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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
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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 Ł050, 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.
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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.
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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.
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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
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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
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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
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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
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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.
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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
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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
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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
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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
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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
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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
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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.
30, January 1968, pp 137-lUo.
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
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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
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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
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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 57lŁ
(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
Łl (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
nlŁpo~
•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 •)
accumulated ODT-ci,
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
TDŁ 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
Ł-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
-------
Ł
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.
Ł
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 (HĄ)
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
------- | |