (1970),
                                                            to detvrolne *8-hour LC50 values for
                                                            • Ixtures of copper and phenol I coooer,
                                                            zinc, and phenoll and coooer, zinc, and
                                                            nickel.  It MBS concluded that acute
                                                            lethal toxlcltles of the mixtures could
                                                            be adeauately described by summations of
                                                            the fractional toxlcltles.
        The five fish soecles are
commonly found In streams and estuaries
                                                                     Nunoqax», et
                                                                     • i (iirott
                           In semi-tropical areas.  C. affinis Mas   AMIC-6S67
                           the most tolerant.  Varied sensitivity to
                           the toxicants  Mere  found.  K.
                           sandvlcensls MBS the aost sensitive fish
                           studied.  The  standard Method procedure
                           •as followed.
                                                                   *••«
                                                                           above.
                                                  ^Honolulu
                                                                   saee as above
                                                                                        same as above
                                                                                        same as above
                                                 ••(contin-         one hundred-forty surface active
                                                 uous aer-  agents, solvent eaulslflers, pesticides,
                                                 •tlon, sea-polychlorlnated blphenyts, pure
                                                 water, and Inorganic* and organic chealcals Mere
                                                                      • 1
                                                                      AHIC-6S67
                                                                                                      NunooaHi, et
                                                                                                      al  (1970),
                                                                                                      1)110-6967
                                                                                                                           Nunoqawa, et
                                                                                                                           al (1970)*
                                                                                                                           •HIC-6567
                                                                     NunogaMi,  et
                                                                     al  (1970).
                                                                     ANIC-6967

                                                                     Portaann,  et
                                                                     al  (1971),
                                                                     •NTC-7701
-------
 Phenols
                      Cardlua edule BSA
                                                       greater then
                                                       Mi (T2t
                      Cranoon
                      eranqon
              BS»   —
                                                       Z3.5 ITZt
Phenols
                      PandaIus
                      eontaqul
                                                       17.5 tret
                dally      evaluated against  as  aany as  ten  aarlne
                solution   organises.  The  authors noted that east
                renewal)   published data of  this type d*al  with
                           toxlclty of chealcals to freshwater
                           organises.

                ae(eontin-        *••• •* above
                uous, aer-
                ation, aea-
                water, and
                daily
                solution
               ,renewal)


                ae( contin-
                uous, aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)


                a«(contin-
                uous, aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)
                                                                                                       Portaann, at
                                                                                                       el U97t>.
                                                                                         see* as above
                                                                                         »a«« as above
                                                                                                       Portaann, at
                                                                                                       al 11971).
                                                                                                       •HIC-7701
                                                                                                       Portaann,  at
                                                                                                       al  11971),
Phenels
Platlcthys
flesus
                                   ss»   —
                                                       33-180 (TZ)
                a* (con tin.
                uous, aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)
                                                                                         save as above
Portaann, at
al (1971),
•HIC-7701
Pnenois
tobassls
ssfeha
                                   BS»   —
13.5 |T1I       a*.                Measureaent of residual dissolved Ballard, et
                seanater   oxyqen during exposure of fish to         al
                           toxicants resulted In data similar to     (1969>,AHXC-
                           that obtained fro" Zd- and *8-hr          300
                           bloassays by the standard aethod.  The
                           residual oxyqcn aethod required only 8 hr
                           to conduct.  Variables studied Included
                           density per unit voluae, teaoerature, and
                           fish size.  The authors conclude that the
                           residual oxygen oethod Is a Quick and
-------
  CoBpound
                        OrganlsB
                                    Field   Field
                                    Study location
                                  Toxtelty,
                                  Active
                                  Ingredient,
                                   Ppa
                                    Experimental
                                    Variables,
                                    Controlled
                                    or  Noted
                                                                                                 Comments
                                                                                                      Reference
Pnenoxylene
                      Crangon
                      crangon
                                    BSA    ~
                                                            reliable procedure  for routine monitoring
                                                            MorK.

                                  greater than 10  a«(contln-         One hundred-forty surface active  Portaann, et
                                  ITZJ             uous, aer- agents, solvent  emulslfiers, pesticides,  al  (1971),
                                                  ation, sea- oolychlorlnated  blphenyls, pure           AHIC-7701
                                                  water, and Inorganic, and organic chemicals Here
                                                  daily      evaluated against as  many as ten marine
                                                  solution   organisms.  The  authors  noted that most
                                                  renewal)   published data of this type deal with
                                                            toxlclty of chemicals to freshnater
                                                            organisms.
PhenoKVtol
                      Pasbora
                      heterororoha
               BCFA   —
               and
               BSA
                                                       135  IT2)
                                    a*,e,e,f.           One  hundred sixty-four            Alabaster
                                    hard (HM1   oestlcldes,  Netting agents,  and           (1969),
                                    or soft    miscellaneous Hater pollutants shotted a   AMIC-5*25
                                    (SW)synthe Hide range of toxlclty spanning 12 orders
                                    tic        of  magnitude.  Knowing the toxlclty and
                                    dilution   percentage of all  components of a
                                    Hater,  or   formulation  did not result In easy
                                    seanater   predictability of  the toxlclty of a
                                    for some   fixture of materials.  Sometimes
                                    species    oestlcldes Here most toxic In hard Hater
                                               and sometimes the  opposite Has true.
                                               Testing the actual material  as sold was
                                               found to be  essential.
Pneny I mercuric
acetate
Pnenyl »ercurie
•cetate
Brachydanlo
rerlo
(breeding
adults and
eqgs)
Sal BIO
g«lrdn*rl

                    0.2 and 1.0 ppb a*,f
                    (01
 BCFA
 and
 BSA
                                                       9.995  IT1)
Pnenyl "arcurie
Salvo
9alrdnerl
BCFA
and
BSA
                                                      0.10* IT?)
a*,c,e,f,
hard
(HHtor
soft (SH)
synthetic
dilution
Hater, or
seaHater
for soa*
species
                                                                      a*,e,e,f,
                                                                      hard
                                                                      tHUIor
                                                                      soft (SHI
                                                                      synthetic
        Eggs Here collected daily from
spawning females which Here continuously
exoosed to nater solutions of the
chemical.  Dead and hatched eggs were
counted daily with dally Hater renewal
and removal of dead eggs.  At 1.0 oob the
number of eggs released was significantly
less, and at 0.2 and 1.0 nob hatching
frequency was significantly reduced.

        One hundred sixty-four
pesticides, Hettlng agents, and
miscellaneous water pollutants showed a
Hide range of toxlcity scanning 12 orders
of magnitude.  Knowing the toxlcity and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of aaterlals.  Sometimes
pesticides Here most toxic In hard Hater
and sometimes the opposite Mas true.
Testing the actual material a* sold Has
found to be essential.

       saae as abova
 Klhlstroa,
 et  al
 (1971),
 AMIC-2707
Alabaster
(1969), ANIC-
Alabaster
(19691,AHIC-
5*2?
-------
 Pnorate
 Ph order*
•ftosalon*
•ttosdrln
»h os drin
                                                                       dilution
                                                                       Mater, or
                                                                       seaMater
                                                                       for son*
                                                                       species
                      Fish (not
                      specified*
                      Crangon
                      crangon
                    greater  than
                    O.n-1.0  IK)
                                                 Approximate  toxlcltles  of
                                        numerous pesticides  commonly used  la
                                        Britain  Here  summarized.  An excellent
                                        brief, qeneral  discussion o» toxlclty
                                        testing  is  also present.
                                    BS*    —•
                    greater  than  10  aofcontln-          One  huncred-forty  surface  active
                    fTZ)             UOUS,,  aor- eqents,  solvent  evuis if ter-s«  pesticides,
                                    ation,  aea-Po'vchl°rlnated  biohenyls,  pure
                                    water,  and inorganic, and organic  chemicals Here
                                    daily      evaluated against  as  many  as  ten *arlne
                                    solution   organisms.   The  authors noted  that nost
                                    renewal)   published data of  this  type deal Mlth
                                              toxlclty of  chemicals to freshHater
                                              organisms.
                                                                     Handesley-
                                                                     Thomas
                                                                     11971),AMIC-
                                                                     10S6
                                                                                  Portmann, et
                                                                                  •I  (1971),
                                                                                  AHIC-7701
                      Rasbora
                      heteroaorpha
BCF*
and
BSA
                                                       O.I. (T2I
                     Cooepods
                     (Cyclops
                     blcusoldust
                     Cyclops
                     varlcans»
                     Cyclops
                     vernal Is,
                     Fucvcloos
                     agll Is.Macroc
                     Macroeyclopa
Fl    State
•nd   Colleget
BS»   Hiss.
             0.059 (91
             percent KZI
                     Orthoeyclops
                     •o4*stus)
                     Conepods
                     (Cyclops
                     bleusnl
-------
   Coveeund
                        Organise
                                    Field  Field
                                    Study Location
                                                      Toxiclty*       Experimental
                                                      Active          Variables,
                                                      Ingredient,     Controlled
                                                        Ppa           or Noted
Pttovdrln
•tiespnaeldon
Ftiosphaaldon
Cueyclops
•gills,
Haorocyelops
'albldus*
Orthoeyelops
•odestusI

TubIfex
tubIf ex
                                    Ft
                                    »nd
                                    BS"
SelionI,
Ml*«.
                      FI«h Inat     ~    ~
                      specified)
                      Lab*o rohlta  8SA   —
                      Ifrvt
                     Hastoeeebolus BS«
                     panealus
                     Necrognethus  BSA
                     aculcatu*
                     Nandus nandus BS»   —
                                                       1.1 INTO
             greater than
             1.0-11.1 IKI
             137.7 1T7I
                                                                                                  Coaaents
                                                                                  Reference
                                                            IT7>
                                                         .7  IT7)
                                                       5*.7  |T7I
                                                                                         saee as above
                                                                                          Approximate  toxlcltles  of
                                                                                 numerous pesticides  conaonly  used  In
                                                                                 Britain  were  suaaarlzed.  An excellent
                                                                                 brief, general  discussion of  toxlctty
                                                                                 tasting  Is also present.
Naovl, et at
(19691,
AN1C-5979

HaHdesley-Th
  oaas(1971)
AHIC-1856
                             a«c,dtetf          OOVP end Pho*oh»«ldon «ere shoiin  Konar
                                        to be selective toxicants that can be     119691,•NIC-
                                        used for eradication of undesirable       SS53
                                        anloals fro* ponds without Injuring carp.
                                         OOVP seeaed superior since less UBS
                                        needed. It Mas not Influenced by
                                        turbidity, and It  'etrxlfled core rapidly
                                        than phosphaaldon.
•»MP»*.l*a»
*>He*p*ael4on
•ttosphaaldon
•hesphaaidon
Fh«*ah**lden
Labeo rohlta
(flngerllna)
Trlchogastar
fasclatus
Channa
punctatus
Ifryl
Channa
punctatus
(f Ingerllngt
Chitnna
punctatus
ledultl
BSA —
BSA ~
BSA —
BSA ~
BSA —
177.0-215.?
IT7I
30. Z IT7t
19.1 CT7)
?5.l ,AHIC-
                                                                                                                            «HIC-5»53
                                                                                                                            Konar
                                                                                                                            (1969).*HIC-
                                                                                  Koner
                                                                                  « 19691, «HIC-
                                                                                  Konar
                                                                                  « 19691, •NIC-
                                                                                                                            Konarll969>,
-------
         Phasenaaldon
          «»•» anaal don
          MiospMaaldon
          anosphaaldon
Aaohlonou*    BSA
cuchla
{younaj

Aaphlpnous    SSA
cuchla
 tadultl

Hrstus        BSA
vitatus
PuntI us       BSA
sophor*
                                                                11. I ITTI
                                                                 ?.* ITTI       ».e.d,».t
                                                                  2.2  IT7I        ate,d.*.f
                                                                       IT7I       a.e.d.atf
                                                                                                   aM as abova
                                                                                                  saaa  as  abova
                                                                                                   San* as above
                                                                                                   >••• as abov*
                                                                                                       Konar
                                                                                                       tl969)
                                                                                                       51.53
                                                                                                       Konar
                                                                                                       (l<)69»j*HIC-
                                                                                                       51.53

                                                                                                       Konar
                                                                                                       11969),
                                                                                                       »MIC-5«.5J

                                                                                                       Konar
                                                                                                       119641.
                                                                                                       AHIC-5V53
          •tiospnaaldon
 Inabas        BSA
 tavtudlnau*
                                                                      ITTJ        atc*dfa»r
                                                                                                   sa*a as abova
                                                                                                       Kcnar
                                                                                                       119691
U)
          •tiosphaaldon
          PhvspnaaMon
          ftio«ona«lden
          PhMpnaalden
Eateropnaoa- • BSA
tea  foaaills
llryl

H»t«ropa«ua- ' BSA
tea  roaailla
                                             BSA   —
danrlea
lfr»)

Ovtlseus sp.  BSA
                                                                 66.8  IT7)        ».c,d.«,«
                                                                 66.1  ITT)        a,Cid»«»r
                                                                 178.2 (T7>       a.e.d.atf
                                                                 1.3 IT7I
                                                                                 a,ctdt*t»
                                                                                                   *••• as above
                                                                                                   sano as abovo
                                                                                                   sa*« as abovo
                                                                                                   •an* as abova
                                                                                                       Konar
                                                                                                       I1960).ANIC-
                                                                                                       5*53

                                                                                                       Konar (1969),
                                                                                                       Konar
                                                                                                       I1969),ANIC-
                                                                                                       5*53

                                                                                                       Konar
                                                                                                       I1Q69I .A1IC-
                                                                                                       5*53
          •»»«sphealdon
Sohacredaaa   BSA
annulatua
                                                                 2.6  IT7)
                                                                                 a.Ctdta«f
                                                                                                   sano as abovo
                                                                                                       Konar
                                                                                                       <19M)
                                                                                                       51.53
          •1i«spha«l4on
Ranatra       BSA
flllforal*
                                                                 2.9 IT7I
                                                                                 a,Ctd.«>f
                                                                                                   SOB* as abovo
                                                                                                       Konar
                                                                                                       (1969),
                                                                                                       »MIC-5I,5J
          PhMpnaaldon
Anl«oot«ra    BSA
Invaphs)
                                                                 1.9 IT7t
                                                                                 a«Ctd«a>f
                                                                                                   saw* as abovo
                                                                                                       Konar
                                                                                                       I1969).AHIC-
                                                                                                       51.53
                               Crblstcr so.  BSA   —
                                                                 2.3 IT7)
                                                                                                   saa* as abovo
                                                                                                       Konar
                                                                                                       I19S9),
                                                                                                       AMIC-5V53
          •ttesphaaldon
                               Napa
                                             BSA   —
                                                                 2.* IT7>
                                                                                                   sana as abovo
                                                                                                       Konar
                                                                                                       (1969).
                                                                                                       »HIC-5*53
          Pnospnaaldon
 Bale«to«a     BSA
 Indlea
                                                                 6.3 (T7t
                                                                                 •tcf
                                                                                                   saa* as abovo
                                                                                                       Konar
                                                                                                       11969)
-------
  Coepovnd
Phospnaeldon
Pne*ona«ldan
•ttosahaaldon
•hesphaaldon
•nosBftaeldon
•tiosphaaldon
•nospnaeldon
Phesphaeldon
Phosptteeldon
•tiesaneelden
•*es»na«ldan
            Field  Field
Organise    Study Location
                      Hydroohltus    BSA    —
                      Volvox
                                   BS»    —
PanderIna     BSA   —


Closterlua    BSA   —


Bracnlonus    BSA   ~


Gastrotrlcha  BSA   ~


CyerIs        BSA   —


Cyetoos       BSA   —


NauDllus      BSA   —


Oepnnla       BSA   —


Cerlodapnnla  BSA   —
                                 Toxlcity.       Cxoerleental
                                 Active          Variables.
                                 Ingredient.     Controlled
                                   Ppe           or Noted
                                                                                                  Coeeents
                                                       9.S  IT7I
                                                       *.•  INTO
                                                       91 (NTEI
                                                       It  INTEI
                                                       It  INTO
                                                       ?.*  (Kl
                                                       ?.*  IK)
                                                      2.5  IKI
                                                      *.•  IKt
                                                                       atCtdtetf
                                                       S.I  (NTE)        a.c.d.e.t
                                                                       e.c.d.etf
                                                           (NTO        a.c.d.e.f
                                                                       a«Ctde.f
                                                                                         saite  as above
                                                                                         saee  as above
                                                                                         save as above
                                                                                         saee as above
                                                                                         «••• as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                        seae as above
                                                                                        seae as above
                                                                                        saae as above
                                                                                                                           Reference
                                                                                                    *NIC-*tS3

                                                                                                    Konar
                                                                                                    (1969),
                                                                                                                            Konar
                                                                                                                            (19691.
                                                                                                                            Kon»r
                                                                                                                            (1469),
                                                                                                    Koner
                                                                                                    (1969).
                                                                                                    iHIC-51.53

                                                                                                    Kon»r
                                                                                                    11069).
                                                                                                                            Konsr
                                                                                                                            (1969).
                                                                                                    Kanar
                                                                                                    (1969).
                                                                                                    »HIC-5«.S3

                                                                                                    Konar
                                                                                                    (1969).
                                                                                                    »HIC-5«.53

                                                                                                    Konar
                                                                                                    (1969).
                                                                                                                            Koner
                                                                                                                            (1969t,
                                                                                                                           Konar
                                                                                                                           (19691.
-------
          Phosphorus
                               Paralabrax
                               clathratu*
                                             FH
vn
          Phosphorus
          Phosphorus
          Phosphorus
         Phosphorus
         Phosphorus
         Phosphorus
         Phosphorus
         Phosphorus
                               Paralabrax
                               clathratus
                               Paralabrax
                               elathratu*
                               Paralabrax
                               clathratus
Paralabrax
clathratus
Paralahrax
elathratus
Paralabrax
clathratus
(gravid
females)

Paralabrax
elathratus
Paralabrax
clathratus
                                             FH
                                             FH
                                             FH
                                             FN
                                             FH
                                            FH
                                            FH
                     Scattergood   6320  (dorsal
                     Steaa)  Plant,  muscle
                     Los  Angeles,  RrSIOUE)
                     Cal.
                    Catallna     7550 (dorsal
                    Island* Cal. muscle
                                 raaldua)

                    Seatterqood  BfcliO (ventral
                    Steaa Plant, muscle
                    Los Angvlas, roaldua)
                    Cal.
                    Catalina
                    Island, Cal.
             6700 (ventral
             •use I a
             residua)
Scatterqood  Z3,6ZO (gonads
Steam Plant, residue)
Los Angeles,
Cat.
Catallna
Island, Cal.
?3.920 loonads
rest duel
CatalInalsla 10.S50(gonads
nd, Cal.     residue)
Scattergood  9600 (liver
Steaa Plant, residue)
Los Angeles,
Cal.

Catallna     7270 (liver
Island, Cal. residua)
                                                Fish  collected  from an effluent
                                        Dlo* of a stean olant and from offshore
                                        waters of Catallna Island Mere analyzed
                                        for trace element content.  Trace element
                                        content oT  the effluent Hater was at
                                        le»*t 1 times qreater than that of normal
                                        sea water for cadmium, copoer, nickel,
                                        zinc, and chromium.  Livers of fish from
                                        the effluent  Mere nearly tHlce the size
                                        of those from the ocean.  Greatest
                                        differences In concentration occurred
                                        Nlth aluminum, cadmium, and nickel.
                                        Silver, barium, lithium, and lead showed
                                        the least differences.  The author
                                        concluded that trace element analysis of
                                        tissues could be used to determine the
                                        effect of pollutants on aarlne organises.

                                               same as above
                                                                     Staoleton
                                                                     (1968),
                                                                     AHIC-5980
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same  as above
                                                                                                  same  as above
                                                                                                 saae  as above
                                                                     Staoleton
                                                                     (19681.
                                                                     AHIC-5980

                                                                     Staoleton

                                                                     AMIC-«98D


                                                                     Staoleton
                                                                     (1968),
                                                                     AMIC-59BO

                                                                     Staoleton

                                                                     AMIC-5980
Staoleton
(19681,
ANIC-^980

Staoleton
(1968),
AHIC-59BO
                                                                     Staoleton
                                                                     (1968),
                                                                     AMIC-S980
                                                                     Stapleton
                                                                     (19681.
-------
I
Compound

Phosphorus
Phosphorus
Phosphorus
Phosphorus
Phosphorus
Phosphorus
Phosto*
Organism

Paralahrax
clathrntus
Paralabrax
clathratus
Paralabrax
el nthrntus
Paralahrax
clathratus
Paralabrax
elathratus
Paralabrax
clathratus
Crangon
crangon
Field Field
Study Location

FH Scattergood
Steam Plant,
Los Angeles,
Cal.
FH Catallna
Island, Cat.
FH Scattergood
St»am PI iint,
Los Angeles,
Cal.
FH Catallna
Island, Cal.
FH Scattergood
Steam Plant,
Los Angeles,
Cal.
FH Catallna
Island, Cal.
BSA —
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments

?53fl « same as above
1 Integument
residue)
2520 -- same as above
(Integuaent
residue)
5800 (heart -- same as above
residue)
5550 (heart -- saae as above
residue)
7800 (eyeball — same as above
residue!
10,d50 (eyeball -- same as above
residue)
greater than 10 a,»(oontln- one hundred-forty surface active
ITZ) uous aer- agents, solvent emulslflers, pesticides,
atlon, sea- polycMorlnated blohcnyls, pure
Reference
AHIC-5980
Staoleton
(1968),
AHIC-5980
Staoleton
(1968),
AHIC-5980
Staoleton
(1968) ,
AHIC-5980
Staoleton
(1968),
AHIC-5980
Staoleton
(1968),
AHIC-5980
Staoleton
AHIC-5980
Portnann, et
al (1971),
AHIC-7701
         Pt»oto»1drln
         Ptiotoaldrln
                               Anaeystls
                               nldulans
                               Agneneltue

                               lloatw
                                             L      —
1.0 (growth
Inhibited)
                                                                NTE
water, and Inorganic, and organic chevlcals were
daily      evaluated against as many as ten marine
solution   organisms.  The authors noted that most
renewal)   published data of this type deal with
           toxlclty of chemicals to freshwater
           organisms.
a»,e»,r            Hetabollc products ot Aldrln,
SH         Oleldrln, and Endrln can be as toxic as
           the parent compounds, as shown by  00
           measurement.

a»,c»,r           saae as above
SH
  Batterton,
et al
(1971),
AHIC-1V71

Batterton,
• t al
11971),AHIC-
-------
Photodleldrln
Photodleldrln
Phygon
                      igmenellum    L
                      ouadruolIcatu
                     Anacystls
                     nldulans
                     Hereenarla
                     •ercenarla
                     f«99*»

                                   L     —
                                 0.5-1.0 (growth a»,e»,r
                                 Inhibited)      SH
                                 0.9-1.0 (growth a'.
                                 Inhibited)      SN
                                                      0.04 
•hygon
Phyqon
Plcloraa (K salt)
                     Mercenarla
                     •ercenarla
                     (larvae)
Crassostrea
vlrqlnlca
                                   l_     ••
                                   |      ^^
                     Grassestrea
                     vlrglnlca
                     I larvae)
                     Rasbora       BCF»
                     heteronorpha  and
                                   BSA
                                                      1.75
                                                      O.Olfc (T2I
                                                      O.OI>1 (Til.)
                                                      tl «TZ)
                                                 hard  (MM)
                                                 orsof t
                                                 (SH)
                                                 synthetic
                                                 dilution
                                                 voter,  or
1U71

Pattertoni
et at
                                          Patterton.
                                          et al
                                          (1971) ,
        sane  as above
        sane  as above
                                                                    The effect of 5? o»stleldes on    Osvls, et al
                                                            embryonic d«vcloo«ent of clams and
                                                            oysters was reported.  Synerqlstlc        H969),AMIC-
                                                            effects with solvents Here also reoorted. 5990
                                                             Most of the compounds affected
                                                            develocment more than survival.  Sonet
                                                            however, drastically reduced larval
                                                            growth.  The authors point out the
                                                            necessity of evaluating the effects of
                                                            pesticides on all life staqes of an
                                                            orqanlsa and note the oosslblllty of
                                                            selecting chemicals for pest control that
                                                            Mould not have serious affect on
                                                            shellfish.
                                                                                        same as above
                                                                                        s»me as above
                                                                                        same as above
                                                                      for soae
                                                                      species
        One hundred sixty-four
pesticldeSf Netting agents, and
miscellaneous Hater pollutants showed a
xH« range of toxjclty scanning 1? orders
of magnitude.  Knowing the toxicity and
percentage of all comoonents of a
formulation did not result In easy
predictability of the toxicity of a
mixture of materials.  Sometimes
pesticides were most toxic In hard Hater
                                                                                                                           Davis, «t al
                                                                                                                           <1969>i««C-
                                                                                                                           5990
                                                                                                                           Oavis, et at
<1969»
5990

Davis, et al

(1969),AHIC-
5990

Alabaster
(1969),
AHIC-StZS
-------
I
Gonoound



PMk















Polycell product








Po lye lens






Polyclens





Toxlclty, Experimental
active Variables*
Field Field Ingredient. Controlled
Organism Study Location Pp« or Noted Comments
and sometimes the ooooslte Mas true.
Testing the actual material as sold was
found to be essential.
Salmo L — 2.0 «S830) 8,e,f (1 Single exposures of fish to
galrdnerl hr oriano*ercury compounds resulted In peak
exoosure concentrations of mercury as follows*
dally for gills, f hri blood. 37 hri liver, 7 dat
up to 11 Kl
-------
                                                                      renewal)
*elycl«ns
                     Crangon
                     er anger>
                                   8SA   —
                                 10-33 (T2)
                             ••(contin-
                             uous aer-
                             ation, sea-
                             water, and
                             dally
                             solution
                             renewal)
                                                                   •••• as above
                                                                                                      Porteann, «t
                                                                                                      81 (19711,
                                                                                                      *NIC-77ei
•*l*clens
                     PandaIus
                     aontagul
                                   as*   —
                                                 a»(eontln-
                                                 uo.ua aer-
                                                 ation, aea-
                                                 vater, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                   saaa as above
                                                                                  Porteann,  et
                                                                                  al
                                                                                  (i97i>,*n-ic-
                                                                                  7701
Polycoaolax »-ll
                     Steel head
                     trout
                     I finger line,* I
                                   as*   —
                                                      i3.e mi
rolyoojcplex A-U
MlyeaeipIeK »
Cobe aalaon   B8A
(flngerlinga) In
              •Ita
Hood Canal,
Hoodaport,
Wash.
                     Carctnus
                     •aanas
                                   8S»   —
                                                      1.5
                                                      100-330 HIC-383<»
                                                            ranking.  Ranking was based on toxlclty
                                                            and oil dispersal effectiveness.  Corexlt
                                                            776t eppeared to have the least toxleltv
                                                            Blth fair to good ell dlsoerslon
                                                            caoabllltv.
aano as aoova
                                                 a*(eontln-         One hundred-forty surface active
                                                 uous, a«r- agents, solvent eeulslflers, pesticides,
                                                 atlon, soa'Polvchlorlnated blohenyls, pure
                                                 water, and inorganic, and organic chemicals Mere
                                                 dally      evaluated against as aanv as ten aarlne
                                                 solution   organises.  The authors noted that Best
                                                 renewal)   published data of this type deal nltn
                                                            toxlclty of cnealcals to freshwater
                                                            organises.

                                                 a»(contln-        saae as above
                                                 uoua, aer-
                                                 ation, aea-
                                                 water, and
                                                 dally
                                                 solution
                                                 ronawal)
                                    Tracy, et al
                                    (1969).
                                    AMIC-383U

                                    Portnann, et
                                    al  (1971),
                                    »MIC-7701
                                                                                                                           Portaann, at
                                                                                                                           al (197l>,
                                                                                                                           •HIC-7701
-------
  Compound
Polycoaplex A
Field Field
Organise Study Location

> • IJaanda BSA —
llmanda

Toxlclty,
Active
Inqredlent,
Ppa

33-101 IT2)

Experimental
Variables.
Control led
or Noted Comments Reference
renewal)
••(contln- saaa as above Portmann, et
uou» aor- el (I97i>,
aUon, aea- ANlc-7701
•mtar, and
solution
renewal)
Roceus        BSA
saxatllls
Polrotlc
»*ta>
fetanlua chloride   Nltzsehla     8S»,
                     linear Is      L
•otasslua chloride   Physa         BS»,
                     tteterastropha L
•otasslua ehroaat*   Lepoals       BS»,
las Crl              aacrocMrus   L
Pat ass I ua cttroaate   NltzscMa     BS*«
las Cr)              llnearls      L
                                                      1.337 (TSI
                                                      940 IT«)
                                                            ITd)
                                                      7.8ITSI
a*>Ctd
-------
Potess'lue; cyanide
(•» cyanide)
Carclnus
                                   BSA   —
greater than 5  ««(oontln-         one hundred-forty surf»e* active
IT?)            uous. «ar- agents, solvent eaulslflers, pesticides,
                fctlon, aoa»oolychtorlnated blohenyls, our*
                water, and Inorganic, and organic chemicals were
                dally      evaluated against as eany as ten aarlne
                solution   organises.  The authors noted that aost
                renewal)   published data of this type deal tilth
                           toxlclty of chealeals to freshwater
                           organises.
Potassluei Cyanide
las cyanide)
Crangon
crangon
                                   BS*   —
greaterthan 29  a«(contin-
                uous, aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)
                                                                   save as above
                                                                                                      Porteanrv, at
                                                                                                      at
                                                                                                      C1971>,»HIC-
                                                                                                      7701
                                                                     Portaann, at
                                                                     al
                                                                                                                           7701
•etasslu* cyanide
(•• cyanldel
Petasslua cyanide
Pandelus
aontagul
                     Leblstes
                     retleulatus
                     (1 aot 1.1
                     cat
                                   BS«   —
                                      U2)
                                   ecr   —
                                                      0.26 IT2)
       liw  cyanide
Leblstes
retleulatus
II ao. 1.1
ea)
                                   BCF    —
                                                           IT1)
                a* (contin-
                uous aer-
                ation, sea-
                water, and
                dally
                solution
                renewal)

                a,c,d,e,f,
                n,q, phos-
                phates,
                carbon-
                ates, bl-
                earbon-
                ates, sul-
                fktas, and
                conduc-
                tance
                                                                   saae as above
                                                                     Portaann, et
                                                                     al (1
-------
  Coajoound
            Field  Field
Organise*    Study Location
                                                      Toxlclty.
                                                      active
                                                      Ingredient,
                                                        PC*
Experimental
Variables,
Controlled
or Noted
                                                                                                 Comments
Reference
                                                                      carbon-
                                                                      ates, bi-
                                                                      earbon-
                                                                      ate», aul-
                                                                      ffttes, and
                                                                      conduc-
                                                                      tance
Potassium* dlchroaate Leoomls       BSA,
fat Cr)              macroehlrus   L
                                                      113 mi
Potassium dlehroaato Nltrsehla     BS».
las Cr)              linearIs      L
Potassium) dlchroeate Ptwsa         85*.
(as Cr)              heterostrettna L
•otasslu* dlchroaata Phoraldlua    L
(as Cr)              aablquua
                                                      0.71 IT5)
                                                      17.3
                               O.S-10.0  (16
                               p«rc*nt
                               growth
                               lanlbitad 14)
                                               a*,a<  and
                                               synthetic
                                               dilution
                                               •atar
                                               »*«e»  and
                                               srntnetlc
                                               dilution
                                               water

                                               »',»,  and
                                               synthetic
                                               dilution
                                               •ater
                   This study Mas conducted to
           determine the relative toxlcltjes of 20
           co**on constituents of industrial wastes
           to a tlsh, an alqa» and an Invertebrate.
           The exoarlnents Here conducted over a
           ID-year period for varied purposes*  The
           authors recon*end bloassays with at least
           three components of the food neb.

                  saae as above
Patrick, at
al 11968),
»MIC-57?J
                                                     Patrick, at
                                                     al C1968),
                                                                                        saae as above
                   Of  7<> chemicals  evaluated as
           alqlcldes,  only 9 Mere more  toxic than
           CulOI..   Non« Inhibited gronfh of
           Bat-forming alqae for  *or* than 2 MeeHs*
           Cu'SOii  formulated with  certain wetting
           agents  Mas  more toxic  than CuSOfc  alone.
           Coeoer  chloranlne was  also found  to be
           more  toxic  than Cu*>0<>.  No netting agents
           •ere  found  to be Inhibitory  at  the
           concentrations Investigated  (0.05 and
           0.005 ooml.   Also reoorted are  factors
           effecting groxth of  al?ae  In canals to
           determine whether there  Mere leads to
           controlling aloae by environmental
           management.   No practical  environmental
           means Mere  tound.
Patrick, at
al
tl96«>,AHIC-
57?0

Otto ri?70>.
4HIC-892
•otasstua dIehrornate Brachydanlo   BS»   —
                                                      56-75 (SB*)
                                                                      a,e.  and
                                                                 Feeding behavior Mas affected by  Cairns, at
-------
                             p«rlo
        •otasslu*
        ventachloroohenate
                     Oncorhynchus
                     klsuteh (CSE
                     119 eabryo
                     cells)
                                           L      —•
                                                              l.fl-120  (SB10)    a*
I
U>
•otatSlu*
•ervanganate
Trachlnotus
carolInus
(Juvenile)
                                   BS»    —
1.6-2.9 «T*>
        Potasslu*
        permanganate
        •otasslu*
        »araan«anata
                     BOCCUS
                     saxatllls
                     (fingerIinqs)
                                          BSA    —
                     Pnoraldlua
                     aablguua

                                                              2.5  (TO
                                 0.9-10.0  (16
                                 percent groNth
                                 Inhlbltadi*)
synthetlcd zinc, cnroalue, and »flS In that mart tl«e al 119671•
llutlen    Has reaulred  for consuming Measured       AHIC-5707
••tar      aoeunts of food.  r**dlnq rcsoonse Mas
           •••so affected by aeration, feeding
           schedule,  light Intensity, and Outside
           disturbances.  The authors note that nuch
           •ore norfc  Is needed to establish the
           reliability of this procedure.

                   Growth of cultured coho salaon    Hanes, et at
           enbrvo cells on Eanle's HEM was oartlally (1970),
           Inhibited at ".0 oon. stronqly Inhibited   AMIC-3753
           at 80 cow, and totally Inhibited at 210
    ,      Dp*.  The SO percent Inhibitory dose »»s
           estimated to he 6ft DO".  * linear
           relationship between dose and effect Mas
           noted,  data on cell counts, population
           volune, dry Melaht, ash, nitrogen,
           orqanlc acids, and organic natter are
           renorted.

•.  None  Inhibited growth of
           •at-fornlng alqie for nore than 2 Meeks.
           CuSOi. foreiulated xlth certain Netting
           aqents Mas more toxic than CuSO
-------
  Comoound
  "Organism
                                   Flald  Flald
                                   Study Location
                                 Toilclty,        Experimental
                                 Active          Variables,
                                 Ingredient,      Controlled
                                   Ppm           or Noted
                                                                                                 Comments
                                                                     Reference
•otasslum salt of
flk-cnlorotolylt
ony-N-metttaxy-acataa
Ide
Phormldlum
aablguum
                                   L     —
•otasslum Mtt of    Phormldlua
J,3,5-trlctiloro-*-or amblguua
rldlnol
Precalne
nydrochlorlde
Neoeorlon
brevlrostrls
11-3 !•«.»
                                   BS»   —
8.5-10.0 (16
percent growth
Inhibited 1%)
                                                      l.f-lO.O(NTE)
                                                      II (NTC 1 hr>    a.c.e
      II
                     Caaarus
                     fasclatus
                                                           m>
                     Fish Inot
                     soeclfledl
                     Mesbors       BCF*
                     heteroBoraha  and
                                   BS«
                                 greater  titan
                                 l«-lia  IKI
                                 10.1  IT?,
                                 hardnater)
                •*,c.e
-------
         Pretia
Rasbora       BCFA
heteromorpha  and
              BSA
                                                               l.t (TZ,
                                                               softiiater)
                                                                               species
                                                 »»,e.*«f»
                                                 hard (HWI
                                                 or soft
                                                 ISWI
                                                 synthetic
                                                 dilution
                                                 Mater, or
                                                 seaMBter
                                                 tor some
                                                 species
         Pro-Next Ish
V/l
         Pro-Noxf Ish
         Pro-Noxf Ish
         PVP-lodlne,
Oncorhynehus  BSA
tshaMytscha
(fry)
Oncorhvnchus  BSA
Klsutch
• fry)

Oncorhvnchus  BSA
Klsufch
(eggs)
                                                               1.0 (SB)
                              Mercenarla
                              aercenarla
                              (eggs»
                                            t     —
                                                               0.135 (Tl)
                                                               1.7 (Tl»
                                                               tT.l
         PVP-tetfln*
                              Harcanarla
                              a*rc*narla
                              IIarwa«>
                                 3».9 (Till
                                                                                          ocstlcldcs H«re aost toxic In hard mt«r
                                                                                          and so»etl»es the ooooslte Mas true.
                                                                                          Tasting the actual material as sold Has
                                                                                          found to be essential.

                                                                                                 sane as above
                                                                                                      Alabaster
                                                                                                      (19691.
                                                                                                      ANIC-5I.ZS
                                                                    Satmonld eqg embryos nay be able
                                                            to survive rotenone treatment that kills
                                                            fish.  Toxlclty to the coho embryos was
                                                            qreater at 53 f than at 39 and «6 F.
                                                            Fgqs burled In gravel  survived better
                                                            than those at the gravel  surface.
                                                            Further field evaluations Mere
                                                            reconmended.

                                                                   save as above
                                                                                                 same as above
                                                                                                                                    Garrison
                                                                                                                                    (1968),
                                                                                                                                    Garrison
                                                                                                                                    (1
-------
   Compound
•yramln
Pyrlmithate
Qulnaldlne
Toxtclty, Experimental
•Active Variables,
Field Field Ingredient, Controlled
1 Orqanlsm Study Location Pom or Noted
"asbora 8CFA — Z8 (T2I a*.e,e,f.
heteromorpha and bard
BSA IHWtor
soft (SHI
synthetic
dilution
Mater, or
seaMater
tor SOB*
soeclos



Fish (not — — • greater than
specified) 10-10D (K)



e Oasbora BCFA ~ t.l IT?) e*.c,etf.
heteromorpha and hard (HH)
BSA or
SOFTISHI
synthetic
dilution
Mater, or
seaMater
for some
species



Neqaorlon BSA — a.? (SB 10 e.Cte
brevlrostrls MINI
(1-3 «q)


Comments
On* hundred sixty-four
pesticides* wettlnq aq«ntst and
nlsc«1 laneeus nater DO! lutants shooed a
old* rar>q* of toxlclty soannln; 1? orders
of naqnltude. KnoMlnq the toxlclty and
percent»o» of alt co»oon»nts ot a
fornulation did not result In easy
credlctaolllty of th« toxlclty of a
•Ixture of oaterlals* So»»tl«*s
oestlcldes Mere mo<;t toxic In hard Mater
and sonetlnes the ooooslte Mas true.
Testing tht actual vaterlal as sold was
found to be essential.
Approximate toxlcltles of
numerous DCS tic Ides commonly used In
Britain Mere sunnarlze'l. An excellent
brief, qeneral discussion of toxlclty
testing Is also oresent.
One hundred sixty-four
pestlcldest wttlnq aq»nts> and
•Iscel laneous Mater ool tutants showed a
Mlde r»nqe of toxlclty scanning l? orders
of laqnltude. KnoMinq the toxlcity and
percentage of all conoonents of a
fornul at ion did not result In easy
predictability of the toxlcity of a
•Ixture of materials. Sonetlnes
pesticides Mere most toxic In hard Mater
and sovetlnes the ooposlte Mas true.
Testing the actual material as sold was
found to be essential.
Data from study of drug effects
on youno, levon sharks Mere treated
mathematically to demonstrate


Reference
Alabaster
(14&9I,
AMIC-91,2%










MaMdesley-
Tho«astl971)
ANIC-10S6


Alabaster
(19691,
ANIC-SI.25










Paldrldqe
11969).
ANIC-3t32
                                                                                 aoollcabl11ty  of  classical  rate  theory  to
                                                                                 the  study  of chemical  sharK deterrents.
                                                                                 Incaoacltatlon '(narcosis)  Mas  the  orlnary
                                                                                 parameter  timed for  effectiveness.   This
                                                                                 Mas  usually quite rapid  for the  more
                                                                                 effective druqs.
ftaynap Sol B
                     Cranqon
                                   BSA   —
                                                      3.3-10 (T?)
m»(eontln-
                                                                                        One hundred-forty surface  active  Portminn, at
-------
RD 1*639
                     Rasbora
                     heteromoroha
                                                      0.5» IT2t
                                   and
                                   BS.
Region*
                     Rasbora
                     heteromoroha  and
                                   BSA
                                 37 (T2,
                                 softMater)
Reglone
Sa I no
galrdnerl
BCF.
and
AS*
TO er
                                                 soft  (SW)
                                                 synthetic
                                                 dilution
                                                 water,  or
                                                 seaMater
                                                 for sea*
                                                 tore Its
                                   a>,e,e,t,
                                   hard
                                   (HW)or
                                   soft (SM)
                                   synthetic
                                   dllutlon
                                   •ater, or
                                   seaxater
                                   for so**
                                   species
                                              aq«nts, solvent  emutslflers, oestlcldes,  a!  (1971)f
                                             'OOlychlorlnated  blphenyls,  our*           AHIC-7701
                                              Inorqanlo  and orqanlc chemicals x«r*
                                              evaluated aqalnst  as  *any as ten marine
                                              orqanisos.   The  authors  noted  that most
                                              published data of  this type deal xith
                                              toxlclty of chenlcals to treshMater
                                              orqantsns*

                                                     One hundred sixty—four           Alabaster,
                                              pesticides, xettlnq aqents. and            (1969),»HIC-
                                              »lsc»l lancous Hater pollutants showed  a   5<>?S
                                              Hide range  of toxlcltv soannlnq  12 orders
                                              of  naqnltude.  Xnowlnq the  toxlcltv  and
                                              percentage  of all  conoonents of  a
                                              formulation did  not result  In  easy
                                              predictability of  the toxlclty of a
                                              •Ixture of  Materials. Sonetlnes
                                              pesticides  were  nost  toxic  in  hard Mater
                                              and sovetlmes the  ooooslte  «as true.
                                              Testlno  the actual naterinl as sold  Mas
                                              found to b* essenfl*).
a*,c,e,f,
hard (HH)
or soft
(SMIsyntne
tic
dilution
Mater, or
seaxater
for so*e
species

a*,c,e,f,
hard (HW)
or
SOFT(SW)
                   One hundred sixty-tour
           pesticides, itettlnq aqents, and
           •Iscellaneous oater pollutants shoMed a
           MMe range of toxlclty spanning 12 orders
           of magnitude.  Knoxlnq the toxieity and
           percentage of alI  comoonents of a
           formulation did not result In easy
           predictability of  the toxlclty of a
           mixture of materials.  Soaetlnes
           pesticides Mere «ost toxic in hard Mater
           and sometimes the  opposite Mas true.
           Testing the actual «aferial as sold was
           found to be essential.

                  same as above
                                                                     Alabaster
                                                                     (1969),
                                                                                                                           Alabaster
                                                                                                                           (1969),
                                                                                                                           AMIC-5MS
                                                                                        cane as above
                                                                                                                           Alabaster
                                                                                                                           (1969),
                                                                                                                           AH.IC-5*??
-------
  Coapound
            Field  ri«ld
Organise    Study Location
                                                       Tonlelty,
                                                      •Active
                                                       Ingredient,
                                                         Pp«
 Experimental
 Variables,
 Control lad
 or  Noted
                                                                                                 Comments
                                                     Reference
KhDdaalne  A
                      Salao
                      galrdnerl
                                    BS»
Rhodaalne B
Rhodaeln* B
RIdzlIK
                      let Blur us
                      punetatus
                                    8S»
                      Leooals        BS«
                      •acroehlrus
                      Crangon
                      cr angon
                                   BS«   —
                                                       $?6  ITU
                                                       379  IT»I
                                                       330-1000  (T?>
                                                                       synthetic
                                                                       dilution
                                                                       •ater, or
                                                                       seaxater
                                                                       tor so»e
                                                                       species
                                                                 The dyes Rhodamlne B and           Harking
                                                         Fluoresceln sodlu* Mere  found to be
                                                         Relatively non-toxic  In  ppe
                                                         concentrations while  antlaycln Has toxic
                                                         at pob  levels.  The author states that
                                                         neither dye at field  us* concentrations
                                                         should significantly  Influence the
                                                         activity of Antlnycin A  against fish.
                                                                                                   Harking
                                                                                                   «1969),
                                                                                                   1MIC-5TZS

                                                                                                   Harking
                                                                                                   (19f.9)t
                                                                                                   »HIC-57?g

                                                                                                   Portoann, et
                                                                                                   at (1971),
                                                                                                   »HIC-7701
Roccal
                     Hercenaria
                     •ercenarla
                                                      0.19 ITZ)
                                                                                        sane as above
                                                                                             as above
••(oontln-         One hundred-forty surface active
uous aer-  agents, solvent enulslfl*rs, pesticides,
atlon, sea-Polvchlorlneted blohenyis,  pure
water, and Inorganic,  and organic chemicals were
dally      evaluated against as many as ten *arlna
solution   organlsns.   The authors noted that eost
renewal)   published data of this tvoe deal  with
           toxlclty of  cheelcals to freshwater
           organises.
                                                                 The effect of 9? pesticides on    Oavls, et at
                                                         enbryonlc  developnont of clams and
                                                         oysters «as reported.  Synergistlc        11969),»MIC-
                                                         eff»cts with solvents were also reported.  5990
                                                          nost  of the compounds affected
                                                         dev«loc»ent More  than survival.  So**,
                                                         however, drastically  reduced larval
                                                         growth. The authors  ooint out the
                                                         necessity  of evaluating the effects of
                                                         pesticides on all  life stages  of  an
                                                         organise and note  the possibility of
                                                         selecting  chealcals tor pest control  that
-------
Roccal
Rola, OSO
                     "ercenarli
                     •ercenerli
                     (larvae)
                     Cranqon
                     crangon
                                   I      ••
                                   BSA   ~
                                                      0.1% UK*
                                                      3.3-10  (TO
                                                                                 HOuld not haw« serious effect on
                                                                                 shellfish.

                                                                                        same as above
 Rosin (ulna
 01 acetate
Phormldlum
amblguum
                                 0.5-10.0 (NTE)
 Rosin A*in* 0
                      Crassostrea
                      vlrglnlca

                                 lets than 0.25
 Rosin Amlne 0
                      Crassostrea
                      vlrglnlca
                                    L     —
                                 less thanO.«?5
                                 ITlM
                                                     Davis,  ct al

                                                     (1969>,A1IC-
                                                     5990

*»(contin-         One hundred-forty surface active  Portmann, et
uous aer-  agents, solvent emutslfiers, pesticides,  at
atlon, sea-P°l'chlorinated Mohenyls, cure           (19^11 ,»HIC-
water, and l"orq»nlc, and orqanlc ch»»lcals were     7701
dally      evaluated aqalnst as •ony as ten »ar|ne
solution   orqanlsns.  T^« authors noted that Host
renewal)   published data of this tyo* deal Kith
           toxlclty of chemicals to  freshwater
           orqanisi»s.

                   Of 71. chemicals evaluated as      Otto (19701,
           alqlcldes, only 9 Here more toxic than    AHIC-892
           CuSOii.  None Inhibited growth of
           rat-for»lnq aliae for more than 7 MeeHs.
           Cu^0>>  formulated with certain Mettlnq
           a9ents »as «or« toxic than CuSQ<» alone.
           Coooer chlorairlne *as also found to be
           •ore toxic than CuSOU.  No wetting aqents
           were tourd to be Inhibitory at the
           concentrations  Investigated (0.05 and
           0.405  cpr).  Also reoorted are factors
           effecting growth of alqae In canals to
           determine whether there Here leads to
           controlling atqae by  environmental
           •anaqerent.  No practical environmental
           means  Here found.

--                 The effect of 5?  oestlcldes on    Oavls< etal
           embryonic development of  clams and        (1969),
           oysters Has reported.  Synerqlstic        AMIC-5990
           effects with solvents were also reported.
            Host  of  the comoounds affected
           develocment more than survival.  Some,
           however,  drastically  reduced larval
           qroxth.   The authors  oolnt out the
           necessity of evaluating the effects of
           pesticides on  all life stages of an
           orqanlsm  and note the possibility of
           selecting chemicals  for pest control that
           Mould  not have serious effect on
           shellfish.
                                                                                         same *s above
                                                     Davis,et al
                                                     (19691.
-------
   Compound
                        Orients*
Field FUld
Study Location
•Toxlclty,
Active
Ingredient,
Pom
Experimental
Variables,
Controlled
or Noted Comments
Bel erenee
 «otenon*
 It o tenon*
 *o-n«et
 (larva*)

 Sal no
 gelrdnerl
                      Lepovls
                      mecrochlrus
                      Gamaarus
                      fasclatus

                                   8S*   —
                                                       0.057 (TO
                                                             (TO
                                                      2.6 IT*)
R-Wti
                     Gamearus
                     fasclatus
                                   8SA   ~
                                                      15.0 (TO
Salicylic acid
(2-hydroxyb*niolc
aeldl
Phoraldlum
aablguua
                                                      0.9-10.0  (NTE)  —
                                           AMIC-5990

          The  pisclcldes  Antlmyeln » and    HoMland
  Rotenone nere  found  to  b« co»oa»lbl» when I19ft<»>«
  alx«4  and furthermore aopeared to have an AHIC-5T2V
  additive effect  in c*bln»tlon.  That Is
  both conpounds Here  *ore toxic In the
  presence of  the  other than alone.
                                                                                        sane a« above
         Of the aquatic weed herbicides
 evaluated. Die Ion* Mas the nost toxic,
 Daohnla MBS oenerally the rost sensitive
 orqanlsn.  Alt of the. Crustacea Mere
 affected by much lexer concentration
 levels of herhlcMes than Indicated by
 the TL sub 5Q values.  All of the anlaats
 reoresent Imnortant food chain links.

         Of the aquatic weed herbicides
 evaluated, Dlclone  Mas the nost toxic,
 Oaohrila xas qenerallv the most sensitive
 orqanlsn.   All of the Crustacea Mere
 affected by nuch  IOMCT concentration
 levels of  herbicides than Indicated by
 the TL sub 90  values.   All of  the  animals
 represent  inoortant  food  chain links.

         Of  7
-------
                                                                                 means were found.
Seas Deep
SeesMeep
S«foll
Steel head
trout
(fIngerlInqs)
Coho salmon   BSA.
 IfIngerlIngs) In
              •Itu
                                                      20.2 CTO
Hood Canal,
Hood sport,
Wash.
                      Agonus
                      cataohractus
                                   BS»   —
                                                      1.5 W
                                                      1001-3300  CT2)
                                                                                         Evaluation of 11 oil  dlspersants  Tracy, at al
                                                                                 resulted In a ranking for each and a
                                                                                 recommendation tor us* according to the   (1969),AHIC-
                                                                                 ranklng.  Ranking Mas based on toxlclty
                                                                                 •nd oil dlsoersal effectiveness.  Corexlt
                                                                                 776fc acocared to have the least toxlclty
                                                                                 xlth fair to good oil dispersion
                                                                                 eaoablllty.
 Safe 11
                      Cranqon
                      crangon
                                   BS»
                                                       1000-3301  ITt)
                                                                                        •ana aa abora
                                                 a«lcontln-         one hundred-forty surface active
                                                 uoua aor-  agents, solvent eeulslflersi oestlcldes,
                                                 atlon, aaa-oolvchlorInated blonenyls< pure
                                                 water, and Inorganic, and organic cherlcals were
                                                 dally      evaluated against  as «any as ten *arlna
                                                 solution   organisns.  The authors noted that lost
                                                 renewal)   oubllshed data of  this tyoe deal with
                                                            toxlclty of cheoleals to  freshHater
                                                            organises.

                                                 a*(eontln-        saae as above
                                                 uoua, aer-
                                                 ation, sea-
                                                 water, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                                                                   et al
                                                                                                      Tracy,
                                                                                                      (1969).
                                                                                                      AKIC-363U
                                                                                  Port»»nn, at
                                                                                  al (1971),
                                                                                  •MJC-7701
                                                                                  Porteann, at
                                                                                  al  (1971).
                                                                                  ANIC-7701
 Selenlua dioxide
                      Caraislus
                      auratus

                                                       12 «T7I
Coregonus
clupeaforals
                                          Hoose  Lake,
                                          Can.
                                                       0.2  (relltlon  to  toxlclty  data.      Heir, at al
                                                            conditioned avoidance resoonse xas         (1970),
                                                            studied  at  sublethal concentrations.   The  AHIC-739
                                                            lOHest concentration of  netal resulting
                                                            In significant  Inealrnent  Mast   arsenic,
                                                            0.101  lead.  0.071  mercury,  0.003! and
                                                            selenium, 0.25.  Deleterious  effects
                                                            occurred at  aetal  concentrations
                                                            aporoxlnately slallar to potable Mater
                                                            standards.
                                                                     Concentrations  of  13  toxic
                                                            elements In  dressed fish  from heavily
                                                            Industrialized  and  non-Industrialized
                                                            areas Mere determined.  Only  mercury
                                                            exceeded regulatory Halts, and
                                                            concentrations  of most  elements  were
                                                            essentially  the same in fish  free both
                                                                                  Uthe, etal
                                                                                  (1971),
                                                                                  •NIC-3S19
-------
3
to
              Coaoound
            Selenlu*
            Selanlu*
           Selenlua
           Selenlua
           Selenlua
           Selenlua
           Sesaaex
           Sesanex
           Sesaaex
           Savin
Organise.

Coregonus
cluoeaforels
Esox tMclus
Esox luclus
Esox luclus
Os«erus
aordax
Perca
f lavescens
Notenlaonus
chrysoleucas
Leooals
eyanellus
Leooals
aeerochlrus
Field Field
Study Location

FL Lake
Ontario,
Can.
FL Moose Lake,
Can.
FL Lake St.
Pierre. Can.
FL Lake Erl*.
Can.
FL Lake Erie.
Can.
FL Laic* Erl*,
Can.
L —
L •"••
L —
toxlclty.
Active
tnoredient.
PM

O.t (residue)
O.t (residual
• .* (residue)
»
0.2 (residue)
B.Z (residue)
0.3 (residue)
? (NTE 1)
t (NTE 1)
^ (NTE t)
ExBerlaental
Variables,
Controlled
or Noted Coaaents
areas.
— - saae as above
saae as above
saae as above
— • saae as above
saae as above
— saae as above
— Fish brain AChE activity MBS not
affected by Sesanex alone but Has
significantly Inhibited by oarathlon.
Pretreataent with Sesaeex at 2 pan
resulted In decreased Inhibition of AChe
activity by oaratnlon.
-- saae as above
saae as above
Reference

Uthe, etal
(19711.
AHIC-3819
Uthe. et al
(1971), AHIC-
Uthe, et al
(1971), AMIC-
3819
Uthe, et al
(1971),A1IC-
3819
Uthe. et al
(1971), AHIC-
3819
Uthe, et al
3819
Gibson, «t
al
(19711, AHI
3799
Gibson, et
at <1<»711,
A1IC-3799
Gibson, et
81(1971),
AMIC-3799
                               Puntlus tlcto —
                                                                3.7 (TM
a,c.d,e,f          Of  the pesticides Investigated,    Bhatla
           the aost toxic MBS Ktofos tot toned In     (19711,
           decreasing  order  by Sumlthlon,  Halathion,  AMIC-S".?J
           Foralthlon,  Olaecron.  Sevln.  and  BHC.  The
           •uthor  cites the.  need  for aore  selective
-------
         S«vin
*asbora       BCT»
hetero*orpha  end
              BSA
a*,c,e,f,
hard IHM)
or soft
ISM1
synthetic
dilution
Hater, or
seanater
tor  SOM
species
          Svvln
                               •alae>on«tes
                               kadlafcensts
                               freslstant)
                                  ITU
0)
          Sovln
          S«»ln
 Palaeaonet**  BSA   —
 fcadlakmsls
 roalatant)

 Tublfex
 tub I fax
                                                   Belzonl,
                                                   HISS.
                                                                1.0*19 (Til
                                                                l.M (NTCI       —
                                             as*
pesticide* nontoxlc to fish or
antagonistic agents for reducing fish
tonlclty.

        Oo« hundred slxtr-»our
0*stlcld*St wettlnq aq*nts, »nd
•lcc*l 1»n*oos KBter ool tutant? s^OMOd a
Mlde ranoe ot toxlclty soannlnq 1? orders
of "aqrliud*.  Knonlnq tn* toxlclty and
p*rcent»q» of all cooeonvnts of a
fornulatlon did not result In easy
predictability of the  toxlclty of a
Mixture of «aterlsl*.  So«etl««s
pesticides Here no^t  toxic In hard Hater
and voaetlaes the oooo^lte was true.
Testing  the  actual Material as sold  Has
found  to  be  essential.
                                         »lob«sto
                                         CUM).
                                                                                                      Naavl. at al
        Bloastays Here conducted with
shrlap tron three areas of Intensive
pesticide use and fro* an unexoased area. iMIC-5519
 Previously exposed snrl«o Mere fro* t to
?•! tines »ore resistant than unexposed
shrlvp.  Both types of shrlap Here also
exoosed In caqes to Maters ot the
contaminated areas.  Susceotlble shrlap
suffered 6f> percent more norfality than
did resistant shrimp.  The toxlclty of
the Insecticides ranked In descending
order Mas as follOHsS  Most toxic,
Endrin, DOT, Methyl oarathlon, Parathlonl
aedlue, toxlclty, Cuthlon, Llndane,
Toxaohene, Strobanel lease toxic
Chlordano, Savin, and Heptachlor.
                                                                                                  sa»e  as  above
                                                                                                                                    Naovl,
                                                                                                                                    (1970),
                                                                                                                                    •HIC-5S19
                                                                                                                                           et al
        Th« response of
pesticide-resistant aquatic organises to
various pesticides Mas coloured to the
response ot non-resistant species.
Pesticide-resistant soecles Mere
coflected at ftetzonl and non-resistant
species at State Colleqe.  Copeoods,
elans, snails, and sludqe «ori.s fron
Belzonl Her* considerably More tolerant
to pesticides than the non-resistant
organisms.  The authors note that the
affect of Increased tolerance In the
erqanlsas Is an Increase In the aaount of
pesticide residues available To anlaals
of higher trophic levels.
                                           Haavl, et
                                           all1969),
                                           •NIC-5979
-------
Compound
Sevln
Field Field
Organism Study Location
Mercenarla L —
•ercenaria
(eggs)
Toxlcity,
Active
Ingredient,
PD»
3.« IT2)
Experimental
Variables,
Control led
or Noted
Comments
-- The effect ot
embryonic development
oysters Mas reported.
?? pesticides on
of clans and
Synerglstlc
Reference

Davis, et at
t.l9&9>.«MIC-
u>
           Sevln
           Sevln
          Sevln
          Serin
          Shamash R1885
          Shaaasti R18S5
 Mercensria
 mercenarla
 (I arvafO

 Crassostres
 vlrglnlca
 (eqqs)

 Crassostre*
 vlrglnlca
 (larvae!
 Wolffla
 papulifar*
                               Crsngon
                               cranqon
                                                                 greater than

                                             8S*   —
                                                                 3  CTZI
                                                                3  ITHI
                                                                1000 (K)
                                                                3.3-10 It21
Panda I us
•ontaqul
                                            BS»
                                                                1.0-3.1  (TZ)
                                                                                            effects  with  solvents  Mere  also reoorted.  S990
                                                                                             Host  of  the  conoounds affected
                                                                                            development more  than  survival.   Sooet
                                                                                            however,  drastically reduced  larval
                                                                                            growth.   The  authors oolnt  out  the
                                                                                            necessity of  evaluating the effects  of
                                                                                            oestlcldes on  all  life stages of  an
                                                                                            orqanls*  and  note  the  possibility of
                                                                                            selecting chemicals for pest control  that
                                                                                            Mould  not  have serious effect on
                                                                                            shellfish.
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                      Davis, et
                                                      al(19691.
                                                      &HIC-5990

                                                      Davis, et al
                                                      (19A9I.
                                                      »MIC-599I>

                                                      Davlsi et al

                                                      (1969).»1IC-
                                                      5990
 Hunter1 a
 .•nodlum
 diluted
 1:5
                                                 «,»( contin-
                                                 uous aer-
                                                 ation,  sea-
                                                 water,  and
                                                 dally
                                                 solution
                                                 renewal)
a«t( contin-
uous, a or-
ation, sea-
water, and
dally
solution
renewal)
          All compounds uere harraful to
 duckweed to nomo decree.   Decreased
 populations woro noted at non-lethnl
 concentrations and some compound3
 (Kalathlon and t-,^-I>) caused terotogenlc
 oTfocts  at concentrations as low as 1 ppn.
 Worthley,  et
 al (1971),
 AMIC-3233
                                                                                                   One hundred-forty surface active  Portmann,  et
agents, solvent emutslfiers. oestlcides,
polychlorlnated biohenyls, pure
inorganic, and organic chemicals Mere
evaluated against as many as ten marine
organisms.  The authors noted that most
published data of this type deal Mlth
toxlcity ot chemicals to freshwater
organisms.
       sane as above
                                                      it  (1971),
                                                      AMIC-7701
Portnann, et
al (19711.
»MIC-7701
-------
          Shell 0-90
                               Sal no
                               galrdnerl
             BCF»
             and
             BS»
                                                                105 (T21
               a',e,*,f,          One hundred sixty-four            Alabaster
               hard       pesticides, wetting agents, and           (1969).
               (HH)or     miscellaneous water pollutants shotted a   ANIC-5*25
               soft  (SHI  "Me rang« of toxlclty scanning  12 orders
               synthetic  of magnitude.  Knowing the  toxiclty and
               dilution   percentage of at I  comoonents  of  a
               Mater, or  formulation did  not result  In easy
               seawater   predictability of  the  toxlclty of »
               for some   mixture of materials.  Sometimes
               soecles    pesticides were  mast  toxic  In hard Hater
                          and  sometimes  the  ooooslte  was true.
                          Testing  the  actual material  as sold  was
                          found  to  be  essential.
           Silver
           •• thane-arsenate
Phormldlu*
amblguum
0.5-10.0 (16
percent growth
lnhlblt«dl<>)
vn
          SiIver
                               Paralabrax
                               clathratus
                                             F«
                   Scattergood  0 (ventral
                   Steao Plantt euscle
                   Los Angeles, residue)
                   Cat.
Otto (1970>»
AHIC-89?
        Of 71. chemicals evaluated as
algiclties, only 9 Here more toxic than
CuSOit.  None Inhibited growth of
mat-forming algae for more than 2 xeeks.
CuSlit formulated with certain wetting
agents was more toxic than CuSOfc alone.
Coooer chloranlne was also found to be
more toxic than CuSOi».  No wetting agents
were found to be Inhibitory at the
concentrations investigated (0.05 and
0.005 com).  «lso reoorted are factors
affecting growth of algae in canals to
determine whether there were leads to
controlling algae by environmental
Management.  No practical envlronaentat
•cans were found.
                                  Fish  collected  from an effluent   Staoleton
                          pioe of a  steam olanf and  from offshore   (196(1!
                          waters of  Catallna  Island  were analyzed   AMIC-598B
                          for trace  element content.  Trace element
                          content of  the effluent water was at
                          least 5 times oreater than that of normal
                          sea water  for cadmium,  cooper, nickel.
                          zinc, and  chromium.  Livers of fish fro*
                          the effluent  were nearly twice the size
                          of those from the ocean.   Greatest
                          differences  In concentration occurred
                          with alurinum, cadmium, and nicKel.
                          Silver, barium, lithium, and lead showed
                          the least  differences.  The author
                          concluded  that trace element analysis of
                          tissues could be used to determine the
                          effect of  pollutants on marine organises.
-------
Coeoound
Silver
Stiver
Silver
Silver
Silver
SI Iver
Stiver
Silver
Silver
Sliver
Orqanlsa
Paral abrax
clathratus
Par»lat>r»«
clathratus
Paral *brax
clathratus
Paral abrax
clathratus
Paral abrax
cl athratus
Paral abrax
clathratus
Paral abrax
clathratus
Par at abrax
Clathratus
(qravld
te»alesl
Paral abrax
clathratus
Paral abrax
clathratus
Field
Study
FM
FH
FH
FN
FM
FM
FN
FM
FM
FH
toxlelty. Experimental
Active Variables,
Field Ingredient, Controlled
Location PO* or Noted Comments
Scatterqood 0.06 Iheart — saae as above
Stea* Plant, residue)
Los Anqeles,
Cat.
Catal Ina 0.16 — saoe as above
Island. Cal. Iheart
residue)
Scatterqood 0.01 (eyeball — sane as above
St*aa Plant, residual
Los Angeles,
Cal.
Catal tna O.OZ — saae as above
Island, Cal. « eyeball
res I duel
Catal In» 0.04 (ventral ~ s»«e as above
Island, Cal. auscle
residue)
Scatterqood 0 (qonad — saae as above
Stean Plant, residue)
Los Anqeles,
Cat.
Catal ins O.W? — s»»e as above
Island, Cal. (oonad
realdue)
Catal ina O.lZaonad ~ saae as above
Island, Cat. residue)
Scatterqood 0 (liver — saae as above
Steaa Plant, residue)
Los Anqeles,
Cal.
Catal Ina 8.03 — saae as above
Island, Cal* (liver
realdue)
Reference
Staoleton
•196B),
AMIC-59V)
Staoleton
(19S8),
AMIC-S9SO
Staol eton
(1968),
AMIC-S980
Staoleton
(19681,
AMIC-99BO
Staoleton
(1968),
»MIC-5980
Staot eton
(1968),
AHIC-S980
Staoleton
(1968),
1MIC-59SO
Staolvton
(1968),
AMIC-S980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
ANIC-5980
-------
        Sliver
                             Paratabrax    FM    Seatterqood   O.ZZ
                             clathratus          Stea» Plant,  (Intequnent
                                                 Los Anqelcst  residue)
                                                 Cat.
                                                                   sane as above
                                                                                                      Staoteton
                                                                                                      (19fiB>,
                                                                                                      AMIC-5980
        Silver
         Sllvex IBEEI
I         Sllvex (BEE)
         Sllvex IBEEI
         Sllvex IBEE)
         Sllvex (BEEI
         Sllvex (BEEI
         SI Ivex (BEEI
         Sllvex  IPGBEI
         Sllvex  IPCBEI
Paralabrax    FN    CatalIna     0.1Z
clathratus          Island, Cat. (Intequnent
                                 residue)
                                                                                                 san« as above
                                                                                                                                    Staoleton
                              Ganaarus
                              faselatus
                                            BS»   —
                                 0.71, (TZ), O.ZS a»
                              Paleonontes   BS»
                              kadlahenils
                                            8S»
                              brevicau'lus
                              Orconectes    BS*
                              nals
                              Oaphnla aaqna BS*
                              CyprldoDSts   BS*
                              vldua
                              Leoonls       BSA
                              •acroehlrus
                              Gamnarus      BS*
                              fasclatus
                              Paleonontes   BS*
                              kadlakensls
                                                               8.0 (TZ)
                                                               ".0.0  (TZ)
                                                               60.t  (T2>
                                                               2.1  (T2I
                                                               *.9  (TZI
                                                               70.0 (TZI
                                  1.0 (TZ),  0.8*   a*
                                  (TW)
                                                               3.Z  ITZ)
                                                                    Of the aauatlc  Heed herbicides
                                                            evaluated, Oletone  »»s  the *ost  toxic,
                                                            Oaohnia Mas  generally the nost sensitive
                                                            orqanisa.  All ol  the Crustacea  were
                                                            affected by  auch  loner  concentration
                                                            levels of herbicides than indicated by
                                                            the  TL sub SO  values.   All of  the animals
                                                            represent Inoortant food chain links.

                                                                   sane  as above
AMIC-S980

Sanders
(1970),
                                                                                                 sane as above
                                                                    saae as above
                                                                                                 saee  as  above
                                                                    saae as above
                                                                    sane as above
                                                                    saae as above
                                                                                                 saae as above
Sanders
(1970),
AMTC-fcSS

Sanders
(19701 ,
*MIC-fcS3

Sanders
(1970),
AMTC-<.S3

Sanders
(19701,
*MIC-<.53

Sanders
(1970),
ANIC-1.53

Sanders
(1970),
 Sanders
 (1970) ,«MIC-
 1.53

 Sanders
 (1970),
 4MIC-V53
-------
 SI I vex (PG8E)
                                    Field  Field
                        Organism    Study Location
                      As*11 us       BSA   —
                      brevleaudus
                      Orconectes    BSA   —
                      nets
•Toxlclty,
Active
Ingredient,
Ppa
o.s m>
Experimental
Variables,
Control led
or Noted Comments
a* sane as above
Reference
Sanders
(1970),
                                 qreater than
                                 100.0 (T2!
                                                                                         saae as above
                                                                                                                            Sanders
 Sllvex (PG8E>


 Silvex (PGBE)



 Sllvex CPG8EI



 Silvex
Sllvex
Slnzlne
                      Oaphnla aagna BSA
Cyprldopsls   BSA
vldua
leoonls       BS»   —
•acroehirus
                      Crassostrea   L      —
                      vlrglnlca
0.16  IT2>


0.20  (T2)



16.6  (T2>



$.9 (T2)
                     Crassostrea   L
                     vlrglnlca
                     (larvae)
                     Fish (not
                     specified!
                                                      0.7 (Tit)
                                qreater than
                                10-100 IKI
                                                                                         sa«e as above
                                                                   saae as above
                                                                   sane as above
                                                                                                                            Senders (1970
 Sanders
 (1970).
 Af1IC-«.S3

 Sanders
 (1970),
 AHIC-493
                                                                    The effect of 5? pesticides on    Davis, et al
                                                            embryonic  develoonent of clans and        (1969),
                                                            oyst«r«  was reported.  Synerqlstlc        AHIC-5990
                                                            effects  with solvents Nere also reported.
                                                            Most  of the compounds affected
                                                            develocment acre  than survival.   Some,
                                                            honevert drastically  reduced  larval
                                                            qroMth.  The authors  oolnt out  the
                                                            necessity  of evaluating  the effects  of
                                                            pesticides  on all  life stages of  an
                                                            organism and note  the possibility  of
                                                            selecting chemicals for  pest control  that
                                                            would not have serious effect on
                                                           shellfish.
                                                                                        same as above
                                  Approximate toxlcitles of
                          numerous pesticides commonly used In
                          Rrltalr Here summarized. An excellent
                          brief, general discussion of toxlclty
                          testing Is also present.
Davis, et  al

(1969),ANIC-
5990

MantSesley-
Th omas
119711, »«1IC-
1056
Slmazlne
                     Sal mo
                                   8CFA   —
                                                      1.3 (T?)
                                                                      a'.c.e.f.
                                                                                        One hundred sixty-four
                                                                                                                           Alabaster
-------
                    gairdnerl
and
BSft
SlMazln*
                     Sal MO
                     galrdnerl
BCF»
•nd
BS»
                                                         (Til
 SlMazlne
 SlMazlne
                      Roccus
                      saxatllls
                      (tInqerlinqs)
                                   BSA
                      Carclnus
                      Maenas
                                   BS»   —
                                                       0.25  (TO
                    qreater than
                    100  ITZI
 SlMazlne
                      CardluM edule BSA   —
                                                       greater than
                                                       100 (TZ)
hard (HMI
or soft
(SM)
synthetic
dilution
Mater, or
seaxater
for soae
species
          pesticides, wetflnq aqents, and            (19691,
          Mlscel laneous Mater oollutants showed a    (HIC-S<>?5
          «Me rjnq« of toxlclfy scanning 12 orders
          of naanitude.  Knonlnq the toxlcltv and
          percentage of all coxoonents of a
          formulation did not result in easy
          predictability of the toxlclty of a
          Mixture of Materials.  Soaetlnes
          pesticides were most toxic In hard xater
          and sometimes the opposite Mas true.
          Testing the actual naterlal as sold Has
          found  to ba essential.
                                                                                        sa«e as above
                                                     alabaster
                                                     (1969»,
s'»c.ett,
hard(HN)
or soft
(SMI
synthetic
dilution
Mater, or
seaMBter
for soae
species

a*,c,d,a,f         Strloed bass  f Inqerllnqs Mere     Wellborn
,p  and     apoarently ouch More  sensitive to         (1969),
iron       theraoeutlc and herblcldat compounds than «MIC-5723
           •any  freshwater fish.
*»(contln-         One  hundred-forty  surface  active
UOUs »«r-  ,aq*nts, solvent  enuls1flers,  pesticides,
»tlon,  sea-oo'vchlorlnated  biohenyts,  pure
water,  and  inorganic,  and organic  chemicals Mere
daily       evaluated  against  as  "any  as  ten Marine
solution    organisms.   The  authors noted that Most
renewal)    published  data of  this  type deal with
            toxlcity of  chemicals to freshwater
            organISMS*

 no(contin-         s*Me as above
 uous,  aer-
 ation, gea.
 water, and
 dally
 solution
 renewal)
                                                      Portaann,  et
                                                      at (1971>,
                                                      mc-rroi
                                                                                          Portaann, at
                                                                                          al  (19711,
                                                                                          ANIC-7701
 SI mine
                      Crangon       BS»
                      crangon
                     qraatar  than
                     100  (TZ)
 «»(contin-
 uous,  aer-
 ation, sea.
 water, and
 dally
 solution
 renewal)
                                                                                         s»Me as above
                                                      PortMann, at
                                                      al (1971),
                                                      *MIC-7701
-------


Coapound


Orqanlsn

Field Field
Study Location
Toxiclty.
Active
Ingredient,
Pp.
Expert nentat
Variables.
Control led
or Noted


Comments


Reference
         SlMZlne
                              Gannarus
                              fasclatus
                                            BS*    —
                                 qreater than
                                 100.0 (TZ>
         SlMZlne
>       SiMZlne
I
         SlMZlne
        SlMZlne
        SlMZlne
        SlMZlne
        SIlcKaone 1
                              Paleonontes   BS*
                              kadlaKensls
Asellus       BSA
brevlcaudus
                              Orconectes    BSA
                              nals
                              Daehnla aaqna BSA
                             Cyprldopsls   BSA
                             vldua
                             Lepouls       BSA
                             •acroehlrus
                             Carclnus
                             Men as
                                           BSA   —
                                 qreater than
                                 180.0 (T2>
qreater than
100.0 (T?)
                                 qreater  than
                                 100.0  IT?)
                                                               1.0  CT21
                                                              3.2  CT?>
                                greater than
                                100.0 IT?)
                                                              33-100 «TZ>
                                   Of the aquatic Heed herbicides
                           evaluated, Olclone  «as the most toxic.
                           Oaohnia Has generally the nest sensitive
                           organism.  All of the Crustacea were
                           affected by much loner concentration
                           levels of herbicides than indicated by
                           the TL sub 50 values.  All of the aniaals
                           represent laoortant food chain links.

                                  saae as above
 Sanders
 (19701.
 ANIC-fcfS
                                                &»( contin-
                                                uous  aer-
                                                ation,  see-
                                                water,  and
                                                dally
                                                solution
                                                renewal)
                                                                                                 sane as above
                                                                                                 sane  as  above
                                                                                                sane as above
                                                                                                sane as above
                                                                                                sane as above
                                  One hundred-forty surface active
                          aqentst  solvent enutsiflers, pesticides.
                          polvch lorinateef blohenyls. Dure
                          Inorganic,  and organic cherlcals Here
                          evaluated aqalnst as nany as ten varlne
                          organises.   The authors noted that «ost
                          published data of this type deal with
                          toxlclty  of  chemicals to freshwater
                          organises.
 Sanders
 (19701, AHIC-
 <>53

 Sanders
 I1970),ANIC-
 <.SJ

 Sanders
 <>SJ

 Sanders
 (1970),
 AHIC-453

 Sanders
 (1970»,
 A1IC-ii53

 Sanders
 (1970) , AHIC-
 ".53

Portnann, at
al (1971),
AMIC-7701
       Sllckgon* 1
                            Cardlua edule BSA   —
                                                             33  (Tz>
                                               a«(contln-
                                                                                               saae as above
                                                                                                                                   Portaann,  at
-------
 Sllcfcaon*  l
                      Crangon
                      cranqon
BSa
                   3.3-10 (T?»
 Sllckaone t
                      Pan«aIus
                      •ontaoul
BS»
                   3.3-18 (T2I
Sllchgone  z
                      Carclnus
                      eaenas
                   H-3S (T2I
Sllekgone
                     Cardlua «dul« BS»   —
                                                       J.S  CT2I
                                                                       uous, aer-
                                                                       ation, aaa
                                                                       vater, and
                                                                       dally
                                                                       aolutlon
                                                                       renewal)
**(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)


a*(contin-
uous aer-
ation, sea.
water, and
daily
solution
renewal)


a«(contin-
uous, aer-
ation, sea.
water, and
daily
aolutlon
renewal)
                                                                      a«( contin-
                                                                      uous aer-
                                                                      ation,  sea-
                                                                      water,  and
                                                                      daily
                                                                      solution
                                                                      renewal)
                                                                                         *»•• as above
                                                                                         *••• as above
                                                                                         *aae as above
                                                     saae as above
                                                                                         »l  (19711.
                                                                                         *HIC-7701
                                                                                                                            Portnann, «r
                                                                                                                            »l CI^TD,
                                                                                                                            *MJC-7701
                                                                                                                            Porteann, et
                                                                                                                            »i riqrn,
                                                                                                                            •MIC-7701
                                                                                                                            Portnann,  et
                                                                                                                            al  C19TH,
                                                                                                                            »HIC-7701
                                                                                        PoPtuson, et
                                                                                        af J197H,
                                                                                        »MtC-7701
Sllekgone
                     crangon
                                   8S»
                                                      3.3-10
                                  a»(contin-
                                  uous aer-
                                  ation,  sea.
                                  water,  and
                                  dally
                                  aolutlon
                                  renewal)
                                                                                        seee as above
                                                                                                                           Portnann, et
                                                                                                                           »l (1971),
                                                                                                                           »HIC-770t
-------
  Compound
              Field  Field
  Organise    Study Location
Toxlctty,
Active
Ingredient,
  Ppa
Experimental
Variables,
Control led
or Noted
                                                                                                  Comments
                                                                                                                           Reference
Sllefcgone
                      PandaI us      BSA   —
                      aontaqut
                                                       3.3-10 ITZt
                                                 renewal)

                                                 «»(contin-
                                                 uous aer-
                                                 ation, sea-
                                                 water, and.
                                                 dally
                                                 solution
                                                 renewal)
                                                                                         same as above
                                                                    Portmann. et
                                                                    al  (19711.
                                                                    AHIC-7701
SI l>
                      Rasbora       BCFA.  —
                      heterovorpha  and
                                    BSA
                                                       8.3 ITZI
                      Carelnus
                      •aenas
                                    BSA   —
                                                       19 m>
SIlK
                      Cardlua edule BSA   —
                                                       33 (T2I
e*,c»e.f,
hard
(HU)or
soft (SH>
synthetic
dilution
Mater,  or
seaiiater
for son*
species
                a«(eontin-
                uous aer-
                atlon,  sea
                vater,  and
                                   One hundred sixty-four
                           pesticides, wetting aq«nts<  and
                                                                       solution
                                                                       renewal)
                                                                       ton
                                                                       renewal)
                                                                                                      Alabaster
                                                                                                      119691.
                                                            «Isc»1 lan*ous Hater  DOllutnnts shoHed a   *MIC-5«»?S
                                                            Mld« range of toxlelty soannlnq I! orders
                                                            of  magnitude.  KnoHlnq the toxlcity and
                                                            Dercentaqe of all  comoonents  of a
                                                            formulation did not  result In easy
                                                            or«rtlctabl 1 1 tv of  the  toxlcity of  a
                                                            nlxture  of materials.   Sometimes
                                                            oestlcldrs Here most toxic In hard water
                                                           •and sovet lines the  ooposltr »ss true.
                                                            Testlno  the actual material as sold was
                                                            found to be essential.
                                                                    One hundred-forty  surface  active  Portaann, et
                                                            aqents.  solvent  eaulslflers.  pesticides,   al  (19711.
                                                            Polyehlorlnated  blonenyls.  oure         .  AMIC-77B1
                                                            Inorqanlc.  and orqanle chetlcals Mere
                                                            evaluated  against  as aany  as  ten marine
                                                            organisms*   The  authors noted that aost
                                                            published  data of  this type deal with
                                                            toxlcity of chemicals  to  freshwater
                                                            organises*
                                                 ae(contin-
                                                 uous aer-
                                                 ation,  sea-
                                                 watar,  and
                                                 dally
                                                 solution
                                                .'renewal)
                                                                                         same  as above
                                                                     Portmann.  et
                                                                     al  (19711.
                                                                     AMIC-7701
SIlK
Crangon
crangon
                                    BS*   —
                                                       100-330 (TZI
                a* (contin-
                uous, aer-
                ation, sea.
                water, and
                daily
                                                                                         see* as above
                                                     Portaann. et
                                                     al (1971).
                                                     AMIC-7701
-------
                                                                                •olutlon
                                                                                ronaual)
          SI I*
                               Os tree edulls BSA   —
                                                                101 ITZI
                                                  *«( contin-
                                                  uous,  aer-
                                                  ation,  aea-
                                                  wator,  and
                                                  dally
                                                  •olutlon
                                                  renewal)
                                                                                                  saae •* above
                                                                                                                                     Porteann.  at
                                                                                                                                     al  11971).
                                                                                                                                     AHIC-7701
          Sill
                               Randalus
                               aontagul
                                             BSA
                                                                10-33 ITZ)
U>
          Snowdrift SC90
                               Crangon
                               crane; on
                                             BSA    ~
                                                                330-1100  IT*)
                                                 a*(contin-        saae a* above                      Portaann, at
                                                 uoua,aer-                                            al I197H.
                                                 atlon, >0a>                                          *ntc-77ti
                                                 vatar, and
                                                 dally
                                                 aolutlon
                                                 renewal)
                                                 a*(eontin—         One hundrcd-Torty surface active  Port«»nn, «t
                                                 UOUa aer-  aq«nts> solvent eeulslflers, oestlcldest  al 11971).
                                                 atlon, B««.Dolych1orln»ted blohenyls, pure           ANIC-7701
                                                 water, and Inorianlo and organic cheolcsls Mere
                                                 dally      evaluated against as many as ten aarlne
                                                 •Olutlon   orqanlsns.  The authors noted that eost
                                                 r«newil)   published data of this type deal xlth
                                                            toxlclty of ch«elcals to freshwater
                                                            orqinlsas.
         Sodlua arsenate
Carass1us
auratus

                                                                   CT7»
                                                                                a.c
                                   In addition to toxlclty data.     Weir, et al
                           conditioned avoidance resoons* »as        119701,»HIC-
                           studieo at sublethal concentrations.  The 739
                           lOHest concentration of netal resulting
                           In significant lapairoent was?  arsenic,
                           B.10I lead, 0.07t Mercury, fl.OIJt and
                           selenium, 0.25.  Deleterious effects
                           occurred at aetal concentrations
                           aoaroxlaately slallar to potable water
                           standards.
                bicarbonate
                               leooals
                               •acrochlrus
              BSA.
              L
0.600 tT«)
                a*.e, and
                synthetic
                dilution
                water
        This study Has conducted to
deternine the relative toxlcltles of 79
coeeon constituents of Industrial wastes
to a fish, an alga, and an Invertebrate,
The experiments were conducted over a
10-year period for varied purposes.  The
authors recoeeend bloassays with at least
Patrick, at
al 119661.
AHIC-S7ZO
-------
Compound
Organise
Field Field
Study Loot Ion
Toxlclty.
Active
Ingredient,
POM
Experimental
Variables,
Control led
or Noted
Comments
                                                                                                                           Reference
Sodium bicarbonate   Nltzschla     BS»,
                     linear Is      L
Sodium carbonate     lepomis       BS»,
                     maerochlrus   L
Sodium carbonate     Nltzschla     BSA,
                     linear is      L
Sodium cM orate
                     Rasbora       BCFA
                     heteronorpha  and
                                   as*
                                                      650 (T5)
                                                      320 (TO
                                                      2*2 (T9)
                                                      S600  Ul)
Sodium chloride      Leoomls       BS1,
                     •acrochlrus   L
t?,9«.6 mi
Sodium chloride      Nltzschla     BSA,
                     linearis      L
                                                             (T5>
                »',«,  and
                synthetic
                dilution
                Mater

                a*,e,  and
                synthetic
                dilution
                • ater

                »•,«,  and
                synthetic
                dilution
                •»t»r
                hard IHH)
                or soft
                (SMI
                synthetic
                dilution
                Mater, or
                seaMater
                for SODC
                soecles
                a*,e, and
                synthetic
                dilution
                Mater
                a*,e, and
                synthetic
                dilution
                water
                                                                                 three eonoonents of th» food neb.
                                  sane as above
                                                                                        sane as above
                                                                                        sane as above
                                                                                                                           Patrick,  et
                                                                                                                           al  (19681,
                                                                                                                           AMIC-S7?0
                                                                                                                           Patrick, et
                                                                                                                           • I  (1968),
                                                                                                                           AMIC-S728
                                                                                                                           Patrick, et
                                                                                                                           al (1968),
                                                                                                                           AMIC-S7ZO
                                                                                         One hundred sixty-four            Alabaster
                                                                                 o««tlcldes> netting aqrnts, and           (1969),
                                                                                 •Iscellaneous Hater pollutants showed a   AHIC-9VZ9
                                                                                 MMe ranoe of toxlclty scanning 12 orders
                                                                                 of magnitude.  Knowing the toxlclty and
                                                                                 Dercentaae of all conoonents of a
                                                                                 formulation did not result In easy
                                                                                 predictability of the toxlcity of a
                                                                                 Mixture of materials.  Sometimes
                                                                                 pesticides Mere most toxic in hard Mater
                                                                                 and sometlnes the ooooslte Mas true.
                                                                                 Testing the actual Material as sold was
                                                                                 found to be essential.
                                                                                         This study Mas conducted to
                                                                                 determine the relative toxlcltles of 20
                                                                                 common constituents of Industrial Hastes
                                                                                 to a fish, an alga, and an invertebrate.
                                                                                 The experiments Here conducted over a
                                                                                 10-year period for varied purposes.  The
                                                                                 authors recommend bloassays Mlth at least
                                                                                 three components of the food web,

                                                                                        same as above
Patrick, et
a I  (196B),
ANIC-5720
                                                                                                                           Patrick, «t
                                                                                                                           al (1968),
                                                                                                                           ANIC-S720
Sodium chloride
                      Agonus
                                   BSA   —
                                                         ,000-33,DOO   a*(contln-
                                   One hundred-forty surface active  Portmann.et
-------
                              cataphractus
                                                               «T2I
        Sodlwe chlorl«l«
                              Carclnus
                              aaenas
                                           BS»    —
        Sodlua chloride
                             Cardlua edule BS*   —
                                 11,000-16,900
                                 ITZJ
                                                              66,001  (TZ)
VJI
                uoua aer—  agents, solvent e>ulslflers, pesticides,
                atlon, aea-polychlorlnated blphenyls, our*
                water, and Inorganic, and organic chenicats Mere
                dally      evaluated against as nany as ten Marine
                solution   organises.  The authors noted that aost
                renewal)   published data of this type deal with
                           toxlelty of chemicals to freshwater
                           organises.

                a«(contin-        sa»e as above
                uoua aer-
                ation, sea.
                water, and
                daily
                solution
                renewal) •

                a*(contin-
                uous aer-
                ation,  sea.
                water,  and
                dally
                solution
                renewal)
                                                                                                                                    a I  (19711,
                                                                                                                                    »MT.C-7701
                                                                                                 saee  as above
                                          Portaann, et
                                          el  (1971),
                                          •NIC-7701
                                                                                                                                   Portnann, et
                                                                                                                                   el  I1471I.
                                                                                                                                   •HIC-7701
        Sodlue chloride
                             Crangon
                             crangon
                                           BS»
                                 16,900-33,000
                                 (T2)
                a«(contin-
                uous aer-
                ation, sea.
                water, and
                dally
                solution
                renewal)
                                                                                                sa»e as above
                                          Portnann, et
                                          at(197i),
                                          •NIC-7701
        •Sodlue cyanide
Negaprlon
brevlrostrls
(1-3 lull
                                           BS»   —
6.6 (S810 aln)  a.c.e
        Sodiu* flueracetate
                             Salao
                             galrdnerl
              BCF»
              and
              as*
                                                              980  ITZ)
                a»,c,*,f,
                hard (HH)
                or soft
                (SH)
                synthetic
                dilution
        Data (roe study of drug effects   Baldrldge
on young  l«ion sharks Mere treated        (1969),
•athenatlcat ly to d««onstrate             AHIC-3832
• pot Icabl 1 1 ty of classical rate theory to
the study of cheolcal shark deterrents.
Incaoacltatlon (narcosis) MBS the prlnary
paraneter tlned for effectiveness.  This
•as usually quite raold for the aore
effective drugs.
        One hundred sixty-four
pesticides. Netting agents, and
•Iscel laneous vater pollutants showed a
Mlde range of toxlelty spanning 12 orders
Of naqnltude.  Knowing the toxlelty and
percentage of all components of a
                                          Alabaster
                                          (1969). AMIC-
                                                                              •star, or  foraulatlon did not result In easy
-------
Field Field
Corn-pound Organism Study Location






Sodium fluoride Crangon BSA —
cr angon







Sodium hydroxide Agonus BSA
cataohraetus





Sodium hydroxide Cardlum edule RSA --






Sodlun hydroxide Crangon BSA —
er angon





Toxlclty, Cxoerimental
Active Variables.
Ingredient. Controlled
Pom or Noted Comments
seawater predictability of the toxlclty of a
for so«e mixture of materials. Sometimes
species oestlcides were most toxic In hard water
and sometimes the oooosite was true.
Testing the actual material as sold was
found to be essential.
greater than a»(contln- One hundred-forty surface active
300 (TZ) uous, eor- agents, solvent emulslflers. oestlcldes,
atlon, sea. uolych lorlnated biphenyls, Dure
uator, and inorganic, and organic chefricals were
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms*
33-100 (T?) a«(contln- same as above
uous, aer-
ation, sea-
water, and
dally
solution
renewal )
330-1000 (T?) ao(eontln- same as above
uous, aer-
ation, sea-
water, and
dally
solution
renewal)
33-100 (TZI a»(contin- same as above
uous aer-
ation, sea-
water, and
dally
solution
renewal)
Reference






Portmann,








etal (19711,
AMIC-7701






Portmann,
al (19711,
AMIC-7701




Portmann,
al (1971),
AMIC-7701




Portmann,
al (1971) ,
AMIC-7701











et






et
i





et
>





Sedlun eolybdate
                     Salmo
                     qalrdnerl
                                   FL
Castle Lake. 3.S Ib per A
Cal.         INTEI
        Molybdenum- fertilization resulted Cordon*,  et
In greater standing crops of  zooplankton  al  (1970).
-------
 Sodium  molybdate
Sodium nltrlt*
SalvelInus    FL
fontlnatis
                      Rasbora       BCFA
                      heteromoroha  and
                                   BSA
                                          Castle Laket  3»'  ">  Dtr A
                                          Cal.          (NTE)
                                                       210  CT2I
                                                             and  bottom  fauna  and  apparently  In
                                                             Increased yields  of rainbOH and  eastern
                                                             brook  trout.   Mitigating  factors nay have
                                                             Influenced  the results.   A second
                                                             experimental  fertilization Has Initiated.

                                                                   same as above
                                                                                                                            AHIC-5750
                                                                                                      Cordon*, et
                                                                                                      al  (1970).
                                                                                                      AMIC-57SO
Sodium
N-methyldlthlo
Phormldlum
»«blguu«
                                   • '     ^—
                                 0.5-10.0tNTE)
Sodium
pentachloroohenate
Sal mo
galrdnerl
             BCF»
             and
             BSA
                                                      9.19 (T3I
 a*tC<«tfi          One  hundred sixty-four            Alabaster
 hard  (HW1  pesticides!  wetting agents,  and           (1969),
 or soft    miscellaneous  water pollutants showed  a   ANIC-5V2S
 CSH)       wide range of  toxlclty spanning 12 orders
 synthetic  of waqnltude.  Knowing the  toxlclty and
 dilution   percentage of  all components of a
 water, or  fornulat Ion  did not result  in easy
 seswater   predictability of the toxlclty of a
 forsome    mixture of materials.  Sometimes
 species    pesticides were most toxic  In hard water
           and sometimes  the ooooslte  was true.
           Testlno the  actual material  as sold was
           found to be  essential.

                   Of 71,  chemicals evaluated as      Otto (1970)<
           alglcides* only 9 were more  toxic than    AMIC-892
           Cu'tOU.  None Inhibited growth of
           mat-formlnq  algae for more  than 2 weeks.
           CuSO", formulated with certain netting
           agents was more toxic than  CuSO* alone.
           Copper chtoramlne was also  found to be
           more toxic than CuSTt.  No  wetting agents
           were found to  be Inhibitory »t the
           concentrations Investigated  (0.05 and
           0.00? oo  wide range of  toxlclty spanning 12 orders
synthetic  of magnitude.  Knowing the  toxlcity and
dilution   percentage of  all components of a
water, or  formulation did not result  In easy
seawater   predictability of the toxlclty of a
for some   mixture of materials.  Sometimes
species    pesticides were most toxic  In hard water
           and sometimes  the opposite was true.
-------
          Compound
                               Organise?
              Field  Field
              Study Location
ToxicIty,
Active
Ingredient*
  ppm
                                                                              Experiment*I
                                                                              Variables.
                                                                              Controlled
                                                                              or Noted
                                                                                                         Comments
                                                                                                                                   Reference
        Sodlue               Phormldiu*    L     —
        pentechlorophenate   aablguua
                                                              0.5-10.0 INTEI  —
OQ
        Sodlua
        pyrldlne-N-oxide

        Sodium sulfate
Phormldlua
amblguum

Lapoals
aaeroehlrus
                                           a      mm
                                           BS»,
                                           L
O.S-10.0 INTE)


13.900 
a*,e, and
synthetic
dilution
•tater
        Sodlua sulfate
                             Nltzsehla
                             llnearls
        Sedlue thlocyenate   Carclnus
                             aaenas
              BSA,
              L
                                           BSA   —
                                                              1,900   Also reported are factors
                                                            affecting growth of alqae In canals to
                                                            determine whether there Here leads to
                                                            controlling algae by envlronaental
                                                            management.  No practical environmental
                                                            •eans Here found.

                                                                   same as above
                                                                     Otto (19701.
                                                                     AMXC-892
                                                     Otto  11970).
                                                     AMIC-69Z

                                                     Patrick, at
        This study Has conducted to
determine the relative toxlcltles of 20   al  (14681.
common constituents of Industrial Hastes  1HIC-97ZO
to a fish, an alga, and an Invertebrate.
The experiments Here conducted over a
IB-year period for varied purposes.  The
authors recommend bioassays Kith at least
three components of the food web.
                a*.e. and
                synthetic
                dilution
                Hater

                a«{contin-
                uous, aer-
                ation, soa.
                water, and
                daily
                solution.
                ranowa.1)
                                                                                                same as above
                   One hundred-forty surface active
           agents, solvent emulslfiers, pesticides,
           polychlorlnated blPhenyls, pure
           Inorganic, and organic chemicals Here
           evaluated against as many as ten marine
           organisms.  The authors noted that most
           published data of this type deal nlth
           toxicIty of chealcats ta freshwater
           organisms.
                                                     Patrick, at
                                                     al  (196M,
                                                     •".IC-5720
                                          Portmann, at
                                          a I  (19711.
                                          ANIC-7701
-------
 SodluM thloeyanate   Cardlua edule BSA   —
Sodltm thlocyanata    Crangon
                      cranqon
                                    BSA   —
Sadlua thleeyanate
                      Panda I us
                      aontagul
                                   BSA
Splll-X
                     Steal head
                     trout
                     (finger)Ings)
                                   BSA    —
                                                       greater than
                                                       SO* (T2I
                                 greater  than
                                 SOI  ITZI
                                 greater than
                                 6.?  (TZ)
                                                       35.5 IT*)
3plll-X
Spl 11 raaovar-
Cobo salmon   BSA   Hood Canal,  1.5 (K)
(finger-lings) In    Hoodsport,
              situ  Wash.
Plaaphata*
proa*I as
                                   8S»    —
                                                      5.ft  mi
Spill raaovar
Spill raaov«r
                                   BS»   —
                     proaclai
Blochealcal   L     —
oxygen deeand
                                                           IHSO
                                                      630,000
                                                  a«(contin-
                                                  uous aer-
                                                  ation,  aea-
                                                  water,  and
                                                  daily
                                                  solution
                                                  renewal)

                                                 "a«(contin-
                                                  uous, aer-
                                                  ation,  sea-
                                                  water,  and
                                                  daily
                                                  solution
                                                  renov&l)

                                                 a*( contin-
                                                 uous, aer-
                                                 ation,  sea.
                                                 water, and
                                                 daily
                                                  solution
                                                 renewal)
                                                                                         saaa as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                                       Portoann,  at
                                                                                                       al  (1971),
                                                                                                       ANIC-7701
                                          Portaann.et
                                          a I  (1971),
                                          •MIC-7701
                                          Portaann, at
                                          al  (1971),
                                          *«C-7701
                                                                    Evaluation of 11 oil  dlsoersants  Tracy, et al
                                                            resulted  In  a ranking for each and a
                                                            r*coi>mi>ndatlon  tor use  according  to the   t!969),»MIC-
                                                            ranKlng.  Ranking Has based on toxiclty   383*
                                                            and oil dlsoersal effectiveness.  Corexlt
                                                            776l> appeared to have the least toxiclty
                                                            with fair to good oil dispersion
                                                            capabllity.
                                                                       c,d,e,f
                                                                      c.d.e.f
                                                                      c,d,e,f
                                                                                        same as above
        Toxlcltv of six oil spill
dlsoersanfs was determined along with
BOO values.  Pond water Mas used as
diluent and oil was Included In the
experiment.  Oil markedly reduced
toxiclty of ell dlsoersants.  Data are
given as "aost probable** 96-hr TL sub a.

       saae as above
                                                                                         sea* as above
                                                                                                       Tracy,  et al
                                                                                                       (1969)
                                                                                                      ZllllCh
                                                                                                       (19691,
                                                                                                      AHIC-Z909
                                                                                                      Zlllleh
                                                                                                      (19691,»HIC-
                                                                                                      7909

                                                                                                      Zlllleh
                                                                                                      (1969),*HIC-
-------
  Compound
            Fiald  Field
Organise;    Study Location
Toxlcity,
Active
Ingredient,
  Ppm
                                                                      Experimental
                                                                      Variables.
                                                                      Controlled
                                                                      or Noted
Streptomycin sultate llenodrllus   I     —
                     SP
Streptomycin sulfate Tublfex sp    I     —
Streptomycin cut fate Peloseolex sp L     —
Streptomycin sulfate Phormldium    L
                     amblguum
                               «.? (Til
                                                      0.5 (Tl)
                                                      0.9 IT1I
                                                      O.S-1B.O  (HTE)
Strobane
                     icpomls       BS*
                     ey*n«llux
                      (Rtslstantt
                                                       o.ta
                                                                  Tubiticid MOTHS  Mere  found  to b«
                                                          •ooroxliiately 300 tines  nore  sensitive
                                                          than tf>elr oxn gut nicroflora.   The
                                                          authors recon»«nd that streptomycin
                                                          should not be IndlscrInlnatelv  applied  In
                                                          aquatic ecosystem.

                                                                 saae as above
                                                                    Col.r,.,  ,,
                                                                    «1968>,
                                                                                                                           Coler,
                                                                                        same as above
                                                                                                    5S60

                                                                                                    Coler.
                                                                  Of 7k chemicals evaluated as
                                                          alqlcides. only 9 were more toxic than
                                                          CuSOfc.  None Inhibited growth of
                                                          •at-fornlng alqae for nore than 2 weeks.
                                                          CuSOd forpulated Kith certain Netting
                                                          aq*nts was more toxic than CuSOfc alone.
                                                          Cooper chloraolne was also found to be
                                                          nor* toxic than CuSO<<.  No netting agents
                                                          were found to be Inhibitory at the
                                                          concentrations investigated (0.05 and
                                                          0.1105 cpm).  *lso reoorted are factors
                                                          affecting growth of alqae In canals to
                                                          determine whether there were leads to
                                                          controlling aloae by environmental
                                                          management.  No practical environmental
                                                          •cans nere found.
                                                                  Green sunflsh from Belzonl, Hiss. Minchen,  et
                                                          •ere resistant To Chlordane, HeDtachlor,  al (1970),
                                                          LIndanet and Strobane. but not to         »MIc-5i,7i
                                                          Parathion.  Golden shiners fro* the same
                                                          location Here resistant to Llndane and
                                                          Strobane, tolerant to Chlordane and
                                                          MeotacMor, and susceptible to Parathion.
                                                           lack of resistance to Parathion
                                                          Indicated lack of agricultural usage of
                                                          organophospnates in that area.  Resistant
-------
 Strobane
                      Lepomls
                      cyan*1I us
                      (Susceptible)
                                    BSA   —
                                                       0.05 (TZ)
                                                             fish  Mere coapared  to susceptible  ones
                                                             collected at  Starkvitte.

                                                                   same as  above
                                                                                                      MlncheM,
                                                                                                      etal  (19701.
 Strobane
 Strobane
Noteiilqonus
crysoleueas
(Resistant)

Notemioonus
crysoleucas
(Susceotlblel
                                    BSA   —
                                    BSA    —
                                                       Z.2Z IT?)
                                                       0.06  (T2t
                                                                                         save as above
                                                                                         seme as above
                                                                                                                            HlncheH,
                                                                                                                            etal  (1470).
                                                                                                                            HlncheH,
                                                                                                                            etal  (1970) i
                                                                                                                            »mc-5«i71
 Strobane
Strobane
Strobane
                      Palaeaonetes  BSA
                      had 1 aliens Is
                      (resistant)
                                 O.OOSt-0.207
                                 IT1I
Palaeaonetes
Hadlahensls
(non-
resistant)

Cooeoods
(Cvcloos
blcusoIduSf
Cycloos
varicansf
Cycloos
vernal Is,
Eucycloos
aqllls.
Kacrocyolops
albldus,
Orthocycloos
•odestus)
                                   BSA
                                   FL    State
                                   and   College,
                                   BSA   Hiss.
                                                      0.0393(11)
                                                      0.10  (KZ)
        Bloassays Mere conducted nlth     Nagvl, et al
shrlnp  from  three areas  of  Intensive      (1970).
pesticide use  and from an unexoosed area. AHIC-S519
 Previously  exposed shrimp  Mere from 1 to
25 times more  resistant  than unexposed
shrimp.  Both  types of shrimp Mere also
exposed In cages to Maters  of the
contaminated areas.  Susceptible shrlvp
suffered 6%  percent more mortality than
did resistant  shrimp.  The  toxlcity of
the insecticides ranked  in  descending
order was as follows:  most toxic.
Endrln, DDT, Methyl parathlon, Parathlonl
medium toxlclty, Cuthlon, Llndane,
Toxaphene, Strobanes lease  toxic
Chlordane, Sevin, and Heptachlor.
                                                                                         saae  as above
                                                                                                                           Naavi. et al
                                                                                                                           (19701.
                                                                                                                           AMIC-5519
        The response of                   Nagvl, et al
pesticide-resistant aquatic organisms to  (1969).
various pesticides Mas compared to the    AtlIC-5979
response of non-resistant species.
Pesticide-resistant soecles Here
collected at Belzoni and non-resistant
species at State College.  Cooepods.
clams, snails, and sludge norms from
Belzonl Mere considerably more tolerant
to pesticides than the non-resistant
organisms.  The authors note that the
effect of Increased tolerance In the
organisms Is an Increase In the amount of
-------
           Compound
                                 Organic*
              Field  Field
              Study Location
                                                                Toxlelty,
                                                                Active
                                                                Ingredient,
                                                                  Ppa
                                   ExoerlHental
                                   Variables.
                                   Control led
                                   or Noted
                                                                                                           Comments
                                                                                                                                    Reference
          Strobane
I
          Strobane
          Strontlu*
CooepodS
(Cyclops
blcusDldus«
Cyclops
varlcans.
Cycleos
vernal Is.
Eucyclops
•9!IIs.laeroc
Macrocyclops
albldus.
Or t hoc ye I oos
aodestus)

TubIfex
tub Ifex
                                             FL
                                             •nd
                                             BSA
      Belzonl.
      Hiss
                   a.to 
-------
                                          Cal.
 Strontlua
 Sfrontlua
Strontium
Strontlw*
Strontlua
Strontlu*
Strontlua
Strontlu*
Strontlua
Strontlve)
Strontlua
Par•••bran
clathratus
Paratabrax
clathratus
                     Paratabrax
                     clathratu*
Paralabrax
clathratus
(qravld
teaates)

Paralabrax
clathratus
                     Paralabrax
                     clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paral abrax
elathratus
                                    FN
                                   FN
                                   FN
                                   FN
                                   FN
                                   FN
                                   FN
       Catallna     1.8 (ventral
       Island*  Cal.  auscle
                    residue)

       Scattergood   2  (gonads
       St*a»  Plant,  rastducl
       Les  Anqvtts,
       Cal.
                    Catallna
                    Island, call
      Catallna
      Island, Cal.
                    3.%  Igonads
                    residue)
3.2
(gonads.
r«iidua)
      Seattcrgood  1.1  (liver
      Stesn Plant, residua)
      Los Angeles,
      Cal.

      Catallna     2.1  (liver
      Island, Cal. residua)
      Scattergood  5.* (Intequaent
      Steam Plant, residue)
      Los Angeles,
      Cal.
FN    Catallna     10.1(Integuaent
      Island, Cal. residue)
FN    Scattergood  2.3 (heart
      Stean Plant, residua)
      Los Angeles,
      Cat.

FN    CatalIna     3.7 (heart
      Island, Cal. residue)
FN    Scattergood  92 (eyeball
      Stea* Plant, residue)
      Los Angeles,
      Cal.
                                                                                         saaa as abova
                                                                                         saae  as abova
                                                                                         saaa  as  above
                                                                                         saaa  as  abova
                                                                                        saaa  as  abova
                                                                                        saaa  as above
                                                                                        saaa as abova
                                                                                        saaa as above
                                                                                        saaa as above
                                                                                        saaa as above
                                                                                        saae as above
                                                                     Staoleton
                                                                     11968),
                                                                     AMTC-S980

                                                                     Staoleton
                                                                     (1966),
                                                                     AMIC-9910
Staoleton
(1968),
ANIC-5<»»0

Staoleton
(19681.
IMIC-^980
                                                                     Staoleton
                                                                     (1968),
                                                                     AMIC-5980
                                                                     Staoleton
                                                                     (19681,
                                                                     AMIC-59SO

                                                                     Staoleton
                                                                     (1968),
                                                                     AMIC-99RO
                                                                    Staoleton
                                                                    (19681,
                                                                    AMIC-5980

                                                                    5taoleton
                                                                    11968),
                                                                    1NIC-5980
                                                                    Staoleton
                                                                     (1968).
                                                                    •MIC-5980

                                                                    Staoleton
                                                                     (1968),
                                                                    ANIC-S9SO
-------
Comoound
Strontium


Strychnine nitrate








Sulf Isoxazote
(Gantrlsln)









Sulfurlc acid








Sulf uric acid






Toxlclty,
Active
Field Field Ingredient,
Organism Study Location Pom
ParalaH-ax FH Catallna 162 (eyeball
clathratus Island, Cal. residue)

Neqaorlon 8SA — 1.7 (SB 10
brevlrostrls MINI
(1-3 Kg»






Fundulus L — 0.96 (5830)
hetereclltu*
(3 in.)








Agonus BSA — 80-90 (17)
cataohractus







Carclnus BS» — 79-SO (TZ»
•aenas





Experimental
Variables,
Controlled
or Noted Comments



e.c.e








a*.q










a»( contin-
uous aer-
ation, sea.
water, and
dall7
aolutlon
renewal)


a«( contin-
uous aer-
ation, sea.
water, and
dally
solution
renewal)
same as above


Data from study of drug effects
on young lemon sharks Here treated
mathematically to demonstrate
• ool Icahl 1 1 ty of classical rat* theory to
the stulv of chemical sharK deterrents.
Incaoacl tat Ion (narcosis) Has the primary
parameter timed for effectiveness. This
Mas usually quite raold for the more
effective drugs.
The sutfa druq caused no
significant difference In qronth rate.
testes Height, Iodine uotaHe, or liver
weight. Varylno degrees of adrenal
Inactivity and adrenal deqranul at Ion
occurred due to treatment. A significant
Increase in hevatocrit Mas noted. As a
result this chemical has become the sulf a
drug of choice In the Rlngham Laboratory
tor controlling sKln infection of
hi 111 fish.
One hundred-forty surface active
agents, solvent emulslflers, pesticides.
colychlorlnated blohenyts, cure
inorganic, and organic chemicals were
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal with
toxielty of chemicals to freshwater
organisms.
same as above






Reference
Staoteton
(1968) <
AMIC-59SO
Baldridge
(1969),
AMIC-383?






CowmeadOH,
et al
(1969),
AHIC-5736







Portmann, et
al (1971),
»HIC-7701






Portmann, at
al (1971),
AHIC-7701




Sulfwrlc acid
                     Cardlurn edule 85*   —
                                                      700-900  (T3)
                                                                       a«(eonttn-
                                                                                         saoe  as above
                                                                                                                            Portmann,  et
-------
                                                                                uous aer-
                                                                                ation,  sea*
                                                                                water,  and
                                                                                dally
                                                                                solution
                                                                                renewal)
                                                                                                       at  (1971),
                                                                                                       4HIC-7701
         SulfurIc acid
                               Cranqon
                               crangon
                                             BSA   —
                                  70-so ITZI
                                                  a»( contin-
                                                  uous aer-
                                                  ation, sea-
                                                  water, and
                                                                                solution
                                                                                renewal)
                                                                    saae as above
                                           Port serin, et
                                           • I (1971).
                                           •HIC-7701
         Sulfvrte acid
                               PandaI us
                               •ontaqul
                                            BS»    —
                                  kt.S  (TZt
VJ1
                                                  »«(contin-
                                                  uous aer-
                                                  ation,  sea-
                                                  water,  and
                                                  (Jaily
                                                  solution
                                                  renewal)
                                                                    sa*e as above
                                           Portaenn, et
                                           al (1971),
                                           AHtC-7701
         Sulfurlc acid
                              Platlcthys
                              fIesu*
                                            BSA    —
                                                                100-330 (T2)
                                                  a»(contin-
                                                  uous aer-
                                                  ation,  sea-
                                                  water,  and
                                                  daily
                                                  solution
                                                  renewal)
        sane as above
                                           Porteann,  et
                                           al  (1971),
                                           •HIC-7701
         Sulfur
         Suleet (tinted)
                              Fish (not
                              stwcltled)
Hercenaria
•ercvnarla
                                            L     —
                                 9reater than
                                 1000  (K)
                                                               greater  than
                                                               too  m>
         Aoproxliiatc  toxlcltles  of          HsHdestey-
nuncrous pesticides  co*«only  used  In      Thonas
Brltiiln  D«re  summarized.  In excellent      (1971),*MIC-
brlef, general discussion of  toxlclty      1096
testing  Is  also  oresent.

         The effect of 5?  pesticides  on     Davis,  et al
urbryonlc develooient of  clams  and         (1969),
oysters  was reoorted.  Synerqlstlc         4MIC-S990
effects  with  solvents were also reported.
 Host of  the  coxpounds affected
develocient "or*  than survival.  Soae,
hoiievcr, drastically reduced  
-------
Coaoound

SulBet (tinted)
Sulaet (untlnted)
Sulf>et luntlnted)
Sulaet luntlnted)
SulBet (untlnted)
SUB 1 till on
Field Field
Organise Study Location

Hercenwla L —
•ercenarla
(larvae)
lercenarls L ~
•erccnar la
(eggs)
Mercenarla L —
•erccnarla
(larva*)
Crassostrea L —
vlrginlca
(eggs)
Crassostrea L —
vlrglnlea
(larvae)
Puntlus tleto — ~
Toxiclty,
Active
Ingredient.
fpm

greaterthan 100
IT1Z)
greaterthan
1000 m>
greater than
1000 (TlZ)
greaterthan 60R
(TZI
greater than
600 (Tli>)
0.0058 (TO
Experimental
Variables*
Control led
or Noted Consents Reference
selecting chemicals for oest control that
Mould not have serious effect on
shellfish.
sa«e as above Oavlst et
(1964).
AMIC-5990
— sane as above Davls» et
(1969),
AMIC-5990
— saae as above Davis, et
(1969),
AMIC-5990
saae as above Davis, et
(1969),
AMIC-5990
-- sa*e as above Davis, et
(1969).
tMIC-5993
a.c.d.e.f Of the pesticides Investigated, Bhatla


al
al
al
al
• 1

Sutan
                     Ganaarus
                     faselatus
                                   BSA   —
                                                      10.0
                                              the nost toxic Mas Ktofos follOMed In     (1971),
                                              decreasing order by Sumithion, Malathlon, AMIC-5i>23
                                              Fomtthlon, Olnecron, Sevln, and BHC. The
                                              author cites the need for more selective
                                              pesticides nontoxlc to fish or
                                              antagonistic agents for reducing fish
                                              toxlclty.

                                                      Of the aquatic Meed herbicides    Sanders
                                              evaluated, Dlclone xas the most toxic,    (19701,
                                              Oaohnia was generally the most sensitive
                                              organism.  All of the Crustacea Here
                                              affected by much loMer concentration
                                              levels of herbicides than indicated by
                                              the TL sub 50 values.  til of the animals
                                              reoresent Important food chain links.
S.O. 39ft?
                     Hasbora
                     heteroBoreha
BCF»
and
8S«
greater than
1,000 (T?)
a'.c.e.f,
hard(HH)
or soft
ISM)
synthetic
dilution
•ater. or
seaMater
for soae
        One hundred sixty-four
pesticides. Netting agents, and
•Iscel laneous Mater pollutants shoMed a
Ml4e range of toxlclty scanning 1? orders
of nagnltude.  Knotting the toxlclty and
percentage of all components of a
f omul at ion did not result In easy
predictability of the toxlclty of a
Blxture of Materials.  SoaetlBes
Alabaster
(1969>,AMIC-
-------
           S.O. 6211
                                Rasbora       BCFA
                                heteroaorpha  and
                                              BSA
3.9 ITZ)
           S.O.  S*»7
>
I
                                Rasbora       BCFA
                                heteroBorpha  and
                                              BSA
                                                                     U2I
          S.N. 5215
                                Rasbora        BCFA
                                heteronorpha   and
                                              as*
                                                                 23 IT2I
                                                                                 species
                a*,c,e.f •
                hard IHWI
                or
                SOFTCSMJ
                synthetic
                dilution
                water,  or
                seawafer
                for some
                seecles

                a*,c,e,f•
                hard IHH)
                or soft
                (SHI
                synthetic
                dllutloh
                water,  or
                seftwater
                for soee
                soecles

                a*,c,e,f»
                hard (HHI
                or
                SOFT(SW)
                synthetic
                dilution
                water,  or
                seawater
                for SOB*
                species
          TCC
                               Mereenarla
                               aercenarla
                               •
                                                                 0.032  IT2>
 pesticides «er« nost toxic In hard Hater
 and soaetines the opoeslt* was true.
 Testlnq The actual material as Sold Has
 found to be essential.

        save as above
                                                                     Alabaster
        sa*>* as abov*
                                           Alabaster
         One  hundred sixty-tour            Alabaster
D»stlcldes,  Mettlnq aqents, and           (1969),
•l^celleneous  water oollutants showed a   AHIC-SK2S
• l<1e range of  Toxlclty  spannlnq l? orders
of naqnltude.  Knowlnq  the toxlcitv and
percentage of  alt comoonents of a
formulation  did not result In easy
predictability of the toxlcity of a
•ixture  of materials.   Sooetlnes
pesticides were nost toxic in hard water
and soifetlnes  the ooposite was true.
Testlno  the  actual «aferial as sold was
found  to be  essential*

        The  effect of 52 pesticides on    Davis, «t al
••bryonlc developvent of clans and
oysters was  reported.   Synerqlstlc        11969)tAHIC-
effeets with solvents were also reported. 9990
 nost of the compounds  affected
development  more than survival.  Sone,
hox»ver, drastically reduced larval
growth.  The authors point out the
necessity of evaluating the effects of
pesticides on  all life stages or an
organ Is* and note the possibility of
-------
Compound
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient*
Ppm
Experimental
Variables.
Controlled
or Noted Comment*
                                                                                                                           Reference
TCC
TCP
                     Hercenaria
                     •ercenarla
                     (larvae)
                     Crassostrea
                     vlrqlnlca
                     
                                                       0.6  ITZI
TCP
TOE
 TOE
Crassostrea
vlrglnlca
I larvae)

Fish (not
specified)
                      White sucker  FRL
                                   L     ~            greater  than
                                                       1.0  (TIM
                                                       greater  than
                                                       0.01-0.1 IK)
                                          Nlse.  states 0.05-3.81
                                                       residue IS8>
 TOE
 TOE
Vet ION oerch  FRL   Hlse. states 0.03-1.%7
                                 residue  (SSI
Chain
pickerel
FRL   Misc. states 0.09 residue
                   (SB)
                                                            selecting chemicals for oest control  that
                                                            would not have serious effect on
                                                            shellfish.

                                                                   sane as above
                                                                                                      Davis, et al

                                                                                                      (ig69»,«HIC-
                                                                                                      5990
                                                                    The effect of 52 pesticides on    Davis, et al
                                                            embryonic development of dans and        (1969),
                                                            oysters was reoorted.  Srnerglstlc        4HIC-5990
                                                            effects with solvents were also reoorted.
                                                             Most of the compounds affected
                                                            develocment more  than survival.  Some,
                                                            however, drastically reduced larval
                                                            orowth.  The authors oolnt out the
                                                            necessity of evaluating the effects of
                                                            pesticides on all  life stages of an
                                                            organism and note  the possibility of
                                                            selecting chemicals for pest control  that
                                                            would not have serious effect on
                                                            shellfish.
                                                                                         sane as above
                                                      Approximate toxlclties of
                                              numerous pesticides commonly used In
                                              Britain were summarized. An excellent
                                              brief, general discussion of toxlclty
                                              testing Is also present.

                                                      The Bureau of Sport Fisheries
                                              continued its  fish monitoring program by
                                              collecting I
-------
 TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
                      Mhltv catfish FRL   Misc.
                      White o«rch   FRL   Misc.
                      Goldfish      FRL   Misc.
                      Punpklnseed   FRL   NIsc.
                                                States 0.37-0.e as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                         save as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                                       Henderson, et
                                                                                                       al (1971),
                                                                                                       Henderson,
                                                                                                       era! (19M)t
                                                                                                       Henderson*
                                                                                                       er al (1371),
                                                                                                       Henderson,
                                                                                                       et al (
                                                                                   Henderson, et
                                                                                   al  (197D,
                                                                                   AMIC-l«i07

                                                                                   Her»l*rson,et
                                                                                   al  (1971),
                                                                                   »MIC-l«i07

                                                                                   Henderson,
                                                                                   et  al (19711 ,
                                                                                   »MIC-1"»07

                                                                                   Henderson, et
                                                                                   al  (1971),
                                                                                   »MIC-l«t07

                                                                                   Henderson, et
                                                                                   al  (1971),
TOE
                     Gizzard shad  FRL    Misc.
                          States 0.37-0.73
                                 residue  (SB)
                                                                                         save as above
                                                                                  Henderson,
                                                                                  etal  (1971),
TOE
TOE
Snotted
sucker
                                   FRL    NIsc.
                     Bluegllls     FRL    Misc.
      states 0.14-0.3?
             residue (SB)
                          states 0.03-0.**
                                 residue (SB)
                                                                                         sane as above
                                                                                         sane as above
Henderson, et
al (1971),
»MIC-1".07

Henderson,
et al (1971),
TOE
Redbreast     FRL
sunfish
NIsc. states 0.02 residue
             (sat
                                                                                         saae as above
Henderson, at
al (1971).
AMIC-U07
-------
  Coaoound


TOC



TOC



TOE



TOC



TOE



TOE



TOC



TOC



TOC



TOC



TOC



TOC
                                    Field  Field
                                    Study location
                                 ToKlelty,
                                 Active
                                 Ingredient,
                                   CxDerlaental
                                   Variables*
                                   Controlled
                                   or Notad
                                                                             Coaaents
Strloed
aullat
Blue catfish
RocH bass
Freshttater
•Ioatar
lake
•hlteflsh
tali* trout
FRL   Hlse. states R.ZO-2.26
                   residua  (SBI
FRl   HIsc. states 0.08 residue
                   I SB)
              FRL   HISC. States ».05-0.59
                                 residua  (SB)
              F*L   Nlse. states 0.20 residue
                                 I SBI
              FRL   Hlse. states 0.15-9.71,
                                 residue  ISBI
FRL   Hlse. states 0.12 residue
                   ISB)
FRL   HIsc. states 0.02-0.15
                   residue  (SBI
White craDDie FRL   Hlse. states 0.22-0.27
                                 residue  (SBI
Blaaeuth      FRL   Hlse. states 0.17-0.60
buffalo                          residue  (SBI
$••11 couth    FRL   Hlse. states 0.1,6 residue
buffalo                          «S«)
Flathead      FRL   HIsc. states fl.SO residue
eat fish                          ISBI
Goldeve       FRL   HIsc. states  1.02-O.ZO
                                  residue  ISB)
                                                                    s**e as above
                                                                    saae as above
                                                                    s«ae as above
                                                                    s**e as above
                                                                    *••• as above
                                                                    save as above
                                                                    saae as above
                                                                    sane as above
                                                                    sane as above
                                                                    saae as above
                                                                    saae as above
                                                                    saae as above
                                                                                                                             Reference
Henderson.et
al (1971).
»HIC-1<>07

Hendersont
• t al (1471).
Henderson,
*t »tll'37i1,
AHIC-li.07

Men<1*rson.
et al (1971).
»Mic-ii.or

Henderson,
et al (1971),
•HIC-1V07

Henderson,
et at (1971),
AHIC-11,07

Henderson,
et al (1971),
AHIC-11,07

Hendrrson,et
al (1971),
»MIC-li,fl7

Henderson, at
il (1971),
• HIC-H07

Henderson.et
al (1971),
»HIC-1*07

Henderson,
etal  (1971),
AMIC-H.07

Henderson,
et al (1971),
-------
                                                                                                                                      AHIC-mO?
          roc
          roe
          TOE
          TOE
Walleye       FRL    Hlsc.  states fl.03-0.Z9
                                  residue (SB)
                               Sauqer        FRL    Hlse.  *t»t«s 0.10 residue
                                                                 (SB)
                               Flannelmouth  FRL    Misc.
                               sucker
                               BlacH         FRL    Hlse.
                               bullhead
                           states O.ZB  residue
                                  (SB)
                           states fl.OZ-0.85
                                  residue  (SB)
                                                                                                   saae as above
                                                                                                   saae as above
                                                                                                   sane as above
                                                                                                   sane as above
                                                                                   Henderson,
                                                                                   et 11(1971),
                                                                                   »MIC-1«.07

                                                                                   Henderson,et
                                                                                   el
                                                                                   (1971),»MIC-
                                                                                   K.07

                                                                                   Henderson,et
                                                                                   al (19711,
                                                                                   »HIC-l«t07

                                                                                   Henderson,et
                                                                                   »t (19711,
                                                                                   *HIC-li>!)7
>
I
          TOE
          TOE
          TOE
                               Unite bass    FRL   Misc.
                          states  0.09'resldue
                                  (SB)
                               Blaefc crapole FRL    Misc. states
Larqescaf*    FRL
sueher
                                                                 residue  (SB)
Misc. states 0.06-0.29
             residue (SB)
                                                                                                   saee as above
                                                                                                   saae as above
                                                                                                   saee as above
Henderson,
• t al (197H,
*MIC-1«.07

Henderson, et
• I (19711,
*MIC-li»07

Henderson, et
*l (19711,
4HIC-H.07
          TOE
S»sllmouth    FRL
bass
                                                   Misc.
      states 0.1<>-0.23
             residue (SB)
                                                                                                   saae as above
Henderson, et
al
          TOE
         TOE
                               Northern      FRL   Misc.
                               Chlselmouth   FRL   Misc.
                          states  0.03-0.".5
                                  residue  (SB)
                          states  0.09-0.<>1
                                  residua  (SB)
                                                                                                   saae as above
                                                                                                   sa*e as above
                                                                                   Henderson, et
                                                                                   al  (19711,
                                                                                   Henderson, et
                                                                                   al  (1971),
                                                                                   4MIC-1I.07
          TOE
         TOE
Klaaath       FRL
sucker
                                                   Misc.
                               •alnbOH trout FRL   Nlsc.
      states 0.01 residue
             (SB)
                          states 0.03-8.16
                                 residua  (SB)
                                                                                                   saae as above
                                                                                                   saae as above
Henderson,
et al(1971),
AMJC-H.07

Henderson,et
al (1971),
         TOE
                               Brldqello     FRL   Misc. states 0.30 residue
                                                                                                   saae as above
                                                                                                                                      Henderson,
-------
Coaoound
Field Field
Organism- Study Location
Toxlclty.
Active
Ingredient,
»»a
Experimental
Variables,
Controlled
or Noted
                                                                                                  Coaaents
                                                                                                                           Reference
roe
roc
toe
TOC
                      sucker
                      Arctic
                      grayling
                      Round
                      •Mteflsh
                      Longnose
                      sucker
                      Enqraulls
                      •ordax
                                                       CS8I
                                   FRL    Misc.  states
                                   FRL    Nlse.  states
                                   FRL    Nlsc.  states
FN    Pacific
      Northwest
      Coast, Grays
      Harbor,
      Hash.
TOC
roe
 ror
 TOC
                      Cancer
                      •eglster
Cancer
•eqliter
                      Paroohrys
                      vetulus
Herlucclus
productus
                                   FN
                                   FN
                                   FN
                                    FN
                                 1.16 residue
                                 CSB)
                                 1.32 residue
                                 (SB)
                                 0.01-I.S?
                                 residue (SB)
                                 0.07-8.?!.
                                 (reslduel
                                                                                         seae as above
                                                                                         saae as above
                                                                                         s»»e as above
                                                                                  et al
                                                                                  *«IC-Hi07

                                                                                  Henderson,
                                                                                  et al(1971),
                                                                                  AMIC-1<>07

                                                                                  Henderson,
                                                                                  et al (19711,
                                                                                  AHIC-U07

                                                                                  Henderson,et
                                                                                  al (19711,
                                                                                  HMIC-1V07
                                                Pesticides front the Colunbll      Stout
                                        Slver Into Puqet Sound aooarcntly         (196A),
                                        contaminated fish constitutlna commercial AHIC-378*
                                        catches In Pacific Northwest waters.
                                        Residues In these earlne products Mere
                                        substantially lower than the FOA
                                        tolerance for beef (7 ponl.  Fish froa
                                        locations near the aouth of the Columbia
                                        River had higher pesticide content  than
                                        ones caught farther away.
Pacific
Northwest
Coast,
Destruction
Island,
Mash.

Pacific
Northnest
Coast,
Iliiaco.
Hash.

Pacific
Northwest
Coast,
fttalne.
Hash.

Pacific
Northwest
Coast,
Sarasota
Passage.
Hash.
                                                       t.tl(rest duel    —
                                                       t.tZ (residue)   —
                                 (.01-1.07
                                 (residue)
                    0.13-0.05
                    treslduel
                                                                                         saae as above
                                                                                         saae as above
                                                                                         seme as above
                                                                                         same as above
                                                                                                      Stout
                                                                                                      (1968),
                                                                                                      AHIC-378W
                                                                                        Stout
                                                                                        (1966).
                                                                                        AHIC-378%
                                                                                        Stout
                                                                                         (1966),
                                                                                        AHIC-378V
Stout
(19681,
ANIC-3784
-------
u>
           TOE
           TOE
           TOE
           TOE
           TOE-
           TOE
           TOE
          TOE
          TEP«
Her luce I us    FN
productus
Herlucclus    FN
produetus
Nerlueclus    FN
productus
(flshaeal)
Sebastode*    FN
alutus
                                Platlchthys   FH
                                stetlatus
Gadus         FN
•acroceohalus
Sebastodes    FN
flavidus
Sebastode*    FH
flavidus
Pocctlla      BCM
r«tlcu1«t«
Pacific       I.03-0.09
Northwest     (rasldua)
Coastt Fort
Susant Hash.
Pacific
Northn«st
Const. Capa
Fou1w«»th«r,
Ore.

Pacific
Northwest
Const.
•brrdeen.
Hash.

Pacific
Northwest
Coast.
Hecate
Strait, B.C.

Pacific
Northwest
Coast *
Rlalne,
Mash.

Pacific
Northwest
Const,
Blalna,
Mash.

Pacific
Northwest
Coast,
Hecate
Strait, B.C.

Pacific
Northwest
Coast*
11 Mace.Hash.
                                                                 t.arireslduet
                                                                 0.03 (residue)
Trace
{residual
                                                                 0.03(r«sldue1
                                                                 0.01 Iresldue)  —
                                                                 0.01(residue)
0.02-0.09
(raslduel
                                                                                                    se»e  as above
                                                                                                   saaa as above
                                                                                                   sa«a as above
                                                                                                   saae as above
                                                                                                   save as above
                                                                                                   saae as above
                                                                                                   saae as above
                                                                                                   saae as above
                                                                     Stout
                                                                     (1968),
                                                                     ANIC-378%
                                                                     Stout
                                                                     (to.6Bt .
                                                                     *NIC-378«.
                                                                     Stout
                                                                     I196HI,
                                                                     *NIC-378 hr each week over a 33 wk
                                        experlaental period to determine the      (1969),«HIC-
                                        affaet of TEP* on reproduction and on the 9<»S7
                                        vlablly, survival, and reproduction of
-------
          Compound
' Organism
Field  Field
Studr Loot ion
ToxlClty.
•etlve
Ingredient.
  PP»
Experimental
Variables,
Controlled
or Noted
                                                                                                          Connents
                                                                                                                                   Reference
>
         TCP*
         TCPP
                              Poecllla
                              r«tlcul»ti
                              Tublfex
                              tublfex
                                           8CH
             Ft
             •nd
             BSA
      Balzonit
      Hits.
                                                               190  IT«i»
                                                               8.00 INTO
         TCP*1
                              Crassostrea
                              vlrglnlca
                              leggst
                                            L      —
                                greater than
                                10.0 m>
                                                                                                     StocH.  et
                                                           the unexposed Fl  generation.   Hat*
                                                           fertility xas adversely  affect-d  at
                                                           concentration levels  that  did  not
                                                           influence resale  reoroductlve  caoablllty.
                                                            Inhibited brood  oroduction was
                                                           associated Mlth atroohled  and  normal
                                                           testes.   The effect varied with
                                                           concentration and exoosure frequency.
                                                           Hale potency aooeared to recover  Hhen
                                                           exoofures Here discontinued.   No  aoparent
                                                           effects  Here observed In the  Fl
                                                           generation.  TFTPA is  a cheoosterl I ant
                                                           used to  Induce sterility In Insect pests.

                                                a«C(d       •     sane as above
                                                                     AMIC-51.57

                                   The response of                   N*ovl> et
                           pesticide-resistant aauatlc orqanlsms to  al(19*>9>t
                           various pesticides was co*oare
-------
          TCP*
          Terramycln
          (concentrate)
Crassostrea
vlrglnjca
(larvae)

Moron*
saxatllls
IfIngerlIngs)
                                             L      •—
                                                                 greater  than
                                                                 10.0  (TIM
                                  165
                                                             would  not have serious affect  on
                                                             shell fish.

                                                                    sane as above
                                                                                         OavlSt  et
                                                                                         aldSKS),
                                                                                         AMIC-5990

                                                                                         M«lI born
                                                                                         (197H,
                                                                                         ANIOSS71
          Tetradlfon
                               Cardlum edule BS»   —
k
                                                  a,C,d,e,r,          All  compounds  were  Invest loafed
                                                  p          because  of  their  probable usage  In
                                                            hatchery production  of  white  bass.
                                                            Compounds that  can be  used  at recommended
                                                            concentrations  were  Aauathol,  Casaron,
                                                            Llndanr,  and  Terramycln concentrate.
                                                            Those  that should not  be used were
                                                            Aerlftavlne,  Baytuscide, Malachite  green
                                                            oxalate,  and  Malathion.

                                 greater than 10  a»(contln-          One hundred-forty surface active  Portmann, «t
                                 ITZ)             UOU3, asp- agents,  solvent emulslflers,  pesticides,  at  (1971),
                                                  ation,  sea-Dolychlorlnated blphenyls,  pure           AMIC-7701
                                                  voter,  and Inorganic, and organic chemicals were
                                                  daily      evaluated against as many as  ten marine
                                                  solution   organisms.  The authors noted  that  most
                                                  renewal)   published data of this type deal with
                                                            toxlcity of chemicals  to freshwater
                                                            organisms.
          T«tradIfon
                               Crangon
                               crangon
                                             BS»
                                 greiter than 10 «*(co.itin-
                                                 uoxis, aer-
                                                 ation, sea.
                                                 water, and
                                                 daily
                                                 solution
                                                 renewal)
                                                                                                  same as above
                                                                                        Portmann, et
                                                                                        al (1971),
                                                                                        AW.IC-7701
          Tetrshydrofurluryl
          alcohol
Rasbora
hetero«orph»
OCFA
and
BSA
                                                                3,1,99
         TFM
                               Petroayzon
                               •arlnus
                                             FLB
                    Harauttte
                    County,
                   3.8-9 (annual
                   treataent.
                                                 a*,c,e,f.           One  hundred  sixty-four             Alabaster
                                                 hardlHM)    pesticides,  wetting  agents,  and            (1969),AMIC-
                                                 or  soft     miscellaneous  water  ool lutants showed  a    5*25
                                                 ISW)        wMe  range of  toxlclty  spanning  1?  orders
                                                 synthetic   of  magnitude.   Knowing  the toxlclty and
                                                 dilution    percentage of  all  comoonents  of  a
                                                 water, or   formulation  did not  result In easy
                                                 seawater    predictability of  the toxlclty of a
                                                 for some    mixture  of materials.   Sometimes
                                                 species     pesticides were most toxic In hard  water
                                                            and sometimes  the  opposite was true.
                                                            Testing  the  actual material as sold was
                                                            found  to be  essential.

                                                 a,f,                TFN, a selective  lamprey         Man Ion
                                                 conduo-     larvlclde, w»s applied  annually  ever a     (1969),
-------


Compound


Organ is*
Toxlclty,
Active
Field Field Ingredient,
Studr Location Pom
ExD*ri«ental
Variables!
» Control 1 ed
or Noted


Comments


Refer«


nee
                                                   Michigan.,   89-96 percent
                                                   Garlic River peculation
                                                   and SauxHead reduction)
                                                   Lake
          Thailtun
                               Crangon
                               crangon
                                             BSA
                                                                IB (Tit)
ON
          Thlmet
Rasbora       BCFA
heteromorpha  and
              BSA
                                                                less than 10
                                                                (ft)
          Thloglycolle acid
Plmephales
oroneIas
                                             BSA   —
                                                                30.0 (UJ
          Thlolutln
                               Phormldlum
                               ambiguum
                                             •      — a|
                                 S.5-18.0 (100
                                 percent growth
tlvlty     3-year period to the Garlic River which   AMIC-3T61
           flows Into Saux Head LaHe.  The final
           TFN treatment contained l oercent
           flayluselde as a syn»rglst and "bottom
           toxicant".  The two compounds In
           combination were considerably "ore
           effective than TFN alone.  The author
           believed total effectiveness Mas not
           achieved because lanoreys avoid lethal
           doses by moving to untreated water.

a«(contln-         One hundred-forty surface active  Porteann.  et
uoua «er-  aqcnts, solvent enulslflers, oestlcldeSt  al  (19711,
at!or., aea'POlychlorlnated ntnhenyls, pur*           ANIC-7701
water, and Inorganic, and organic chemicals were
dally      evaluated against as many as ten marine
solution   organisms.  The authors noted that most
reneval)   published data of this tyoe deal with
           toxlclty of chemicals to  freshwater
           organisms.

a*,c,e,f.          One hundred sixty-four            Alabaster
hard (HH)  pesticides, Mettlnq agents, and           (1969),
or         miscellaneous water oollutants showed a   »HIC-S<.ZS
SOFTtSH)   wide range of toxlclty spanning It orders
synthetic  of magnitude.  Knowing the toxlclty and
dilution   percentage of all components of a
water, or  formulation did not result In easy
seawater   oredlctabl11ty of the toxlclty of •
for som*   mixture of materials.  Sometimes
species    pesticides were most toxic In hard water
           and sometimes the ooooslte was true.
           Testing the actual  material as sold was
           found to be essential.

a*,d,«,o,          Halathion and Its hydrolysis      Bender(19S9),
•nd F«     products were evaluated with the finding  AHIC-37S7
           that one such product (dlethyl fumarate)
           was lore toxic than Nalathlon to fathead
           minnows.  Synergls" occurred between
           Halathion and two products of hydrolysis.
            Continuous exoosure resulted In
           Increased toxlclty.

                   Of 71. chemicals evaluated as      Otto 119701,
           alglcldes, only 9 were more toxic than    AMIC-S92
-------
                                                                Inhibited
          Thluaet
                               Rasbora       BCFH  —
                               heteromorpha  and
                                             BS»
                                                                1Z ITtl
>
I
          Thorlu*
                               Alosa
                               psoudo-
                               harengua
         Thorlua
         Thorlu*
                               Coregonus
                               artedll
                                            FL
Coregomis     FL
clupeaformls
                                                 a*,c.e,f,
                                                 hard (HH)
                                                 or soft
                                                 (SHI
                                                 synthetic
                                                 dilution
                                                 Mater, or
                                                 seawater
                                                 lor some
                                                 spec1es
                    Great Lakes
                    - Superior,
                    Michigan,
                    and ErU
                                                                O.OOt(resldue)   ~
Great Lakes
- Superior.
Michigan,
•no Erie

Great Lakes
- Suoerlor,
Nlchlgjn,
and Erie
                                                                O.OOJIresldue)   ~
                                                                0.00*(residue)   —
CuSOU.  None  inhibited growth of
•at-formlng aloae  for more than ? NeeHs«
CuSOii  Tornulated Mlth certain wetting
agents  was nor* toxic than CuSOd alone*
Coooer  chloramlne  Has also found to be
•orp toxic than CuSOd*  No wettina agents
were found to be Inhibitory at th*
concentrations Investigated (0.55 and
0.015 Dovl.  Also  reoorted are factors
affecting qrowth of algae In canals to
determine whether  there were leads to
controlling algae  by environmental
management.  No practical environmental
means were found.

        One hundred sixty-four            Alabaster
pesticides, wetting agents, and           (1964),
miscellaneous water pollutants showed a   AHIC-St25
wll* range of toxlclty scanning 1? orders
of magnitude.  Knowing the toxlclty and
percentage of all  coioonents of a
formulation did not result In easy
predictability of  the toxlelty of a
mixture of materials.  Sometimes
pesticides were most toxic In hard water
and sometimes the  opooslte was true.
Testing the actual  material as sold was
found to be essential.

        trace element content  of  fish     Lucas, et
from LrKes Sunerior, Michigan, and Erie   (19701,
was determined by activation analysis.    AHIC-3778
Hhole body and IIver residues  were
determined.  Concentrations varied with
species and lake.  Other elements found
were!   antimony - 5 to 100 Rpb,  barium -
0.2 ppm, cesium - 3 ppb, lanthanum - 1 to
20 oob, mercury - 10 ppb,  rhenium - 0.$
to S peb, rubldiu*  - 0.06 to 6 ppa,
scandium - ? ppb, selenlua - 0.1  to 2
ppb, silver - 0.001 PPb.

       same as above                      Lucas, et al
                                          (1970),
                                                                                                                                              al
                                                                                                 same as above
                                          Lucas,  et
                                          (197Q),
                                          ANIC-37T«
                                                                                                                                              al
-------
Compound
Thorium
Thorium
thorium
Thorium
Thorium
Thorium
Thorium
Thorium
Thorium
Organise
COP eq onus
hoyl
Prosoolum
eyl Indraceum
Salvellnus
namaycush
Osmerus
mordax
Carassius
auratus
Notropls
hudsonlus
Percoosls
omlsco**ycus
Roecus
chrysops
Perce
flave«c«n«
Field
Study
Ft
FL
FL
FL
FL
FL
FL
FL
FL
Field
Location
Great Lakes
- Suoerlor,
MIehlqan,
and frle
Great LaKes
— Superlort
Mlchlqan,
and Erie
Great LaKes
- Superior,
Mlchlqan,
and Frle
Great LaKes
- Superior,
Michigan, and
Frle
Great Lakes
- Superior,
Mlchlqan,
•nd Erie
Great LaKes
- Superior,
HIchlqvi,
and Erie
Great LaKes
- Superior,
Michigan,
and Frle
Great LaKes
- Suoerlor,
Michigan, and
Trie
Great LaKes
- Superior,
Nlchlqan,
and Erie
Toxlclty, Experimental
Active Variables,
Ingredient* Controlled
Pp» or Noted Consents
O.BIZtCreslduet -- sane as above
O.OtO*(resldue) -- saae as above
O.OOtlresldue) — saie as above
? (residue! — sane as above
93lresldue) — sane as above
.O.OOS9(resldue> — saae as above
V.flOZlif residue) — saoe as above
t.003(resldue) — sa«e as above
O.OOJfresIdue) — sa«e as above
Reference
Lucas, et al
(1970) ,
»MIC-3778
Lucas, et al
(1970) .
•MIC-377S
Lucas, et al
(1970).
AMIC-3778
Lucas, et al
(1970).
AMIC-3778
Lucas, et al
(19701 .
AMIC-3778
Lucas, et al
11970),
AMIC-377*
Lucas, et al
(1970),
AMIC-3778
Lucas, et at
(1970).
AMIC-3778
Lucas, et al
(1970),
AnTC-3778
Thorium
                     Stlzostedlon  FL
                                         Great Lakes  8.002(resldue>   —
                                                                                        saae  as above
                                                                                                                          Lucas, et al
-------
                      vltreum
                      vltrtun
                     -  Superior,
                     Michigan,
                     and Erla
 Thyroxlne
                      Gadus morhua  L     ~
                                                       i.oooeii isati   —
 Tlasan (ethyl         Sal mo
 •ercury phosphate)    galrdnerl
              L     —
                                     (SB 1-ZI
                                                 a,e,f (1
                                                 hr
                                                 exposure
                                                 daily for
                                                 up to 11
                                                 days I
Tin
Coregonus     FL
clupeaforals
Moosa Lake,  3.6 trasldual
Can*
Tin
Tin
Tin
Coregonus     FL
etupemformls
                     Esox luclu*   Ft
                     Esox luclus
Lak*
Ontarlot
Can.

Meosa Lakaf
Can.
                                                      O.S  (residua)   —
                                                           (residua)   ~
                    Lakt St.     0.7 (residua)
                    Plarrat Can.
                                                                                   (1970),
                                                                                   •HIC-37TJ
         Line-caught  Juvenile cod held  In  woodhead
Snail  tanks  of  seaxater rcsoonded  to      (1970) ,*HIC-
Thvroxln*  Injection  by a 35 percent       3129
Increase In  sulmnlnq speed.  Large
replication  resulted In hlqhly
slqnltlcant  ,
Industrialized and non-industrial izad     11110-3819
areas were determined.   Only mercury
exceeded regulatory limits, and
concentrations of most  elements were
assent laity the same In fish froa both
areas*

       same as above
                                                                                        saaa as above
                                                                                        same as above
                                          Uthe,  et
                                          ALM971),
                                          AMIC-3819

                                          Uthe,  et al
                                          <1971>,»HIC
                                          3»19

                                          Uthe,  et al
                                          11971),
TIN
                     E*ax luclus   FL    Lake Erie,   0.5  (residue)   —
                                                                                        saae as above
                                                                                                                           Uthe, at al
-------
Coaoound

Tin
Tin
TN
Organise

Osmerus
•ordax
Perc*
f lavescens
Fundulus
heterocl 1 tus
Field Field
Study Location
Can.
FL Laka Erie,
Can.
FL laka Erl«.
Can.
8S» —
Toxlclty,
Active
Ingredlenti
Po»

1.2 Ires 1 due)
0.6 (residue!
0.000008-0.0001
9 CTO
Experimental
Variables,
Controlled
or Noted Comments

•• seae as above
-- sane as above
a*(c,e, 4 laboratory procedure based on
»"d Standard Methods tor -hr toxlcity
synthetic deter* Ins t Ions of crurte oil and
Reference
11971),
•MIC-3819
Uthe, et al
U971),»HIC-
381-3
Uthe, et al
(1971) .AMIC-
3819
LaRoehe, et
81 (1470),
AHIC-I.1,5
TN
TOR
                     Nereis vlrens 8S*
                     Gei*«arus
                     fasciatus
                                   BS»   —
                   0.00006-0.00033 a>,c.e.
                               and
                                   synthetic
                                   seaHater

                   e.3o
                                   seanater   oll-dlsp«rsant mixtures was described.
                                              The dlsoersants varied considerably in
                                              toxlcity, ranging from 0.01 to 7.1 ml/I,
                                              TL50 for 96 hr.  These did not differ
                                              slinl f Icsntl y from 2i«0 hr values.  The
                                              dlsoersants were designated as CX, DO.
                                              Cl, 00, AO, PC, MM, TN, BP, and MA Hith
                                              no further descrlotloft of their chemical
                                              nature or source.  Only a fen bloassays
                                              were conducted Hith shrino.  MollusHs and
                                              echlnoderns xere suggested as suitable
                                              test animals.  The authors stated that
                                              the method could be used to test any
                                              product for toxlcity In seaxater.

                                                     sa»e as above
                                                                                                                           leBoche.et
                                                                                                                           al (19701,
                                                                                                                           »nJC-«ii.5
Tordon C
                     Rasbora
                     heteroeorpha
BCFR
and
8S*
                                                          IT2J
a»                 Ot the aouatlc weed herbicides    Sanders
          Devaluated, Olclone «as the most toxic,      (1970),
          'Oaohnle was generally the most sensitive  »HIC-<>53
           organism.  All of the Crustacea Here
           affected by much lower concentration
           levels of herbicides than Indicated by
           the TL sub <>0 values.  All of the animals
           reoresent Important food chain links.

a*,c,e,t.          One hundred sixty-four
hard (HH)  pesticides, wetting agents, and
or soT*    miscellaneous water pollutants showed a
(SHI       wMe range of toxlcity spanning 12 orders
synthetic  of magnitude.  Knowing the toxlcity and
dilution   percentage ot all comoonents of a
water, or  formulation did not result In easy
seawater   predictability of the toxlcity of a
for some   mixture of materials.  Sometimes
species    pesticides Mere most toxic in hard Hater
Alabaster
(1969),
-------
 Tordon N
                      Rasbora       8CF*
                      heteromorpha  and
                                    8S»
                                                       IBS IT2)
 Toxephene
                      Ictalurus
                      punctatus
                                    BSA    —
                                                       0.013 «Tfcl
 Toiaphene
Toxaphene
Toxaphene
Toxaphene
Toxaphene
Toxaphene
                      Ictalurn
                      ••las
                      Carasslus
                      auratus
                      Cyprlnus
                      carplo
Plmeohales
pr oii
                                   BSA   —
                                   BSA
                                   BSA   —
                                   BS»
Leoomls       BSA
•acrochlrus
leoouls       8S»
micro!oohus
                     Hlcrppterus   8S»
                     sal no Idas
                                                       O.OD5  (Tli)
                                                      0.014  (TM
                                 0.004 IT4)
                                                      0.01%
                                                      0.01»  (Ti.)
                                                      0.013 (T4I
                                                      0.002  IT*)
                                                             and sonetIves the opposira Mas true.
                                                             Testing the actual Material as sold Has
                                                             found to b* essential.

                                                  aSCit,f,          saaa as above                      Alabaster
                                                  hard 
-------
  CoMtound
              Field  Field
  Organise    Study Location
                                                      Texlelty.
                                                      active
                                                      Ingredient,
                                                 Experimental
                                                 Variables,
                                                 Controlled
                                                 or Noted
                                                                                                 Cements
                                                                                                                           Reference
Telephone
Texopttene
Texapheno
Texephene
Texaphene
Seleo         BSA   —
galrdnerl


Salao trutta  BSA   ~
Oncorhynchus  BSA   ~
nlsutch
                      •erea         BS*
                      flevescens
Palaeeonetes  BS»    —
kadlakensls
(resistant!
                                                      •.111 ITM
                                                      ».D«3 IT*)
                                                      I.lit (TM
                                                      1.112 IT»I
                                                      ITU
                                                 test water

                                                 e.
                                                 synthetic
                                                 test nater
                                                 syntnetlc
                                                 test Hater

                                                 a<
                                                 synthetic
                                                 test Hater

                                                 a,
                                                 synthetic
                                                 testoater
Toxephene
Tovapnene
Palaeeonete*  BS*   —
fcedlekensls
reslatant)

Cooepods      FL    State
(Cyclops      and   Col 1090*
bleusoldus,   BSI   Miss.
Cyclops
v Orleans,
Cycloos
                                 !.•?••      a*
                                                       percent K8)
                                                                                        save as above
                                                                                        saae as above
                                                                                        saae as above
                                                                   saee as above
                                                                                                                           Hacek, etal
                                                                                                                           I1WO).
                                                                                                                           AHIC-SS10
                                                                                                                                  et
                                                                                                                           al(1470).
                                                                                                                           Hac«k,et at
                                                                                                                           (19701,
                                                                                                               at
                                                                                                                            (19/0),
                                                                    Bloassays Here conducted with     Naovl, et al
                                                            shrleo fron threr areas of Intensive      (19701,
                                                            pesticide use and froe an unexoosed area. ANIC-5519
                                                             Previously eitoosed shrlep Mere from 1 to
                                                            25 tlaes "ore resistant than unexposed
                                                            shrlep.  Both tyoes of shrlep nere also
                                                            exposed In cages to Maters of the
                                                            contaminated areas.  Susceotlble shrlep
                                                            suffered 66 oercent aore aortal Ity than.
                                                            did resistant shrleo.  The toxlclty of
                                                            the Insecticides ranked In descending
                                                            order «as as folIOMS*  eost toxic,
                                                            fndrln, DOT, Methyl oarathlon, Parathlonl
                                                            •edlue toxlclty> Guthlon, Llndane,
                                                            Toxaphene, Strobanel lease toxic
                                                            Chi ordene, Sevln, and Heptachlor.
                                                                                        saoe as above
                                                                    The response of
                                                            pesticide-resistant aquatic organises to
                                                            various pesticides Mas coooared to the
                                                            response of non-resistant species.
                                                            Pesticide-resistant species Mere
                                                            collected at Belzonl and non-resistant
                                                                                                                           Naovl, et al
                                                                                                                           (19701,
                                                                                                                           AN.IC-5519
Maovl. et al
(1969).
•HIC-5979
-------
         Telephone
>
Jr
         Tmaphene
         Toiaohene
         Toirophene
         T«*apnene
         Telephone
         Te«»pn«ne
                               v«rnalIt,
                               Eucycloos
                               agllls.Maeroc
                              Hterocyelops
                               •ibldus,
                               Orthocyeloos
                               •odestust
Cooeoods
(Cyclops
blcusoldus.
Cycloes
varl cans,
Cyeloos
vernal Is,
Eucyctoos
C9l lls,
-------
  CoBoound
                       Organls*
Field
Study Location
Toxlclty,
Active
Ingredient,
  Po»
Experimental
Variables.
Controlled
or Noted
                                                                                                 Cooments
                                                                                                                           Reference
Toxaphene
Toxlon
                     Nercenarla
                     •ercenarlo
                     (larvae!

                     Care I nut
                                   I     —
                                   USA   —
ToBlon
                     Cerdlue edule SS*   —
Toilen
                     Crengon
                     crengon
                                   8S»   —
TexIen
                      PandaIus
                      •ontagul
                                   SS*   —
less than t.Z5
IT12)
1S3 CTZ)






?7.% (Til





«.6 IT2)






(.9* ITZ)






--

••(contin-
uous, aer-
ation, aaa
water, and
daily
solution
renewal)
a*( contin-
uous, aer-
ation, sea.
wator, and
daily
solution
renewal)
a«( contin-
uous, aer-
ation, gea>
water, and
daily
solution
renewal)
a« (contin-
uous, aer-
ation, saa.
water, and
dally.
solution
renewal)
                                              necessity of evaluating the effects of
                                              pesticides on all life stages of an
                                              organise and note the possibility of
                                              selecting cheelcals for pest control that
                                              would not have serious effect on
                                              shellfish.

                                                     saae as above
                                                                                        se«e as above
                                                                                        OavlSt  et
                                                                                        al(1969>,
                                                                                        HMIC-5990

                                                                                        Portnann.  et
                                                                                        al  119711.
                                                                                        •HIC-7701
                                                                                          One hundred-forty surface active Portmann, et
                                                                                          solvent enulsMlers> prstlcldest al (1971),
                                                                                  polychlorlnated blohenyls. pure          AMIC-7701
                                                                                  InorqarlCt and orqanlc cheilcals Mere
                                                                                  evaluated against as nany as ten aarine
                                                                                  organls»*.  The authors noted that aost
                                                                                  published data of this type deal »lth
                                                                                  toxlclty of chenlcals to fresh«ater
                                                                                  organlsa««
                                                                                        sa«e •* above
                                                                                        Portaann. et
                                                                                        al 119711,
                                                                                        *nIC-7711
                                                                                        sa*e as above
                                                                                        Portaann, et
                                                                                        al 11971),
                                                                                        AHIC-7701
-------
          Trace organic*
          «CCC»
                               Rainbow trout BSA   •«-
                                                                36  IT1)
 I

U>
\n
          Trace organic*
          ICCE)
                               Rainbow trout BSCH  —
          Trace organic*       Rainbow trout BSCH
          ICCEI
          Tract organic*
          ICCE)
                               Gotdan shiner BSA
          Trace organic*       Blue-green    BS»
          ICCE)                 ionfish
         Trace organic*  (CCE   Rainbow trout  BS»
         and C»E)
         Traca organic*  ICCE   Rainbow trout  BSCH
         and CIE)
         Trace organic*  (CCE   Rainbow trout BSCH
         and C*E)
                                                                IB 
-------
>
t-



Compound

Trace organic* (CCE
•nd CAE»

Trace organic* (CCE
•nd CAEI

Trace; organic* (CCC
•nd C*r>

Trace organlcs (CCE
•nd CAE>

Trac* organlcs (CCE
•nd C*EI

Trace organlcs ICCC
•nd CAE)

Traflan C.C.












Trail an E.C.










Flatd Field
Organise Study Location

Olue-green BSA —
sun fish

Red shiner BS» —


Red shiner BSCH —


Red shiner BSCH —


Col den shiner BSA —


Hosaultoflsh BSA


Rasbora BCFA «
heteromorpha and
BSA










Rasbora BCFA — -
heteroaorpha and
BSA






Toxlcltr.
Active
Ingredient*
Po»

137-166IT1I


195 IT1)


?«. (T ZO-301


S.6 .
*MIC-993
Smith, et
al (1970),
AHIC-993
Smith, et *l
doro),
AMIC-993
Smith, et
al (1970),
&HIC-993
Smith, et
al (1970),
AMIC-993
Alabaster
(1969) <
AMIC-S1.85










Alabaster
(1969),
AHIC-S1.Z5






-------
                                                                       spec Us
 Trlbutyl tin
 chloride
 Phormldlum
 amblguu*

                    0.5-10.0
                    percent
                    growth
                    inhibited Hi)
                                                                 (100
 Trlbutyl  tin oxide
                      Sal ao
                      qalrdner I
              BCF»
              and
              BS«
                                                       0.027 (Tl)
Trlbutyl tin  oxide
Sal no
galrdnerl
BCFm
and
BS»
                                                       0.0?0 (T2>
                                    a*«c,e.f.
                                    hard  (HH)
                                    or
                                    SOFTISW)
                                    synthetic
                                    dilution
                                    itater, or
                                    seawater
                                    for some
                                    soeeles
                                                                       a*,c,e.f,
                                                                       hard (HtO
                                                                       or soft
                                                                       (SMI
                                                                       synthetic
                                                                       dilution
                                                                       Mater, or
                                                                       seawater
                                                                       for some
                                                                       species
Triealne
•ethanesul tonate
(lingual)
SalvetInus
fontlnalls
                                                       100 CNTEI
        Of  7(» chemicals  evaluated  as       Otto  (1970),
alqlcldes,  only  9  Here  more  toxic  than    ANIC-S92
CuSOi..  None  Inhibited  growth  ot
niat-forning algae  for wore than t  weeks.
CuSOt*  formulated with certain  Mettlnq
aqent«  was  more  toxic than CuSOfc alone.
Coooer  chlorawlne  Mas also found to be
• ore toxic  than  CuSO<>.   No Mettlnq aqents
•ere found  to be Inhibitory  at the
concentrations Investtoated  (0.05  and
0.905 DDK).  Also  r«oorted are factors
affecting growth of alqae In canals to
determine whether  there  were leads to
controlling alqae  by environmental
• ai*g>**ient.  No  practical environmental
•cans were  found.

        One hundred sixty-four             Alabaster
oestlcldesi wetting agents,  and            (1969),
• Isce I laneous water oollutants showed  a    *NIC-5<»25
wide range of toxlclty scanning 1? orders
of nagnltude.  Knowing the toxlclty and
percentage of all  co»oonents of a
formulation did  not result In easy
predictability of  the toxleity of a
• Ixture of Materials*  Sometimes
pesticides were  most toxic In hard water
and sometimes the  ooooslte was true.
Testing the actual  material  as sold Mas
found to be essential.

       sane as above                      Alabaster
                                           (19691,
                                          »NTC-5«5
                                                      Anesthetization of brook trout
                                              resulted In alterations of hemoglobin,
                                              tissue and Plasma water content,
                                              electrolytes, aortic pressure, and
                                              ventllatory rate and amplitude.  Flnguel
                                              apparently exerted depressive Influence
                                              on central autonoalc functions.  Handling
                                              alone resulted In changes In plasas
                                          Houston,  et
                                          al  11971),
                                          •MIC-38Z3
-------
             Compound
                                  Organise
              Field  Ft ft 
           TrlcMorobenzane
                                 Hercenarla
                                 •arcenarla
                                 (•qqs)
                                              •     ^^
                                 greater
                                 thanlO.O tTZI
           TrIchIorobenzene
           Tr leM orobenzene
           Trlfturalin
Merc en aria
mercenarla
(larvae)

Crassostrea
vlrqtnlca
(eqqs)

•set I us
brevlcaudus


                                               BS»    —
                                                                  greater  Than
                                                                  10.0  (T1ZI
                                                                  3.13 ITZ)
                                                                  ?.0 ITZt
           Trlfluralin
Oreonacta*
nal«
                                                                 50.0  (TZI
                           glucose and lactate content,  and  In a
                           number of electrolytes.

                                   Study of the effects  of           Houston, at
                           anesthesia, handling,  and experimental    at  (19T1),
                           oreoaratlon of brook trout resulted  In    AMIC-382?
                           alterations In henatoloqlcal
                           characteristics* hyoerqlycemla, changes
                           In oI asms, tissue, cellular Ion
                           concentrations, and e-Jul I Ibrlun
                           conditions.  Short-term  (?-•>  hr)  effects
                           correlated with clearances of the
                           anesthetic while oerslstent effects  Here
                           believed to be associated with
                           generalized enoocrlne resoonse to trauaa.

                                   The effect of 52  pesticides  on   Davis,  et  at
                           embryonic devetooment of  clans and        (1969),
                           oysters was reported.   Synerglstlc       »HIC-?990
                           effects with solvents were also reported.
                            Host  of the compounds affected
                           develocnent more than survival.   So*e,
                           however, drastically reduced larval
                           growth.  The authors oolnt out the
                           necessity of evaluating  the effects  of
                           pesticides on all  life stages of  an
                           orqanls* and note  the possibility of
                           selecting chemicals for pest  control  that
                           would  not have serious effect on
                           shall fish.
                                                                                                    saae  as  above
                                                                                                    saae as abova
                                                                     Davis,  et  at
                                                                     (19691,
                                                                     »MIC-5990

                                                                     DavlS*  at
                                                                     al(1969),
                                                                     AMIC-5990
                                   Of the aouMlc weed herbicides    Sanders
                           evaluated, Olclone was the irost toxic,    (14701,
                           Oaohnla was generally the most sensitive  »MIC-<>5*
                           orqanlsm.  »ll of the Crustacea were
                           affected by much lower concentration
                           levels of herbicides than Indicated by
                           the TL sub SO values.  AM of the animals
                           renresent Important food chain links.
                                                                                                   same as above
                                                                                                                                      Sanders
                                                                                                                                      (19701.
                                                                                                                                      AHIC-f.53
-------
 Trtflur«Un



 Trlfturalln


 Trlfluratln



 Trl Mural In
Banhnla naqna BSA   —
Cyorldoosls
vlitua

Lepovls
aacrochlrus
                      Caaaarus
                      faselatus
              BSA   —
BSA   —
                                    BS»   —
                                  8.56  IT21



                                  «.2«  »T2>


                                  •••19 CT2I



                                  1.8 IT2t
                                                                                         saae as abova
                                                                   sane as abova
                                                     saae as abova
                                                                   saaa as abova
                                                                                                                            Sanders
                                                                                                      Sanders(1971>.
 Sanders
 (19701.
 AHIC-t*3

 Sanders(19731.
Trlfluralln
Trloxon*
                      Paleoaonta*
                      kadi aliens Is
Salao
9«lrdn«rl
                                   BSA   —
              BCF»
              and
              •S*
                                                       i.i mi
                                                       !• ITZI
                                                                                                      Sanders
                                                                                                      (19701.
Trlnabon
Rasbora
heterooorpna
              BCF»
              and
              BS*
                                                            (TZ)
                                                                       ••,o,a,,
                                                                       bard (HW)
                                                                       or soft
                                                                       (SW)
                                                                       •ynthatle
                                                                       dilution
                                                                       water or
                                                                       aoa.ua tar
                                                                       for some
                                                                       spacloa
                                   a>,e,a>tt
                                   hard (HNI
                                   or
                                   SOFT(SM)
                                   synthetic
                                   dilution
                                   •ater, or
                                   saawatar
                                   for soaa
                                   soecles
                                                                                         saae as above
                                                      One hundred sixty-four            Alabaster
                                              pesticides. MCttlnq agents, and           119691.
                                              miscellaneous Mater pollutants shotted a   ANIC-5fc25
                                              • Me range of toxlcity spanning 12 orders
                                              of eignltude.  Knotting the toxlelty and
                                              percentage of all components of a
                                              foraulaflon did not result In easy
                                              predictability of the toxlelty of a
                                              alxture of Materials.  Soaetlaes
                                              pesticides Mere aost toxic in hard water
                                              and soaetlaes the opposite Mas true.
                                              Testing ttie actual aaterlal as sold Mas
                                              found to be essential.
                                                                                         saae as abova
Alabaster
(19691.
ANIC-M2S
TubatOK
                      Rasbora
                                    •CM   —
                                                       •.27 IT2I
                                                                       ••tC,a»f*
                                                                                          One  hundred sixty-four
                                                                                                                            Alabaster
-------
  Compound
                       Organise


                     heteroaorpha
                                   Field  Field
                                   Study Location
                                   •nd
                                   BS*
                                 Toxlclty*
                                 Active
                                 Ingredient,
                                   Pp.
                             Experimental
                             Variables,
                             Controlled
                             or Noted
                                                                                                 Comments
                                                                                                                          Reference
Uranlu*
                     A lose
                     paeudo-
                     harangua
                                   FL
Uranium
Urenlua
Uranlua
Uranium
                     Percoosls
                     omlscomaycus
                     Roccus
                     chrysocs
                     Perca
                     Haves eens
Stlzostedlon
vltrtum
vltreua
                                   FL
                                   FL
                                                 hard (HH)
                                                 or
                                                 SOFT(SH)
                                                 synthetic
                                                 dilution
                                                 water,  or
                                                 seawater
                                                 for some
                                                 species
                    Great Lakes  0.9026
                    - Superlort  (residue!
                    Michigan,
                    •nd Erie
Great Lakes  t.OOta(residue)
• Superior,
Michigan,
and Erie

Great Lakes  O.OOZ(resldue)
- Superior,
Ulchlg»n,and
Erie
Great Lakes
- Superior,
Michigan,
•nd Erie

Great Lakes
- Superior,
Michigan,
and Erie
                                                      0.0009(resldue» —
0.001
(residue)
                           pesticides,  netting agents,  and            (1969),
                           miscellaneous water pollutants showed a    AMI
                           •Ide  range of toxlclty  spanning  12  orders
                           of  magnitude.  Knowing  the  toxiclty and
                           percentage of all  components of  a
                           formulation  did not result  In easy
                           predictability of  the toxlclty of a
                           mixture  of Materials.   Sometimes
                           pesticides Mere most toxic  In hard  water
                           and sometimes the  opposite  Has true.
                           Testing  the  actual  material  as sold was
                           found to be  essential.

                                   Trace element content of fish      Lucas, et al
                           from  Lakes Suoerlor, Michigan, and  Erie    (19701,
                           was determined by  activation analysis.     AMIC—3778
                           Whole body and liver residues were
                           determined.   Concentrations varied  with
                           species  and  lake.   Other  elements  found
                           •erel  antimony -  5 to  100  ppb,  barium -
                           0.? ppm,  ceslu* -  3 ppb,  lanthanum  - 1 to
                           70  pob,  mercury -  10 ppb, rhenium - 0.5
                           to  5  ppb. rubidium - 0.06 to 6 ppm,
                           scandlua - 2 ppb,  selenium  - 0.1 to t
                           ppb,  silver  - 0.001 ppb.

                                 same  as above                      Lucas, et
                                                                     (19701,
                                                                     AMIC-3/78
                                                                                                                                     • I
                                                                                        same as above
                                                                                        sane as above
                                                                                        same as above
                                                                                                      Lucas,  et  at
                                                                                                      (1970),
                                                                                                      AMIC-377S
                                                                                                      Lucas,  et  al
                                                                                                      (1970),
                                                                                                      •MIC-3778
Lucas, et at
(1970),
•HIC-J77S
-------
 Uranlua
 Uranlua
 Uranlue
 uranlue
 Uranlua
Uranlua)
Uranlua
Urenlua
                      Coreqonus     Fl
                      artedll
                      Ceregonus     Ft
                      cluveaforals
                      Cereqonu*     FL
                      hey I
                      Prosoolue     Ft
                      eyllndraeeua
                      SalvetInu*    Ft
Osaerus       FL
•ordax
Carasslu*     FL
euratus
Motrools      FL
hud«onlu*
                                   FL
                      cluoastoral*
                     Great  Lakts
                     -  Suotrlor,
                     Rlchlqan,
                     •nd frl«

                     Great  Lakes
                     -  SuoerloPt
                     Michigan,
                     and Frle

                     Great  Lake*
                     -  Sooerlor,
                     Michigan,
                     •nd Erie

                     Great  Lake*
                     •  Suoerior,
                     NIeMaant
                     and Erie

                     Great  Lakes
                     -  *uoerlor«
                                                       g.H2(re«lduel  —
                                                       l.flltfretlduel
                                                       l.ltVSIretlduel  ~
                                                       I.O*Z(resldue>   —
and trie

Great Lakes
- Suoerlort
Hlchlqan.and
Erie

Great Lakes
- Suotrlor,
MIcMeant
•nd Frla

Great Lakes
• Suoerlort
Hlchlaan.
and Erla

Hoose Lake.
Can.
                                                       I.••{(residue!
                                                      I.0fl9(reslduel
                                                      I. lift(residue) —
                                                      S  (residue!     —
Uranlua
Coreaonus
cluoeefarals
                                    Fl
lake
Ontario.
Can.
                                                      f  (residual     —
                                                                                         save as above
                                                                                         *••• as above
                                                                                         saae as above
                                                                                         saae as above
                                                                                         sane as above
                                                                                         cane as above
                                                                                         saae  as above
                                                                                        sane  as above
                                                                    Concentrations of  13 toxic
                                                            elements In dressed fish fro* heavily
                                                            Industrialized and non-Industrialized
                                                            areas Mere determined.  Only *ercury
                                                            exceeded regulatory Malts,  and
                                                            concentrations of  Host eleaents Here
                                                            essentially the saae In fish froa both
                                                            areas.

                                                                   saae as above
                                                                                  Lucas, at al
                                                                                  (197BI,
                                                                                  •MIC-JTT8
                                                                                  Lucas, et at
                                                                                  C19TO),
                                                                                  •HIC-377H
                                                                                  Lucas, et al
                                                                                  •19701,
                                                                                  »NIC-3778
                                                                                  Lucas, et al
                                                                                  (19701,
                                                                                  ANIC-377C
                                                                                  Lucas, et al
                                                                                  (19701,
                                                                                  »MIC-S778
Luces,  et  al
(19701,
•HIC-37T8
Lucas, et al
(1970),
»HIC-J778
Lucas, et al
(19701,
AHIC-3778
Uthe, et
»L<1971I,
INIC-3819
Uthe, et
»L«1971I,
•HIC-3S19
-------
Conoound
Uranlun


Uranlun


Uranlun


Uranlua


Uranlun


Uraabor












Vaaldothlon









Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppn or Noted Comments
Esox luclus Fl Moos* Ush«, 3 (residue)
Can.

Esox luclus Fl Lake St. f (residue)
Plerret Can.

Esox luclus FL Lake Erlet 1 (residue)
Can.

Osmerus FL Lake Erie* 2 (residue) --
aordax Can.

Perce FL Lake Erie, 1 (residue)
flaveseeis Can.

Sel«o BCF* — 925 (T2I »»,c,e.t.
galrdnerl and hard ,Hw)
BS» or
SOFT(SH)
synthetic
dilution
•ater, or
seawater
for some
species



Rasbora BCF» ~ «60 (T2I a»,c,*,f.
heteroaoroha and hard (HW)
BSI or
SOFT(SH)
synthetic
dilution
xater, or
seaxater
for soae
soecles
saae as above


sane as above


sane as above


sane as above


sane as above


One hundred sixty-tour
pesticides, wetting agents, and
nlscel lancous Hater pollutants shoned a
Hide ranqe ot toxlclty spanning 12 orders
of magnitude. Knonlnq, the toxlclty and
oe^c^ntaQ* ot alt eomoonents ot a
formulation did not result In easy
Dredlctabll 1 ty of the toxlclty of a
Mixture of materials. Sot"* tines
pesticides Here most toxic in hard nater
and sonetlnes the opposite Has true.
Testing the actual naterlal as sold Has
found to be essential.
saae as above









Reference
Uthe, et al
119711, AHIC-
JB19
Uthe, et al
J197U,»MIC-
3819
Uthe, et al
(19TH,»»1IC'
J819
Uthe, et al
tl97H,»MlC
J«19
Uthe. et al
(1971), »1IC-
3819
Alabaster
(1969) .
*MIC-5<.25










Alabaster
(1969),
AHIC-S«25







-------
          Vanadium
 Paralabrax
 clathratus
                                             FM
U)
          Vanadium
          Vanadium
         Vanadium
         Vanadium:
                               Paratahrax
                               clathratus
                               Paralabrax
                               elathratut
                               Paralabrax
                               elathratut
Paralabrax
clathratus
                                            FH
 Scatterqood  3.3 (dorsal
 Steam  Plant,  museI•
 Los Angelas?  r«sldua»
 Cal.
                    Catallna     1.9  (dorsal
                    Island, Cal. auscl*
                                 residue*
                                                       Fish  collected  from  an effluent
                                              ploe  of  a  steam  plant and  from offshore
                                              Maters of  Catallna  Island  oere analyzed
                                              for trace  element content.   Trace element
                                              content  of  the effluent water was at
                                              least 5  times greater than that of normal
                                              sea Miter  for cadmium, copoer, nickel,
                                              zinc, and  chromium.  Livers  of fish from
                                              the effluent  Here nearly twice the size
                                              of those from the ocean.  Greatest
                                              differences In concentration occurred
                                              •1th  aluminum, cadmium, and  nlcKel.
                                              Silver, barium,  lltnluit, and lead showed
                                              the least  differences.  The  author
                                              concluded  that trace element analysts of
                                              tissues could be used to determine the
                                              •fleet of  oollutants on marine organises.

                                                     same as above
FH    Scatterqood  3.2 (ventral
      Steam Plant, muscle
      Los Anqeles, residue)
      Cal.

FH    Catallna     1.7 (ventral
      Island, Cal. muscle
                   residual

FH    Scatterqood  5.7 (gonads
      Steam Plant, reslduel
      Los Anqeles,
      Cal.
                                                                                                  same  as above
                                                                                                 Same as above
                                                                                                 saee as above
 Staoleton
 (19681,
 1MIC-5980
                                                                                                                                    S t ao I f t on
                                                                                  IHIC-5980

                                                                                  Staoleton
                                                                                  (1968).
                                                                                  Staoleton
                                                                                  (1968) ,
                                                                                  »HIC-':980

                                                                                  Staoleton
                                                                                  (19681,
                                                                                  4MIC-59BO
         Vanadium
Paralahrax
clafnratus
                                            FH
Catal Ina     *.2 (qonads
Island, Cal. residual
                                                                                                 same as above
                                                                                        Staoleton
                                                                                        119681 ,
                                                                                        1MIC-S980
         Vanadium
         Vanadium
         Vanadium
Paralabrix
elathratus
(qravld
females)

Paralabrax
elathratus
Paralabrax
clathratus
                                            FH
                                            FH
                                            FH
Catallna
Island, Cal.
                                                                Iqonads
                                                                residua)
Seetterqood  Z.K (liver
Steaip Plant, residue)
Los tnqeles,
Cal.
Catallna
Island, Cal<
                   3.1 (liver
                   rasldual
                                                                                                 same as above
                                                                                                 same as abova
                                                                                                 same as abova
                                                                                        Staoleton
                                                                                        (196(11.
                                                                                        »MIC-S980
                                                                                       Staoleton
                                                                                        (19681.
                                                                                       »HIC-5980
Staoleton
(1968),
-------
  Compound
Vanadlua
Vanadlua
Venedluii
Vanadium
Vanadlua
Vanadlwa
VIM*
Velslcol •« 516
l»7.e percent olus 9
percent E»eol H-1%6.
Field Field
Organise Study Location
Paralabrax FN
elathratus


Paralabrax FN
elathratus
Paralabrax FN
clathratus


Paralabrax FN
clafhratus

Paralabrax FH
elathratus


Paralabrax FN
clathratus

Raxbora BCFA
heteroKorpha and
8S*










Pasboro BCF»
heteroaorpha and
BSA
Scatter good
Steam Plant,
Los Angeles.
Cat.
Catal Ina
Island. Cat.
Scatterqood
Steam Plant.
Los Angeles.
Cat.
Catal Ina
Island, Cal.

Scatter good
Steaa Plant.
Los Angelas.
Cal.
Catallna
Island. Cal.

_












M.


Toxlclty, Experimental
Active Variables.
Ingredient. Controlled
Pp» or Noted Comments
2.9 lln tegument ~
resldue)


?.9 (Integuaent --
residue)
3.Z Iheart
residue)


3.2 Iheart
residue)

9 (eyeball
residue!


r.t, (eyeball
residue)

I.1S IT?) a'.c.e.f.
hard(HH)
or soft
(SW>
synthetic
dilution
Hater, or
seawater
tor seme
species



r.t Oil a*,c.e.f.
hard
(NH)OT
saae as above



saae as above

saae as above



saae as above


saae as above



same as above


One hundred sixty-four
pesticides. Netting agents, and
miscellaneous water pollutants showed a
Hide range of toxlclty scanning 12 orders
of magnitude. Knowing the toxlclty and
percentage of all components of a
formulation did not result In easy
prellctabll 1 ty of the toxlclty of a
•Ixture ot materials. Sometimes
pesticides Here most toxic In hard Hater
and sovetlaes the opposite Has true.
Testing the actual material as sold was
tound to be essential.
One hundred sixty— four
pesticides, netting agents, and
miscellaneous water pollutants showed a
Reference
Stapl»ton
I i9f»M ,
AHIC-5988

Staoleton
(196M.
Staoleton
(19661,
ANIC-S910

Staoleton
(19601,
ANIC-S980
Staoleton
(196M ,
AHIC-598H

StaDleton
(196*1 ,
AMIC-S980
Alabaster
(19691.
ANIC-5«Zf










Alabaster
( 19691, AHIC-
S*25
-------
          t pereentCmeol
          H-SOOX, l.Zoercent
          Eplchlorhydrln)
          Vctslcol  A« 506 189
          percent plus 9
          percent Emcol  H-ll>6f
          8  percent Emcol
          H-5IOXI
 ftasbora
 heferoaorpha
BCF»
•nd
BSA
                                  9.2 (TZJ
 >



V/l
         Venzar
                               Rasbora       BCF«
                               heteromorpha  and
                                             85*
                                                               51  (TZ>
                                                  sort tswi
                                                  synthetic.
                                                  dilution
                                                  Mater, or
                                                  seawater
                                                  forsome
                                                  species
 a»,c,e,f,
 hard (HH>
 or  so It
 CSH)
 synthetic
 dilution
 Hater, or
 seawater
 for some
 soeel«s

 a*,c,e,f,
 hard
 IHUIor
 soft  (SH)
 synthetic
 dilution
 Mater, or
 seawater
 for soae
species
         Ver9en«ter tlallne  Sal no
         verqlclde •••dklller galrdnerl
         •I
               BCF*
               •nd
               BSA
                                                                   «TZ»
                                   a>,e,e,f,
                                   hard  IHW)
                                   or soft
                                   (SHI
                                   synthetic
                                   dilution
                                   Hater, or
                                   seaMater
                                   for soae
                                   species
         Vernol ate
Caxvarus
fasciatut
                                            BS»
                  ?0.8  |T2>t 13.1 a*
                  mt
                                                   ranqe of toxlclty soannlnq 12 orders
                                              of maqnltude.  KnoMlnq the toxlclty and
                                              percentage of all coooonents of a
                                              femulation did not result In easy
                                              predictability of the toxlclty of a
                                              •Ixture of materials.  Sometimes
                                              pesticides Mere most toxic In hard Mater
                                              and soeetlmes the opposite Has true.
                                              Testlne. the actual material as sold Has
                                              found to be essential.

                                                     same as above
tlabaster
119691.,
                                                                     One hundred sixty-four            Alabaster
                                                             pesticides, xeftlnq agents,  and           (19691*
                                                             miscellaneous  water pollutants showed a   INIC-SfcH
                                                             Hide  range  of  toxlclty  soannlnq  12  orders
                                                             of  magnitude.   Knowing  the toxlclty and
                                                             percentaoe  of  all  comoonents  of  a
                                                             formulation did not result In easy
                                                             predictability  of  the toxlclty of a
                                                             mixture  of  materials.   Sometimes
                                                             pesticides  Here most toxic In hard  water
                                                             and sometimes  the  opposite Mas true.
                                                             Testing  the actual  material as sold Mas
                                                             found  to be essential.
                                                     same  as above
                                                     alabaster
                                                     (1969),
                                                     •HIC-ftZS
                   Of  the aouatlc  Heed  herbicides    Sanders
           evaluated,  Olclone  Has  the most  toxic.    (1970).4HIC-
           Oaphnla Mas generally the  eost sensitive  *5J
           organism.   All  of the Crustacea  Mere
           affected by much  loner  concentration
-------
  Conoound
              Field  FUld
  Organism    Study location
Toxic!ty,
Active
Ingredient,
  Ppn
Experimental
Variables,
Controlled
or Noted
                                                                                                 Convents
                                                                                                                           Reference
Vernolate
Verne)ate
                     Pateonontes   BS»
                     kadlakensls
                     Asellus       BSA
                     brevlcaudus
                                                       1.9  IT2I
                                                      5.6  CT2»
                                                                                  levels of  herbicides  than  Indicated by
                                                                                  the Ti sub SO values.  All  of the anlnals
                                                                                  represent  laoortant food chain  links.

                                                                                        sane as above
                                                                                                                           Sanders
                                                                                        same as above
                                                                                                      Sanders
                                                                                                      119701,
VernotBte
Vernolate
Vernolate
Vernolate
Vinyl acetate
                     Oreonectes    BS»
                     nals
                     Daphnla magna BSA
                     CvnrldoDsls   BSA
                     vldua
                     •acrocMrus
Asterlas
rubens
                                   BSA
                                   BSA   —
                                 71.. B U2»



                                 1.1 (T7»



                                 O.Z*i (TZI


                                 9.2 (TZ)



                                 330-1000 ITZ)
Vinyl acetate
                     Cranqon
                     crangon
                                   BSA
                                                      10-100  IT2t
                a»(contin-
                uous «ar-
                atlon, sea.
                water, and
                dally
                solution
                renewal)
                                                 ao(contin-
                                                 uous aer-
                                                 ation, sea.
                                                 water, and
                                                 dally
                                                 solution
                                                 renewal)
                                                                                        sane as above
                                                                                        sane es above
                                                                                        same as above
                                                                                        sane as above
                   One hundred-forty surface active
           aaents, solvent e*ulslflers, pesticides*
           oolych lorlnated blphenyls, pure
           Inorqanlc, and organic  chenlcats Mere
           evaluated against as eany as ten narlne
           organises.  The authors  noted that aost
           published data of this  type deal with
           toxlcity of ehenlcals to freshwater
           orqanlsos.

                  sane as above
                                                                     Sanders
                                                                     (19701,
                                                                     Sanders
                                                                     119701,
Sanders(1970t,
AHIC-W53

Sanders
11970) ,
AHIC-SSS

Portnann, et
al (1971),
AHIC-7701
                                                                     Portnann,  et
                                                                     al  (1971),
                                                                     AKIC-7701
-------
 Vinyl acetate
                      Platlcthys
                       ftesus
                                    BS»    ~
                                  greater than
                                  100  «TZ»
                 ml contin-
                 uous aer-
                 ation, sea-
                 water, and
                 daily
                 solution
                 renewal)
                                                                                          saee as above
 Porteann, at
 el (1971*.
 AHIC-7701
  Meedazot T-L
                       Crane, on
                       crangon
                                     BS»    —
                                                        1000-3001  (TZI
                                                  »«•( contin-
                                                  uous aer-
                                                  ation, sea-
                                                  water, and
                                                  dally
                                                  solution
                                                  renewal)
                                                                                          saee as »bov«
                                                                      Portmann, et
                                                                      • I 119711,
                                                                      »nIC-77fll
 Meedazol
                      Rasbora       BCF«
                      heteromoroha  and
                                    BS*
                                                       9*0  (TZ)
 m.
                      Rasbora       BCF*
                      heferoaerpha  and
                                    8S»
                                                            (T?>
                                                  **,Cf«,f,
                                                  herd
                                                  (MM)OP
                                                  SOft (SHI
                                                  synthetic
                                                  dilution
                                                  «at«p, or
                                                  seanttep
                                                  lor son*
                                                  soeetes
                                                  h»p
-------
Compound
Ye 1 1 OH phosphorus
Organism
Gammarus
oeeanlcus
Field Fltld
Study Location
BCF» —
Toxlcity,
»ctlv«
Ingredient,
Pom
S-* CHI!
Experimental
Varl ablest
Control led
or Noted Comments
•*tCtf sane as above
                                                                                                                           Reference
Tell OH phosphorus    Salvellnus    BCFA  —
                     tontlnalls
                                 0.0009 IT 200
                                 hrl
Ye11OH phosphorus


Ye 11 OH phosphorus



Ye 11 OH phosphorus



Ye11 OH phosphorus



Young"* OafIV
Salvellnus
fontlnalis


Osmerus
mordax
Oseerus
•ordax
Clup«a
harengus
                                   BCF»  —
BCF»
              BCF»  ~
              BCF»  —
Rasbora       BCFA
heteroaorpha  and
              BS»
                                                      1.2 IT f.T hr)
                   O.OOOS (T 190
                   hrl
                                 1.0 (T 12 hrl
                                 0.1 IT 3.6 hr)
                                  .s mi
                                                                                                                           ZltKo,  et  al

                                                                                                                           (1970),AMIC-
                                                                                                                           3S17
        the data were presented at LT sub Fletcher,  et
50 (tire to 50 percent lethality).  The   al <1970>,
approximate TL sub m data cited were      AHIC-8J9
Interpolated from plotted TL sub 50
values.  Redness, henolvsls, and reduced
heiiatocrlts correlated directly with
toxlclty to brook trout.  No redness or
hemolysls occurred In smelt although
reduced henatocrlts occurred.  Herring
also turned red with hemolysls and
redness around head and fins.  In time
phosphorus Has toxic at concentrations as
I OH as 0.5 micron/1.

       same a* above                      Fletcher,  et
                                          al(1970),
                                          »MIC-»J9

                                          Fletcher,  et
                                          al(t970>.
                                          »MIC-S39

                                          Fletcher,  et
                                          at (1970),
                                          AMIC-839

                                          Fletcher,  et
                                          al(1970),
                                          AHIC-839

                                          Alabaster,
                                          (19691,ANIC-
                                                     sane as above
                                                                   sane as above
                                                                   sane as above
Zectran
Ictalurus
punctatus
                                   BS»   ~
                                                      11.»0 (T»l
                                   a*,c,e,f.          One hundred sixty-four
                                   hard       pesticides, wetting agents,  and
                                   (Hw)or     miscellaneous Hater pollutants showed a
                                   soft (SM)  Hld» range of toxlclty spanning 12 orders
                                   synthetic  of magnitude.  Knowing the toxlclty and
                                   dilution   percentage of all  components of a
                                   Hater, or  formulation did not result in easy
                                   seanater   predictability of  the toxlcity of a
                                   for some   mixture of materials.  Sometimes
                                   species    pesticides Here most toxic in hard Hater
                                              and sometimes the  opposite Has true.
                                              Testing the actual material  as sold Has
                                              found to be essential.

                                   •t                 Organochtorine Insecticides Here Hacek,et  ml
                                   synthetic  the most toxic compounds,                  (19701,
                                   test nater organoohosphates intermediate,  carbamatas AHIC-5510
                                              the least  toxic.  Brown trout  Has the
-------
 lectren
 loctran
 Zectran
 7eetran
 Zectran
 Zectrafl
Zee t ran
Zeetran
Zeetren
Zectren
Zectr«n
Zinc chloride  tes
tlncl
                      Ictalurus
                      ••las
                      Carass 1us
                      auratus
                      Cyorlnus
                      carolo
                      Pleephales
                      or ore I *s
                      Leoeeils
                      •acroeMrus
                      leoeuls
                      elcroloehus
Mlcropterus
sal noI das
Sal BO
<*a Irdner I
                                    BS>   ~
                                    B3»   —
                                    BS*
                                    BS»
                                    8S»   —
                                    BS*   —
                                    BS»   —
                      Saleo trutta  B5»   —
Oocorhynchus  BS«
klsuteh
                                                       16.TO IT*)
                                                       19.1* IT»»
                                                       13.1.0

, •MIC-5910 Macek, etal (1970)t »«IC-551Q Macek, et a)I1970)t •MIC-S510 Hacek.et al (19701, AHIC-SSIO Meeek, etal •HIC-5510 Macek, etal 11970)t •HIC-5510 Macek, etal (1970), •HIC-SSIO Hacek, et •t(1970)t et •1(1970), »HIC-5510 HaceKt etal (197Q), Br«chyd«nle BSI rerle J.7-».7 (SB*) a,e, and Feedlnq behavior Has affected by synthetic zinc, chroulu*, and aftS In that eore tlae dilution Has rtoulred for consunlnq eeasured water amounts of food. Feeding response Has Macek, et al(1970)t 4HIC-5510 Calrnst et al (1967),»M,IC- 9707

-------
Compound
Field ri«td
Organise: Study Location
Toxlclty,
*ctlve
Ingredient t
Pp«
Experimental
Variables.
Control led
or Noted Comments Reference
Zinc chloride  (a*
Znl
                              Leoomls
                              •acrochlrus
                                   BS*.
                                   L
                                                               3.3  (T%»
>
Zinc chloride (as    Nltzsehia      BS»,
Znl                  linear Is      L
                                                      *.3 ITS)
ae,«> and
synthetic
dilution
water
                                                                      a»,e, and
                                                                      synthetic
                                                                      dilution
                                                                      water
also affected by aeration, feedinq
schedule,  llqht Intensity, and outsld*
disturbances.  The authors note that much
•ore work  is needed to establish the
reliability o1 this procedure.

        This study was conducted to       Patrick, et
determine  th« relative toxlcltles ol 20   al (19S8),
common constituents of Industrial  Hastes  AMIC-5770
to a fish, an alga, and an Invertebrate.
The experiments Here conducted over a
10-year period for varied purposes.  The
authors recommend bloassavs with at least
three components of the food »eb»

       sane as above                      Patrick, et
                                          al (H68),
                                          4MIC-57ZO
Zinc chloride (as
Znl
                             Physa         BSft,
                             heterostropna L
                                                              0.9S
                                                                      a*,a,  and
                                                                      synthetic
                                                                      dilution
                                                                      Water
                                                                                        sane as above
                                                     Patrick, et
                                                     a I  (19681,
Zinc chloride
                     Leblstes      BCF
                     retleulatus
                     (1  mo,  1.1
                     cm!
Zinc chloride
                     Leblstes
                     retleulatus
                     (1 BO. 1.1
                     ee)
                                   BCF   —
                                                               0.56  CTM       a,C,d.e,f,         Toxlclty  thresholds and a
                                                                              n,q, ph03- dilution mixture  threshold Here
                                                                              phates,    calculated  from fish bloassav data  for
                                                                              carbon-    zinc chloride  and ootassiun cyanide.
                                                                              •tea, bi-  Threshold concentrations  for rlnc and
                                                                              Carbon-    cyanide Mere  found to be  0.33 and 0.736
                                                                              fttes, sill- mo/I, resoectlvety.  A orocedure for
                                                                              fates, and determining toxlclty threshold
                                                                              conduc-    concentrations for mixtures of chemicals
                                                                              tanoe      »as also presented.  A zinc-cyanide
                                                                                         dilution ratio for toxlcltv threshold
                                                                                         (THn9) Has  found  to be a  linear function
                                                                                         of the concentration of the tno Ions
                                                                                         taken separately,  and therefore:  THDR
                                                                                         eouals 1 .?f>-0. 86CN-1.'2Zn.  Based on a
                                                                                         multlco*ponent equation,  mixtures ot zinc
                                                                                         •nd cyanide exhibit an antagonistic
                                                                                         •ffeet.  This  appears to  be a significant
                                                                                         advance In an  approach to estimating safe
                                                                                         concentrations for Hater  pollutants.

                                                               1.0 (T 1.51     a,c,d,e,f,        same as above
                                                                                                                           Chen.et al
                                                                                                                           (19691,
                                                                                                                           »HIC-3»3i
                                                                      a,c,d,e,f,
                                                                      n»q» phos-
                                                                      phates,
                                                                      carbon-
                                                                      ates, bl-
                                                     Chen, et al
                                                     (19691,
                                                     ANTC-3631

-------
                                                                                carbon-
                                                                                ates, sul-
                                                                                fates, and
                                                                                conduc-
                                                                                tance
          Zinc
                               Phormldlum
                               amblguum
                                                                1.5-lO.t (NTEI  —
>

M
          Zinc hyoT«Kyoulnon«  Rasbora       8CFA
                               hateromorpha  and
                                             SS«
                                                       0.10  (TZ»
                                                                       a*,C.e,f•
                                                                       hard
                                                                       (HWIor
                                                                       •oft  (SHI
                                                                       synthetic
                                                                       dilution
                                                                       water, or
                                                                       seawater
                                                                       for some
                                                                       species
         Of  7V chemicals  evaluated  as
 •Iglcldest  only  9  were more  toxic  than
 CuSOV.   None  Inhibited growth  of
 mat-forming algae  for more than 2  weeks.
 CuSOV  formulated with certain  wetting
 agents  Mas  more  toxic than CuSO«AHIC"
Zinc sodium citrate
(as Znl
                               Watersloora
                               cueullata
                               I larva*)
                                                      33 IT t hrl
 ••Cflt  and          This study Mas conducted to
 salinity   determine sovcles of marine  larvae
           suitable for use in test screening
           antlfoullng chemicals.  A. sallna (brine
           shrimnt  appeared to have the best
           potential for this purpose.  A. sallna
           larvae sensitivity Mas greatest starting
           at mge 20-ao hr, and tolerated relatively
           IOM pH (5.01.
                                          wisely,  et
                                          at  (1«6»,
         Zinc sodlua citrate
         (as Zn)
                     SPlrorbM
                     lamellose
                     (larvnel
                                                               ••• IT Z hrl
•tCtli and
salinity
                                                                                                 same as above
                                         Mlsely
                                         al
                                         AMIC-5708
                                                                                                                                            et

-------
           Compound
Orqanls*
Field Flald
Study Location
Toxlclty.
»etl»e
Ingredient,
»»•
Fxperlmental
Variables,
Control led
or Noted Comments Reference
vn
ro
         Cine sodium citrate   Buqula
         los Znl               nerltlne
                               (1erv»«l

         line *ulfate(as  Znl   Acroneurla    BSA
         Zinc suit ate  (as     Cphemerella   BSA
         Znl
         Zinc «ulf>to  let     Hydroosyche   BS*
         Znl
                                                                   IT Z hrl
                a,c,I, and
                ••Unity
                                  son* e* above
MIsely, et
• I (19671.
         Zinc suit ate
                              lave*Is       BSCF
                              •aeroehlrus
                                                               SZ (Tit)
                                                               16 (T10I
                                                               32 (Tilt
                                                               2.55 ISBI
                                                                                                                                    »«TC-S767
                a*,c,d,e,f         Cphemerella (mayfly)  Mas the most Marnich, at
                           sensitive aquatic Insect of those
                           studied, and copper the most  broadly
                           tonic metal.  The authors suggest that
                           aquatic Insects nay not be as sensitive
                           to heavy metals as fish.

                a*,e,d,e,f        same as above                      Warnlefc, et
                                                                     al
                                                                     I19S9),»«IC-
                                                                     J767

                                                                     MarnlcK, et
                                                                     .1(1969),
                                                                     »HIC-3767
                                                                               a*,c,d.e,f
                                                                                                 sa*e as above
         Zinc sol fate
         Zinc sulfate
                              Sal ao
                              Salao
                              qalrdnerl
                                            BCF   ~
                                            BCF   —
                                                               0.0056
                                                               (avoidance)
                a,c,d,a,f,         Results of nonltorlnq fish        Cairns, et
                r»»t*      brssthlnq frequency were orlnarlly        al  (19711,
                           reoortml.  The Indicated 7n concentration AMIC-3232
                           •as the lowest detectable.  Reproduction
                           and qroMth of blueallls Mere aooarently
                           not Affected by 0.079 and 0.07? nq/l.   «t
                           a concentration of 0.?5 mq/l spawning  HIS
                           Inhibited and neMlyhatchrd fry Here
                           killed.  The authors suggest ways of
                           lnorovlng this technique and suqqest
                           simultaneous use xlth fish movement
                           change (See Cairns and Waller,  1971).

                                   The threshold avoidance llHlt  Mas Sprsgue
                           essentially the same at 4.5 and 17.0 C.   (196B),
                           The value noted Is 0.01 of the lethal      ANIC-3760
                           threshold concentration, according to  the
                           author.  Improvements In the test
                           procedure are described.
                                                                                 ,c,f
0.56 (threshold a»,c,f
toxlcltyl
                                                                                                 saaa as above
Sorague
(196S).
AMIC-3760
         Zinc sulfafe
                              Plmephales    BCFCM —
                                                               0.1$ (SBI
                                                                               a,c,d,a,t,
                                   Hatching was unaffected at the
                                                                                                                                    Brungs

-------
                      preaeles
                      II. 3-1.* 0)
 Zinc suitate
 >
t
 line sulfate
 Zinc sulfate
                      Xll
                      •aculatus
                      Ml
Plaephales
preaelas  1*
MalnbOM trout I
tftTC-2 eenad
cell
                                    BS«   —
                                                       K.I IT*I
 lc*«d,e**
f»a
Zinc faiws copper,
nickelI
                     Salao
                                                      I.9-1.I  ITtl
                                                                      e,c,e
                                                                                         save as above
                                                                                                 Tissue culture study using the
                                                                                         Eagles MEM eedluH resulted In 71 percent
                                                                                         reluct Ion In eltotlc Index and eytotoxtc
                                                                                         cn«no.«s In cell «oro»»oloqY.
                                                                                         Concentrations at I to 19.0 pp* tine had
                                                                                         no significant effect.  The trout cells
                                                                                         were less sensitive than cultured cells
                                                                                         of fathead alnnon.
                                                                                                 Rainbow trout were exposed to    Brown,  of  al
                                                                                         concentrations of fluctuating levels of    119*9),
                                                                                         aeeonla, phenol,  and zinc and to constant ANIC-S993
                                                                                         •Ixtures of  the three.  Tests with
                                                                                         fluctuating  levels of toxicants showed
                                                                                         that ICSO values  were stellar to those
                                                                                         for  constant  concentrations es lone es
                                                                                         the  periodicity of the fluctuation did
                                                                                         not  exceed the resistance tlee for the
                                                                                         poison.   Except when zinc oredonlnated In
                                                                                         the  •Ivtures,  the fractional  toxlcltles
                                                                                         could be sueeed to give  the toxlclty of
                                                                                         the  •Ixture.

                                                                                                 Rainbow trout were exposed to    Brown.et al
                                                                                         cooper,  phenol, zinc, or  nickel  solution* 11971),
                                                                                         to determine  M-hour ICSI values for      AHIC-S99*
                                                                                         •Ixtures of copper and phenoli  copper,
                                                                                         tine*  and phenol I  end cooper,  sine, and
                                                                                         nickel*   It Mas concluded that  acute
                                                                                         lethal toxlcltles  of  the  •Ixture* could

-------
Field Field
Compound 'Organism Study t»catlen
Toxlclty,
Active
Ingredient,
Ppm
Experimental
Variables.
Controlled
or Noted Consents Reference
line (plus copper,
phenol I
tine
Salmo
galrdnerl
                                   BS«
                                                       0.&-?.«.« (T2t
                                                 a.cte
                                                                                 be adeouately described bv summations of
                                                                                 the fractional toxlcltles.

                                                                                        sane as above
                                                                                                     Broun,et al
                                                                                                     (1970),
Coregonus     FL    Great Lakes  38(resldue)
artedll             - Superior,
                    Michigan,
                    and Erie
line
Zinc
Zinc
Zinc
Zinc
                     Coregonus     FL
                     elupeaforais
                     Coregonus     FL
                     hoyl
Prosoolua     FL
cyllndraceuei
Salve!Inus    FL
naaaycush
Caress1us     FL
auratux
                    Great  Lakes
                    - Superior,
                    Michigan,
                    and  Erie

                    Great  LaKes
                    - Superior,
                    Mlehloan,
                    and  Erie

                    Great  LaKes
                    - Superior,
                    Hlchlqan,
                    and  Erie

                    Great  Lakes
                    - Superior,
                    Hlchlqan,
                    •nd  Frle

                    Great  Lakes
                    - Superior,
                    Michigan,
                    •nd  Erie
                                                      ?3lres!due>
                                                      th(residue)
                                                      11(residue)
                                                      ta(residue)
                                                      36lresldue)     ~
                                                                                         Trace eleeent content of fish
                                                                                 fro* Lakos Suoerlor, Michigan, and Erie
                                                                                 Mas determined by activation analysis.
                                                                                 Whole body and liver residues Here
                                                                                 determined.  Concentrations varied with
                                                                                 species and  lake.  Other elements found
                                                                                 • ere!  antimony - 5 to 100 ppt>, barium -
                                                                                 O.Z ppm, cesluit - 3 ppb, lanthanum - 1 to
                                                                                 ?0 ppb, mercury - 10 aob, rhenium - O.f
                                                                                 to 5 PCb. rubidium - 0.06 to 6 ppm,
                                                                                 scandium - 2 ppb, selenium — 0*1 To 2
                                                                                 pob, silver - 0.001 ppb.

                                                                                        same as above
                                                                                                      Lucas,
                                                                                                      (1970),
                                                                                                      »nic-s77»
                                                                                                                                  et al
                                                                                        same as above
                                                                                        same as above
                                                                                        same as above
                                                                                        saae as above
                                                                                                      Lucas, et al
                                                                                                      (19701,
                                                                                                      •MIC-3779
                                                                                                      Lucas, at
                                                                                                      11970).
                                                                                                      tMIC-3778
                                                                                                                                     • I
                                                                                                                           Lucas, et al
                                                                                                                           11970).
                                                                                                                           AMIC-3778
Lucas, et al
(19701,
•MIC-3778
Lucas, et al
(1970).
•NXC-3778
Zlne
                     Roecus
                                   FL    Great Lakes  28(residue)
                                                                                        saee as above
                                                                                                                           Lucas* at al

-------
          Zinc
                               chrysoDS
                               Coregenus     FL
                               clupeatormls
VJ1
vn
          Zinc
          Zinc
          Zinc
         Zinc
         Zinc
         Zinc
         Zinc
                               Coregonus     FL
                               elupeaformls
                               Esox luclus   FL
                               Esau luelus   FL
                               E*ox luclu*   FL
Osaerus       FL
•ordax
Peres         FL
flaveseens
Parel abrax    FN
elathratus
                     - Superior,
                     Michigan,
                     and frit

                     Moos* Lake,  i* (residue)
                     Can.
                     Lake
                     Ontario*
                     Can.

                     Moos*  Lake,
                     Can.
                     Lake  St.
                     Pierre, Can.
                                                                12 (residue)
                                                                19 (residue)
                                                                14 (residue)     —
                                                   Lake Frle,
                                                   Can.
Lake Erie,
Can;
Lake Erie,
Can.
Scattergood
Steaa Plant,
Los Angelas,
Cat.
                                                                11 (residue!
                                                                it (residue)
                                                                17 (residue)
Z6 (dorsal
auscla
residue)
                                                 Concentrations  of  13  toxic
                                         eleoents In  dressed fish  fro* heavily
                                         industrialized and  non-IndustrialIzed
                                         areas  Here determined.  Only  aercury
                                         exceeded regulatory Halts, and
                                         concentrations of aost  elements Her*
                                         essentially  the saae In fish  Iron both
                                         areas.

                                               saae  as above
                                                                                                  sane as above
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                  saae as above
                                                                                                  saae  as  above
        Fish collected fro* an effluent
Dloe of a steaa plant and froa offshore
waters of Catnllna Island Mere analyzed
for trace element content.  Trace eleaent
cottent of the *ffluent xater Mas at
least *> tlaes greater than that of normal
sea Mater for cadalum, copoer, nickel,
zinc, and chroalua.  Livers of fish froaj
the effluent Here nearly t«lc« the size
of those froa the ocean.  Greatest
differences In concentration occurred
•Ith aluminum, cadmium, and nickel.
Silver, barium, lithium, and lead showed
the least differences.  The author
concluded that trace eleaent analysis of
                                                                                                                                     (1970),
                                                                                                                                     •H!C-37r«
                                                                     Othe, at
                                                                     •L11971),
                                                                     •MIC-3S14
                                                                                  Othe, et
                                                                                  M.U971),
                                                                                  •NIC-SSI?

                                                                                  Uthe, et al
                                                                                  (1971). «1IC-
                                                                                  3819
                                                                                                                                           et  al
                                                                                  Uthe,
                                                                                  C1971
                                                                                  3819
Uthe, at  al
11971). MUC-
3819

Uthe, et  al
(19711, MIC-
3819

Uthe. et  al
(19M),»HIC-
3S19

Staolaton
(1968).
4HIC-598B

-------
Compound

Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Organise;

Paralabrax
clathratus
Paralabrax
elathrafus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrix
clathratus
(gravid
feaates)
Paral abrax
clathratus
Paral abrax
clathratus
Paralabrax
elathratus
Paral abrax
clathratus
Field
Study

FN
FN
FN
FN
FN
FH
FN
FN
FH
FH
Field
location

Catallna
Island, Cal.
Seattergood
Steaa Plant,
Los Angeles,
Catal ina
Island, Cal.
Seattergood
Steaa Plant,
Los Angeles,
Cal.
Catallna
Island, Cal.
Catallna
Island, Cal.
Seattergood
Sttaa Plant,
Los Angeles,
Cal.
Catallna
Island, Cal.
Seattergood
Steam Plant,
Los Angeles,
Cal.
Cafallna
Island. Cal.
Toxielty.
Active
Ingredient.
Pee

10 (dorsal
•uscle
residue)
1? (ventral
•use 1 •
residue)
9 (ventral
•usele
residue)
172 Igonads
residue)
119 (gonads
residua)
Igonads
residue) •
61 (liver
residue)
100 (liver
residue)
Z?J (Integument
residue)
190 1 Integument
residue)
Experimental
Variables,
Controlled
or Noted CoMents
tissues could be used to determine the
effect of pollutants on Marine organism.
— saee as above
— same es above
same as above
saee as above
— same es above
— same es above
~ same as above
~ same as above
— same es above
same) as above
Reference

Stvolete*
(1968),
AHIC-5980
Staoleton
ANIC-5980
Staoleton
11968),
AHIC-S980
Staoleton
11968),
AKTC-S980
Steoleton
(1968),
ANIC-S980
St»oleton
(19681,
ANIC-S980
Staoleton
(1968),
AHIC-5980
Staoleton
(19681.
AHIC-5988
Staoleton
11968),
ANIC-S980
Staoleton

-------
                                                                                                                                   •MIC-59SO
>
        Zinc
        Zinc
        Zinc
        Zinc
        Zinc
                             Par a I abrax
                             elathratu*
                             Paratabrax
                             et athratu*
                             Paralabrax
                             clsthratus
                             Par at abrax
                             clathratus
 Salao
 galrdnerl
                                           FN
                                           FN
                                           FH
                                           FH
                     Scatterqood  »? (heart
                     Stcaa Plant* residua)
                     Los Angeles,
                     Cat.
                     Cataltna
                     Island* Cal<
 98  (heart
 r as I dual
                     Scatterqood  701 (eyeball
                     Steae Plant• resIduel
                     Los Angeles,
                     Cat.

                     Catatlna     6«« (eyeball
                     IsIandt Cat. residual
                                                                                                saae  as above
                                                                                                sane as above
                                                                                                save as above
                                                                                                saae as above
                                                                     Stapleton
                                                                     (1968),
                                                     Staoleton
                                                     (1968).
                                                     »NIC-S9«0

                                                     Staoleton
                                                     (19*8).
                                                     ANIC-9990
                                                                     Stapleton
                                                                     (1968),
                                                                     »HIC-59«0
                                           •Sft   —
                                                              1.99-9.19
                                                              (fluctuating
                                                              cone, T
                                                              !3%0-!96I Bin)
                a,c*,d.e*.
                                   Ralnbon trout were exposed to     Brown, et al
                           concentrations ot fluctuating levels of   (1969),
                           aaaonlHi phenol, and zinc and to constant AHIC-S99J
                           alxtur«s of the three.  Tests with
                           fluctuating levels of toxicants showed
                           that LC50 values were slallar to those
                           for constant concentrations as lonq as
                           the periodicity of the fluctuation did
                           not exceed the resistance tlae for the
                           poison.  Except «hen 2lne predominated In
                           the alxturesf the fractional  toxlcltles
                           could be sunned to 9lve the toxlelty of
                           the alxture.
       Zinc
       Zinc
Salvo
oalrdnerl


Salao
qalrdner!
                                           8S«   —
3.9 IT
a In)
a,c»,d,a*,
t.a
                                                                                                save as above
BroMn, at
al 119691,
•NIC-9993
                                                                  ITZI
       ZnSO* .
       t 01 US I
               THZt (as Zn
Lepoals
aaerochlrus
              and
              CF
                a,Cte              PalnbOH trout were exposed to     Brown,  at  at
                           cooper, phenol, zinc, or nickel  solutions (19701.
                           to determine da-hour LC90 values for      AHIC-999*
                           alxturei of coooer and phenol I cooper,
                           zinc,  and phenolt  and eoooer,  zinc,  and
                           nickel.  It Mas concluded that acute
                           lethal  toxlcltles  of  the Mixtures could
                           be adequately descrlb«
-------
           Compound
                                Organism
                                   Field  Field
                                   Study Location
                                 Toxlclty,
                                 Active
                                 Ingredient*
                                   Pp«
                                   Exotrl»«nt*l
                                   Variables.
                                   Controlled
                                   or Noted
                                                                                                          Comments
                                                                                                                                    Reference
ZnSOt . 7H20
2 plus)
                      las Zn
vn
OO
ZnSOt . 7HZO (as Zn
? olus)
Zn, Ml* Cr, CH, Cu,
and Zn
                              Notemlgonus
                              crysoleueas
                              Carasslus
                              auratus
                              Catostonus
                              commersonl
                                            8S»   —
                                            BSA
                                                               7.5 
                    Igan
BSACF Grand River  betiieen
IHL»  at           1.25-3.75
      Mypalng.Hlch percent IT3»
      Igan
                                                 a,c,d,e,t,
                                                 r,t
                                                 a,c,d,e,r,
                                                 r,t
                                                            lOHest detectable concentration causing
                                                            significant movement changes.  Values for
                                                            qolden shiners and goldfish nere obtained
                                                            In preliminary studies.  At 1/10 the
                                                            Indicated concentration, gronth end
                                                            reoroduetlon of bluet) 11 Is Here
                                                            Significantly affected but not at 1/100
                                                            dilution.  Considerable discussion and
                                                            additional data are presented.

                                                                   same as above
                                                                                                 saae as above
                                                                                        Cairns, et
                                                                                        el 11971*.
                                   a,c,a, con-        A mobile bloassay unit Mas
                                   ductlvity, utilized to conduct this study of
                                   Hl,Cu,Cr,  municipal MasteHater containing the
                                   CH, and Zn Indicated toxicants.  River Hater ••*
                                              used as diluent.  The conclusion Mas
                                              reached that synerglstlc or additive
                                              toxic vffects occurred since toxlcltv Mas
                                              greater than that e» any ol the Ions
                                              singly.
Cairns, et
119711,
ANIC-3231

Zllllch
(19691 ,
AHIC-?906
                                                                      a.c.s, con-
                                                                      ductivity,
                                                                      Hi.Cu.Cr,
                                                                      CH, and Zn
                                                                                                 sane as above
                                                                                                                al
Zllllch
(19691,
AHIC-Z906
         l,l--methylenedl-2-  Ptyehochellus USA   ~
         napbthol             oregonensls
                              171 ••)
                                                      0.8B6-0.815 IK
                                                      6-31 hrt
                                                                                                  The chemical studied Mas found to MacPhee,  et
                                   and        be selectively lethal to soua«flsh at
                                   conduo-    concentrations 3 to 100 times more toxic
                                   tlvity     to th»se species than to salmonids.
                                              Potency varied positively Hlth
                                              concentration and temperature.
                                              Concentrations cited are for 10-U C.  A
                                              sheep and ducks showed no ill effects
                                              over a 7-day period Mhen forced to drink.
                                              Mater containing in ppm of the naphthol.
                                              A field application In a small lagoon
                                              containing several species of fish
                                              resulted only in kill of P. oregonensls.
                                              This chemical appears to be an effect Iva
                                              Ptsclclde that Is selective tor
                                              squanfish.
                                                                                                      al
                                                                                                      «19691,AHIC-
                                                                                                      5*51
-------
vn
          nephthol
          1. l"-»«thy lenedl-?-
          naphthol
          ltl"-«ethylenedl-?-
          naphthol
          l,l"-e>ethylenedl-2-
          naphthol
l,l"-a*thylenedI-Z-
naphthol
          1,2 dleMoroprooane
                      Ptychochellus  8S«
                      IMDQliae  158
                      mi)
                     Salvellnus    BS«
                     fontlnalls
                     191 ••)
                     Oncerhynchus  BS»
                     tshawvtseha
                     18* ••)
                     Oncorhynchus  BS»
                     klsutch
                     M)
Salao
qcl
M)
                     Crsngon
                     crsngon
                                         (66
                                             BSI
                                  8.01-0.03IK
                                  6-ZO hr)
                                                                 0.3 (SB*>
                                                                 (.1  ISBd)
                                                                 8.6-t.JISB»>
                                                                0.6-1.3  ISBkl
                                             BSA   ~
                                         than
                                 180 (TZ>
 a'.c.d.l,
 and
 conduc-
 tivity

 a*.c(d«rt
 and
 conduc-
 tivity
 and
 conduc-
 tivity

 •••e«dtf •
and
conduc-
tivity

 a*tc«dt ft
and
 conduc-
 tivity

a«( contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
                                                                                                   sane as above
                                                                                                   sea* as above
                                                                                                   *••• as above
                                                                                                   seae as above
                                                                                                   saae as above
    heet et
al  ll<*6«>«
»HIC-5I.50
                                                                                                       HacPhee,  at
                                                                                                       al  tl<>6«>.
                                                                                                       •HIC-5«,50
                                                                                                       HacPhee.  *t
                                                                                                       al  f 19691.
                                                                                                       »HIC-5«.50
         at
al
I1969I,»HIC-
5*50

NacPheet et
al (1969),
»HIC-5<,50
                                             t     —
                                                                0.9-10.0  IMTF)  —
         ro-l,*-••than*       anblguua
         t.»t»»t»a-tatrahydro
         -5,e-naohth«Qulnoo«
         One  hundred-forty  surface  active
         solvent  emulilflers,  pestleldest
polychlorlnated  blphenyls,  oure
Inorqtnlc, and organic chemicals Mere
evaluated against  as  many  as  ten marina
organises.   The  authors noted that »ost
published data of  this tyoe deal with
toxlclty of  chealcals to freshwater
organisms.

        Of 71, chemicals evaluated as
alglcldes, only  9  were more toxic than
CuSTt.  None  Inhibited growth  of
•at-foralnq  algae  for more  than ? weeks.
CuSOU  formulated with certain  wetting
agents was more  toxic than  CuSOfc alone.
Coooer chlorarln*  was also  found to be
more toxic than CuSOt.  No  wetting agents
were found to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 com).  Also reoorted  are factors
affecting growth of algae In canals to
determine whether there were leads to
controlling algae by envlronaental
manegement.  No practical  envlronaental
aeans were found.
Porteann,
al (1971)
•NIC-7701
                                                                                                                                                et
                                                                                                                           Otto  11978),
                                                                                                                           »HIC-»9Z
-------
  Compound
Organise)
Field Field
Study location
Toxlclty.
Active
Ingredient,
Exoerlmental
Variables,
Controlled
or Noted
                                                                                                 Cements
                                                                                                                           Reference
Z-a«lno-3-eMoro-l,*  Phoraldlua
-nephtheouInane       eablguu*
                                 0.*-iO.OI16oer
                                 cent growth
                                 Inhibited 1M
t-ehloro-*.*i-bls
lethyl««lne>
S-trlazlne
•normldlua
•eblouuti

1.5-10.0 tNTE)
<-dlmethyt-aalno-l,* Pnoraldlua
-naohtheoulnone      •ablauu*
                                 0.9-10.OU&oer
                                 cent growth
                                 Inhibited Ul
        Dt 71, chemicals evaluated as      Otto (1970)*
•lalcldest only 9 Here nore toxic than    AHIC-89Z
CuSOd.  Non« Inhibited qronth of
•at-formlng algae lor more than ? weeks.
CuSOt formula ted with certain Netting
aqents Mas more toxic than Cu50t alone.
Cooper chloramlne Mas also found to be
•ore toxic than CuSOfc.  No wettlnq aqents
Mere found to be Inhibitory at the
concentrations Investigated (0.05 and
O.OQ* DOM).  Also reoorted are factors
allotting growth of algae In canals to
determine whether there Mere leads to
controlling alcne by environmental
•antqerent.  No practical environmental
•evns Here found.

        Of T<» chemicals evaluated as      Otto (1970),
•tqlcldes, only 9 Here nore toxic than    ANXC-842
CuSOt.  None Inhibited growth of
•at-for*Inq algae for more than 2 Meeks.
CuSOJ. formulated nlth certain xettlnq
aqents Mas «or« toxic than CuSOU alone.
Coooer chloravlne Has also found to be
•ore toxic than CuSO<«.  No Netting agents
Mere found to be Inhibitory at the
concentrations Investigated (II. OS and
0.00$ DP*),  llso reoorted are factors
affecting growth of algae In canals to
determine Mhether there Mere leads to
controlling algae by environmental
•anagevent.  No practical environmental
means Mere found*
                                   Of  71.  chemicals  evaluated as      Otto
                           alqlcldest  only 9  Mere more  toxic than    »HIC-89?
                           CuSOt.   None  Inhibited qroHth of
                           mat-foraing algae  for more than ? meeks.
                           CuSO*  formulated Mlth certain netting
                           agents  Mas  more toxic than CuSO*  alone.
                           Coooer  chtoranlne  Mas also found  to be
                           •ore toxic  th»n CuSO<>.   NO wetting agent*
                           •ere found  to  be Inhibitory  at the
                           concentrations investigated  tO.05 and
                           O.tlS »o»).  Also  reoorted ere factors
-------
 t-Hereaotedlethyl
 succlnato
 Plveohales
 proa* In
 35. •  (Ul
 g-oreeenai
 faereleln)
Phormldlu*
aablguum
                                    L     —
1.9-10.8  166
percent gromth
Inhibited !«.»
?-preo«n«-l-ol
tallyl alcoholl
PhormldlUB
•mblguum
r-tert-butylamlno     ffiorvidlue)
^-ethyl-amlno         amblguum
t-methyl S-trlazlne
                                    I     —
                                   •      _,.^
0.5-10.8 116
oereent
growth
Inhibited 114.)

V.5-10.0 «**
percent growth
Inhibited 1*»
                                                                                  affecting growth  ot algae  In canal*  to
                                                                                  determine whether th*r* «»r« leads to
                                                                                  controlling alga* by environmental
                                                                                  aanaqeacnt.  No oractical environmental
                                                                                  •eans Her* tound.

                                                                       a* chemicals evaluated as
                                                                                  alqlclOeSt only 9  M*T* more toxic than
                                                                                  CuSOt.  None Inhibited growth of
                                                                                  aat-foralnq algae  tor More than f HOCKS.
                                                                                  CuSO". foreulated with certain wetting
                                                                                  aqents was nore toxic than CuSOt alon*.
                                                                                  Coooer chloraelne Has also found to  be
                                                                                  •or* toxic than CuSOt.   No netting agents
                                                                                  •ere found to be  Inhibitory at the
                                                                                  concentrations Investigated 11.05 and
                                                                                  0.005 noiil.  »lso reported are factors
                                                                                  aftectlno growth of alga* in canals to
                                                                                  deternine whether there Here leads To
                                                                                  controlling algae by environmental
                                                                                  aanaqeaent.   No practical  environmental
                                                                                  •eans were found.

                                                                       —                same as above
                                                                      Bender
                                                                      (19641,
                                                                      •HIC-3707
Otto (19701.
•HXC-vtt
                                                                                                                            Otto (14701,
                                                                                                                            •NIC-09Z
                                                                                          Of  Tfc  chemicals  evaluated  as
                                                                                  alglcldes,  only  9  Here more  toxic  than
                                                                                  CuSOi..   None  Inhibited growth of
                                                                                  aat-forming algae  for more than Z  Heeds.
                                                                                  CulO*  formulated with certain netting
                                                                                  agents  Has  more  toxic than CuVJt alone.
                                                                                  Coooer  cMor»«|n«  Mas also found to be
                                                                                  •ore toxic  than  CuSOfc.   No wetting agents
                                                                                  Here tound  to  be Inhibitory at the
                                                                                  concentrations Investigated  (0.05  and
                                                                                  0.405 opmt.  Also  reported are factors
                                                                                  affecting growth of algae In canals to
                                                                                  determine whether  there Here leads to
                                                                                  controlling algae  by environmental
                                                                                  •anagement.  No .practical environmental
                                                                                                      Otto (1970),
                                                                                                      ANIC-89Z
-------
Ceewound Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient,
Ppa
Experimental
Variables,
Control led
or Noted Comments
Reference
        Z.3-dtcMoro-l,*»    Phoraidlua    L     —
        Mphthftq"**""!*       amblguu*
                                                              0.5-10.0 (NTE>   --
i
                                                            •cans Here found.

                                                                    Of 7i» chemicals evaluated as
                                                            algtcldes, only 9 were more toxic than
                                                            CuSO"..  None Inhibited growth of
                                                            •at-formlng algae for more than Z weeks.
                                                            CuSOd formulated with certain wettlnq
                                                            agents was more toxic than CuSO* alone.
                                                            Cooo«r cMorawlne was also found to be
                                                            nore toxic than CuSOii.  No wetting agents
                                                            •ere found to be Inhibitory at the
                                                            concentrations Investigated 10.OS and
                                                            0.005 DDF).  Also reported are factors
                                                            affecting growth of algae in canals to
                                                            determine whether there were leads to
                                                            controlling algae by environmental
                                                            •anagerent.  No practical environmental
                                                            weans Here found.
                                                                     Otto (19701.
                                                                     AHIC-B9?
        Xt*-0 (acid)
Gaanarus
feselatus
                                           BS*   —
                                                              3.7 IT?)
        ft»-0 facldl



        <«%-O (add)



        >t%-0 IBEEJ
Oaphnla «a
                                   Of the aquatic weed herbicides    Sanders
                           evaluatedt Die I one Mas the vest toxic,    (19781,
                           Oaohnla DCS generally the *ost sensitive  »HIC-*SS
                           orqanlsas.  All of the Crustacea Here
                           affected by much lower concentration
                           levels of herbicides than Indicated by,
                           the TL sub 50 values.  All of the anlaals
                           represent Important food chain links.
                                                                   sane as above
                                                                   saae as above
                                                                                                saae as above
Sanders
119701. AHIC-
•.53

Sanders
11970).
AHIC-WJ

Sanders
(19701, A1IC-
              (BECI
Paleonontas   BS*
HadlaHensls
                             Asellus       BS*
                             br««le*udu«
                                                                  IT2)
                                                                  IT2I
                                                                                                saae as above
                                                                   saae as above
                                                                     Sanders
                                                                     (19701.
                                                                     ANIC-4.5J

                                                                     Sanders
                                                                     (19701,
-------
 ?,»-0 IBEEI
Orconectes    BSA
nail
greater than
100.0 JTII
                                                                                              as abov*
                                                                                                                            AMIC-tS]

                                                                                                                            Sanders
       IBEEI
 «t%-0 IBEEI
 Z»*-0 IBEEI
 t,*-0                ftasbor*
 Ibutoxyethylester)   heteromorpha  and
                                    BSA
Oaohnla maqna BS»   —
Cvorldopsls   BSA
vldua
lepomls       BSA
aacrochlrus
                                                       9.6
                                                       1.1 
                                                       t.t ITZ1
       lei ay bascdl    Kasbora       BCM
                      httaroaerorta  and
                                    BS»
                                     ITII
                                                 hard (HH)
                                                 or soft
                                                 ISM)
                                                 synthetic
                                                 dilution
                                                 ••tor,  or
                                                 se»H»ter
                                                 for sone
                                                 toecles
                                                 ••tCte.f .
                                                 hsrd(HHt
                                                 or  soft
                                                                       synthetic
                                                                       dilution
                                                                       ••ter, or
                                                                       se*M*ter
                                                                       for so«e
                                                                       •DOC I a*
ttk-D ldla«thvlaatn« Cra«*«str«a   L
•altI                vlrglnlea
                                                            IT2I
                                                                     Sanders
                                                                     I19»«1.
                                                                     INIC-VS3

                                                                     Sanders
                                                                     119701.
                                                                     *HIC-»5J

                                                                     Sanders
                                                                     119*01,
                                                                                         saa* as abov*
                                                                                         <••• as above
                                                                                         «••• as abov*
                                   One hundred sixty-four            Alabaster
                           pesticides, netting agents*  and           119691.
                           •Iscet lereous neter pollutants shewed a   AHtC—9%K
                           nlde range of toxlclty spanning li orders
                           of magnitude.  KnoHlng the toxlclty and
                           Percentage of all  components of a
                           formulation did not result In easy
                           Predictability of  the  toxlelty of  a
                           mixture of materials.   Sometimes
                           pesticides nere aost tonic In hard natar
                           •nd sonatinas the  opposite Mas true.
                           Testing the actual  aaterlal  as sold »as
                           found to be essential.
                                                                                         save as above
                                                                    Alabaster
                                                                    I1969I.AHIC-
                                                                    The effect of 52 pesticides on
                                                           embryonic development of clans and
                                                           oysters  Mas reported.  Synerglstlc
                                                           effects  with solvents Here also reported.
                                                            Host of the compounds affected
                                                           development more than survival.  Some.
                                                           however, drastically reduced larval
                                                           qronth.  The authors point out the
                                                           necessity of evaluating the affects of
                                                                    Oavls. etal
                                                                    119691.
                                                                    AHIC-S990
-------
  Coaoound
                       Organise
                                   Field  FUld
                                   Study Location
                                                      Toxlclty,
                                                      Active
                                                      Ingredient.
                                                        POB
Exoerlaental
Variables.
Controlled
or Noted
                                                                                                 Convents
                                                                                                                           Rotoronce
      (dlaethyl**lne  Cr»ssostrea   L
••Itl                 vlrglnlca
                      flervaet
Z.fc-0 (dleethrlaalne Caevaru*
•altt                feiclatus
                                   BSA   —
                                                      6».S ITU)
                                                      greater
                                                      thanllt.O (T2I
                                                                                 pesticides on all life stages of an
                                                                                 organ Is* and note the possibility of
                                                                                 selecting chealcats for oest control that
                                                                                 Mould not have serious effect on
                                                                                 Shellfish.

                                                                                        saae as above
                                                                                                                           Oevls. et al
                                                                                                                           114691.
                                                                                                                           ANIC-9990
                   Of the aquatic need herbicides    Sanders
           evefuatedf Olelone M»S the aost toxic.    119701.
           Oeohnlt nas generally the east sensitive  »HJC-*53
           organism.  All of the Crustacea were
           affected by *uch loner concentration
           levels of herbicides than Indicated by
           the TL sub SO values.  All of the anlaals
           reoresent Important food chain links.
*,»-D (dlaethylealne Paleoaontes   US*
seltl                MdlaHensls
Z.V-0 Idlwathylanlne Astllus       BS»
salt I            '    brevlcaudus
»,»-0 Idlaethylaalne Orconectes    BS»
saltl                nals
                                                      greaterthan
                                                      101.• tTtl
                                                      greater than
                                                      greater than
                                                      lit.I ITZ)
                                                                                        saae as above
                                                                                        saee a* above
                                                                                        saae as above
                                                     Senders
                                                     (11TO),
                                                                                                                           Senders
                                                                                                                           (19701.
                                                     Senders
                                                     (19701,
Z.*-0
••Itl
Z,»-0
••Ml
      Idlaethylaalne Daohnla aagna 8S»   —
      fdleethylaalne CyorldoosU   BS»
                     vldua
                                                      ••.0
                                                      •.0 IT2I
                                                                                        saae as above
                                                                                        saae as above
                                                     Senders
                                                     (14701.
                                                     AHIC-W1

                                                     Sanders
                                                     119701 ,»1IC-
      fdl«ethyl»«li*e lapoals       BS«
                     aacrochlrus
••Itl

Z,%-0 (ester!
                     Crassostraa   L
                     vlrglnlea
                     leoesl
                                                      greater than
                                                      110.I IT2I
                                                      t.O IT2I
                                                                                        saae as above
                                                                                        saaa as above
                                                     Sanders
                                                     119701.
                                                     AMIC-1,53

                                                     Davis, et al

                                                     (1969t,AMIC-
-------
 8,»-0  fester)
                      Crassostrea   L
                      vlrolnlca
                      tlervael
 2*t-0 INa salt*      ftasbora       8CF»
                      heteroeorpha  and
                                    es*
                                                       i.r* IMVI
                                  1.1*1 (Til
 t,»-D (PGDC)
 Gaaaaru*
 fesclatus
                                    8S*   —
                                                       ».« ITZtt  2.S
                                                       ITM
                                                     5999

                  saae as above                      Davis, et al

                                                     (1969>.»MIC-
                                                     5990

e*«c
-------
0\
Toxlclty, Cxoerlmental
Active Variables,
Field Field Ingredient, Controlled
Comoound Organism Study Location pom or Noted Comments

?,»-0 fresln basedl Rasbora BCFA —
heteromoroha and
BSA










Z,t-0 fresln based) Sal mo BCFA —
galrdnerl and
BSA







Z,*,-0 Fish «not « —
specif led)



2,lt-D Wolffla L
papullfera




2««tO (T2) a*,c,e,f.
hard(HH)
or soft
(SHI
synthetic
dilution
nater, or
seaxater
for same
soecies



1,920 IT2) a'.e.e.f.
hard
(HW)or
soft (SW)
synthetic
dilution
Hater, or
seaxater
for some
species
greater than —
0.1-1.0 (K)



1000 (K) Hunter's-
raediun
diluted
1:5



One hundred sixty-four
oestlcldes, xettlnq qqents, and
miscellaneous Hater pollutants shoxed a
Hide range of toxiclty spanning IZ orders
of m*qnltude. Knonlnq the toxlclty and
percentaqe of all components of a
formulation did not result in easy
predictability of the toxlclty of a
mixture of materials. Sometimes
pesticides Here most toxic In hard Hater
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
same as above









Approximate toxlcltles of
numerous pesticides commonly used In
Britain Here summarized. An excellent
brief, general discussion of toxlclty
testing Is also present.
All compounds were harmful to
duckweed to some degree. Decreased
populations were, noted at non-lethal
concentrations nnd some compounds
(Malathlon and 2,k-*>) caused teratogenlc
effects at concentrations as low as 1 pp»,
Reference
AHIC-I.S3
Alabaster
•19691, ANIC-
5*25










Alabaster
(1969),
AMIC-5%2S







Haxdesley-
Thomas
(19711.AHIC-
1056

Worthier, at
al (1971).
AKIC-3233


t
               dlnlfroohenol    Neqaorion     BSA
                                brevirostrls
                                                                 10 (NTE 3 nrl   a.c.e
«t»,5-T
Ibutoxyethylesterl
                                Rasbora       8CFA
                                heteroeorpha  and
                                              •SA
                                                                 1.0 (TZ»
a*,c.e,f,
hard (HH)
•r left
        Data  fro* study of druq effects   Baldrldq*
on young  Ienon'sharks Here treated        (19691,
Mathematically to demonstrate             AMIC-3832
aoDllcablllty of classical rate theory To
the study of chemical shark deterrents.
Incaoacltatlon (narcosis) Has the or!aery
parameter timed for effectiveness.  This
Has usually quite rapid for the aore
effective drugs.

        One hundred sixty-four            alabaster
pesticides* netting agents, and           (19691t
Miscellaneous na.ter pollutants shoved •   ANIC-54Z*
-------
                      Fish  (not
                      specified)
 Z'-broao-l-nltrosall Salao
 eylanltlde           galrdnarl
BS»   —
                    greater  than
                    8.1-1.1  IK»
                    1.8  IK  I hrl
 8"-bro»o-3-n I trosa 11 Carass tin
 cylanlllde           auratus
 Z"-»ro»io-3-nltrosall Cvorlnus
 cylanlllde           carolo
 ?"-bro*>o-3-nltre«ell Plmephales
 cylanlllde           proaelas


 Z'-broao-S-nltrosall Ictalurus
 cylanlllde           Betas
Z~-bro«o-3-nltrosell  leooals
cylanlllde            eyenellvs
BS»   —
                                    as*   —
                                    BS»
as*   —
                                    as*
?"-bro»o-3-nltrosaII Leooals       BSA
cylanlllde           aacroehlrus
Z"-broao-3-nltrosall Perca         8SA
cylanlllde           flavescens
                   - Salao         BSA    —
                     oelrdnerl
3-nitro»«llcyl-
anillde
                   10 (Kit
                   1.8 IKt)
                                                       1.0 IK S Iwl
                   t.O IK1I
                                                       10 IK 3 hrl
                                                       10  IK 3hr)
                                                       1.0  IK1)
                                                       1.0  IK 3 hrl
ISUt       wld* pang* of toxlclty ioannlnq 12 orders
synthetic  of «aqnltud«.  Knowing the toxlclty and
dilution   o*re<«nt»q« of all co«Don«nts of a
••t*p, or  fop*ulatlon did not result In easy
seaiiater   predictability of the toxlclty of a
for soa*   Mixture of materials.  Sonetlnes
species    pesticides Mere »ost toxic In hard Hater
           and soaetlnes the ooooslt* Has true.
           Testing the actual Material as sold was
           found to be essential.

—                 Approximate toxlclties of         W»wdeiley-
           numePous pesticides eoaaonly used In      Tho*as
           Britain were summarized.  An excellent     H9ri»,»«IC-
           bPlef, general discussion of toxlclty     1056
           testlnq Is also present.

••                 Twenty-nine nltrosal Icylant I Ides  Markinq,*t
           and related coaoounds Here evaluated for  at  11970)*
           their relative toxic effect to selected   ANTC-63tl
           fish.  Potency varied with type and
           position of  substitutions.  Several
           compounds were selectively toxic to
           yellow perch.   Goldfish Her* the aost
           resistant to the  sallcy tanllldes.

a*                «••• as above                      Narhlnq,
                                                     •tal  114701 •
                                                     •HIC-6391

                                                     •farhlnq.at
                                                     al  (1470).
                                                     AHIC-6341

                                                     Herkinq.et
                                                     al  119701.
                                                     AM.IC-6391

                                                     Narklnq,
                                                     •tal  119701*
                                                     •HIC-6391

                                                    Narhlnq.et
                                                    al  119701*
                                                    AHIC-6391

                                                    Harfclnq.et
                                                    • I  119701*
                                                    •HIC-6341
                                                                       a»
                                                                                         saae as above
                                                     saae as above
                                                     saae as above
                                                                                         saae as above
                                                                                         saae  as above
                                                                                         saae  as above
                                                                                        saae as above
                                                                                       • fat  119701.
                                                                                       AHIC-6391

                                                                                       Narhlnq. et
                                                                                       • I (19701,
                                                                                       ANIC-a391
-------
  Compound
                                                      Toxlclty,       experimental
                                                      *ctlve          Variables,
                                   Field  Field       Ingredient*     Controlled
                                   Study Location       Ppa           or Noted
                                                                                                 Convents
                                                                                                                           Reference
?"-eMoro-i>"-»«thyl- Carasslus     BS*   —
3-nltrosallcyl-     , auratus
anlllde

?"-ehloro-«i"-»ethyl- Cyprlnus      BS*   —
3-nltrosallcyl-      carpio
anllide

Z"-cMoro-*~-»*tnyl- Plnephales    BS*   —
3-nltroaalierl-      prowela*
anllide

f~-cnloro-*~-«ethyl- Ictalurus     BS*   —
3-nltrostllcyl-      •»I as
•nillde

?"-ehloro-*"-««thyl- Lepoalc       8S»   —
3-nltro»«llcyl-      cyan* I l\is
anlllda

*"-ehlor»-»"-»«thyl- Lapoals       BS»   —
3-nltrosallerl-      ••croehlrus
•nllida

?"-chloro-«i"-»«thyl- Perca         BS*   —
3-nltroMlleyl-      tlavescan*
•nlllda

*"-ehloro-«»"-nltro-3 Salao         BS»   —•
-nllrosalleylanlllde qalrdnarl
«"-ehloro-»"-nltro-J Carassl«n     BS*
-nltrosalIcylanllld» auratus
J"-ehloro-*"-t»ltro-3 Cvorlnus      BSA
-nltrosallcylantlId* carpio
J--chloro-*"-nltro-S Plaepltalas    BSA   ~
-nltrosalleylanlllde croaalas
                                                      1.0 (K 3 hrl
1.9 IK1I
1.0 IK1I
1.0 IK1I
t.O IKtl
1.0 (Kit
1.0 fKll
1.0 IK 3 lw>
                                                      1.0 IK1I
                                                      1.0
                                                      1.0 fKll
                                                                                        sea* as above
                                  saae as above
                                  sa*e as above
                                  saae as above
                                  saae as above
                                  sane as above
                                  saae as above
                                  saae as above
                                                                                        save a* above
                                                                                        saae as above
                                                                                        *aae as above
Harking, *t
al 114701.
•NIC-6391

Marking, at
al (11791.
Harking, *t
al (1970),
•HIC-6391

Harking, at
al (19701,
ANIC-6391

Harking, at
al 119701 ,
•HIC-6391

Harklnq, *t
al (19701,
Harking, et
al (19701,
AHIC-6391

Harking, et
al (19701,
kHIC-6391

Harking, et
al (1970).
•NIC-6391

Narking, et
al (1970).
AHTC-6391

Narking, at
al 11970).
*NIC-63«1
                     Ictalurw*
                                   BS*   ~
                                                      1.0 CR 3 hr|
                                                                                        saae as above
                                                                                                                           Narking, at
-------
 -nltrosallcylanllId* a* I as
  F*-eh>lero-»*-nltro-3  lepoals
  -nltrentlcvlanllld*  cyan* 11 us
 l--ehloro-»"-nItro-3  Lcooals
 -nltrosalleylanllld*  •aerochlrus
 •"-€hloro-»~-nltro-3 P«re»
 •nltracalleylantlIda (lav**c*ns
 f"-ehlor*-S-nltro
 •tliejrUaiilde
 8"-ehIoro-*-nlfro
 «"-*•»! OPO-«-l»ltP«
 •alleylanllid*
 J"-cMoro-5-nitro
 •alloylwtllld*
 r*-chl*r»-»-i»ltr«
 Mllejrlanlllde
8"-eh1ore-»-nitre
aallcjlanlllda
?"-eM ore-5-oI fro
8"-ehlor«-»-nlfro
•Blleylmnlllda
r-.lodo-3-nltra
 Sclao
 aalrdn*r|
                      Car»«slu«
                      auratux
 earole
 Pt«*Dhal*s
 prea*f»*
                      Ictaturu*
Ivpoals
cyahellus
                     Lcpoal*
                     •acrechlrus
P*rea
flav*«e*n«
Salae
qalrdn*rl
               •s*   —
               BS»   ~
                                    BS*   —
                                    as*
                                    BS»   —
                                    BS»
                                    BSA   —
                                   BS«    —
                                   BS«   —
                                       (K2I
                                  l.t (Kit
                                  i.n
1.1 IK 3 hr»    a»
                                                       10 IKtl
                                  10 IK 3 hrl      a*
                                                       10 IK 3 hr)     a*
                                                       1.0 (KZI
                                                       10 IK 3 hrl      *•
                                                       10 IK 3 hr)      »•
                                                       10  IK  3  hr)      a*
                                                       l.OIK  3 hr)      a*
                                                                    sa«* as abov*
                                                                    <*•• as abov*
                                                                    *••• as abov*
                                  saw* as abov*
                                                                    San* as ataov*
                                                                    ••a* as abov*
                                  saa*  as  abov*
                                                                    *aa*  as  abov*
                                 *••• as abova
                                                                                         saa* as abov*
                                                                                         saa*  as  abov*
                                                                                         saa*  as abov*
 •I  11970).
 4MIC-6391

 Marking. *t
 • I  11970).
 AMIC-6391

 Harklnq. *t
 • I  (1970).
 IHIC-6391

 Marking, *t
 • I  (19701,
 AHIO6391

 Marking. *t
 • I  (19/0).
 »NIC-*J9l

 Carklng. *t
 • I  (1970).
 IHIC-6391

Harking. *t
• I  (1970).
«NIC>6391

Narking, at
al  (1970),
AHIC-6391

Marking. *t
al  11970),
                                                                    Harking, at
                                                                    al (1970).
                                                                    »HTC-6391

                                                                    Marking, *t
                                                                    al (1970),
                                                                    (HIC-6391

                                                                    Narking, *t
                                                                    al (1970),
                                                                    ANIC-6391

                                                                    Harking, *t
                                                                    al (1970).
                                                                    ANIC-6391
f-lade-3-nltr*
                     CarassIus
                                   BSA    —
                                                       10  IK1)
                                                                                        saa* as abov*
                                                                                                                           Narking,
-------
Field Field
Coaoound Organise Study Location
Mllcylinillde auratus
l"-l*do-3-nltrosallc Cyorlnus BS» —
ylanlllde carplo
t"-lodo-3-nltrosalle Plnephates BS» —
ylanlllde proe*1as
f-lodo-3-nItrosallc Ictalurus BS» —
ylanlllde metes
Jr- Z--lodo-3-nltrosallc Leoonls BS» ~
—4 vlanlllde cyanellus
O
Z"-lodo-3-nltrosalIc Leponls BS*. —
ylanlllde nacroehlrus
Z"-Iodo-3-nltrosallc Perca BS» —
ylanlllde flavescans
l"-aethOKy-*~-«ltro- Salao SS» —
3-nltrosaJ.lcyl- galrdnrrl
•nUlde
Z"-netbo»y-l»"-nltro- Carasslus BS» —
3-nltroaalicyl- auratus
anlllde
?"-aathoxy-li"-nltro- Cyorlnus OS* —
3-nltrosalloTl- earplo
oaUlde
Z"-«ethoxy-»"-nItro- Plneohales BS« ~
3-nltroaalicyl- prone las
anlllde
2"-»«thoxy-*"-nltro- Ictalurus BS» —
3-nltro»«llcyl- nelas
anil Ida
Toxlelty, Expcrlaental
Active Variables,
Ingredient, Controlled
Poa or Noted

1.0 tKll ••
1.0 IK1I a>
10 (Kl) a*
10 (K 3 hr) a*
10 IK 3 hrl a*
1.0 IK1I a*
10 IK 3 hr) a*
10 (Kl) a*
10 (Kl) a*
10 (Kll a*
10 (Kl) a*
Conaents

sane as above
save as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
saae as above
Reference
«ral (1970),
Marking, et
al (1970),
»MIC-6391
Marking, et
al (1970),
»HIC-6391
Marking,
etal (1970).
*MIC-639t
MarHInq,et
al (1970),
*MTC-6391
Marking, et
al (1970),
Marking, et
al (1970),
»HIC-»>391
Marking, et
al (1970),
Marking, et
al (1970),
4MIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
»MIC-639l
Marking, et
al (1970).
AMIC-6391
-------
8"-«athoiiv-*"-nltro-
3-nlirosftllcyl-       crane ttus
aollide
                                   es»    —
3-altroMllcrl-
anllide
                     Leooals       BS*
                     •aeroehlrus
*"-««thoiev-*"-r«ltre>-  P«rc»
3-nltrosallcyl-       flaveseam*
anlllda
                 -     Sala«
nltroaalicylanlllde   qalrdncrl
f-.»"-dl«etnyl-3-     Carasslira
nltrosaJ.leylanU.lde  auratus
r*.*~-dl»«thvi-s-
                      Cvorinus
                      carol o
  ,
nltro»«lloyl«Jilll
-------
CoMound
t-tV-dlbr o*o-3-
nitroaaliejaanllida
*~,*--dIbr o*o-3-
nltroaallorlanillde
J-.V-dlbr oao-3-
al troaal loylanU. Ide
e",S"-dlbr o*o-S-
nltroaaaicylenllld*
8", V-dl or o*o-l-
nltroaalleylanllid*
«-,S--dlbr o*o-S-
nitroaallcylanilld*
*",S"-dl*ethoxv-»"-
ohloro-3-nltrosa-
l-,5"-dl*«thox»-*"-
obloro-3-ni troaa-
llcylanillda
ofiloro-3-nl troaa-
chloro-3-4U.trosa-
lloyluillld*
chlOTO-3-Altroaa-
llvflanliid*
Z-,5--dl**thox»-»--

cerelo
P^:.?:,"
tetelurus
•alas
Leoovls
crenel I us
Lepoats
•acrochlrus
Perca
flevescens
Sal no
Carasslus
auratus
Cvorlnus
carpi o
proa* las
Ictalurus
••fas
Leooais
Toxlclty,
•ctlve
Field Field Ingredient.
Study Location Pe*
as* — i.o i«t
as* — 1.1 IKII
as* — 1.1 tKii
as* — i.o IKII
as* — 10IK 3 hrl
BS» — 1.0 IK S hrl
BS* — 1.0 IK 3 hrl
as* — i.t iKti
BS* — 1.0 IK2I
as* — i.o IKII
as* — i.o IKII
as* — i.o IK;I
Experimental
Controlled
or Noted Comments
a* so** as above
a* seme as above
a* seme as above
*• seme as above
a* same as above
a* saae •» above
a* saae as ebove
a* saae as above
a* saae as above
a* same as above
»• same as above
a* seme- as above
Reference
Narklnq.et
al (1970),
•MIC-6391
Nerklnq. et
al (19701,
•H1C-6391
Narklnq, et
al (19?OI,
AHIC-6391
al 119701,
Harking, et
al (1970).
AMIC-6391
Nerklnq, et
al <1«70).
»HIC-6391
Harking, et
el (1970),
AHIC-6391
Harking, et
al (1970),
•MIC-6391
Harking, et
al (197D),
AHIC-6391
Harklnq, et
al (1970).
«HIC-6391
Harking, et
al (1970),
AHIC-6391
Narking, et
-------
 •blaro-3-altvoM-    cywwllu*
 aioylamllldo

 Z",S~-dI»othoxy-V-  L*oo«Is
• c6loro-3-nltro«B>-    ••crecMru*
                                                                                                                            • I
 f-,*--dlB»thoicr-»--  P«re»
 eUaro-3-altroM-    flavaseon*
 f«,»"-dlothyl-l,S-dl Saleio
 nltrobanzanllld*     salrdnerl
'f",«,"-dl*>th»l-3.»-dl  Carasslws
nltrob*nzanllld*      auratus
 f,«"-
                                                       it INTCI
                                                          INTCt
                                                       It INTE)
                                                       it INTCI
                                                       It INTCI
                                                       It INTEI
                                                       tt INTO
                                                       It 
nl tr«b«nxan| 1 1 d«
                      f I •««sc.«n«

                                                                       h«rd(HM)
                                                                       or soft
                                                                       (SHI
                                                                       synthetic
                                                                       dilution
                                                                       •otor. or
                                                                       ««*M»t«r
                                                                       for •«••
                                                                                          »»« •* *bev*
                                                                                          ••• •« »bov«
                                                                                                 »bov«
                                                                                              •* «bov«
                                                                                              •* •be««
                                                                                              •* *bow«
                                                                                              •* »bov«
                                                                                         •••• •* cbov*
                                                                                                 cbev*
                                                                                                 abev*
                                                                                         On* hundred sixty-four
                                                                                 pesticides, wetting agents, and
                                                                                 •Iscellaneous »at«r oollutants sho«od •
                                                                                 Hid* range of toxlclty scanning H orders
                                                                                 of •aqrltud*.  Knotting the toxlclty and
                                                                                 percentage of all coaoonents of a
                                                                                 formulation did not result In easy
                                                                                 predictability of the toxlclty of a
                                                                                 •Ixture of aaterlals. Sonetlaes
                                                                                 pesticides nor* aost toxic In hard nat*r
                                                                                 •nd «o»*tla«s th* opposlta was true.
 (••rklnq. «t
 • I  (19781,
 Marking, »t
 • I  C1970),
 »HIC-%391

 Nark I no, «t
 • I  (19701.
 AMIC-6391

 H«rklnq. «t
 • I  (197ttt
 •HTC-6391
                                                                                                                                   .  «t
                                                                                                                            • I  (19701.
                                                                                                                            *NtC-6391

                                                                                                                            N.rklng.  *t
                                                                                                                            • I  (19701.
Marking, *t
al  (1970).
ANIC-6391

Narking, *t
•I  11970).
•NTC-6391

Marking, *t
al  (19781,
mc-639i

Marking, et
• I  (1970).
AH1C-6391

Alabaster
(1969>.A«tC-
»»2»
-------
Compound
3 1 p-ch 1 oropheny 1 1

Organism
Phormldlum

Field Field
Study Location
L

Toxlclty,
Active
Inqredlentt
0.5-10.0 INTO

Experimental
Variables,
Controlled
or Noted
species

Comments R«f *>r«nc«
Of 7 it chemical* evaluated as Otto (197<

-J
fr
           3,»-dlchlorobenzyl
           •ethyl  carbamate
Phormldlum
ambiguua
           3»*-dIhydroxybenzolc Phormldlum
           acid  (protocatechulc amhlguum
           acldl
           3t*«5-trlhydroxy
           benzole acid
           (gallic ftcld)
Phormldlue
amblguum
              L     —


0.5-11.0(16
percent growth
Inhibited !"•)

0.5-10.0(50
percent growth
Inhibited 1*)

0.9-10.0 IMTEt  —
           3t5-dlbreno-*-hy
Phoreldlu*
••bIquue
                                              t     —
                                                                 0.5-lO.i INTE)  ~
                                                            CuSOl,.   None Inhibited growth of
                                                            mat-forming aloae for  more than ? weeks.
                                                            CuSOt* formulated with  certain wetting
                                                            agents  was more toxic  than CuSOi* alone.
                                                            Coooer  cMoraiMne was  also found to be
                                                            more toxic than CuS1.   None inhibited growth of
                           •at-formlno algae for  more than 2 weeks.
                           CuSO<> formulated with  certain wetting
                           agents  was  more toxic  than CuSOi,  alone.
                           Cooo»r  chloraolne was  also found  to be
                           nore toxic  than Cu50it.  No wetting agents
                           were found  to be Inhibitory at the
                           concentrations Investigated (O.OS and
                           0.005 ppn).  Also reoorted are factors
                           affecting growth of alqae In canals to
                           determine whether there were leads to
                           controlling algae by environmental
                           •anaqevent.  No practical environmental
                           •cans were  found.

                                   Of  7«, chemicals evaluated as      Otto (1970),
                           alglcldest  only 9 Here aore toxic than    ANIC-892
-------
 J,5-dllodo-*-hydroxy Phormldlum
 droxybansonitrlls    amblguu*

 3,5-«fImethyltetrahyd Phormldlum
 hydro 1,3*5,2-       amblguum
 3.9,7-trfaza-l-azonl Phormldlum;
 Mania •jdaiaantane   amMguum

 3™-bromo-3-nltrosall Sal no
 cylanlllde           galrdnerl
 3"-bPomo-3-nltrosall  Carasslus
 eylanltide            auratus


L     —
BS«   —
                                    BS»
                                                       0.5-10.0  «NTEI  —
                   n.5-tn.o
                   (16p*PC*nt
Inhibited 1*1

0.9-10.0 (NTEI  --


1.0 IK 3 hr>    a»
                                                       10 IX 3 hr»
                                              CuSOt*.   None  Inhibited  gpOMth  of
                                              mat-forming al<;ae  IOP mart  than 2  Hecks.
                                              CuSO(»  formulated Mlth ceptaln  Mettlnq
                                              aqcnts  was morr toxic than  CuSOfc alone.
                                              Cooo«r  chlopanlne  Has also  found to be
                                              •ore toxic than Cu^flfc.  No  netting agents
                                              wep* found to be Inhibitory at the
                                              concentrations Investigated (0.05  and
                                              0.105 com).   Also  reoopted  ape factors
                                              affecting growth of alqae In cranats to
                                              detepmlne whether  there Here leads to
                                              controlling algae  by environmental
                                              management.   No practical environmental
                                              •cans Her* found.

                                                      same as above
                                                     same as above
                                                                                         same as above
                                                                     Otto (1970),
                                                                     •MIC-89Z

                                                                     Otto (1970).
                                                                     AHIC-89?
                                                                                                                            Otto (1970).
                                                       THenty-nlne nltrosalIcylanllldes  HarKlng.et
                                              and related compounds Here evaluated for  al (1470).
                                              their  relative  toxic effect  to selected   AHIC-6391
                                              fish.  Potency  varied with type and
                                              position of substitutions.  Several
                                              compounds Here  selecttvely toxic to
                                              yelloH perch.   Goldfish Here the most
                                              resistant to the s»IIcylanllldes.
                                                                                         same as above
                                                                                        Mark|i-iq,et
                                                                                        al  <1970),
                                                                                        •NIC-4391
3"-bromo-J-nitros»ll  Cyprlnus
cytanltld*            carol a
S"-bromo-3-nlfrosal|
evlanllld*
cylanilld*
                     Ictalurus
                     ««las
3--bPO«o-J-nltPO«ll L«DO*ls
eylanllld*           eyancllu*
3"-broeo-3-nltrosall tepomls
cylanlllde           maeroehlrus
                                    BS»   —
                                    BS»   —
                                    BS«    ~
                                   BS»    —
                                                       1.0 IK1)
                                                       1.0  IK 3 hp)
                                                       1.0  IK  3  hrt
                                                       10  IK  3 hP>
                                                       1.0  IKlt
                                                                                         same as above
                                                                                         same as above
                                                                                         same  as  above
                                                                                         same  as above
                                                                                        same  as above
                                                                                        Harking,
                                                                                        etal  (1970).
                                                                                        • MIC-6J
-------

  Ceajoound
3"-bro«o-3-nttrosal 1
cylanl lid*
3"-enlore-S-nltreben
zanlllde
3"-ch 1 or o-S-n I trobtn
zanlllde
3"-cMoro-3-nItroben
zanllltfe
3"-chloro-3-nltroben
zanllld*
3"-ch 1 oro- 3-n 1 t r oben
zenlllde
3"-eh t oro- 3-n 1 troben
zenltlde
3"-cM or o-3-nl troben
zanitlde
3"-chloro-5-nltro
3"-eM oro-5-nI fro
sallcylanllldo
3"-cn 1 oro-5-nl tro
•alieylanllldo
Field Field
Organise) Study Location

Perca BS* —
flavescens
Carasslus BSA — -
auratu*
Cyprlnus BS* — -
carplo
Plaephates BS* —
Ictalurus BS* —
aelas
leooals BS* —
cyanellus
lepoals BS* ~
aaerochlrus
Perca BS* —
f laveseens
Sal 0)0 BS* —
gelrdnerl
Carasslus BS* ~
auratus
Cyorlnus BS*
carplo
Toxiclty, Exoerlaental
Active Variables.
Ingredient, Controlled
Ppa or Noted

t.O IK 3 nr) a*
10 IK 3 hr) a*
10 IK 3 hr) a*
10 IK 3 nr-) a»
10 IK1) a*
10 IK S hr) a*
10 IK1I a«
10 IK 3 hr) a*
1.0 IK*,) a>
10 IK1) a*
10 IK 3 hr) a*
Consents

saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above
saa* as above
Reference
AHIC-6391
Harking, et
al (19701,
AHIC-5391
Marklno. et
al (1970),
Harking, et
al (1970),
AHIC-6391
Harking, et
al (1970),
AMIC-6391
Harking, et
al (1970),
Harking, et
al (1970).
Harking, et
al (1970),
AHIC-6391
Marking, et
al (1970),
AHIC-6391
Harking, et
al (1970),
AHIC-6391
Harking, et
al (1970),
AHIC-6391
Marking, et
al 11970),
AHIC-6391
-------
3"-ehloro-5-nltr»
saj.lcyl«nlllde
S"-chloro-*-nlfro
•aaicylantlldo
3"-ch I oro-*-f» 1 tr o
a»licyl«nil5d«
3"-ehlaro-f-nltro
aallcylanlllda
Ictaturus
aelas
Lepoels
cyan*I I us
aacrocMros
Pare a
f I avcsc*n*
3"-lodo-3-nltro«alIc Carasslus
vlanlllde            auratus


3~-la«lo-S-nltrosalle Cyprlnus
ytanil Id*            carplo
3"-lodo-J-nltrosalle
ylanillde             proaeias


3"-Iodo-3-n! trosal le  tetalurws
ylanillde             aelas


3*-lodo-S-nl»resallc  lepoals
ylanillde             cyanellus


3"-lodo-J-nltrosatIc  Lepoels
y I anil Id*             aacrochlrm


3"-lodo-3-nltPOsallc  P*rea
y I anil Id*             llavasc*ns


3"-lo«lo-3-nltrosal le  Salao
yI anil Id*             galrdnerl


                      Satao
                                   BSft   —
                                   BS«   —
                                   8S»
                                   BS»   —
              BS»
                                   BS*
                                   BS«
                                   BS«   ~
                                   BS*
                                   as*
                                   BS*   ~
                                   BS*   —
                                                       16  IK 3 hr»
                                                       IB  fK 3
                                                      II  fK 3 hr»
                                                      1.1  (K2I
                                                      ia  IKII
                                 IB IK 3 hr>
                                                      l.a  (Kit
                                                      IB IK 3 nrl
                                                      l.a (Kll
                                                      i.a IKII
                                                      l.a IK 3 hr)
                                                      ia IK 3 hrl
                                                      l.B IK 3
                                                                                        saac as abov*
                                                                                        saa* as abava
                                                                                        saa* as abava
                                                                                        saa* as abov*
                                                                                        saa* as abov*
                                                                   saa* as abov*
                                                                                        saa* as abava
                                                                                        saa* as abova
                                                                                        saa* as abava
                                                                                        saa* as abov*
                                                                                        saa* as abova
                                                                                        saa* as abova
                                                                    Twenty-nine nltrosallcylanllld*s
                                                            and r*lat*d coapound* «*r* evaluated for
                                                            thalr ralatlv* toxic *tt*ct to s*t*ct*d
                                                            fl«h.  Potency varied tilth typ* and
al  (1970) t
*NIC-639t
       , et
al (19701.
•MIC-6391

Marking, et
al 11470),
1NIC-6391

Harking, et
al 11978),
AHIC-6391

Marking,
•tal  (19701,
41IC-6J")!

Marking, at
al(1970),
•MIC-6391

Marking, et
al (1970),
AHIC-6391

Mark I no.,
etal  (19701.
• MIC-639-1

Marking, «t
al (1970),
AMIC-6391

Marking, et
al (1970),
AMIC-6391

Marking, et
al 11970),
AMIC-6391

Marking, et
al (1970).
AHIC-6391

Marking, at
al (1970),
AMIC-6391
-------
            Coaoound
Organise
Field Field
Study Location
Toxlclty,
active
Ingredient,
Pom
Experimental
Variables,
Controlled
or Noted Comments
Reference
i
          3",*"-dIchloro-3-    Carasslus     8Sa.   —-
          nitroaalicylanllldo  auratus
          3-.*--dlchloro-3-    Cyprlnus      BS»   —
          nltroaallcylanlllde  carpi«
3~»*"-dlehloro-3-    Plmeohales    8S»   —
nltroaallcylanlllde  promelas
S",li~-dlchloro-3-    Ictalurus
nitroaallcylanllide  eel as
          3",l.--dlchloro-3-    Leoomls       BSA    —
          nitroaa.llc>lanllldo  cyanellus
          3",i."-dIch I oro-3-    Leoomls       8S»    —
          nltroaallcylanlllda  macrochlrus
          3",^--dlchloro-3-    Perca         8S»
          nltrosalIcylanllide  flavescens
          *-cyaoo-?«
          *-dllodophenyl-N-
          nethyl carbamate
                     PhoraldiuB
                     amblguua
                                                                i.aiKii
                                                                1.0 IKlt
                                                                0.1 CK2I
                                                      0.1 IKlt        ••
                                                                1.0IK1I
                                                                0.1 IKdt
                                                                0.1 IK«>
                                                                0.9-10.0 (NTEI   —
                                                                                           position of substitutions.  Several
                                                                                           compounds Mere selectively toxic to
                                                                                           yelloH perch.  Goldfish mere the most
                                                                                           resistant to the salicylanltIdes.

                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                                  same as above
                                                                                         Of 7i» chemicals evaluated as
                                                                                 alqicldeSt only 9 H<*re more toxic than
                                                                                 CuSOit.  None inhibited qroxth or
                                                                                 mat-formlnq al^ae for more than ? weeks.
                                                                                 CuSO<> formulated »lth certain wettlnq
                                                                                 aoents «as more toxic than Cu50<» alone.
                                                                                 Coooer chloravlne was also found to be
                                                                                 more toxic than CuSOfc.  No xettlnq agents
                                                                                 Mere found to be Inhibitory at the
                                                                                 concentrations Investigated (0.05 and
                                                                                 0.105 op«t.  Also resorted are factors
                                                                                 affecting growth of algae In canals to
                                                                                 determine whether there Here leads to
                                                                                                                           Marfcino. et
                                                                                                                           al  114701.
                                                                                                                           4MIC-6391

                                                                                                                           Marking, et
                                                                                                                           al  (19/0),
                                                                                                                           *MIC-fj39l

                                                                                                                           Marking, et
                                                                                                                           al  119701,
Marking, et
al (1970),
»HIC-fiS91

Harking, et
al (1970),
»«IC-6391

Harking, et
al (1970),
• HIC-S391

Harking, et
al (1970),
WC-6391

Otto (19701,
mC-892
-------
                                                                                           controlling algae by environmental
                                                                                           •anaqemtnt.  No oractlcal  environmental
                                                                                                 Here found.
I
          V-aiophenyl-3-nltro Salve
          sellcylanlllde       galrdncrl
                                   BS»   —
                                                      t.l IK1I
          *"-8»ophenyl-3-nltrp Caresslus
          sallcyfan!tide       auratus
          *~-azophenyl-3-nltro Cyprlnus
          set Icy I anil Id*       carole
%~-azophenyl-3-nltro Plm«phales
•allcylanlllde       proeelas
          *--azopher»yl-3-nltro Ictalurus
          •allcyfanlllda       aela*
         *--az»phenyl-3-n!tro Lepoals
         sellcylanlllde        eyanellus
         •/•-azophenyl-3-nltro  lepoal*
         sallcylanlllde        aacrochlro*
         V-azophenyl-S-nltrp Ptrea
         sallcylanllld*       fla»€*e«n»
         V"-bro«o-?-««thyl-3- Salvo
         nltro«allcylanllld«  g»lr
-------
Coa/pound Organise
*"-broi«o-7-a*thvl-3- Pleephates
nltrosal Icvlanl lid* provetas
»"-broao-2-e>*thyl-3- Ictalurus
nltrosal Icvlanl 1 Id* velas
*"-broao-?-a*thyl-3- L*po*>ls
nltrosal Icy 1 anil Id* c vane II us
V*-broao-Z-«*thyl-S- lepoais
nltrosal Icvlanl lid* aacrechlrus
»"-bro»o-Z-»*thyl-3- P*rca
nltrosalleylanlllda tlavescans
*"-broBo-3-nl trosall Salao
Cylanllld* galrdnerl
*"-broao-3-nl trosall Carasslus
Cylanltld* auratus
V*-bro*o-3-nl trosall Cyprlnus
cylanllld* carplo
a "-broeo-3-nl trosall Pla»phal*s
cylanllld* pro»*las
eylanllld* a*las
cylanllld* cyanellus
Toxlclty, Exoerlaental
Active Variables,
Field Field Ingredient, Controlled
Study Location Ppa or Noted
BSA — 1.0 (Xl> a»
BSA — 1.0 (K 3 hrl a*
BSA — 1.0 (K 3 hrl a*
BSA ~ 1.0 (Kll a*
BSA — O.KKZI a*
BSA — 1.0 (K 3 nrt a*
BSA — 1.0 (Kl) a«
BSA — o.l IK 3 hrl a»
BSA — 1.0 (K 3 hrl a*

BSA — 1.0 IK 3 ttrt a*
Coneents
saae as above
saae as above
saa* as abov*
saae as above
saae as above
saae as above
saae as above
saae as above
saae as above

saae as above
Reterenc*
(,
Marking, et
al (1970),
MHC-6391
Marklng,et
al (19701.
AMIC-6391
al (1970).
Harking,
• tat (1970),
AHIC-S391
Marking, «t
al (1970),
AHIC-6391
al (1970),
AHIC-6391
Marking, et
al (1970),
AHIC-6391
*"-bro«o-3-nItrosall lapoals
                                   BSA   —
                                                      1.0 (Kl)
                                                                                        saa* as above
                                                                                                                           Harking, *t
-------
cylenltld*
                     aaeroehlrus
V-broao-3-nltrosall Cere*
cytanlllda           ftaveseens
               ja-3-  Salao
 nttrosallcylanlltd*  aatrdnarl
»"-bro«o-«.-bro«o-3-   Car ass 1 us
nltresat leylanlllde   auratus
nltrosalIcylanlllda  carpio
V-bro*>o-9-broMO-3-   Plavohalas
nifrasaltevlanlllda   pronalas
V-braao-9-bromo-S-   Ictalurus
nltraxllcylanllid*  •»!•*
%"-bro«o-*-bro«o-3-
                   l- Plm«phal«s
nltrosalIcylanlltda  proavla*
%--ehlor*-r<-a«thyl- letalurus
n|tro«alleylanlUd«  a»ia«
nllrosalleylanllld*  eyanclius


            <-»athyl- lao«al«
                                   8S»   —
                                   ss»   —
                                   BS»
                                   BS*    —
nltrosallcylanlllda


%"-bro»o-5-br o*o-3-  Lapoals       8SA
nltrosal Icylanlllda  aaeroeMrus
                                   8S«    —
                                   BS«
                                   BS«    —
                                   as*
                                                       (.1  
                                                       1.0  IK  3  hrl
                                                       1.0  IK1)
1.0 IK1I
                                                                      a*
                                                                                        «••* as above
                                                                                             as abov*
                                                                                        sa>c as abav*
                                                                                        saa« as abova
                                                                                        «••• as abova
                                                                                        saa*  as above
                                                                                        saaa as abova
                                                                                        saaa as abova
                                                                                        *»••  as abova
                                                                                        san* as abova
                                                                                        saaa  as abova
                                                                                        saaa as abova
                                  saaa as abova
                                                                    al  11970).
                                                                    AHIC-6391

                                                                    M«rKlngtet
                                                                    al  (1970),
                                                                    AHIC-&391

                                                                    M»pKlng,«t
                                                                    at  (1970),
                                                                    ANIC-6391
                                                                    al  (1970).
                                                                    ANIC-6391

                                                                    H«rKlnq,
                                                                    etal  (1970) (
                                                                    AHIC-6I91
                                                                    al  (1970),
                                                                    AI1IC-S391

                                                                    N»rKlntj,«t
                                                                    at  (1970),
                                                                    AMIC-S391
                                                                    al  (19701,
                                                                    AMTC-6391

                                                                    M»Phlng,«t
                                                                    al  (1970),
                                                                    ANIC-6391

                                                                    Harking, et
                                                                    al  (19701,
                                                                    ANIC-1J91

                                                                    Marking, «t
                                                                    al  (19701,
                                                                    ANIC-6391

                                                                    HarHInq, «t
                                                                    at  (1970),
                                                                    ANIC-6391

                                                                    Harfcln?, «t
                                                                    at  (1970),
                                                                    AHIC-6391

                                                                    Marking, at
-------
Coaoound
nltrosal Icylanlllde
%--chloro-?"-«afhyl-
nltrosal lev lanl llde
V-cMoro-2"-«ethyl-
nltrosal ley lanl tide
V-ehloro-Z"-nethyl-
nitrosal Icylanlllde
%"-chl oro-2"-aethy 1-
nltrosal Icylanlllde
%"-chl oro-3-nl trosal
Icylanlllde
V-ehloro-3-nltrosal
Icylanlllde
V-ch 1 oro-3-nl trosal
Icylanlllde
*"-chl oro-3-nl trosal
ley lanl llde
V-ehloro-3-nltrosal
Icylanlllde
V-chl oro-3-nl trosal
Icylanlllde
V-ehloro-3-nl trosal
Icylanlllde
Field Field
Orqanlsa Study Location
•acrocMrus
Perca BSA —
f lavescens
Sal«o BSA —
galrdnerl
Car ass 1 us BSA ~
auratus
Cvorlnus ASA —
earolo
Salao BSA —
9alrdnerl
Carasslus BSA
auratus
Cyorlnus BSA —
earolo
Placonalas BSA —
Ictalurus BSA
••las
Leooals BSA
cyanellus
Leooals BSA —
aaere*Mrus
ToKlcitv. Exoerlaental
Active Variables.
Ingredient. Controlled
Poa or Noted

1.0 IK 3 hrl a*
1.0 IK 3 hr) a*
1.0 (Kll a*
1.0 (Kll a>
1.0 (Kll a*
1.0 (Kll a*
1.0 (Kll a*
l.t (K3 hrl a*
1.0 (K 3 hrl a>
1.0 (Kll a*
1.0 IK1) a*
Conaents

saaa as above
saae as above
saae as above
saae as above
saae as above
saoe as above
saaa as above
seae as above
saae as above
saae as above
saaa as above
Reference
al (1970).
AMIC-6391
Harking, et
al (1970),
Harking, et
al (1970),
AMTC-6391
Harking, et
al 11970),
AMIC-6391
Harking, et
al (1970),
AHIC-6391
Harking, et
al (1970).
»HIC-6391
Harking, et
al (1970),
AMTC-6391
Harking, et
al (1970),
AMIC-6391
Harking, et
(I (1970).
Harking, et
«( (1970),
AMIC-6391
Marking, «t
al 11970).
AMIC-6391
Marking, «t
at (1970).
ANIC-639X
-------
fe
00
          <--ehlore-5-nltrosal Parea         8S«   —
          Icylanllld*          flavaseans
          V-ehloro-5-bro«o-nl Salao         8S«   ~
          trosalleylanlllde    valrdnerl
V-€h)oro-5-bro»o-nl Carasslus     BS»   —
trosal ley I anil Ida    awatus


V-cnloro-5-brono-nl Cyprlnus      BS»   —
trosalleylanlllda    carolo
          %»-cnloro-9-bro«o-nl Pla«oh*l*«    8S»   —
          tr«s«llcylmllld«    pren«fn
                               Ictclurus     8S*   ~
                               l*oml«       8S*
                               cy»o«1lus
                               L«DOKl«       BSI
                               ••erochlrtM
                               P«re»         BS»
                               fl»v«se«ns
Salao         BS*
qatrdncri
Carasslus     BS*
auratus
Cyorlnu*      BS»
carolo
Plaaphalas    BSt
proaalas
           tre«»llcyl*nlllda
          tro«»lleyl»nllld«
          tro«»lleyl»nllld«
          *"-chloPc-5-nltrosal
          Icy Ian! I Id*
          «'-chlore-t-nltr*sal
          lerlanlllda

          »"-ehloro-5-nltro»al
          leylanlllda
          V*-cMoro-*-nltrosal
          leylanlllda
                                                                1.0 CK1I
                                                                1.1 CK1I
                                                                1.0 (Kl)
                                                                0.1 IKZI
                                                                O.i IKZ)
                                                                1.0 IK 3 tori
                                                                0.1 IK%>
                                                                0.1 (K2I
                                                                0.1 IK1I
                                                                1.0 (Kl)
                                                                10 IK2I
                                 10 (Kfct
                                                                l.OIKlt
                                                                                                  *••• «s abova
                                                                                                  saaa as abova
                                                                                                  saaa as abeva
                                                                                                  saaa as abova
                                                                                                  saa* as abava
                                                                                                  •aaa as abova
                                                                                                  sane as abova
                                                                                                  saaa as abova
                                                                                                  saaa as abova
                                                                                                  saaa as abova
                                                                                                  saaa as abova
                                                                   saaa as abova
                                                                                                  saaa as abowa
                                                                                                      Marking, «t
                                                                                                      al  (1970).
                                                                                                      HarKing<  at
                                                                                                      al  (1970).
                                                                                                      HarKlnat  at
                                                                                                      at  (1970) t
                                                                                                      AHTC-6391
                                                                                                             ,  at
                                                                                                      al  119701.
                                                                                                      • NI06391

                                                                                                      Marklnq,  at
                                                                                                      al  (1970).
                                                                                                                           Harking,  at
                                                                                                                           al  (1470).
                                                                                                                           AHIC-S391

                                                                                                                           Harking,  at
                                                                                                                           al  (1970).
                                                                                                                           AHIC-S391

                                                                                                                           Harking,  at
                                                                                                                           al  (1970).
                                                                                                                           ANIC-S391

                                                                                                                           Harking,  at
                                                                                                                           al  (1970).
                                                                                                                           •HIC-6391

                                                                                                                           Harking,  at
                                                                                                                           at  (1970).
                                                                                                                           41IC-6391

                                                                                                                           Harking,  at
                                                                                                                           al  11970).
                                                                                                                           4HIC-6391

                                                                                                                           Harking,  at
                                                                                                                           al  11970).
                                                                                                                           AHIC-6391

                                                                                                                           Harking,  at
                                                                                                                           al  (1970),
                                                                                                                           AHXC-6391
-------
Compound
»"-ehloro-5-nltro
sallcylanlllde
*"-chloro-5-nltro
sallcylanlllde
V-ehloro-5-nItro
sallcylanlllde
»"-chl oro-5-nI tro
sallcylanlllde
»"-lodo-3-nl tro
sallcylanlllde
Field Field
"Organise Study Locaflor
let slur us BSA
•el as
leoomls BSA
cyanel lus
teoomls BSA
macroehlrus
Perca BSA
f 1 avescens
Ictalurus I
nebulosus
(Z.5-6.01n.t
Toxlcltyi Experimental
Active Variables,
Ingredient, Controlled
t Ppn or Noted Comments Reference
1.0 CK1I a* same as above Marking, et
al (1170),
AMIC-6391
1.0 (Kit a* same as above Marking, et
al (19701,
AHIC-6391
1.0 (Kit a* same as above Marking, et
al (1970),
AMIC-6391
1.0 (Kl) a* same as above Marking, et
al (1970),
AMIC-6391
5.0 (Kl a,c«9 Broun bullheads were subletted to Loeb, et al
solutions of V-lodo-ni frosal Icyl anl 1 ld« (1966),
In laboratory Jars some of which AMIC-6199
»"-Jodo-3-nltro
sallcylanlllde
*"-lodo-3-nltro
salleylanlllde
Ic,talurus
nebulosus
(Z. -5-6.0
IN.I
Salmo
galrdnerl
**-lodo-3-nltro
sallcylanlllde
%~-Iodo-3-nltro
sallcylanlllde

                                   BSA   —
                                                      Kl
                                                          (partial
                                                      0.1 IK2)
Carasslus
auratus
Cyorlnus
carple
                                   8SA
                                   BSA   —
                                                      1.0 IK 3 hr)
                                                      0.1 (Kl)
                                                            contained  bottom  sediments  of  different
                                                            deaths  up  to  Z  Inches.  Upon exposure  to
                                                            the  toxicant, some  of the bullheads
                                                            burled  themselves In  the sediments
                                                            thereby surviving the chemical  treatment
                                                            1  to 16 days.   The  phenomenon  of  burying
                                                            appeared to be  temperature  dependent.

                                                 a,c,g             same as  above
                                                                                        Twenty-nine nltrosalIcylanlI ides
                                                                                and related comoounds  were evaluated for
                                                                                their relative  toxic effect  to selected
                                                                                fish.  Potency  varied  with type and
                                                                                position of substitutions.   Several
                                                                                comoounds Here  selectively toxic  to
                                                                                yet Ion perch.   Goldfish were the  most
                                                                                resistant to the sal icytanlI Ides.

                                                                                       same  as  above
                                                                                        same as above
Loeb, et al
(1966),
AMIC-6199
                                                                                                     Marking, et
                                                                                                     al  (1970),
                                                                                                     AMIC-6391
Marking,et
al (1970),
AMIC-6391

Marking,
etal (1970),
AMIC-6391
V-lodo-3-nltro
                     PImephales
                                   BSA   —
                                                      0.1 (Kl)
                                                                                        same as above
                                                                                                                           Marking,et
-------
           lallcylanillde
                                pronelas
                                                                                                                                      al  (1970),
fe
\n
4"-lodo-3-nItrosallc
r I en tilde
*"-lodo-3-n|trosallc
ylanlllde
*"-lo<»o-3-nltrosaUe
ylantllde
%"-Iodo-3-nItrosallc
ylanlllde
%"-lo
                                                      1.0 IK?)
                                                                 1.0  IK2)
                                                                 1.0  (Kl)
                                                                                 a*
                                                                                                   saae  as above
                                                                                                   sa»e  as above
                                                                                                   sane  as  above
                                                                                                   sane  as  above
                                                                                                  saae as stove
                                                                                        sane as above
                                                                                                  sane  as above
                                                                                                  saae as above
Harking,
efal  (19701,
HMIC-6391

Marking. et
al  (19701,
•KIC-6391

Marking, et
al  (1970),
»NIC-6391

Marking, «t
al  (1970).
AMI06J91

MerKlng, et
at  (1970),
AHIC-6391

Harking,
etal  (1970),
ftMIC-6391

Marking, et
al 11970).
AMIC-%391

Marking, et
al
%"-lodo-5-nltPOsal Ic
riant tide
S"-lod»-S-nltrosalle
y I ant tide
%--Iodo-5-nItrosellc
ytanllld*
                                tctalurus
                                me I as
                                Leponls
                                cyanetlus
                                Leponls
                                aaeroehlru*
                                              BSA
                                              BS4
                                              BSft
                                                                 1.0  IK1>
                                                                 l.D  IK2I
                                                                 1.0  IK1I
                                                                                                  sane  as above
                                                                                                  sane  as above
                                                                                                  saae  as above
                                                                                                                           Marking, et
                                                                                                                           81(1970,
                                                                                                                           4MIC-S391

                                                                                                                           Marking, et
                                                                                                                           al (1970),
                                                                                                                           AHIC-6391

                                                                                                                           Harking, et
                                                                                                                           81(1970),
                                                                                                                           ANIC-6391
-------
Conoound
»~-lodo-5-nl trosal le
ytanillde
*"-a«f hoxy-2~-nl tpo-
3-nltrosallcyl-
anlllde
Field Field
Organism Study location
Peres BSA —
f 1 sveseens
Sal no BS*
galrdnerl
Toxlclty,
Active
Ingredlentt
Pom
1.0 
1.0 (Kit
Experimental
Variables.
Control led
or Noted Contents
a*
a»
sane as above
THenty-nlne nltrosal Icy lanl 1 1des
their relative toxic effect to selected
fish. Potency varied tilth type and
position of substitutions. Several
compounds Here selectively toxic to
yellow perch. Goldfish were the »ost
resistant to the sallcytanl 1 ides.
Reference
Marking, et
al (1970).
»MTC-63
                                 10 IK 3 nrl
                                 10 (K 3 hr)
                                 1.0 IK1I
                                 10 (Kll
                                 1.0 (Kll
                                 1.0 (Kll
                                 1.0 (K 3 hr)
                                                                      a»
                                                                   save as above
                                                                   sane as above
                                                                   saae as above
                                                                   sane as above
                                                                   sane as above
                                                                   sane as above
                                                                   sane as above
                                          MarKInq,  et
                                          al  (1970),
                                          »MTC-S3
-------
  5-brono-J-nltrosal Ic Carasslus
  rile acid            auratus
  S-browo-3-nltrosalIc Cyprlnus
  rile acid            carplo
  5-bro«o-3-nltrosallc Plmeohales
  rile  acid            promelas
 5-bro»o-J-nitrosal Ic  Ictalurus
 yllc  acid             »elas
 5-brono-3-nltrosallc Leoouls
 rile acid            cyanellus
 S-brono-J-nltrosallc leponls
                                     BS»   —
8S«
                                     BS*
BS*
                                    BS«
                                    8S»
 rile acid
                      •acrochlrus
 9-bro«o-3-nltrosalIc Perea
 rile acid            flavescens
 *-bro«o-3-«ac-butrl- Phormldlum
 6-»«thyluraclI        amblquun
                                    L     —
                    1.0  (Kl)
                    1.0  IK1I
                   1.0 (Kl)
                   1.0 IK1I
                   1.0 (Kl)
                                                       1.0 (Kl)
                                                       0.1 (Kl)
                                                       0.5-10.0 (NTE)  —
                                              eenoounds  were selectively  toxic  to
                                              yalIOM  perch.  Goldfish were  the  «ost
                                              resistant  to  the sal ley I anil Ides.

                                                      sa*e as above
                                                     sane as above
                                                     same as above
                                                     sane as above
                                                     sane as above
                                                                                         sane as above
                                                                                         same as above
                                                      Of  7ii  cheilcals  evaluated  as
                                              alqleldes,  only  9  Here more  toxic  than
                                              CuSCNt.   None  Inhibited growth  of
                                              •at-fornlng algae  for more than 7  weeks.
                                              CuSO<>  formulated with certain  wettinq
                                              agents  was  more  toxic than CuSOW alone.
                                              Cooper  chtpraiKlne  was also found to be
                                              more toxic  than CuSOU.   No wettinq agents
                                              were found  to  be Inhibitory at the
                                              concentrations investigated (0.09 and
                                              0.005 ppn).  Also reported are factors
                                              affecting growth of algae In canals to
                                              determine whether there  were leads to
                                              controlling algae by environmental
                                              •anageoent.  No practical environmental
                                              •cans were  found.
                                                      Marking, at
                                                      al 11470).
                                                      4MIC-6391

                                                      MarKlnq, et
                                                      al (1470).
                                                      MsrKinq, et
                                                      al (1970),
                                                      4HIC-6J91

                                                      MarKlnq, et
                                                      al (1070),
                                                      ONIC-6391

                                                      Harklnq, et
                                                      al (1970),
                                                      AMIC-6391

                                                      Marking, et
                                                      al  (1970),
                                                      •MIC-6391

                                                      Marking, et
                                                      al  (1970).
                                                      •MIC-6391

                                                      Otto  (1970),
                                                      »MIC-B«
          -          Rasbora       8CF»
(l.mathyl-n-heptyl)  hetarenorDha  and
-U,6-dlnltrophenyl-                BS»
                                                       0.92  (TZ)
a*tC«e«f«          One hundred sixty-four
hard (HM)  pesticide*, wetting agents, and
or soft    mlscal laneou* water pollutants showed a
                                                                                       Alabaster
                                                                                       11969).
-------
Organise
                                    Field
                                    Study Location
                               ToxicltVt
                               Active
                               Ingredient*
Experiment*)
Variables,
Controlled
or Noted
                                                                          Comments
                                                                                                   Reference
thlel carbon»»e
S,8-dlhydroxyl-l,Z,3  Phormldlum
•».9t9-hexachloro-lt  amblguum
t-methano-l.b-rtlhy
dronaphthaiana

                               0.5-10.0 (33
                               percent growth
                               Inhibited l*i
*"-chloro-2"-metho»v Salmo
-3-nltrosallcyl      galrdnerl
anlllde
            as*   —•
                               1.0 IK 3 hr>
iSw)       Hide range of toxlclty spanning  1? orders
synthetic  of magnitude.  Knowing the toxlclty and
dilution   percentage of all  components of  a
water, or  formulation did not result In easy
seawater   predictability of  the toxlclty of  a
for some   Mixture of material!.  Sometimes
species    pesticides Mere aost toxic In hard water
           and sometimes the  opposite was true.
           Testing the actual material as sold Has
           found to be essential.

                   Of 7,
           their relative toxic effect to selected   ANIC-6391
           fish.  Potency varied with type  and
           position of substitutions.  Several
           compounds Mere selectively toxic to
           yellow  perch.  Goldfish Mere the most
           resistant to the sallcylanllldes.
»"-chloro-?"-m»thoxy Carassius     8S»   —
-3-nltrosalleyl      euratus
•nltlde

5"-ehloro-?"-methoxy Cyprlnus      BS»   —
-3-nltrosallcyl      carplo
anlllde

5"-ehloro-?~-metho«y PImephales    8S»   —
-3-nItros»IIcyl      promelas
anlllde
                                                      II
                               1.1 IK1I
                               1.0 IK1)
                                                                                        same as above
                                                                 same  as above
                                                                 same  as above
                                                     HarKlnq,  et
                                                     at  11970).
                                                     •HIC-6391

                                                     Marhlng,  et
                                                     • I  (1970),
                                                     1HIC-6391

                                                     MarKIng,  et
                                                     al  (1970),
                                                     »MIC-%391
-------
 5~-eMoro-Z~-««»hony Ictaturus      8S»    —
 -3-nltr»salleyt   .•:  act as
 •nil Id*

 S~-chloro-?"-«ethoxy l«Donls        BS«    —
 -'S-nltrosalleyl       cyan*11us
 •nit Ida

 5"-ehloro-?"-aetho*y LCDo*Is        BS»    —
 -3-nltrosalleyl       •acroehlrus
 anil Id*

 »"-eM •ro-r*-«*tho*y Pert a          BSA    —
 -3-nttr»s«>fIcyl       tlav*sc«ns
 1.1 IK1I
 1.9 (Kll
 t.O IK1I
 1.1  IK1I
                                        a* »bov«
                                   *••• as above
                                   sane as above
                                   saa*  as above
                                                                      Marhlnq, «t
                                                                      •I  (1970).
                                          Marking, «t
                                          al (1
-------
                              APPENDIX B
                             SPECIES INDEX


^ccipiter cooperii - A -159, 360
Acroneuria - A-5U, 76, 82, 92, 2U?, 280, 306, 330, U52
Acroneuria lycorias - A -269
Aechmophorus occidental! s - A-115, 130, 157
Agmenellum quadruplicatum - A-7, 199, 23^, 278, 376, 377
Agonus cataphractus - A-23, 2U, 26, 28, 1*9, 50, 53, 75, 80, 8l, 103,
    206, 221, 232, 301, 311, 33^, 393, ^k, U06, inU
Alewife - A-17U, 206
Algae - A-1^9
Alosa pseudoharengus - A-29, 55, 76, 82, 96, 117, 131, 166, U27, M»
Ambassis safgha - A-308, 369
Ambloplites rupestris - A -117, 119, 131, 133, 166, 176
Ameirus nebvdosus - A-118, 132, 176
American smelt - A-17^, 206
Amia calva - A«l8
Amphidinium carter! - A-105, 335
Amphipnous cuchla - A-l8o, 263., 373
Anabaena - A -9
Anabas testudineus - A -178,  26j» 373
Anacystls nidulans - A-7, 199, 233, 278,  376, 377
Anas cyanoptera - A -158, 360
Anguilla rostrata - A-113, 121, lUl, 266,  355
Anlsoptera - A-178, 26^, 373
Anisotremls davidsoni - A-1U9, 351*
Aplodlnotus grunniens - A -19
Aquatic plants  - A-1U9
Aquila chrysaetos - A-159, 202, 360
Archoplites interruptus  - A-115, 116
Arctic grayling - A-U6,  12U,  lU6,  197,  35^,  ^22
Artemia  salina  - A -307
Artemia  spp.  - A-1U8
Asellus brevicaudus  - A-lU,  l8U, 190,  191, 217, 2U6,  320,  397,  398,
     ItOl,  ^38, V6, U62,  »«6U,  U65
Asplanchnopus - A -112,  121,  136, 313
Asterias forbesi  - A -68
Asterias rubens - A-10,  65,  75,  302,  331*,
 Backswimmers -
 Belostoma indica . A-180,  26^,  373
 Benthic insects - A -177
 Betta splendens - A-U8, 2kk
 Bigmouth buffalo - A-U5, 123, iWt, 196, 352, U20
 Birds - A. 150
 Black bullhead - AJ+5, 123, 1^5, 197, 353, ^21
 Black crappie - A-U5, 12U, 1^5, 197, 353, U21
 Bloater - A-UU, 123, l1^,  17^,  195, 207, 352, U20
                                  B-l
-------
Blue catfish - A-M*, 71, 122,  ll*U,  26l, 352, 1*20
Bluegills - A-l*l*, 122, 1U6, 195,  3^6,  351, 1*19
Blue-green sunfish - A-l+35, 1+36
BOD - A-22, 66, 100, 2?6,  292,  1*09
Bottom Invertebrates - A-168
Boyeria vinosa - A-269
Brachionus . A -179, 265, 371*
Brachycentrus americanus - A-269
Brachydanlo rerio - A-2, 7, 62, 211,  250, 370. 382, 1*1*9
Bridgelip sucker - A-U6, 124,  1U6,  197, 35^, &21
Brevoortia patronus - A-27
Brook trout - A-269
Brown bullhead - A-1*3, 71, 125, 1^7,  175, 195, 207, 260, 351,  1*19
Bucephala clangula - A-115
Bugula neritina - A-89, 306, 1*52

Callibaetis sp. - A-185, 186,  218
Callinectes sapidus - A-27, 28
Cambarus bartoni - A-150
Campeloma decisum - A-9^,  95
Campeloma sp. - A-119, 133, 176
Cancer magister - A-127, ^22
Carassius auratus - A-l8,  30,  Ul, 52,  55, 61*, 97, 11**, 128,  15!*,  155,
     16U, 235, 21*7, 2U8, 258, 277, 279,  2&0, 28U, 298, 308, 309,  317,
     365, 391, 1*03, ^28, 1*31, 1*1*1, 1*1*9,  l*5U, 1*58, 1*67, 1*68, U69,  1*70,
     1*71, 1*72, 1*73, ^75, 1*76, 1*77, 1*78,  1*79, Wo, 1*81, 1*82, 1*83,  1*81*,
     1*85  1*86  1*87  1*88
Carcinus maenas -*A-3, 33, 31*,  1*7,  W,  68, 79, 86, 87, 90, 103,  170,
     205, 213, 22U, 227, 2U2, 252, 25**,  270, 279, 307, 329, 33^,  337,
     31*0, 368, 378, 379, 381. 399, 1*00,  1*01, 1*02, 1*05, 1*08, UlU,  1*31*.
Cardium edule - A-10, 22,  2U,  26, 28,  29, 32, 33, 31*, 1*7, !*9,  50, 54,
     65, 67, 75, 79, 80, 81, 85, 86, 91, 101, loU, 110, 170,  l8l,  206,
     213, 221, 221*, 225, 227, 232, 2U2,  2U5, 250, 253, 25U, 278,  279,
     291, 301, 302, 207, 311, 323, 329,  331*, 337, 3M, 3»*6, 3»*9,  369,
     378, 379, 399, **00, 401, 1*02, 1*05,  1*06, 1+09. ^l1*, **25, 1*3U
Carp - A-l*3, 71, 122, H*7, 175, 195, 260, 351, ^19
Carpiodes cyprinus - A-20
Carpiodes sp. - A-198
Catostomus coramersoni - A-20,  82, 105,  108, U7, n8, 131, 133,  165,
     176, 277, 297, 337, !*58
Ceriodaphnla - A-179, 265, 376
Cerorhinca monocerata - A-161,  362
Chaetoceros sp. - A-105, 335
Chain pickerel - A-1*3, 125, ll*6,  19!*,  350, 1*19
Channa punctatus - A-7, 177, ISO, 181,  863, 372
Channel catfish - A-t*o, 1*3, 71, 122, ll*7, 175, 195, 207, 26o,  31*?,
     351, U19
Chara sp.  - A-31*5
Chironoraus sp.  - A-7, 129,  130, 131*, 135
Chironomus tentans - A-313
Chiselmouth - AJ*6,  12U, ll*5, 197,  353, **21
              arcuata - A-8, 203
                                  B-2
-------
Chrosomus eos - A-18
Closterium - A-179, 265, 376
Clupea harengus - A-113, 121, lUl, 266, 355, ^7, UU8
Coho salmon - A-6, 69, 101, 175, 207, 2U6, 253, 268, 276,  365,  379,
    393, U09
Coleps - A-112, 120, 136, 313
Copepods - A-72, 73, 203, 20U, 238, 239, 267, 285,  286,  299,  300,
    371, Ull, U12, U32
Coregonus artedii  - A-29, 55, 82, 96, U27, Mn, U5U
Coregonus clupeaformis - A-17, 29, 30,  31, 51,  55,  56, 77, 82,  96,
    97, 280, 281,  302, 310, 331, 393, 39U, U27, U29, UUl,  k5k,  1+55
Coregonus hoyi - A.29, 51, 55, 83, 96,  U28,  UUl,  hjk
Coscinodiscus - A-112, 120, 137, 313
Cottus bairdi - A-llU, 126, 138, 151, 200
Crangon crangon -  A-2, 3, 5, 10, 22, 23, 2U, 26,  28, 29, 32,  33,  31*,
    36, 38, 1*7, U9, 50,  5U, 66, 67, 79, 80,  8l. 86, 87,  91, 101,
    102, 103, 10U, 107,  110, 182, 206,  213,  2lU,  221,  22U, 225, 227,
    231, 232, 2U2, 2U3,  2U5, 2U8, 250,  251,  251*,  255,  256, 257, 268,
    270, 277, 286, 287,  289, 301, 302,  307,  3H,  319,  323, 328, 329,
    337, 338, 3U1, 3U6,  3^9, 363, 36U,  369,  370,  371,  376, 378, 379,
    381, 386, 388, 389,  391, 39U, 399,  Uoi,  U02,  1+03,  U05, Uo6, U09,
    1+15, 1+25, 426, 1+31+,  kk6, UU7, U59
Crangon septemspinosa -  A.67
Crassostrea conmercialls - A-307
Crassostrea virglnica -  A-U, 13,  lU.  26,  103,  169,  181,  20«*, 205,
    217, 220, 223, 230,  231, 233,  2Uo,  260,  28U,  300,  301, 305, 326,
    3^0, 3^3, 36U, 367,  377, 389,  39^,  398,  Ul6,  In8,  U2U, U25, »*38,
    W3, Mk, U65
Crepldostomum farionls - A-222
Culex plpiens - A-112,  120,  133,  13^,  136, 312
Cybister ap.  - A-178,  26U,  373
Cyclops  - A-179, 265,  371*
Cyclops bicuspidatus  - A-72,  73,  168,  203, 20U, 238, 239, 285, 286,
    299, 300, 371, Ull,  U12, U32,  U33
Cyclops varicans  - A-72, 73,  168,  203,  20U,  238,  239,  285, 286, 299,
    300, 371, Ull, M2,  U32,  U33
Cyclops vernalis  - A-72, 73,  168,  203,  20U,  238,  239,  285, 286, 299,
    300, 371, Ull, U12,  U32,  U33
Cyclotella nana - A-105, 335
Cynosclon nebulosus - A-27
Cypridopsis vldua - A-lU.  185, 191, 217, 2U6, 320, 397, 298, UOO,
    U39, UU6, U63, U6U,  U65
Cyprinodon varlegatus - A-68,  176,  2Ul
Cyprinus carplo - A-9, 19,  Ul, 6U,  U7, 118, 131,  132,  16U,  166,
    176, 198, 258, 277,  28U,  296, 298, 299, 317, U31, UU9, U67,  U68,
    U69, U70, U71, U72,  U75, U76, U77, U78, U79, U8o, U8l, U82,  U83,
    U8U, U85, U86, U87, U88
Cyprls - A-279,  «65, 37U

Daphnla -  A J.79,  26U, 267, 37U
Daphnla mgna - A-6,  7, lU, 69, 112. nU, 115, 120, 128, 129,
     133,  13U, 136, 18U, Ml, 217, 2^, 312, 320, 397, 398, UOO,
     UU6,  1+62, i»63, U6U, U65, U66
                                  B-3
-------
Diaptoraus - A-180, 264
Diatomella - A -112, 120, 137, 313
Diatoms - A -112, 120, 137, 313
Diploneis - A-112, 120, 137, 313
Dragonflies - A-40
Dunaliella tertiolecta - A -105, 335
Dytiscus sp. - A-178, 264, 334, 373

Elanus leucurus - A-159, 360
Emerald shimer - A -174
Enallagma sp. - A -189, 190, 218
Endomychura craveri - A-155, 201, 231, 357
Engraulis mordax - A -126, 422
Ephemerella - A -54, 76, 82, 92, 248, ;>80, 306,  330,  452
Ephemerella subvaria - A -269
Esomus danrica - A-178, 263, 373
Esox lucius - A -17, 18, 31, 56, 77, 97, 98, 119, 133,  176,  198,  199,
    270, 271, 277, 281, 303, 310, 315, 331, 391*, **29,  442,  ^55
Esox niger - A-113, 117, 121, 131, l4l, 166, 266, 297, 355
Estigmene acrea - A -111, 119, 135, 312
Eucalia inconstans - A -20
Euclanis - A-112, 121, 136, 313
Eucyclops agilis - A-72, 73, 168, 203- 204, 238, 239,  283,  284,  299,
    300, 371, 411, 412, 432, 433
Euglena - A -9
Eupera singleyi - A-239,
Falco columbarius - A-159, 36l
Falco peregrimis - A-162, 201, 202, 2tl, 356
Falco sparverius - A-159, 160, 36!
Fathead minnow - A-74
Fish (not specified) - A-7, 13, 34, 62, 88, 109,  1^3,  150,  l8l,  193,
    212, 216, 221, 223, 225, 231, 233, 277, 28l,  286,  295,  301,  305,
    365, 371, 372, 386, 388, 398, 415, 4l8, 466,  467
Flannelmouth sucker - A-45, 123, 1^5, 196, 353, ^21
Flathead catfish - A-45, 123, 144, 196, 352,  420
Fregata magnificens . A -158, 359
Freshwater drum - A-44, 122, 144, 170, 196, 206,  352,  420
Freshwater mussels - A-150
Fulmanus glacialis - A -157, 358
Fundulus diaphanus - A -132, 167
Fundulus heteroclitus - A -23, 51, 54, 68, 79.  108,  117,  131,  166,
    227, 228, 319, 327, 3»H, 3te, 363, UlU, 430
Fundulus ma Jails - A -68
Gadus macrocephalus - A -127.  153,
Gadus morhua - A -121, 355, 429
Galeolaria caespitosa - A-89, 306
Gambusia affinis - A-112, 120,  136,  l4l,  142,  147,  169,  205,  236,
    237, 238, 286, 312, 368,  390
Gammarus fasciatus - A-13, 35,  4l, 129, 133,  131*,  184,  190,  191, 215,
    217, 222, 242, 246, 271,  273,  319,  338,  363,  384,  397, 400, 4l6,
    ^30, 439, ^5, ^2, 464,  465
                                 B-4
-------
 Qammarus  oceanlcus  - A-2U,  25,  101,  102,  448
 Gamraarus  pseudolimnaeus  - A-69,  95,  271
 Gamraarus  sp.  - A-llU,  126,  138,  151, 200, 235
 Gastrotricha  - A.179,  26U,  376
 Gerris -  A.267
 Gizzard shad  - A-44, 71, 122, lU3,  171*, 195, 208,  261,  351,  419
 Golden shiner -  A-435, 436
 Goldeye - A-U5,  145, 196, 351,  352,  ^20
 Goldfish  - A-43, 123,  125,  1^6, 170, 19^, 419
 Green sunfish -  A-3U6

 Haliotus  corrugata - A-ll+9, 355
 Haliotis  rufescens - A-149, 35U
 Halocyptena microsoma  - A-163,  357
 Heteropneustes fossilis - A-178, 263, 33*S 373
 Hexagenia bilineata -  A-7,  129, 133, 135
• Hinnites  multirugosis  - A-149,  35^
 Hippoglossoides platessoides - A-121, 356
 Homarus americanus - A.M7
 Hyallela azteca - A-189, 219
 Hydrophilus sp.  - A-179, 265, 374
 Hydroprogne caspia - A-l6o, 362
 Hydropsyche - A-54, 76, 82, 92, 248, 280, 306, 330, 452
 Hydropsyche betteni - A-269

 Ictalurus catus - A-20, 116, 165
 Ictalvirus melas - A-20, 4l, 63, 164, 199, 258, 277, 28U, 298, 317,
     431,  449, ^67, ^68, 469, ^70, 471, 472, 473, ^75, ^76, 477,
     ^79,  U80, 481, 482, 483, ^8U, 485, 486, 487, 489
 Ictalurus nebulosus - A-21, 117. 131,  166,  350, 48U
 Ictalurus punctatus - A-7, 20.  40,  59, 63,  163, 198, 2^9, 258, 277,
     283, 298, 315, 316, 390,- 431, 448
 Ictiobus cyprinellus  - A-20, 198
 Invertebrates - A-150
 Ischnura verticalis - A-129, 134, 135
 Isochrysis galbana - A-105, 335
 Isogenus  frontalis - A-270

 Kelletia  kelletii  - A-1^9, 355
 Kiyi  - A-171, 208
 IO,amath  sucker  - A-124, 145, 353, 421
 Kuklia sandvicensis - A-169, 205,  287,  368

 Labeo rohita  -  A-177, 266, 333, 372
 Lagodon  rhomboides - A-25, 27,  28
 Lake  herring  -  A.171, 208
 Lake  trout - A-44, 123, iWt, 171,  196, 208, 352,  420
 Lake  whitefish  - A-4U,  123, l^1*, 171,  196,  209,  352, 420
 Largemouth bass - A-43, 71, 125, 147,  195,  351,  419
 Largescale sucker  - A-46,  124, 145, 197, 353, 421
 Larus delawarensis  -  A-115, 130
                                   B-5
-------
Larus heermani  - A-156,  357
Larus occidentalls  - A-160,  36l
Larus spp.  - A-115, 130
Lavlnia exilicauda  - A-116
Lebistes  reticulatus - A-169,  205,  267,  287,  368,  381,  450
Leiostoraus  xanthurus - A-25
Lepdotius floridanus - A-199
Lepisosteus platostomus  -  A-17
Lepomis auritus - A-118, 132,  167
Lepomis cyanenus - A-20.  72,  116,  201,  238,  262,  277,  283, 316, 347,
     348,  394, 410,  4li,  467, 468, 1*69,  470,  471, 472,  1*73, 475, 476,
     477,  ^78, 479,  480,  48l, 482, 483,  484,  485, 486,  487, 489
Lepomis gibbosus -  A-19, 116,  131,  165
Lepomis macrochirus -  A-2, 3,  4,  14,  16, 19,  21, 41, 58, 59, 64, 87,
     93, 108, 117, 131, 156,  164,  166, 168,  185,  186, 191,  192, 199,
     217,  239, 240,  241,  246, 249, 258,  277,  284, 295,  298, 315, 317,
     320,  323, 327,  344,  347, 358, 367,  380,  382, 388,  390, 394, 397,
     398,  4oo, 403,  4o4,  4o8, 431, 439,  446,  449, 450,  452, 457, 462,
     463,  464, 465,  467,  468, 469, 470,  471,  472, 473,  475, 476, 477,
     478,  479, 480,  481,  482, 483, 484,  485,  486, 487,  489
Lepomis microlophus -  A-19,  4l, 64, 164, 240, 258, 271, 284, 298, 431,
     453
Libellula sp. - A-129, 130,  134,  135, 187,  219,  228
Llmanda limanda - A-34,  49,  101,  382
Lepomis megalotis - A-19
Limnephilus rhombicus  -  A-113, 125, 137, 150, 199, 235
Llmnephllus sp. - A-187, 188,  219
Limnodrilus sp. - A-410
Longnose  sucker - A-46,  124, 146, 197,  354,  422
Loomelania  melanla  - A-163,  357
Lophodytes  cucullatus  -  A-150
Lymnaea stagnalls - A-17

Macrocyclops albidus - A.72, 73,  168, 203,  204,  238, 239,  285, 286,
     299,  300, 371,  411,  412, 432, 433
Macrognathus aculeatum - A-l8o, 372
Mastocembelus pancalus - A-l80, 372
Megaceryle  alcyon - A-150
Mercenaria  mercenarla  -  A-4, 8, 9,  10,  69,  70, 102, 103, 181> 185,
     221,  222, 223,  225,  226, 233, 247,  257,  260, 286,  323, 325, 326,
     327,  328, 336,  340,  342, 343, 367,  377,  385, 388,  389, 394, 415,
     416,  417, 4l8,  433,  434, 438
Mergus merganser -  A-115,  150
Merlucclus  productus - A-123,  128,  152,  153,  422,  423
Microcystis - A-9
Micropogon  undulatus - A-27
Micropterus dolomieul  -  A-19,  117,  131,  166
Micropterus salmoldes  -  A-19,  4l, 64, 116,  130,  164, 188,  259, 284,
     299,  316, 317,  431,  449
Mlnytrema melanops  - A-20
Monochrysls lutherl - A-106, 335
                                 B-6
-------
Morone saxatilis - A-5, 22, 39, 67, 102, 285, 295, 299,
Mosquitofish - A-U36
Muds - A-150, 3^5
%a arenaria - A-68, 220
Myriophyllum spicatum - A-221
hfystus vitatus - A-180, 2651 373
Mytilus edulis - A-68, 121, 307, 355
tfytilus edulis planvilatus  - A-89

Nandus nandus - A-180, 265, 372
Nannochloris occulata - A-106, 335
Nassarius obsoletus - A-69
Nauplius - A.179, 26U, 37^
Navicula - A-112, 120, 137, 313
Negaprion brevirostris - A-69, l8l,  2U2,  267,  323,  333,  365,  381*,
    386, 1*05, UlU, 1*66
Nepa sp. - A-179, 265, 375
Nereis virens - A-23,  51,  69,  79,  108,  228,  319,  327, 3^2, 363,
Nine-spined  stickleback -  A-172,  209
Nitzschia closterium  - A-106,  335
Nitzschia linearis  - A-2,  3,  U,  16,  59, 60,  87, 327, 367, 380, 382,
    kok, 1*08, 450
Northern squawfish  - A-l*6, 12**,  1U5, 197, 353, ^23
Notendgonus  crysoleucas  -  A-72,  117, 131, 166, 262, 283, 297, 316,
    3^7, 3W, 3^9,  391*, Ml,  ^58
Notomatta  -  A-112,  121,  136,  313
Notonecta  sp.  - A-178,  265
Notropis analostanus  - A-132, 167
Notropis hudsonius  -  A-30, 5U, 76, 82, 97, 1^28, bkl
Notropis cornutus  - A-117, 132,  166
Nuclearia  -  A-112,  120,  136,  313
Nycticorax nycticorax - A-l6o, 361

Oceanodroma  homochroa - A-157, 359
Oedogonium cardiacxm - A-112, 120, 136, 312
Olisthodiscus luteus - A-106, 335
 Oncorhynchus kisutch - A-35, Ul, 63. 6k, 1U8.  152. 16U,  235,  252,
     259,  28U, 296,  299, 317, 336, 383, 385, U32, &1+9, ^59
 Oncorhynchxis nerka - A-337
 Oncorhynchus tshawytscha  - A-9U, 336,  387, U59
 Ophiogomphus rubinsulensis - A-269
 Orconectes nais - A-lU, Uo, 133, 13^,  18U, 190, 191,  217, 2U6, 320,
     397,  398, too,  UUo, UU8, W3, U6U, U65
 Orconectes rusticus - A-9U
 Orthocyclops roodestus - A-72, 73, 168, 169, 203, 20U, 238, 239, 285,
     286,  299, 300,  371, Ull, U12, 1*32, 1*33
 Orthodon microlepidotus - A-115
 Oscillatoria - A-9
 Osmerus mordax - A-17, 30. 31, 55,  57, 77, 83, 96,  98,  281, 303, 310,
     331,  391*, te8, U30, Wll. UU2, UU8, 1*55
 Ostrea edulis - A-U9, 91, 2U3, 255,  307, 329,  U03
                                   B-7
-------
Pacific oyster - A-6, 101
Pagurus longicarpus  - A-68
Palaemonetes kadiakensls - A-13,  72,  110,  111,  115,  129,  133,  134,
    165, 184, 170, 191, 217, 228, 237, 246,  259,  262,  263,  285,
    317, 318, 320, 348, 393, 397, 4oo, 4ll,  1*32,  439,  446,  462,  464,
    465
Palaemonetes vulgaris - A-68,  342
Pandalus montagui - A-379, 381, 394,  401,  402,  403,  409,  4l5,  434
Pandion haliaetus - A-159, 236, 361
Pandorina - A-179, 26k, 37k
Pandulus montagui - A-32, 35,  49, 80, 91,  182,  213,  224.  225,  227,
    243, 247, 253, 254, 256, 279, 280, 307,  329,  337,  34l,  369
Panopenus herbstii - A-199
Panulirua interruptus - A-149, 355
Paralabrax clathratus - A-ll,  12, 13, 37,  38,  57, 58,  60, 61,  77, 78,
    79, 83, 84, 85, 98, 99, 100,  274, 275, 281,  282, 283, 289, 290,
    292, 293, 303, 304, 305, 320, 321, 322,  331,  332,  333,  375,  376,
    395, 396, 397, 412, 1*13, klk, 443, 444,  455,  456,  457
Paralabrax nebulifer - A-149,  354
Paralichthys sp. - A-26
Paramecium - A-112, 120, 136
Parophrys vetulus - A-127, 152, 422
Pelecanus occidentalis - A-158, 202,  236,  259
Peloscolex sp. - A-UlO
Penaeus duorarum - A-25, 27, 28
Penaeus setiferus - A-27
Perca flavescens - A-17, 19, 30,  31,  M,  56, 57,  6k, 77,  83,  97, 98,
    116, 118, 130, 132, 164, 165, 176, 259,  281,  285,  297,  299,  303,
    310, 317, 331, 39^, ^28, 430, 432, kkQ,  kk2,  kk$,  1*55,  U67,  468,
    469, 470, 471, 472, 473, 476, 477, 478,  479,  480,  481,  482,  483,
    484, 485, 486, 487, 489
Percopsls omiscoraaycus - A-30, 56, 77, 83, 97,  428,  440
Petromyzon marinus - A-425
Phalacrocorax pelagicus - A-158,  360
Phalacrocorax peniciliatus - A-158, 359
Phalaropus fulicarus - A-160,  362
Phormidium amblgutan  - A-4, 9,  10, 15, 47,  48,  59, 70,  76, 85,  87, 88,
    89, 90, 92, 107, 109, 183, 215, 222,  223,  266, 271. 273,  313, 322,
    328, 330, 339, 382, 383, 384, 389, 390,  395,  407,  408,  410,  426,
    437, 451, 459, 460, 461, 462, 473, 474,  475,  478,  487,  488,  489
Physa gyrina - A-204, 239, 433
Physa heterostropha  - A-2, 17, 109, 327,  367,  380, 382, 450
Physa Integra - A-95
Physa spp. - A-lll, 119, 136,  312
Pilodictus olivaris  - A-20
Pimelometopon pulchrum - A-149, 354
Pimephales proraelas  - A-20. 22, 4l, 47, 64,  66,  69,  73, 8l, 93,  100,
    105, 108, 140, 153, 164, 211, 214, 215,  235,  237,  245,  258,  272,
    276, 278, 284, 287, 291, 292, 297, 298,  301,  317,  337,  346,  347,
    409, 426, 431, 449, 452, 453, 458, 461,  467,  468,  469,  470,  471,
    472, 473, ^75, 476, 477, ^78, 479, ^80,  481,  482,  483,  484,  485,
    486, 487,
                                 B-8
-------
Pisidium sp. - A-119, 133
Pizonyx viversi - A-163, 357
Plankton - A -115
Plants - A-1U9
Platessa vulgaris - A -250
Platichtbys flexus - A-91, 110, 225, 251, 308, 3Ul, 369, M5,
Platichthys stenatus - A -127, 153, ^23
Platymonas subcordiformls - A-105, 335
Pleuronectes platessa - A-10U, 170, 3^9
Podiceps caspicus - A-163
Poecilia latipinna - A -193, 19*4-
Poecilia reticulata - A-U23, b2h
Pomoxis annularis - A -156, 198, 358
Pomoxis nigromaculatus  - A -19, 115, 118,  132,  156,  16?,  198,  358
Porphyridium cruentum - A -105, 335
Procambarus simulans - A-^0
Prosopium cyllndraceum  - A -29, 51,  55,  83,  96, 1*28, kbl,
Protozoa - A -112, 120,  136, 313
Pseudopleuronectes americanus  - A -92,  93
Pteronarcys dorsata  - A -270
Ptychocheilus  oregonensis - A-U58
Ptychocheilus  umpquae - A-l*-59
Ptychoraraphus  aleuticua - A-l6l,  362
Puffinus creatopus - A -157, 358
Puffinus griseus  - A -157, 359
Puffinus tenulrostris - A-157, 359
Pumpkinseed -  A-^3,  125,  1^7,  19^, 351, Ul9
Puntius sophore - A-8,  177, 180,  265,  33^,  373
Puntius ticto  - A -46, 212,  252,  278,  297, 39^,
Pygoscelis  adeliae - A -156,  358
 Rainbow trout - AJt6,  12k, 1^5, 197, 3^5, 353, ^21, U35,
 Rana teraporaria - A -128, 15 U
 Ranatra fillformls - A -178, 265, 33^, 373
 Rasbora heteromorpha - A-3, 5, 6, 11, 15, 16, 21, 23, 31, 32, 33, 31*,
     35, 36, 38, 39, Ul, U2, 51, 52, 53, 6l, 65, 66, 67, 73, lh, 75,
     87, 102, loU, 106, 109, 110, 137, 139, lUl, 1U2, 1^3, 182, 183,
     18^, 185, 192, 193, 211, 212, 216, 226, 229, 230, 232, 2Ul, 2U^,
     2U5, 2U6, 2U8, 2U9, 252, 255, 256, 257, 261, 267, 273, 275, 276,
     288, 391, 293, 29^, 297, 305, 306, 310, 318, 319, 32U, 325, 326,
     327, 338, 339, 3^, 3^5, 366, 367, 370, 371, 377, 38^, 385, 386,
     387, 393, U02, UoU, U07, ^16, Ul?, U25, te6, U27, ^30, U31, ^36,
     ^39, M*2, W*, W*5, U7, W*8, ^51, ^63, U65, ^66, U73, ^87
 Redbreast sunfish - A-122, lU6, 295, 351, U21
 Redhorse sucker - AJtf, 71, 122, 1^3, 195, 351, 14-19
 Red shiner - A-U36
 Rhinichthys atratulus - A-llU, 118, 126, 132, 138, 139,  151,  167,  200,
     201
 Rita rita - A-1&0
 Roccus americanus - A-118, 132, 166
 Roccus chrysops - A-30, 52. 56, 83, 97,  199, ^28,  14-1*0, 1+5^
 Roccus saxatilis - A-Uo, 9^, 220, 229, 252, 256, 277, 380, 383,  399
 Rock bass - A-UU, 122, lU4, 171, 195, 209, 352, U20
                                  B-9
-------
Rotifers - A-112, 120, 136. 313
Round whitefish - A-46, 124, 146, 171, 197, 209, 354, 422

Salmo aquabonita - A-223
Salmo clarki - A-21, 62, 63, 148, 234, 296
Saline gairdneri - A-14, 15, 18. 21, 35, 41, 48, 63, 64, 70, 73, 91,
    95, 100, 106, 148, 154, 164, 191, 192, 213, 217, 226, 229, 234,
    249, 250, 251, 259, 267, 272, 276, 284, 294, 296, 299, 315, 317,
    322, 324, 325, 330, 333, 336, 343, 366, 368, 370, 378, 387, 388,
    390, 395, 398, 399, 405, 406, 407, 429, 432, 437, 439, 442, 445,
    449, 452, 453, 454, 457, 459, 466, 467, 468, 469, 470, 471, 472,
    473, 475, 476, 477, 479, 4&0, 481, 482, 483, 48U, 485, 486, 488
Saljno salar - A-23, 24, 101, 113, 121, 141, 155, 266, 355, 447
Salmo trutta - A-l8, 4l, 64, 142, 143, 164, 251, 259, 284, 299, 315,
    317, 432, 449
Salvelinus fontinalis - A-18, 62, 98. 107, 114, 126, 137, 138, 147,
    150, 151, 152, 155, 167, 200, 234, 295, 296, 315, 407, 437, 438,
    441, 448, 459
Salvelinus namaycush - A-l8, 30, 51, 55, 83, 96, 309, 310, 314, 315,
    428, 454
Sauger - A-45, 123, 145, 196, 353, 421
Scardium - A-112, 121, 136, 313
Scomber scombrus - A-113, 121, l4l, 266, 355
Sea lamprey - A-172, 209
Sebastodes alutus.- A-128, 153, 423
Sebastodes flavidus - A-127, 153, 423
Sebastodes marinus - A-121. 355
Sebastodes sp. - A-149, 354
Semotilus atromaculatus - A-114, 117, 126, 131, 138, 150, 151, 166,
    200
Semotilus corporal!s - A-117, 131, 166
Slalis ep. - A-114, 126, 138, 151, 200, 235
Simulium venustum - A-168
Siphlonurus sp. - A-13U, 135
Skeletonema costaturn - A.105
Slimy sculpin - A-172, 209
SmallBouth bass - A-46, 124, 145, 197, 353, 421
Smallmouth buffalo - A-U5, 123, 144, 196, 261, 352, 420
Sorghum halpense - A-lll, 119, 311
Sphaerodema annulatum - A-178, 265, 373
Spirogyra sp. - A-9, 345
Spirorbis lamellosa - A-89, 306, 451
Spottail shiner - A-172
Spotted sucker - A-44, 122, 143, 195, 351, 419
Steelhead trout - A-6, 69, 100, 245, 253, 268, 276, 365, 379, 391,
    409
Stenonema candidum - A-313
Stenonema rubrum - A-269
Sterna forsteri - A-160, 361
Stizostedion vitreum - A-19, 30, 52, 56, 83, 97, 198, 314, 428, 440
Stolephorus purpurea - A-169, 205, 287, 368
Stonecat - A-172
                                B-10
-------
Striped mullet - A-UU, 71, 122, lM*, 195, 351, 1*20
Strongylocentrotus franciscanus - A-1U9, 35^
Sturnella neglecta - A-l6l, 363
Sula leucogaster - A-158, 202, 236, 359
Synthliboraraphus antiquum - A-l6l, 362

Taeniopteryx nlvalis - A-313
Taenlopteryx maura - A-269
Tendipedidae - A-220
Thalasseus elegana - A-156, 357
Tilapia mossamblca - A-169, 205, 287, 368
Trachinotus carolinus - A-5, 93, 252, 383
Trichogaster fasciatus - A-177, 265, 372
Triturus cristatus - A.128, 15^
Trout perch - A-173
Tubifex sp. - A-U12
Tubifex tubifex - A-8, 73, 169, 20U, 215, 228, 239, 2UU, 259, 277,
    286, 300, 318, 3^9, 36U, 372,  393, M2, U2U, U33
Tubificids - A-267
Tyto alba - A-161, 363

Ulothrix sp. - A-8, 203
Uria aalge - A-161, 362
Urophycis tenuia - A-121,  355
Urosalpinx cineria - A.68

Volvox - A-179, 26U,  37U
Vorticella - A-112, 120,  136,  313

Walleye - AJ*5, 71, 123,  1^5,  173, 196,  210,  353,
Watersipora cucullata . A -306,  *»-51
Whirligig beetles - A-Uo
White bass - AJ*5 , 123,  1^5,  173, 197,  210,  353,
White catfish  - A-U3, 125,  1&6, 19U, 350, Ul9
White crappie  - A-U5, 123,  iW;, 196, 352, U20
White perch - A-U3, 71, 125,  l1^,  173,  191*, 210, 350,  Ul8
White sucker - A-U2,  71,  125,  1^3, 173,  191*,  210,  350,  Ul
Wolffia papiilifera -  A-105, 1^7,  18^, 211, 272, 301,  391*,

Xiphophorus maculatus - A-U53

Yellow perch - A-U2,  125, 1^6,  173, 191*, 2U, 350

Zenaidura macroura -  A-l6l, 363
                                B-n
-------
                             APPENDIX C
                  IDENTIFICATION OF COMMERCIAL CHEMICALS

    (Note:  Many of the names Included In this list are tradenames
            and should be treated as  such.)
Chemical Name

ABS
Acrlflavlne
Acrolein
Actusol
Aflatoxin Bl
Agridip
Amitrole
Amltrol-T

Amphenone B

Antimycin A
Aphitox
AQ
Aquaclene
Aquaclene 100
Aqualin
Aquathol

Aroclor 1221

Aroclor 12U2

Aroclor 12U8

Aroclor 1251*

Aroclor 1260

Aroclor 1262

Asuntol (Sheep dip)
Asulum

Atlas 1901
Atlavar
         Composition

Alkyl benzene sulfonate
Mixtures of 2,8-diamino-10-
    methylacridinium chloride
    and 2,l*-diaminoacridine
see Aqualin
No information available
C17H1206
No information available
3-Amino-l,2,U-triazole
3^Amino-l, 2, U-triazole-ammonium
   thiocyanate mixture
3,3-Bis  [p-aminophenyl]-2-butanone-
   2-dihydrochloride
C28HUON209
Fluoroacetamide and Ilssapol
No information available
No information available
No information available
2-Propenal
Disodium salt of endothal
     (19.2 percent-H-Pennsalt)
Commercial PCB with 21 percent
   chlorine
Commercial PCB with U2 percent
   chlorine
Commercial PCB with k& percent
   chlorine
Commercial PCB with 5U percent
   chlorine
Commercial PCB with 60 percent
   chlorine
Commercial PCB with 62 percent
   chlorine
 see  Coumaphos
Methyl-U-aminobenzene sulfonyl-
     carbamate
No information available
Sodium chlorate,  2,luJ),  Monuron
   mixture
                               C-l
-------
Chemical Name
         Composition
Atrazine

Avadex

Avadex BW

Azinphosmethyl
Balan
Banner DG01
Banner DG02
Banner DG03
Banner DGOU
Banvel
Barban
Basol AD6
Basol 99
Bayer 3900?
•Bayluscide

Baytex
Baywood k3

Benazolin
Bensulide
Betasan
BHC
Borasceu
BP
BP 1002
BP 1100
BP 1100X
Brakontrole
Bromophos
Bromoxynil
Busan 90
Busan 88l
Canal Bank Weedkiller
Captan

Carbaryl
Carbophenothion
Carbyne
Caeol
Casoron
Casoron G
Casoron 133
Chem-floe
Chevron NI-0
2-Chloro-U-ethylamine-6-isopropyl-
   amino-s-triazine
S-2,3-Dichloroallyl diisopropylthio-
   carbamate
S-2,3,3-Trichloroallyl-diisopropyl
   thiolcarbamate
see Guthion
see Benefin
No information available
No information available
No information available
No information available
3,6-Dichloro-o-anisic acid
h-Chloro-2-butynyl-m«<;hlorocarbanilate
No information available
No information available
N-methyl 2 isoprqpoxyphenyl carbamate
2',5J>ichloro J*1-nitrosalicylanilide
   ethanolamine
see Fenthion
Maleic hydrazide, 2,Uj) as triethanol,
   amine salt, vetting agent, water
No information available
see Betasan
S-(0,0-Diisopropyl phosphorodithioate)
   ester of N-(2-mercaptoethyl)
   benzene sulfonamlde
Benzene hexachloride
No information available
No information available
No information available
No information available
No information available
U-CPA
see QMS-658
3,5-Dibrono-k-hydroxybenzonitrile
No information available
Organosulfur formulation
No information available
cis -N-( (trichloromethyl)thio)-
   4-cyclohexene-l,2-dicarboxlmide
1-Naphthyl methylcarbamate
see Trithion
see Barban
No information available
see Dlchlobenil
see Dlchlobenil
see Dichlobenil
Isopropyl N-phenylcarbamate
No information available
                               C-2
-------
Chemical Name

Chloramphenicol
Chloral hydrate
Chlorainine
Chlorax
Chlordane
Chlorea
Chlorfenvinfos

Chloroflurazole
Chloropropylate
Chlorthiamid
CI
Cleanosol
Clophen A30
Clophen AUO
Clophen A50
Clophen A60
Compass
Cooper's Fly Dip
Co-Ral
 Corexit ?66U
 Corexit 8666
 Coumaphos
 Craine QBE
 Crossguard
 Crotothane
 Crow Solvent  M
 Cunilate RQ 2k
 Cuprinol
 CX
 Dalaclde

 Dalapon
 D.B. Granular
 DBF
 DDD
 DDE

 DDT

 DDVP

 Decamethdnium dibromlde
 De De Tane
 Delrad
         Composition

(Chlororaycetin) D-(-)-threo-2-
   dichloroacetamido-1-p-nitrophenyl-
   1* 3-propanediol
2,2,2-Trichloro-l,1-ethanediol
(N^hloro-p-toluenesulfonamido) sodium
No information available
Mixture of 60 percent octachloro-li.,7-
   methanotetrahydroindane and Uo
   percent related compounds
see Monuron
2,U -Dichlorophenyl-1-chloroethylene
    diethyl phosphate
No information available
No Information available
No information available
No information available
No information available
No information available
No information available
Commercial mixture of PCS
No  information available
No  information available
see Chlorfenvinfos
0,0-Diethyl 0-3-chloro-U-aethyl-2-
    oxo-2H-l-benzopyran-7-yl-
    phosphorothioate
No  information available
No  information available
see Co-Ral
No  information available
No  information available
 see Karathane
No  information available
Oxine copper
No  information available
No  information available
DalaponJfa,  Sodium 2,2,3*trichloro-
    propionate
 2,2 Dichloropropionlc acid
 No Information available
 U, U' -J)lchlorobenzophenone
 see TDE
 l,l-Cichloro-2,2-bis (p-chlorophenyl)
    ethylene
 1,1,l-Trichloro-2,2-bis(p-chlorophenyl)
    ethane
 0,0-dimethyl-0-( 2, a^Llchlorovlnyl)
    phosphate
 No Information available
 see DDT
 Dehydroabiethylamine acetate
                                C-3
-------
Chemical Name
         Composition
Delrad 70
Demeton methyl
Dermol
Diazinon

Dicamba
Dicapthon

Dichlobenil
Dichlone
Dichlorofenthion
Dichlorophen
Dichlorvos
Dicofol

Dieldrln
Dlfolatan

Dimanin

Dimecron
Dimethoate

Dimite
Dinocap
Dinoseb
Diphenamid
Dipterex
Diquat

Dispersol SD
Disulfoton

Di-Syston
Diuron
DNOC
Dobs .JN
Dobs 055
Dowicide A
Dowicide G
Dowpon
Doxide (C 102)
DSS
DTMC
Dursban

Dylox

E-31U
EC-90
Technical grade of dehydroabietylamine
see Meta-Systox
No information available
0,0-Diethyl 0-( 2-isopropyl-6-methyl-
   U-pyrimidinyl) phosphorothioate
see Banvel
0-(2-Chloro-U-nitrophenyl)0,0-
   dimethyl phosphorothioate
2,6J)ichlorobenzonltrile
2,3-Eichloro-l,U-naphthoquinohe
see VC-13
2,2'-Methylenebis [4-chlorophenol]
see DDVP
1,l-bis(p-Chlorophenyl)-2,2,2-
   trichloroethanol
Not less than 85 percent of 1,2,3,^,
   10,10-hexachloro-6,7-epoxy-l,U,Ua,
   5,6,7,8,8a-octahydro-l,U-endo-exo-
   5,8-dimethanonaphthanlene
cis-N-[(l,l,2,2-Tetrachloroethyl)thio]-
   U-cyclohexene-1,2-dicarboximide
Alkyldlmethylbenzyl ammonium chloride
   plus urea
see Phosphamidon
0,OJ)imethyl S-(N-methylcarbamyl-
   methyl) phosphorodithioate
1,l-bis(p-Chlorophenyl)ethanol
see Karathane
2-( sec-Butyl) -14-,6-dinitrophenol
N,N J)imethyl-2,2-diphenylacetamid
see Dylox
6,7-Dehydrodipyrido [l,2a:2',l'c]
   pyrazinedium salts
No information available
0,0 J)iethyl-S-[2-(ethylthio)-ethyl]
   phosphorodithioate
see Disulfoton
3-( 3, k J)ichlorophenyl) -1.1-dimethylurea
2-Methyl-U,6-dinitrophenol sodium salt
No information available
No information available
0-phenylphenol, sodium salt
Sodium pehtachlorophenate
see Dalapon
No information available
see Dioctyl sodium sulfosuccinate
see Dicofol
0,0-Diethyl 0-3,5,6-trichloro-2-
   pyridyl phosphoro thioate
0,0-dimethyl (2.2,2-trichloro-l-
   hydroxyethyl) phosphonate
No information available
No information available
                               C-U
-------
Chemical Name
         Composition
Econal 13086
Emcol H-ll*6
Emcol 702
EMID
Emkem Spill Wash
Empilan
Emulsifier .Blend 350
Endosulfan
Endothal
Endothall

Endrin
Epichlorohydrin
Eptam
Eserine sulfate
ESSO Solvent FG-155
Essolvene
Ethanediol
Ethion

Ethomeen S-25
Ethyl Parathion
EVIK

Fenac

Fenoprop
Fenthion

Fentin acetate
Fenuron
Finasol ESK
Finasol OSR2
Finasol SC
Flock O.P. Fly Dip
Florescein sodivun

Fluorokill
F.O. 300B
Foilzoil
Folpet
Formothion
Furfural
Gamlen CW
Gamlem D
Gamlen OSR
2,U,5-T (as butoxy ethyl ester)
No information available
No information available
2,U-Dichlorophenoxy-acetamide
No information available
No information available
No information available
6,7,8,9,10,10-Hexachloro-l,5,5a,6,9,
   9a-hexahydro-6,9-methano-2,kt3-
   benzodioxathiepin-3-oxide
see Endothall
7-Oxabicylo(2.2.1)heptane-2,3-
   dicarboxylic acid
1,2,3t b,10,10-Hexachloro-6,7-epoxy-
   l,4,l^a,5,6,7,8,8a-octahydro-l,U-endo«
   endo-5> 8-dimethanonaphthalene
l-Chloro-2,3-epoxypropane
S-Ethyl dipropylthiocarbamate
No information available
No information available
No information available
No information available
0,0,0',0'-Tetraethyl S,S'-methylene
   biophosphorodithioate
No information available
see Parathion
2-(Ethylamino)-U-(isopropylamino)s
   6-(methylthio)-s-triazine
2,3»6-Trlchlorophenylacetic acid or
   sodium salt
No information available
0,0 J)imethyl-0-[ U] (methylthio) -m-
   tolyl]-phosphorothioate
No information available
3 Phenyl-1,1-dimethylurea
No information available
No information available
No information available
see Dichlorofenthion
9-(0-carboxyphenyl) «^-hydroxy-3-
   isoxanthenone
Fluoroacetamide
No information available
No information available
N-(Trichloromethylthio)-phthalimide
Phosphorodithioic acid 0,0-dimethyl
   ester S-ester with N-formyl-2-
   mercapto-N-methylacetamide
2-Furaldehyde
No information available
No information available
No information available
                               C-5
-------
Chemical Name
         Composition
 Gamlen FBX
 Gamlen WBX
 Gamma  BHC
 Gesapax
 Globe  Terramycin Pet Tabs
 Gloquat C
 Gramoxone  W
 Griseofulvin
Gulf Agent 1009
Guthion

Heptachlor

Heptachlor epoxide
Herbane

Hillvale Fly Dip
Histamine phosphate
Hobstone OSD
Hoc  SC 1780
Holl-Chem 622
Houghtosolve
Hydrothol 191

IAA
laline Brushweed Killer
laline grass growth regulator
   (Regulox)
laline Vergicide Weedkiller D
laline Vergicide Weedkiller
I.C.I. Sunnier Sheep Dip
loxynil
loxynil Na
IPC
Jansolv-60
Juglone
Karathane

Karmex
Kelthane
Ketoendrin
KLofos
LAS
Lenacil
Lindane
No information available
No information available
see Lindane
see EVIK
Oxytetracycline hydrochloride
No information available
see Paraquat
7-Chloro-2f,U,6-trimethoxy-6'p-methyl-
   spiro-[benzofuran-2(3H),l' [2]
   cyclohexene]-3,^'-dione
No information available
0JOJ)iethyl-s-[U-oxo-l,2,3-benzotriazin.
   3(to)-ylmethyl]-phosphorodithioate
Jk percent l,U,5,6,7,8.8a-Heptachloro-
   3a,U,7a-tetrahydro-U,7-methanoindene
Photoisomer of Heptachlor
3-(Hexahydro-4,7-methanoinden-5-yl)-1,
   a-dimethylurea
Dichlorofenthion
No information available
No information available
No information available
No information available
No information available
Mono (N,N-dimethylalkylamine) salt of
   endothall
Indole-3-acetic acid
No information available
see Maleic hydrazide

No information available
see Vergemaster
see Pyrimithate
3,5-Diodo-luhydroxybenzonitrile
No information available
see Chem Hoe
No information available
5-Hydroxy -1, k- naphthoquir.one
2-(1-Methylheptyl)-^,6-dinitrophenyl
   crotonate
see Diuron
see Dicofol
No information available
No information available
Linear alkylate stilf onate
3-Cyclohexyl-6,7-dihydro-lH-
   cyclopentapyrimidine-2, (3H, 5H) -
   dione
1,2,3,k,5,6-Hexachlorocyclohexane
   containing at least 99 percent
   gamma isomer
                               C-6
-------
Chemical Name
         Composition
Linuron

Lirostanol
Lissapol IPA

Llssapol NM

Lissapol NX

Lubrol APNS
Lubrol L
Magic Power
Malathion

Maleic hydrazide
Manazon
Mancozeb
Maneb
Manoxol
MCPA
Mecarbam
Mecoprop
Menazon

Meta-Systox

Methoxychlor

Methyl parathion

Methylpentynol
Mevinfos  (Mevinphos)

Milbex
MM
Moaspill
Mobilsol
Molinate
Monoxone
Monuron
Morphothion
MS-222
Mystox LSC-P
Mystox LSE-L
Mystox LSE-P
Mystox LSL
Mystox LSL-L
 Mystox LSL-P
N-3^52
3-( 3* ^ J)ichlorophenyl) -1-methoxy-l-
   methylurea
Fentin acetate
Mixture of the sodium salts of
   sulfated fatty alcohols
Mixture of the sodium salts of
   sulfated fatty alcohols
Mixture of the sodium salts of
   sulfated fatty alcohols
No information available
No information available
No information available
0,0-Dimethyl phosphorodithioate of
   diethy1 mercaptosuccinate
1,2-Dihydro-3,6-pyridazinedione
No information available
No information available
Manganous ethylene blsdlthiocarbamate
No Information available
2-Methyl-U-chlorophenoxyacetic acid
No information available
No Information available
S-(k,6-Diamino-s-triazin-2-ylmethyl)
   0,0-dlmethyl  phosphorodithioate
Isomeric mixture of  0-[2-(ethylthio)
   ethyl]0,0-dimethyl phosphorothioate
2,2-bis(p-Methoxyphenyl)-1,1,1-
   trichloroethane
0,OJ)imethyl 0-p-nitrophenyl
   phosphorothioate
No information available
2-Carbomethoxy-1-methy Ivinyl
   dimethyl phosphate,  evisomer
No Information available
No Information available
No information available
No Information available
 see  Crdram
No Information available
 3-(p-Chlorophenyl)-1,1-dimethylurea
No information available
Tricaine methanesulfonate
 No Information available
 No information available
 No Information available
 No information available
 No Information available
 No information available
Alkyl(C8-Ci8)dimethyl benzyl ammonium
    chloride
                                C-7
-------
 Chemical Name
         Composition
 NA
 Nabam
 Nalco 201
 Nalco 2UO
 Nalco 2U3
 Neburon

 Nemagon
 Mew BP 1100
 Nitrofurazone
 Nitrofen

 Norea
 Norseman
 NPH 1253
 NFH 1313
 Nucidol Diazlnon Sheep Dip
 Nystatin
 OD
 Oil Herder
 Ordram

 Omazene (Omazine)
 OMS-658

 Paraquat
Parathion

PC
PCB
Pebulate
Penetone X
Perolin No.
Perthane
Petrolite W-ll*39
Phenkapton (Phencapton)

Phenobarbital
Phenoxylene
Phenoxytol (Phenoxetol)
Phorate

Phordene
Phosalone
Phosdrin
2-Chloro-l-nitropropane
No information available
Disodium ethylenebisdithiocarbamate
Chlorinated phenol formulation
Organobromine formulation
Organosulfur formulation
l-n-Butyl-3-(3,ludichlorophenyl)-
   1-methylurea
1,2-Dibromo-3-chloropropane
No information available
5-Nitro-2-furaldehyde semicarbazone
2,U-Dichlorophenyl p-Nitrophenyl
   ether
see Herban
No information available
see loxynil
see Mecoprop
see Diazinon
No information available
No information available
No information available
S-Ethyl hexahydro-lH-azepine-1-
   carbothioate
Cupric dihydrazinium sulfate
0-( l4~Bromo-2,5-dichlorophenyl)
   0,0-dimethyl phosphorothioate
1,1' -Dimethyl-U,k'-bipyridinium
   dichloride or 1,1* ^Dinethyl-U,!*1-
   b ipyridiniumb i s [ methylsulfate]
0,0-Diethyl-O-p-nitrophenyl
   phosphorothioate
see Phosphocreatine
Polychlorinated biphenyl
see Tillam
No information available
No information available
1,l-Dichloro-2,2-bis(p-ethylphenyl)
   ethane (88 percent) plus related
   compounds, 12 percent
No information available
0,0-Diethyl-S-(2,5-dichlorophenyl-
   thioraethyl) phosphorodithioate
5-Ethyl-5-phenylbarbituric acid
No information available
2-Phenoxyethanol
0,0-Diethyl S-(ethylthio)-methyl
   phosphorodithioate
No information available
see Zolone
see Mevinfos
                               C-8
-------
Chemical Name
         Composition
Phosphamidon

Phosphocreatine
Phostox
Photoaldrin
Photodieldrin
Phygon
Picloram
PMA
Polycell Product
Polyclens
Polycomplex A
Polycomplex A-ll
Polyotic
Polyram
Praparat Alfol WV 1019
Princep
Procaine hydrochloride

Pro-Noxfish
Propanil
Propham
Protim

PVP-Iodine

Pyramln

Pyrazon
Pyrimithate
Quinaldine
R-1910
Raynap Sol B
RD 11*639
Reglone
Rhodamlne B
Ridzlik
Roccal
Rola OSD
Ro-Neet
2-Chloro-N,N-diethyl-3-( dimethoxy-
   phosphinyloxy)crotonamide
N-(Phosphonoamidino)sarcosine
No information available
Photoisomer of Aldrin
Photoisomer of Dieldrin
see Dichlone
U-Amino-3,5,6-trichloropicolinic acid
Pyrldylmercuric acetate
Sodium carboxymethyl cellulose
No information available
No information available
No information available
Tetracycline hydrochloride
Mixture of 5.2 parts by weight (83.9
   percent) of ammoniates of [ethylene-
   bis-(dithiocarbamate)] zinc with 1
   part by weight (16.1 percent)
   ethylene bis[dithiocarbamtic acid],
   bimolecular and trimolecular cyclic
   anhydrosulfides and disulfides
Hexadecanol
2-Chloro-U, 6-bis( ethylamino) -s-triazine
p-Aminobenzoyldiethylaminoethanol
   hydrochloride
Rotenone
3, ^-Dichloropropionanilide
see Chera Hoe
Copper pentachlorophenate plus
   chloronaphthalene and dieldrin
l-Vinyl-2-pyrrolidinone polymers,
   iodine complex
5-Amlno-U-chloro-2 phenyl-3 (2H).
   pyridazinone
see Pyramin
Phosphorothioic acid 0-[2-dimethylamino)-
   6-methyl-U-pyrimidinyl] 0,0-diethyl
   ester
2-Methylquinoline
Ethyl-N,N-diisobutyl thiolcarbamate
No information available
N-methyl carbamate derivative
Diquat-dibromide
[ o/.( O-carbcoyphenyl) -6-diethylamino) =
   3H-xanthene-3-ylidene]diethylammonium
   chloride
No information available
Benzalkonium chloride
No Information available
S-Ethyl N-ethyl-N-cyclohexylthio.
   carbamate
                               C-9
-------
Chemical Name
         Composition
Rosin Amine D
S.D. 3562 (Bidrin)


S.D. 8211

S.D. 8UU?

Seasweep
Sefoil
Sesamex
Sevin
Shamash R1885
Shell D-50
Silvex

Simazine
Slickgone 1
Sllckgone 2
Slix
S.N. 5215
Snowdrift SC98
Spill Remover
Spin-X
Streptomycin Sulfate
Strobane
Sulfisoxazole

Sulmet

Sumithlon

Sutan
TCC
TCP
TDE

TEPA'
TEPP
Tetradifon

TFN (Lamprecid)

Thimet
Thiolutin
Thiumet
Thyroxine
Tinam
Tlmsan
TN
see Delrad 70
Phosphoric acid dimethyl ester, ester
   with cis-3-hydroxy-N,N-dimethylcrotan.
   amide
Phosphoric acid, 2-chloro-l-(2,5-
   dichlorophenyl)vinyl dimethyl ester
2-Chloro-l-(2, U, 5-trichlorophenyl) vinyl
   dimethyl phosphate
No information available
No information available
No information available
see Carbaryl
No information available
2,^,0 amine (triethanolamine salt)
2-(2,^,5-Trichlorophenoxy)-propionic
   acid
see Princep
No information available
No information available
No information available
No information available
No Information available
No information available
No information available
2 C21 H3oN70ip.3HoS(\
Terpene poiycnlorinates
Nl-(3,U-Dimethyl-5-isoxazolyl)
   sulfanilamide
(Sodium sulfamethazine) sodium (U,6-
   dimethyl-2-sulfanilamidopyramldlne)
0,OJ>imethyl O-(U-nltro-m-tolyl)-
   phosphorothioate
S-Ethyl diisobutylthiocarbamate
3,M'-Tricnlorocarbanilide
Tritolyl phosphate (CgiHpiC^P)
1,l-Dichloro-2,2-bis(p-chlorophenyl)
   ethane
tris-(l-Aziridlnyl)phosphine oxide
Tetraethyl pyrophosphate
U'-Chlorophenyl 2,U,5-trichlorophenyl
   sulfone
S^Trlflucromethyl-Ji-nltrophenol,
   sodium salt
see Phorate
No information available
see Polyram
No information available
S-Propyl butylethylthiocarbamate
6.25 Percent ethyl mercury phosphate
No information available
                               C-10
-------
Chemical Name
         Composition
TOK
Tordon C
Tordon M
Toxaphene

Toxion
Treflan E.C.
Trifluralin

Trioxone
Trithion

Trixabon
Tubotox
Ureabor
Vamidothion
Vapam
VC-13

Velaicol AR 50G
Venzar
Vergemaster
Vernam
Vernolate
Weedazol
Weedazol T-L
WL U205
Young's Defly
Zectran

Zolone
see Nitrofen
Picloram (potassium salt) plus mecoprop
Picloram (potassium salt) plus MCPA
Chlorinated camphene with 67-69 percent
   chlorine
No information available
see Triflurolin
o/t oft a-Trifluoro-2,6-dinitro-N,N-dipropyl-
   dipropyl-p-toluidine
No information available
S-[[p-Chlorophenyl)thio]methyl]
   o,o-diethyl phosphorodithioate
loxynil plus Dimexan, cycluron,
   BIPC, emulsifier, methyl alcohol,
   propionic acid, and solvent
   naphtha
see Dinoseb
No information available
No information available
Sodium N-methyl-dithiocarbamate
0-2,l»-Dichlorophenyl 0,0-diethyl
   phosphorothioate
No information available
see Lenacil
No information available
S-Propyl dipropylthiocarbamate
see Vernam
see Amitrole
No information available
A triazine
see Trithion
luDimethylamino 3»5-JCylyl methyl-
   carbamate
0,0-Diethyl S[(6-chloro-2-
   oxobenzoxazolin-3-yl)methyl]
   phosphorodithioate
2,U-Dichlorophenoxyacetic acid
2,U,5-Trichlorophenoxyacetic acid
                                C-U
-------
SELECTED WATER
RESOURCES ABSTRACTS

INPUT TRANSACTION FORM
                                                      W
 4  Title  WATER QUALITY CRITERIA DATA BOOK - VOL. 5 -
 EFFECTS OF CHEMICALS ON AQUATIC LIFE
 7. Author(s)

 Kemp, H. T.| Little, R. L.) Holcman. V. L.| Darby, R. L.
                                                       S. Report T>ate

                                                     "6.

                                                     " • $, Performim; Organization
                                                         Report No,
 Battalia Manorial Institute,  Columbus, Ohio
 Columbus Laboratories
                                                                   18050 HLJt

                                                                   . 13»> Tsse of Report and
                                                                   *       Covered
15. Supplementary Notes
   Environmental Protection Agency report number,  18050HLA09/73
16. Abstract
            Ibis report is an extensive compilation of data on the  effects of chemicals
 on aquatic life which were extracted from literature published during the period
 1968.1972.  It is an update  of an earlier report entitled "Water Quality Criteria Data
 Book, Volume III, Effects of Chemicals on Aquatic Life" (Kemp, et  al.,  1971).  The data
 are arranged alphabetically  by chemical and are concisely represented in a columnar
 format which Includes organism names, typo of study, chtmlr^i effect,  controlled
 parameters, significant comments  on the test, and source of the  data.   The data were
 compiled using a program prepared as part of the work.  (Llttle-Battelle)
 i?a. Descriptors Toxicity, Water pollution effects, Industrial wastes. Pesticides, Aquatic
 plants, Aquatic animals, Absorption,  Reviews, Marine fish, Freshwater fish, Chlorinated
 hydrocarbon pesticides, Carbamate pesticides. Phosphothioate pesticides. Organic acids,
 Antibiotics (pesticides), Heavy metals,  Metals.  Inorganic pesticides, Biochemical oxygen
 demand, Thiocarbamate pesticides, Triazine pesticides, Organophosphorus pesticides,
 Polychiorinated biphenyl
 Organic pesticides, Zoop
 Chlorophyta, Pyrrophyta,
 Aquatic Insects, Benthic fauna,          „               ,        .
 Marine animals, Newts, Toxins, Phenolic  pesticides, Dyes, Chemicals,
                             Nutrients. Urea pesticides. Organic cc
                             ankton. Aquatic algae, Marine algae,  Wat
                               ophyta, Crustaceans, Mollusks, Annelids,
                             .,  Invertebrates, Diatoms, Euglenophyta,  Frogs,
 17b.  Identifiers
 Anesthetics, Oil dlspersants, Eehlnoderms,  Macrolnvertebrates

 I7c. COWRR Field i Group   OJC, OJB,
 18. Availability
                                          Send To:


                                          WATCH MKSOUMCKS KIKNTIflC INFORMATION CENTER
                                          UJ. DEPARTMENT Of THE INTERIOR
                                          WASHINQTON. OX. *Ot4O
 Abstractor
Robert L. Little
iBatfeeUe's Columbus Laboratories,  Columbus, Ohio
WRSIC 102 (REV. JUNF 1971)
                                                         U. S. GOVERNMENT PRINTING OFFICE : 1974 720-125/511
-------