\
S WATER POLLUTION CONTROL RESEARCH SERIES 18050HLA 09/73
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 5580U
for the
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. Environmental Protection Agency
Washington, D.C. 20U60
September 1973
For sole by the Superintendent of Documents, 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. 68-01-000?, 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 Bioassay 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 Multivariate
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
kok M Street, S.W.
Washington, D.C. 2002U
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 TLm.
These were usually selected but other values were included when these
were not available. 96-hr TLm is designated as Tk to abbreviate this
notation. T2 was used for U8-hr TLm, and so on. When EC^o, LC5Q, and
LD5o were Judged to be essentially equivalent to TLm °r TL^o, 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 were 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 (qj
(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-12U9, UC-11,
June 1973, 2U8 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, 1967, P 1^7.AMIC-5758.
Johnson, D. W., "Pesticides and Fishes - a Review of Selected
Literature", Transactions of the American Fisheries Society, Vol. 97»
1968, pp 398-^25"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 Kins",
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, llU 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, 196ti,
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 HOb-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, March/
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-3768.
Anderson, J. M., Peterson, M. R.
"DDT: SUBLETHAL EFFECTS ON BROOK TROUT NERVOUS SYSTEM", Science, Vol. 16U,
April 25, 1969, PP WK)-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 331-33^.
AMIC-37b2.
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 1277-1253. 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. kf,
No. 2, March 1969, pp 163-166. AMIC-3«35.
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. 38A, 1971, PP 279-28U,
AMIC-3808.
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. , Matsumura, F.
"GROWTH RESPONSE OF BLUE -GREEN ALGAE TO AIDRIN, DIELDRIN, ENDRIN AND
THEIR METABOLITES", Bulletin of Environmental Contamination and
Toxicology, Vol. 6, No. 6, November /December 1971, pp 589-59^. AMIC-1U71.
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-
AMIC-5908.
Bender, M. E.
"THE TOXICITY OF THE HYDROLYSIS AND BRh^KDOWN 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-573L
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. if-, 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.
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 1*31 -W. 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-599U.
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 272-279. AMIC-545S.
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-3781.
Burton, D. T.
"LACTIC AND PYRUVIC 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, ^5 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 Vf-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^-R30^4~ 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-5M60.
Cooke, A. S.
"SELECTIVE PREDATION BY NEWTS ON FROG TADPOLES TREATED WITH DDT", Nature,
Vol. 229, January 22, 1971, PP 275-276. AMIC-381U.
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 1971,
pp 1877-1882.AMIC-3291.
Duke, T. W., Lowe, J. I., Wilson, A. J., Jr.
"A POLYCHLORINATED BIPHENYL (AROCLOR 125^) 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. AMIC-55ol
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Eaton, J. G.
"CHRONIC MALATHION TOXICITY TO THE BLUEGILL (LEPOMIS MACROCHIRUS
RAFINESQUE)", Water Research, Vol. k, October 1970, pp 673-68U. 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 1225-1234.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-R275.AMIC-^9.
Ferguson, D. E., Ludke, J. L., Finley, M. T., Murphy, G. G.
"INSECTICIDE-RESISTANT FISHES: A POTENTIAL HAZARD TO CONSUMERS",
Mississippi Acadeny of Science Journal, Vol. 13, 1967, pp 138-lUo.
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 1379-13^. AMIC-539.
Fredeen, F. J. H., Duffy, J. R.
"INSECTICIDE RESIDUES IN SOME COMPONENTS OF THE ST. LAWRENCE RIVER
ECOSYSTEM", Pesticides Monitoring Journal, Vol. 3, No. 4, March 1970,
pp 219-226. AMIC-53^.
Gardner, G. R., Yevich, P. P.
"HISTOLOGICAL AND HEMATOLOGICAL RESPONSES OF AN ESTUARINE TELCOST TO
CADMIUM", Journal of the Fisheries Research Board of Canada, Vol. 27,
No. 12, 1970, pp 2155-2193.AMIC-3527.
Garrison, R. L.
"THE TOXICITY OF PROJIOXFISH TO SALMONID EGGS AND FRY", The Progressive
Fish-Culturist, Vol. 30, January 1968, pp 35-38. AMIC-571U.
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Gibson, J. R., Ludke, J. L., Ferguson, D. E.
"SOURCES OF ERROR IN THE USE OF FISH-BRAIN ACETTLCHOLINESTERASE ACTIVITY
AS A MONITOR FOR POLLUTION", Bulletin of Environmental Contamination and
Toxicology, Vol. k, No. 1, 1969, PP 17-23. AMIC-37«3.
Gibson, J. R., Ludke, J. L.
"EFFECT OF SESAMEX ON BRAIN ACE1YLCHOLINESTERASE 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 2225-2232.
AMIC-3526.
Grosch, D. S.
"POISONING WITH DDT: SECOND- AND THIRD-YEAR REPRODUCTIVE PERFORMANCE
OF ARTEMIA", Pollution - Foundations for Today, Vol. 2, 1971, PP 8MJ5.
AMIC-2090.
Guthrie, J. E., Acres, 0. E.
"TOXICITY TO FISH OF TWO ORGANIC REACTOR COOLANTS", Bulletin of
Environmental Contamination and Toxicology, Vol. 5> No. 2, March/
April 1970, pp 1U5-151.AMEC-721.
Hanes, 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 62-6b.AMIC-5753.
Hansen, D.J., Parrish, P.R., Lowe, J.I., Wilson, A.J., Jr., Wilson, P.D.
"CHRONIC TOXICIIY, UPTAKE, AND RETENTION OF AROCLOR 125U 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-1U07.
16
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Hiltibran, R. C.
"A PROPOSED BIOCHEMICAL MECHANISM OF THE TOXIC ACTION OF DDT", Trans-
actions of the Illinois Academy of Science, Vol. 6^, No. 1, 1971,
pp 46-5^.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. U, 1971, pp 610-612.AMIC-3«2^.
Holland, H. T., Coppage, D. L.
"SENSITIVITY TO PESTICIDES IN THREE GENERATIONS OF SHEEPSHEAD MINNOWS",
Bulletin of Environmental Contamination and Toxicology, Vol. 5, No. ^,
July/August 1970, pp 362-367. 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 635-642. AMIC-3822.
Houston, A. H., Madden, J. A., Woods, R. J., Miles, H. M.
"SOME PHYSIOLOGICAL EFFECTS OF HANDLING AND TRICAINE ME THANE-SULPHONATE
ANESTHETIZATION UPON THE BROOK TROUT, SALVELINUS FONTINALIS", Journal of
the Fisheries Research Board of Canada, Vol. 28, No. 5, May 1971,
pp 625-633. AMIC-3823.
Rowland, R. M.
"INTERACTION OF ANTIMYCIN A AND ROTENONE IN FISH BIOASSAYS", The
Progressive Fish-Culturist, Vol. 31, January 1969, pp 33-3^. "AlttC-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., Dowden, 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, 1967,
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. U8, 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-3B20.
Kawatski, J. A., SchmullDach, 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 565-567. 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.) SPAV/NING IN WATER CONTAINING SMALL AMOUNTS OF PHENYLMERCURIC
ACETATE", Environmental Research, Vol. U-, No. U, October 1971,
PP 355-359. AMIC-2707.
Konar, S. K.
"TOXICITY OF HEPTACHLOR TO AQUATIC LIFE", Journal Water Pollution Control
Federation, Vol. U2, No. 8, Part 2, August 1970, pp R299-R303.
AMIC-WJ.
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-5435.
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 430-^37. AMIC-5453.
Konar, S. K.
"LETHAL EFFECTS OF THE INSECTICIDE DDVP ON THE EGGS AND HATCHLINGS OF THE
SNAKE JffiAD, CHANNA PUNCTATUS (Bl) (OPHIOCEPHALIFORMES: OPHIOCEPHALIDAE)",
Japanese Journal of Ichthyology, Vol. 15, No. 3* February 15, 1969,
pp 130-133. AMIC-6355.
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 1069-1571.AMIC-1253.
LaRoche, G., Eisler, R., Tarzwell, C. M.
"BIOASSAY PROCEDURES FOR OIL AND OIL DISPERSANT TOXICITY EVALUATION",
Journal Water Pollution Control Federation, Vol. U2, No. 11, November
1970, pp 19B2-19a9. AMIC-V4-5.
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 CLEAE LAKE ANIMALS", California Fish and Game. Vol. 55,
No. 3, 1969, pp 16U-178. AMIC-5521. ~~
18
-------
Lloyd, R., White, W. R.
"EFFECT OF HIGH CONCENTRATION OF CARBON DIOXIDE ON THE IONIC COMPOSITION
OF RAINBOW TROUT BLOOD", Nature, Vol. 216, December 30, 1967, pp 13^
AMIC-3721.
Loeb, H. A., Starkey, R. J.
"SURVIVAL OF BURIED BULLHEADS SUBJECTED TO U'-IODO-3->NITROSALICYLANILIDE",
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. 2?, No. U, 1970, pp 677-604.
AMIC-3770.
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-3039.
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, 1965, 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 1^96-1490.AMIC-044.
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 676-684. AMIC-5450.
Manion, P. J.
"EVALUATION OF LAMPREY LARVICIDES 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. 4, 1971, pp 599-607,
AMIC-3079.
19
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Marking, L. L.
"TOXIC ITY 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 510-51^
AMIC-5517.
Marking, L. L.
"TOXICITY OF RHODAMINE B AND FLUORESCEIN SODIUM TO FISH AND THEIR
COMPATIBILITY WITH ANTIMYCIN 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 1+18-14.19. AMIC-5U22.
Mawdesley-Thomas, L. E.
"TOXIC CHEMICALS - THE RISK TO FISH", New Scientist, Vol. U9, No. 73^,
January lU, 1971, pp 7^-75. AMIC-1056^
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. Ik, 1968, pp Il6-121~AMIC-5^75.
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 1553-1559. AMIC-3525.
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.
AMEC-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-1592T
McReynolds, H. E.
"PRACTICALITY OF ENDRIN AS A FISH TOXICANT", Indiana Academy of Science
Proceedings. Vol. 79, 1969, pp l^-lSl. AMIC-105.
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-1U95.
20
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Mlnchew, 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. AMZC-51*?!.
Mitchum, D. L., Moore, T. D.
"EFFICACY OF DI-JN-BUTYL-TIN OXIDE ON AN INTESTINAL FLUKE, CREPIDOSTOMUM
FARIONIS, IN GOLDEN TROUT", The Progressive Fish-Culturist, Vol. 31,
July 1969, pp 1U3-1W3. 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-1^52.
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. k, 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 11S3-11B5. 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 2^9-21*57- AMIC-3765.
Munson, T. 0.
"CHLORINATED HYDROCARBON RESIDUES IN MARINE ANIMALS OF SOUTHERN
CALIFORNIA", Bulletin of Environmental Contamination and Toxicology,
Vol. 1, No. k, April 1972, pp 223-223.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-1505.
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 551-508. AMIC-1^70.
Naqvi, S. M., Ferguson, D. E.
"LEVELS OF INSECTICIDE RESISTANCE IN FRESH-WATER 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. Ik, 1969, PP 121-127- AMIC-5979.
Nimmo, D. R., Blackman, R. R., Wilson, A. J., Forester, J.
"TOXIC ITY AND DISTRIBUTION OF AROCLOR 125 U 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 TOXICITIES 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-191^ 8o8.
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 'ALGISTAT1 TO FISH AND ALGAE",
Fishery Technology, Vol. 5, No. 2, July 1968, pp 101-103. AMlC-575^.
Patrick, R., Cairns, J., Jr., Scheier, A.
"THE RELATIVE SENSITIVITY OF DIATOMS, SNAILS, AND FISH TO TWENTY COMMON
CONSTITUENTS OF INDUSTRIAL WASTES", The Progressive Fjsh-Culturist, Vol.
30, January 1968, pp 137-1^0. AMIC-5720.
Pickering, Q. H., Thatcher, T. 0.
"THE CHRONIC TOXICITY OF LINEAR ALKYLATE SULFONATE (LAS) TO PIMEPHALES
PROMELAS, RAFINESQUE", Journal Water Pollution Control Federation, Vol.
U2, No. 2, Part 1, February 1970, pp 2^-3-2^. 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-1512.
22
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Rabe, F. W., Wissmar, R. C.
"SOME EFFECTS OF ANTIMYCIN IN AN OLIGOTROPHIC LAKE", The Progressive Fish-
Culturist, Vol. 31, July 1969, p 163. AMIC-5732.
Rachlin, J. W., Perlmutter, A.
"RESPONSE OF AN INBRED STRAIN OF PLATYFISH AND THE FATHEAD MINNOW TO ZINC",
The Progressive Fish-Culturist, Vol. 30, October 1968, pp 103-20?.
AMIC-5722.
Rachlin, J. W., Perlmutter, A.
"RESPONSE OF RAINBOW TROUT CELLS IN CULTURE TO SELECTED CONCENTRATIONS OF
ZINC SULFATE", The Progressive Fish-Culturist, Vol. 31, April 1969,
pp 9U-98. AMIC-57251.
Ragab, M. T. H.
"GAS CHOMATOGRAPHIC ANALYSIS OF MALATHION IN WATER AND IN FlSH",
Bulletin of Environmental Contamination and Toxicology, Vol. 3* No. 3,
1965, pp 155-163. AMIC-37201.
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-5433.
Reinert, R. E.
"PESTICIDE CONCENTRATIONS IN GREAT LAKES", Pesticides Monitoring Journal,
Vol. 3, No. U, March 1970, pp 233-2^0. AMLC-196.
Risebrough, R. W., Rieche, P., Peakall, D. B., Herman, S. G., Kirven, M. N.
"POLYCHLORINATED BIPHENYLS IN THE GLOBAL ECOSYSTEM", Nature, Vol. 220,
December lU, 1968, pp 1098-1102. AMZC-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-5733.
Sanders, H. 0.
"TOXICITIES OF SOME HERBICIDES TO SIX SPECIES OF FRESHWATER CRUSTACEANS",
Journal Water Pollution Control Federation, Vol. k2, 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
:MkCROCHIRUS)" Journal of the Elisna Mitchell Scientific Society,
Vol. 85, No. 4, 1969, pp 150-151. AMIC-5S3S.
23
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Shaw, T. L., Brown, V. M.
"HEAVY METALS AND THE FERTILIZATION OF RAINBOW TROUT EGGS", Nature, Vol.
230, No. 5291, March 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 499-50b.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 PROMELAS
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 PARAIABRAX CLATHRATUS
(GIRARD)", Bulletin of the Southern California Acadeny of Sciences, Vol.
67, No. 1, 1965, pp 49-5«.AMIC-59«0.
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 280-267. AMIC-5457.
Stout, V. F.
"PESTICIDE LEVELS IN FISH OF THE NORTHEAST PACIFIC", Bulletin of Environ-
mental Contamination and Toxicology, Vol. 3, No. 4, 1966, pp 240-246.
AMIC-37b4.
Tracy, H. B., Lee, R. A., Woelke, C. E., Sariborn, G.
"RELATIVE TOXICITIES AND DISPERSING-EVALUATIONS OF ELEVEN OIL-J5ISPERSING
PRODUCTS", Journal Water Pollution Control Federation. Vol. 41, No. 12,
December 1969, pp 2062-2069.AMIC-3834.
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 706-765.AMIC-3B19.
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. U3, 1969, pp 191-194. AMIC-5709.
Warnick, 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 1969, PP 280-254. 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-3287.
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-377U.
Weir, P. A., Hine, C. H.
"EFFECTS OF VARIOUS METALS ON BEHAVIOR OF CONDITIONED GOLDFISH", Archives
of Environmental Health, Vol. 20, January 1970, pp 45-51. 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-557L
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 438-443. AMIC-5452.
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-5708.
Woodhead, P. M. J.
"AN EFFECT OF THYROXINE 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. G., 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 Amy, Biomedical Laboratory, Edgewood Arsenal, Maryland,
Technical Report EATR U595, December 1971, P 12. AMIC-3233-
Young, R. G., St. John, L., Lisk, D. J.
"DEGRADATION OF DDT TVY GOLDFISH", Bulletin of Environmental Contamination
and Toxicology, Vol. 6, No. U, 1971, PP 351-35^.AMIC-379°.
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, U 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 SAIAR), LOBSTER (HOMARUS AMERICANUS), AND BEACH FLEA
(GAMMARUS OCEAN1CUS)", 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-^70. AMIC-3715.
26
-------
SECTION VI
APPENDICES
-------
Abbreviations for Appendix A
Note: Names of chemicals atid 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 = 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 = TLm, 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. ECjQ,
LCjQ, and similar designations for 50 percent lethality were all
considered as TI^ 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 = 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 AMIC-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
-------
>
Compound
*BS
ABS
»es
»BS
Acetaldehyd*
•cet aldehyde
»e«t aldehyde
Toxlclty, Experimental
Active Variables,
Field Field Ingredlentt Controlled
Orq»nls» Study Location Pp» or Noted Comments
Brachydanlo BSA —
rerlo
Leponls BSA,
•acrochlrus I
Nltzschla BSA, —
llnearls I
Physa BSAt
heterostropha I
Leoomls BSAi —
•acrochlrus I
Nltzschla BSA, —
llnearls I
Crangon BSA
crangon
32 (SB"») a.e, and
synthetic
i4 1 1 11 1 1 nn
a l i u T i on
• ater
17.1. (Tli) a«,e, and
synthetic
d 1 1 ut 1 on
xater
in ITS) a'.e, and
synthetic
dl tut Ion
Hater
3i».2 (Tl>) a'.e, and
synthetic
dilution
Hater
53
-------
water, and
dally
solution
renewal)
•eetlc acid
Leoomls
•acrochlrus
BSA,
L
75 (TU
>
Acetic acid
Acetic acid
Nitzschia
linear Is
Carclnus
•aenas
BSA,
L
BSA
(T5)
180 (TZ)
Acetic acid
Crangon
crangon
BSA
greater than
100 (TZ)
a*,e, and This study Has conducted to
synthetic determine the re I atIve' toxlclties of ?0
dilution common constituents of Industrial Hastes
Hater to a fish, an alqa, and an Invertebrate.
The experiments Here conducted over a
10-year period for varied purposes. The
authors recommend bloassays with at least
three components of the food web.
a»,e, and
synthetic
dilution
water
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
a«(contin-
uous aer-
ation, ssa-
water, and
daily
solution
renewal)
same as above
One hundred-forty surface active
agents, solvent emulslflers, pesticides,
.oolychlorlnated blohenyls, oure
Inorganic, and organic cheiricals 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 freshnater
organisms.
sane as above
Patrick, et
al (1968),
»HTC-57?0
Patrick, et
a I (1968),
AMIC-5730
Portaann, «t
al
(1971),AMIC-
7701
Portmann,
al (1971),
AMTC-7701
Acetone
Rasbora BCFA
heteronorpha and
BSA
It,000 (T?)
a',c,e,f,
hard(HH)
or soft
(SMI
synthetic
dilution
Hater, or
seawater
for some
species
One hundred sixty-four
pesticides, netting agents, and
miscellaneous water pollutants showed a
Hide range of toxlclty spanning 1? orders
of magnitude. Knowing the toxlclty and
percentage of alI 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 Hater
and sometimes the opposite Has true.
Testing the actual material as sold Has
Alabaster
(1969),
AMIC-51,25
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredientt Controlled
Compound Organis* Study Location Ppn or Noted Comments
Acvton* lepomls BSAt -- 8,300 (T**> &<*,£., and
macrochlrus I synthetic
dilution
water
Acttone Nltzschla BSA, — 11,1.93 (fit a», e, and
llnearls L synthetic
dilution
Water
Acetone Hercenarla I -- greater than
mercenarla 100.0 (T2)
(eggs)
found to be essential.
This study Has conducted to
determine the relative toxlcltles of ?0
common constituents of Industrial wastes
to a fish, an alga, and an Invertebrate.
10-year period for varied purposes. The
authors recommend bloassays with at least
three components of the food Heb.
same as above
The effect of 5? Dpstlcldes on
embryonic development of cla-ns and
ovstors Has reoortpd. Synprqlstlc
Reference
Patrick, et
al (1968),
AMIC-57?0
PatrlcH, et
al (1168) ,
AMIC-ST?O
0»v 1 s , et
al (1969),
AMIC-S990
Acetone
Acetone
Acetone
Mercenarla
nercenar1 a
(larvae)
Crassostrea
vlralnica
(eggs)
Phomldlun
••blguun
greater than
100.0 (T12)
greater than
100.0
0.5-10.0 (NTE)
effects nlth solvents were also reported.
Most of the compounds affected
development more thgn survival. Some,
however, drastically reduced larval
groHth. The authors point out the
necessity of evaluating the effects of
pesticides on all life stages of an
oraanlsm and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
shell fish.
same as above
same as above
Of 7i» chemicals evaluated as
alqlcides, only 9 were more toxic than
CuSOit. None inhibited growth of
nat-forwlnq algae for more than 2 weeKs.
Cu^CKt formulated with certain wetting
ao^nts xas more toxic than CuSOU alone.
Davis, etal
(1989) ,
AMIC-5990
Oavls, et
al (1969),
AMIC-5990
OttO
»MIC-8«
-------
Acrlf|«vlne
(neutral)
Moron*
saxatitls
(f Ingerlings)
BSA
vn
Acrlflavlne
Trachlnotus
carolinus
(luvenlle)
BSA
Aero I* In
Rasbora
heteromorpha
BCFA
and
BSA
Acrrlonltrlie
Crangon
crsngon
BSA —
Coooer chloramlne was also found to be
more toxic thar CuSOi». No wetting agents
were found to be Inhibitory at the
concentrations Invest Iqated (0.05 and
0.005 ppm). Also reported are (actors
affecting growth of algae In canals to
determine whether there were loads to
controlling aloae hy environmental
management. No practical environmental
means were found.
16.If (Tif) a,Cid,e,f, All compounds wore investigated Wellborn
p because of their probable usaqe In (1971),
hatchery production of white bass. AHIC-5571
Compounds that can be used at recommended
concentrations were ftquathol, Casaron,
Undone, and Terramycin concentrate.
Those that should not he used were
Acrlflavlne, flaylusclde. Malachite green
oxalate, and Malathlon.
im-118 (T<() a,c,e,f,l, In this study of poiioano salinity BIrdsong, et
and was controlled at lOi ?0» and 30 pot and a! (1971),
sul(ate, Invest I dated as a variable. ftcrlflavln, AMIC-5570
sodium, formalin, and potassium permanganate Her*
calcium, sIlQhTIv more foxlc at tho highest
potassium, salinity, while cooper sulfate xas
maqneslum, sllahtly l
-------
>
o\
Conoound
»c tutol
•c tusol
Actusol
Afl»toxln 01
Agrldlo
Toxlclfy,
Active
Field Field Ingredient,
Organls* Study Location Ppm
Steelh^aiJ BSA — ?it.O IT".)
trout
( ( Ingerl Ings)
Coho salmon BSA Hood Canal, 1.0.0 (K>
(f Inqerl Ings) In Hoodsport,
altu Wash.
Pacific BSA — ?0. 0-1.0.0 (S)
oyster
( 1 arvae)
Brachydanlo — — 1.0 (K)
rerlo (eggs)
Rasbora BCFA — 1.9 «T2)
heteromorpha and
BSA
Fxper 1 men ta 1
Var 1 ab IPS,
Control 1 ed
or Noted Comments
solution
renewal)
—
__
a'
a*,c,e, f ,
hard
(HW)or
soft {SHI
syn thet Ic
dl tut Ion
water, or
seawater
for some
species
oraanlsms. The authors noted that dost
published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
Evaluation of 11 oil dlspersant*
resulted In a ranking for each and a
recommendation for use according to the
ranking. Ranking Has based on toxlclty
and oil dispersal effectiveness. Corexlt
776<» appeared to have the least toxlclty
with fair to good oil dispersion
caoabi 1 1 ty.
same as above
same as above
This fungal toxin was acutely
toxic to Hrachydanlo rerlo embryos and
larvie, especially the latter. The
authors suggest this response as an
easily performed assay tor aflatoxln.
same as above
Reference
Tracy, et
a) (l^&g) .
AMIC-1831.
Tr acey , « t
al (1969) ,
AMIC-393<»
Tracy, et
al (1969),
AMIC-38JI.
AbedUet al
(1968) ,
AHIC-3717
Alabaster,
(1969) .AMIC-
5
-------
Aldrln (C-lt
labelled)
Aldrln (C-ll>
labelled)
Aldrln (C-K.
labelled)
Aldrln (C-l*
labelled)
Aldrln CC-1*
labelled)
Aldrln
Aldrln
Aldrln
Aldrln
Aldrln
AI dr 1 n
Aldrln
Hexaqenla
bl llneata
(nymph)
Chlronomus
so. (larva)
BCF
BCF
Oaohnla maqna BCF
(adult)
Hexagenla
blllneata
(nymph)
Chlronomus
so. (larva)
Fish (not
specified!
Tctalurus
punctatus
Wolffla
papulifera
Anacystls
nldulans
Agmenellum
quadrup-
licatura
Channa
punctata
Channa
punctata
BCF
BCF
FRLO Iowa
BSA
BSA
0.7 (residue) a*
0.5 (residue) a*
0.0001 (SB3) a*
0.0001 (SB3) a*
O.OOOKSB3) a*
greater than
0.001-0.01 (K)
0.91
(accunulatlont
SB)
1000 (K)
NTE
NTE
Hunter1a
medium
diluted
1:5
SM
a»,e»,r
SM
0.000166 (K Z a*,c
hr)
0.000333 (K 30 a',c.
mln)
food chain.
same as above
same as above
same as above
same as above
same as above
Approximate toxlcJtles of
numerous pesticides commonly used In
Rrltaln wpre summarized. An excellent
brief* general discussion of toxlclty
testing is also present.
Johnson, et
al (1471),
AHIC-3820
Johnson, et
al (1971),
AMrc-3820
Johnson, et
al (1971),
A1IC-3S70
Johnson., et
al (1971),
AMIC-3920
Johnson.et
a I (1971),
AMIC-3S30
Maudes! ey-
thomas
1056
Edible flesh of fish collected Morris, et
from rivers, lakes, ponds, and reservoirs al(1971),
was analyzed. Fish taken In areas AMIC-H52
receiving agricultural runoff shoned
highest accumulation, especialIv In
bottom feeding fish.
All compounds were harmful to Worthier, •*
duckweed to some degree. Decreased al (1971),
populations were noted at non-lothal AMIC-3233
concentrations and sone compounds
(Mf\lathian and 2,!4--D) caused teratocenic
effects at concentrations as low as 1 ppia.
Metabolic products of Aldrln, Batterton,
Dleldrln, and Endrln can be as toxic as et al (1971),
the parent compounds, as shown by 00 AMIC-Uj.?!
measurement.
same as above Batterton,
et al
(1971).AHIC-
11.71
Aldrln was shown to be more toxic Kathur (1969),
than POT, BHC, dleldrln, and llndane. AMXC-51i22
Behavioral responses prior'to death were
recorded In some detail.
same as above
Hathur
(1969),AMIC-
-------
>
Compound
Aldrln
Aldrln
Aldrln
Aldrln
Aldrin
* 1 dr 1 n
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppm or Noted Comments
Puntlus BSA — 0.000166 (K 1.5 a",c
sophore hr)
Puntlus BSA — 0.000133 (K 30 a",c
sophore mln)
Chlamydotheca BSCH — 0.00001-0.001
arcuata and (120-1700
A ppbresidue 6<«
»k)
Chlamydotheca BSCH — 0.0015 (Tl)
arcuata and
A
Ulothrlx sp. BSCH — 0. 00001-0. 001
(120-1700 opb
residue 33-<»8
wk>
Tublfex FL Belzonl, 3.0 (KITE)
tublfex and Miss.
BSA
same as above
same as above
The organisms were exposed to
O.ni and 0.1 cpb of the toxicants tor ?5
weeks after which time the amounts added
each week were increased ten-fold over
the Initial amounts. Ulothrlx occurred
spontaneously in the test tanKs. The
results show that chronic accumulations
In Ch 1 am ydo t heca exceeded levels which
were toxic in acute tests. Residues In
Chlamydotheca ranged from 12,000 to
260,000 times greater than the
theoretical concentrations In the watert
those in Ulothrlx were 235-3,000 times
exposure levels.
same as above
same as above
The response of
pesticide-resistant aauatic organisms to
various pesticides was compared to the
resoonse of non-resistant species.
R e f er ence
51.22
Mathur
( 1969) ,AMIC-
Hathur
(1959) ,A1IC-
5
-------
frtdrtn
H«re«nari»
•ercenarla
(eggs)
10.0 (TZ)
Aldrln
Alglstat
Alqlstat
Alglstat
Algistat
Algistat
Alglstat
»lkyl dimethyl
Denzytai»onlua
chloride
Hereenarla L
•ercenarla
I larvae)
Cyprlnus
carpio
Splroqyra
• ^^
Oselllatorla L
Anabaena
Mlcrocystls I
Buglena
Phoraldlua I
amblquun
O.«.l CT 12)
0.66 (K)
0.8 (K>
0.66 IK)
0.66 (K)
0.66 (K)
1.0 (N7E)
0.9-10.0
(33percent
qrowth
Inhibited !<.)
Th* effect »1 52 ttestleides on Davis, et al
embryonic development of clams and (1969),
oysters was reported. Synerqlstlc AMIC-5990
effects with solvents were also reported.
Host of the compounds affected
development npre than survival. Sonet
honevert drastically reduced larval
qroHth. The authors point out the
necessity of evaluatlnq the effects of
pesticides on all life staqes of an
orqanlsn and note the possibility of
selecting chemicals for pest control that
Mould not have serious effect on
shellfish.
same as above Davis, et al
(1969).AMIC-
5990
The results are described as Pal, et at
preliminary and the authors state that (1968),
further testlnq should be conducted AMIC-">75«»
before Alqlstat is used in hatcheries and
rearinq ponds.
sane as above
same as above
same as above
aama as above
same aa above
Pal, et al
(196BI,
AHIC-S7SI.
Pal, et at
(1968), AHIC-
575*
Pal, et al
(1968) ,
AHIC-575*
Pal, et al
(1968).
Of 7. No wetting aqents
Here found to be Inhibitory at the
concentrations Investigated (0.05 and
0..005 ppm). Also reported are factors
affecting growth of algae in canals to
Pal, et al
11968),
AKIC-575U
Otto (1970),
AMIC-89Z
-------
Field Field
CoBpound Organism Study Location
Alllden* dlacatate Phormlolun L
amb i guum
Allyl alcohol Hercenarla I
mercenarl a
(eggs)
Toxlclty,
Active
Ingredient,
Ppn
0.5-10.0 (NTE)
1.03 C.T2)
Exper Imental
Variables,
Con tro lied
or Noted Comments
determine whether there were leads to
controlling algae by environmental
management. No practical environmental
— same as above
The effect of 52 pesticides on
embryonic development of clams and
oysters was reported. Synerglstlc
effects with solvents were also reported.
Re f er ence
Otto(1970) ,
AMIC-892
Davis, .et al
11969) .AMIC-
5990
Allyl alcohol
Ally! alcohol
Mercensrla
mercenarla
(larvae)
Asterlas
rubens
BSA
less than 0.25
(T12)
10-33 (T3)
Allyl alcohol
Cardlum edule BSA
greater than
100
-------
• lpt»8-«»lno-2.6-
dlchlorobenzal-
doxlne HC1
crangon
Rasbora BCFA
heteromorpha and
BSA
100 (T?>
190 (T2)
• lpha-anlno-2,6 Rasbora
dlchlorobenzaldoxlne heteromorpha
BCFA
and
BSA
1.1.0 (T?)
AI in l«u»
Paralabrax
clathratus
FM
Scattergood 25 (dorsal
Steam Plant, muscle
Los residue)
Angeles,Cal.
Aluilnua
Paralabrax
clathratus
FM
Catalina 8 (dorsal
Island, Cal. muscle
residue)
uous aer-
ation, gea-
water, and
daily
solution
tt»,c,e,f,
hard
or soft
UW) syn-
thetic
dilution
water, or
seawater
for aone
species
a«,c,e,f,
hard (HW)
or soft
(SH)
synthetic
dilutIon
water, or
seawater
for some
species
One hundred sixty-four
pesticides, nettlnq aqents, and
miscellaneous water pollutants showed a
wide range of toxlclty scanning 12 orders
of maqnltude. Knowing the toxlclty and
percentage of alI components of a
formulation did not result In easy
predictability of the toxiclty 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 Mas
found to be essential.
same as above
al (1=171),
AMIC-7701
Alabaster
(1969),
Alabaster
(1969),
Fish collected fron an effluent
pipe of a steam plant and from offshore
waters of Catalina Island werp analyzed
for trace element content. Trace element
content of the effluent water was at
least 5 tlmos qreater 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 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 marine organisms.
same as above
Staoleton
(1968),AHIC-
5980
Staoleton
(196.8),
-------
Compound
A 1 UB 1 HUB
A 1 UB 1 nuB
A 1 UB 1 nuB
Aluminum
Alualnum
AlualnuB
A 1 UB 1 nuB
AluBlnuB
AluBlnuB
Aluminum
Orqanlsm
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
el athratus
Paral ihrax
cl athratus
Paral abrax
el athratus
(gravid
females)
Paralabrax
el athratus
Paral abrax
el athratus
Paral abrax
cl athratus
Paralabrax
el athratus
Paralabrax
cl athratus
Field
Study
FM
FM
FM
FM
FM
FM
FH
FH
FH
FH
Field
Locat Ion
Scat t erqood
Steam Plant,
Los
Angel PS, Cal .
Catal Ina
Island, Cal.
Sea 1 1 erqood
Steam Plant.
Los
Anqel es.Cal .
Catal Ina
Island. Cal.
Catal Ina
Island. Cal.
Scatter good
Steam P 1 ant .
Los
Anqel es.Cal .
Catal Ina
Isl and. Cal .
Scattergood
Steam Plant.
Los
Angeles. Cal .
Catal Ina
Island. Cal.
Scatterqood
Steam Plant,
Los
Toxlclty, Experimental
Aetlv* Variables,
Ingredient, Controlled
Ppm or Noted
Z5 (ventral
muscle
residue)
8 (ventral —
muse 1 e
residue)
?8 (gonads --
resl due)
38
(gonads
residue)
2? (gonads
residue)
78 (liver
residue)
( 1 Iver
residue)
69 (Integument — -
residue)
( Integument
residue)
16 (heart
residue)
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
Reference
ANIC-S9BO
S t ap 1 eton
(1968) ,
•MIC-S980
S taol eton
(1968) ,
AMIC-5980
S taol eton
( 1968) ,
AMIC-S980
S t a o 1 e t on
(1968).
AMIC-S980
Staol eton
(1968) ,
AMIC-5980
S t a o 1 e t on
(1968) ,
AMIC-5980
Staol eton
(1968),
AMTC-S980
Staoleton
(1968) ,
»MIC-"980
Staoleton
(1968) ,
4MIC-5980
Staoleton
(1968),
AMIC-S980
-------
Angeles,Cal.
AIu«Inun
Alualnu*
Aiinotrlazol*
»BltPOl-T
••ltrol-T
Aaltrol-T
Aaltrol-T
Paratabrax
clathratus
FM
Paralahrax FH
clathratus
Paralabrax
clathratus
Fish (not
specified)
Grassestr«a
virglniea
(eggs)
Crassostrea
ylrglnlca
(Iarvae)
Ganmarus
fasclatus
Paleonontes
KadlaKensls
FN
Catalina
Island, Cal.
Scattergood
Steam Plant,
Los
Angeles,Cal .
Cataltna
Island, Cal.
8S» ~
BSA
1.
(heart
residua)
33 (eyeball
residue)
3Z pesticides on
embryonic development of clams and
oysters Has reported. Synerqistlc
effects nlth solvents Here also reported.
Most of the compounds affected
development more than survival. Some,
however, drastically reduced larval
qrowth. The authors point out the
necessity of evaluatinq the effects of
pesticides on all life stages of an
orqanlstr and note the possibility of
selecting chemicals for pest control that
Hould not have serious effect on
shell fish.
same as above
Staoleton
(1968),
AMIC-^SO
Staoleton
(196S),
AHIC-5980
Staoleton
(1969),
AMIC-5980
Mawrtesley-
Thonas
(1971),»«IC-
1056
Davis, et
al(1969).
AMIC-S990
Of the aquatic weed herbicides
evaluated, Olclone was the most toxic,
Oaohnla was generally the most sensitive
organism. AlI of the Crustacea Here
affected by much lower concentration
levels of herbicides than Indicated by
the TL sub 50 values. All of the animals
represent Important food chain links.
same as above
Davis, etal
(1969),
AMIC-S990
Sanders
(1970),AMI
U53
Sanders
(1970),AHIC-
1.53
-------
>
Compound
••Itrol-T
Amitrol-T
Amltrol-T
Amltrol-T
Amltrol-T
Amltrol
Field Field
Organism Study Location
Asellus BSA
brev Icaudus
Orconectes BSA
nals
Daphnla naqna BSA —
Cyprldopsls BSA
vldua
tenon Is RSA —
macrochlrus
Crassostrea I —
vlrqlnlca
(eqqs)
Toxlclty,
Active
Tnqredlent,
Ppm
qreater than
100.0 IT2)
qreater than
100.0 (T2)
30.0 (T2)
32.0 (T2)
qreater than
100.0 (T2)
733.7 (T2)
Experimental
Variables,
Control led
or Noted Comments
a* same as above
a* same as above
a* same as above
a* same as above
a* same as above
The effect of 52 pesticides on
eirbryonlc development of clams and
oysters was reported. Synerqlstlc
effects with solvents were also reported.
9ef erence
Sanders
(1970) .AMIC-
1.53
Sanders
(1970) .AMIC-
Sanders
(1970) ,
Sanders
(1970) ,
AMIC-1.53
Sanders
(1970) ,«MIC-
1.53
Davis, et al
(1969) .AMIC-
5990
Aaitrol
Crassostrea
vlrglnlca
(Iarvacl
Ammonia (plus phenol Salmo 8SA
and zinc) galrdnerl
Most of the compounds at fpcted
developtrent mere than survival. Some,
nonever, drastically reduced larval
groHth. The authors point out the
necessity of evaluating the effects ot
pesticides on all life staqes of an
organism and note the possibility of
selecting chemicals for pest control that
Mould not have serious effect on
shell fish.
255.1. (Tm) —• same as nbove Davis, et al
(1969)tA«1IC-
5990
0.5-2.51. (T?) a,c*,d,e", Palnbox trout Here exposed to 8ro«n, et 11
f,» concentrations of fluctuating levels of (1969)«
amTionla, phenol, and zinc and to constant AMIC-5993
mixtures of the three* Tests with
fluctuating levels of toxicants showed
that LC50 values were similar to those
for constant concentrations as long as
the periodicity of the fluctuation did
not exceed the resistance time for the
poison. Except when zinc predominated In
the mixtures, the fractional toxlcltles
could be summed to give The toxlclty of
the mixture.
-------
AnBonla
A«onla
Salno BSA
qalrdnerl
Sal mo
galrdnerl
BSA
Anmonlum carbonate Phorraldium L
plus Copper aulfate
Aomonlum chloride
plus Copper sulfate
(liZ)
Fhormldiua
ambiguum
33.5-67.5 a,c»,d,e*
(fluctuating 1,n
cone, T 370-
greaterthan 700
inln)
25
Alabaster
(1969),
AMIC-51.35
Anonlun sultanate Rasbora
3,200 (Tl, pH a'.c.e.t,
same as above
Alabaster
-------
Field Field
Compound Organism Study Location
he teroii»orpha and
RSA
Aaaonlu* sulfanate Rasbora QCFA —
he t eromorpha and
BSA
A«onlu« sulfanate Rashora BCFA
heteronorpha and
8SA
Auoniu* (as NH3) Leoomls BSA, —
•acrochlrus L
A«»onlu« (as NH3) Nltzschla BSA, —
llnearls I
Toxiclty, Exnprlmental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
5.7) hard
-------
Ammonium (as NH1)
Amohenone B
AntlBony
Antimony
Antimony
Antimony
Antimony
Antimony
Antimony
Antlmycln A
Physa 8SA,
heterostrooha L
Lymnaea
staqnal Is
(adults)
90.0 (T<>)
10.0 (SB7)
a«, e,. and
synthetic
dilution
water
a»,q
Coregonus FL Moose Lake, 0.002
clupeaformls Can. (residue)
Coregonus
cluoeaformls
Esox luelus
Esox luelus
Esox luelus
Osmerus
fflordax
Perca
f lavescens
FL
FL
FL
FL
FL
FL
Lake
Ontario,
Can.
Moose Lake,
Can.
Lake St.
Pierre, Can.
Lake Erie,
Can.
Lake Erie,
Can.
Lake Erie,
Can.
0.003
(residue)
0.003
(residue)
0.00t»
(residue)
0.00".
(residue)
0.00
-------
Compound Organism
Antjaycln A Amla cafva
AntloycInA Sa 1 mo
galrdnerl
Antlnvcln A Sa 1 nt o t r*u T t a
>
i
I—1 Antlnycln A Salvellnus
03 Tontlnalls
Antlnycln 1 Salvellnus
namaycush
Anflaycln A Esox luelus
Antl«ycln A Carasslus
auratus
Flel d Field
Study Locat Ion
DSA, —
FO
BSA. —
FO
P ^ •
FO
BSA, —
FO
BSA, —
FO
RSA, --
FO
BSA, —
FO
Toxlcl ty,
Active
Inqred len t ,
Ppm
0.015 (60
Dercent K".l
0.0 000 3-0. 00 00 8
(Tli)
OaOO? (K3)
D. 00003-0. 00006
(Tl,)
0.00007 (Tl.)
0. 00011-0. 00055
(Tl,)
0.00070-0.001
(Tfc)
Experimental
Variables,
Control led
or Noted
succumbed to 0
toxlcantl only
0.0?5 ppm.
a,c,e,f,c, same as
doionized
water
a,o,o,r,c, same as
doionized
water
a,Ctetf,Q, same as
delonlzed
water
a,c,e,f,g, same as
deionizecl
water
a,c,e,f,q, same as
delonlzed
water
a,c, e, ( ,q, same as
delonlzed
Mater
tt»c,e,f,g, same as
deionized
water
Comments
.005 opm or less of the
certain catflshes survived
above
above
above
above
above
above
above
R eT er ence
Berqer, et
f\ (iqf.9) ,
AMIC-^l.95
Berqer, et
a 1 M96>4) .
AMIC-51.95
(1969) ,
AHIC-51.95
Berqer, et
at (1969),
AMIC-51,95
Berqer, et
al (1969),
AMIC-"^1;
Berqer, et
al (1969),
AMIC-5i.qS
Berqer, et
al (1969).
AHIC-5it95
Antl«ycln A
Chrosonus eos BSA,
0.00009-0.00052 a,c,e,f,q,
same as above
Berjer, «t
-------
Antlnycln A
Leoonls
glbbosus
BSA,
FO
0.00005-0.00021. a,C,e,f,E,
deionized
water
sane as above
Berger, et
a I (1969).
A«IC-5ii9S
Antlnyeln A
Leoomls BSA.
•acrochlrus FO
0.00006-0.0005 a,C,e,f,3,
deionized
wator
same as above
Bergert et
al (1969).
Antlnycln A
Antlnycln A
Antlnycln A
Leoomls
negalotls
BSA,
FO
Leoonls BSA,
•icroloohus FO
Hlcpooterus BSA,
dolonleul FO
0.00008 (T<«) a,c,e,f,g,
deionized
nater
0.00009 (T<>) a,c,e,f,q,
deionized
nater
0.0000<»-0.0000e a,c,e,f,g,
(Ti.) dilution
water
same as above
same as above
same as above
Berqer, et
al (1969),
AMIC-5V95
Berger, et
al (1969),
AMIC-5ii95
Berqer, et
al (1969).
AHIC-5A95
Antlaycln A
Mlcrooterus BSA,
salmoldes FO
0.00009-0.OOOli, a,c,e,f,s,
deionized
water
same as above
Berqer, et
al (1969).
AMIC-SI.9S
Antlaycln A
Antlcycln A
Pomoxls
nlgro-
maculatus
BSA, —
Perca BS»,
Tlavescens FO
0.001 (<>3
percent K)
a,c,e,f,G,
deionized
water
o.00003-0.oooiz a,c,o,r,e,
doionized
wator
same as above
same as above
Berger, et
al (1969),
AMIC-5«i9S
Berqer, et
al (1959),
Antlaveln A
Stlzostedlon BSA,
vltreum FO
0.00002-0.OOOOit a,c,e,f,g,
«Ti.) dilution
water
same as above
Berqer, et
a I (1969).
Antlaycln A
Antlaycln A
Aplodlnotus BSA,
grunnlens FO
Cyprlnus
earplo
BSA,
FO
0.00002-0.0001". a,c,e,f,C,
(Tl») deionized
water
0.00012-0.000<»3 a,o,o,f,g,
(T<>) deionized
water
same as above
sane as above
Berger, et
al (1969).
AHIC-51.95
Berger, et
a I (1969).
AMIC-5W95
-------
Compound
AntlB/cln A
Antlaycln A
Antlaycln A
Antlayeln A
1 Aritlvycin A
IV)
O
Antl»ycln A
Antl»ycln A
Antlaycln A
Antlaycln A
Antlcycln A
Antl«rcln A
Orqanlsn
Plirieohales
prone 1 as
Carplodos
cyorlnus
Catostomus
conmersonl
Ic 1 1 obus
cypr Inel lus
Ml ny tr ena
•e 1 anops
Ic t a 1 urus
catus
Ic talurus
•el as
Ic t al urus
punc t a tus
PI lodlctls
01 Ivarls
Eucalla
inconstans
Leoonls
cyanel lus
Field Field
Study Location
BSA, --
FO
BSA, —
FO
BSA, —
FO
BSAt ——
FO
BSAt
FO
BSAt — ~
FO
BSA, —
FO
BSAt —
FO
BSAt —
FO
BSAt —
FO
BSA, —
FO
Toxlclty,
Active
Ingredient,
Ppm
0.00006-0.00020
(Tl,)
0.003 m
0.005 IK".)
0.005 (Kii)
0.002 (K)
0.? (Kit)
0.021-0.088
(Tit)
0.0052-0.0105
(Tli)
0.? (>«•)
O.OOOOI.-0. 00055
(Tl»)
0.00011-0.0005
(T
Fxoer 1 men tal
Var 1 ab les.
Control 1 ed
or Noted
a,c, a,f ,2,
doionlzed
water
a.c,e,r,q.
delonlzed
water
a,c >e, f ,9,
del onl zed
water
del onlzed
water
del onlzed
water
delonlzed
water
a,c,e, f ,9,
delonl zed
water
a,c,e,f,g,
dilution
water
a,c,e,T,g,
delonlzed
water
aiC,e,f,c,
delonlzed
water
a,c,e,r,6,
deionlzed
water
Comments
same as above
same as abova
same as above
same as abovo
same as abovo
same as above
same as above
same as above
same as above
sane as above
sane as above
Reference
Berqer, et
al (1969) ,
ANIC-51.95
Perqer, et
al (19*9),
AMIC-51.95
Berqer, et
s \ (19(>9) ,
Ber qer , e t
a 1 (1969),
B er qer , e t a 1
(1969) ,
AMIC-51.91;
B cr QCP * f T
al (1969),
AMIC-51.91;
Berqer, et
al (1959),
AMIC-51.95
Berqer, et
al (1969),
AMIC-5U95
Berqer, et
al (1969),
AMIC-51.95
Berqer, et
al (1969),
AMIC-51.95
Berqer, et
al (1969),
AMIC-51.95
-------
FO
delonized
water
al (19691.
Antliycln A
Antlayeln A
AntlBvcln A
Sal >o
galrdnerl
Leponls L —
•acrochlrus
0.00003 mi
0.00016 mi
Sal BO clarm FL Copper Lake, 0.005 (K)
Idaho
Antlaycin A
Salno
galrdnerl
BSA
0.00005 (Tit) a*
Antl.ycln A
Antlaycln A
Aphltox
letalurus
punctatus
Lepomls
•acrochlrus
BSA —
BSA
Rasbora BCFA
heteronorpha and
BSA
0.011.7
0.0001«AHIC-
nlxed and furthermore appeared to have an 57?S
additive effect In cmblnatlon. That Is
both compounds were more toxic In the
presence of the other than alone.
same as above
a.Cid.e Rapid fish Kill occurred In a
ollgotrophlc situation and toxlclty
persisted for at least 10 days tot lowing
application. Plankton Has also reduced.
Later the lake Has successfully stocked
nlth cutthroat trout. The rapidity of
hill and persistence Indicated that the
AntlTiycln concentration was hlqher than
necp^sary. The authors recommended
further research.
The dyes Rhodamtne B and
Fluoresceln sodium Here found to be
relatively non-toxic In ppm
concentrations Hhlle antlmycln Has toxic
at ppb levels. The author states that
neither dye at field use concentrations
should significantly Influence the
activity of Antlmycln A aqalnst fish.
same as above
a* same as above
Hox I and
(1969).
AMIC-57Z5
Rabe, et at
(19691,
AMIC-5732
ao,c,e,f, One hundred sixty-tour
hard (HW) pesticides, Hettlnq aoents, and
or soft miscellaneous Hater pollutants shoned a
(SW) ayn- wide range of toxlclty scanning 12 orders
thotic of magnitude. Knowing the toxlclty and
water, or percentage of all components of a
aoawator formulation did not result in easy
for some predictability of the toxlclty of a
apeclea mixture of materials. Sometines
Marking
(1969).
AMIC-57J9
Marking
(1969),
•NIC-5729
Harking
(1969),
AHIC-5729
Alabaster
(1969),
ANIC-S«5
-------
no
ro
Compound
«HU*cl«n* 100
Ao.uecl«ne 100
Aquiclen* 100
»ou«cl«n«
Aquae lent
Aquathol
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organic* Study Location Pom or Noted Comments
Plmephnlvs BSA
pronel as
Plfflephales RSA
prone 1 as
Blochenlcal I --
oxygen denand
Cardlum edule BSA
Crangon BSA —
cr angon
Morone BSA —
saxatllis
species
25.0 (T>i) c.d.e.f
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal )
710 (U> a,c,d,e,r.
c
pesticides were most toxic In hard Nater
and sometimes the opposite was true.
Testing the actual material as sold was
tound to be essential.
Toxlclty of six oil spl 1 1
dlsoersants Has determined along with
BOO values. Pond water was used as
diluent and oil was Included In the
experiment. Oil markedly reduced
toxlclty of all dlsoersants. Data are
qlven as "most probable" "56-hr TL sub m.
same as above
same as above
One hundred-Tor ty surface active
aaents. solvent emulsltlers, pesticides.
po 1 yen 1 or 1 na t ed blohenyls, pure
Inorqanlc, and organic chenlcals 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
All compounds were Investigated
because of their probable usage In
S«f erence
Zll 1 Ich
(19S9) , AMIC-
?909
71 1 1 Ich
(1969) .AW.IC-
2909
71 1 llch
(1969) .AHIC-
2909
Portmann, «t
al (1971),
AHIC-7701
Por t minn, e t
al (1971),
AMIC-7701
Wellborn
(197D,
(finger!Ingst
hatchery production of white bass. AMIC-5571
Comoounds that can be used at recommended
concentrations were Aquathol, Casaron,
Llndane, and Terramycln concentrate.
Those that should not he used were
Acrlflavlne, Bayluscide, Malachite green
oxalate, and Halathlon.
-------
AQ
Nereis vlrens BSA
0.00011-0.000l»<> a»,c,e,
(TO and
synthetic
seawater
Arkotlrw DOT
Fundulus BSA
heteroclltus
Rasbora BCFA
heferonorpha and
BSA
0.0003Z-0.00035 a'.c.e.and
(Tit) synthetic
seawater
A laboratory procedure based on
Standard Methods for 96-hr toxlclty
determinations of crude oil and
oll-dlsperssnt mixtures Has described.
The dlsoersants varied considerably In
toxlcltyi ranging from 0.01 to 7.1 ml/1,
T150 for 96 hr. These did not differ
significantly from 2
-------
>
ro
Field Field
Compound Organism Study Location
Aroclor !?!,( Agonus BSA — •
eataphractus
Aroclor 121.8 Cardlua edule BSA —
Aroelor 12
-------
Aroclor 125"» (with Gammarus
corexlt 766i», oceanlcus
emulsion)
Aroclor 1351.
ra
V/l
»roclor
•roc lor 125<»
•roctor
Aroclor l?Si>
•roctor 135«>
Aroclor
Aroclor
Laqodon
rhomboIdes
(luvenlle)
Lelostomus
xanthurus
Lelostomus
xanthurus
Lelostomus
xanthurus
Lelostomus
xanthuPus
Lelostomus
xanthupus
Lelostonius
xan thupus
Lelostomus
xanthurus
BSA
BCFCH —
BCFCH «
BCFCH —
8CFCH —
BCFCH —
BCFCH —
BCFCH —
BCFCH —
0.01-0.10(thres a* (weeKly
hold solution
concentration) change,
seawateP >
sublethal bPnchlal edema at
concentPations doxn to D.19 DDI". The
author notes a oosslble synerqlstlc
effect between the two compounds.
same as above
0.005 (K
K.-15)
0.005 (K
H.-15)
o.ooi
salInlty
salInlty
a.
salInlty
0.001 (8.3 ppm a,
brain residue salinity
56 d)
n.OOt (>>6 ppm a,
qllls Pesldue salinity
56 d)
0.001 (13 Dom a,
heart Pesldue salinity
56 dl
0.001 (83 pom a,
liver pesldue salinity
56 d)
0.001 (65 Dpm a,
muscle residue salinity
56 d)
Exposure of spot and plntlsh to
this PCB Incpeased susceptibility to
disease as Hell as being toxic at .005
PDm. The compound was papidly stOPed In
tlssuesi pePslstlng fOP aoppoxlmately 3
mo. The authops recommended fupthep
chponlc exposure studies.
same as above
same as above
same as above
same as above
same as above
same as above
same as above
Wlldlsh
(1970).
AMIC-69
Hansent et
al (1971),
AHIC-1811
Hansen, et
al (1971),
ftMIC-lSll
Hansen,et at
(1971) ,
HMIC-1S11
Hansen, et
81 (1971),
&1IC-1811
Hansen, et
al (1971),
AMIC-1811
Hansen, et
al (1971),
AHTC-1811
Hansen, et
al (1971),
AHIC-1811
Hansen, et
al (1971),
AHIC-1811
APOCloP 125<>
APOCloP l?5«t
Lelostomus
xanthurus
Penaeus
duoraPu»
BCFCH —
L
(ACF)
0.001 (27 ppm a,
whole Body salInlty
pesldue 56 d)
1.0 ppb(K15, a»
Juvenl le)
same as above
In addition to mortality,
APochloP accumulation In shrimp
Hansen, et
al (1971),
AHIC-1811
Hlmmo, at al
(1971),
-------
Co«oound
Field Field
Organism Study Location
Toxlclty.
Active
Inqredlentt
Ppm
ExperImenta!
Variables,
Control led
or Noted
Comments
Ret erence
(fuvenlle)
Aroclor
Agonus BSA
ca t aphrac tus
>
ON
Aroclor
Cardlun edule BSA
heo*topancreas was marked (up to 510
PPM). The biological halt-lite tor this
chemical was found to he 17 days with
tissue distribution In the shrimp being
similar to that of ODT. Delayed
mortality with no prior poisoning
symptoms was also observed. Considerable
additional data are presented.
greater than 10 a«(contin- One hundred-forty surface active
(T2) UOU3 aar- aqents, solvent emulsltlers. Pesticides,
ation, sea-poIychI or 1nated blphenyls, pure
water, and Inorganic, and organic chemicals were
da.'ly evaluated against as many as ten marine
aolution organisms. The authors noted that most
renewal) published data of this type deal with
toxlclty of chemicals to treshwater
organ Isms.
same as above
AHIC-Z61.5
greater than 10 a«(contln_
uous aer-
ation, sea-
water, and
dally
solution
renewal)
Portmann, «t
al (1971),
AMIC-7701
Portmann, «t
al (1971),
AHIC-7701
»roclor
Crangon
crangon
8SA
3-10
a«(contin-
uous aer-
ation, aea-
watcr, and
daily
aolution
renewal)
sane as above
Portmann, at
al
(1971),AMIC-
7701
ArocloP
Parallchthys
so.
FM
Escanbla
Bay, Fla.
»..5-181,
(residue)
Pesldue analysis of dead and
dying animals led to the source of the
PCB which was an accidental leakage from
an Industrial clant. The concentrations
of the PCR In water and sediment were
less than 0.03-i»86 and less than 0.001
ppm, respectively. Bioassavs showed
Juvenile shrimp to be the most
susceptible species, but Inhibition of
shell growth of oysters Mas the most
sensitive parameter studied. Continued
surveillance and long-term testing at
subletral concentrations Mere pointed out
as urgently needed.
Duke, et al
(1970) ,
AMIC-730
-------
kroclor
»PoclOP 125i>
Apoclop 125*
Apoclop
ArocloP
APOCIOP 125<.
APOCIOP 125,
AMIC-720
Duke, et
ALU970),
AHIC-720
Duke, et at
(1970),AHIC-
720
OuKe, et at
(1970) ,
AMIC-720
Duke, et
ALI197D),
AMIC-720
Duke, et a I
(1970) ,
AMIC-720
Duke, et
AL(1?70),
AMIC-720
Duke, et al
(1970) ,
AMIC-720
Duke, et al
(1970) ,
AHIC-720
Duke, et al
(1970) ,
AMIC-720
Duke, et al
(1970),
AMIC-720
Duke, et al
(1970),
-------
ro
CD
Compound
Aroclor 1251.
Aroclor 125"»
Aroclor 125<,
Aroclor 1260
Aroclor 1260
Aroclor 1260
Aroclor 1262
Field Field
Organisn Study Location
Calllnectes F» Escambla
sapldus Bay, Fla.
Laqodon BSA —
rhomboldes
(Juvenile)
Penaeus BSA —
duorarum
(|uvenll«)
Aqonus BSA
cataphractus
Cardlun edule BSA —
Crangon BSA ~
crangon
Agonus BSA
cataphractus
Toxlclty, Experlmenta
Active Variables,
Ingredient, Controlled
Ppm or Noted
1.0-7.0
(residue)
0.1 (NTE)
0.01 (K2>
less than 10 a»( contln-
-------
Aroclor 1362
Cardlum edule BSA
less than 10
a«(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
sane as above
Portmann, et
al (1971),
AMIC-7701
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Alosa
pgeudo-
harengua
FL
Coregonus FL
irtedll
Coregonus FL
clupeafornls
Coreqonus FL
hovl
Prosoplun FL
cvlIndraceun
Great Lakes
- Superior,
Michigan,
and Erie
0.023(resldue) —
0.069(resldue)
O.OlMresldue) —
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes 0.063(residue)
- Superior,
Michigan,
and Erie
Great Lakes 0.0056(residue)
- Superior,
Trace element content of fish
from Lakes Superior, Michigan, and Erie
Has determined by activation analysis.
Whole body and liver residues were
determined. Concentrations varied with
species and lake. Other elements found
Heret antimony - 5 to 100 ppb, barium -
0.2 opm, cesium - 3 ppb, lanthanum - 1 to
20 ppb, mercury - 10 opb, rhenium - 0.5
to 5 ppb, rubidium - 0.06 to 6 ppn,
scandium - 2 ppb, selenium - 0.1 to 2
ppb, silver - 0*001 ppb.
same as above
Lucas, et al
(1970),
AMIC-3778
same as above
same as above
sane as above
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AHIC-3778
Lucas, et al
(1970),
-------
Compound
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Organism
Sa 1 vel Inus
nanaycush
Osmerus
mordax
Car ass 1 us
aura tus
Notropls
hudson 1 us
Pereoosls
onlscomaycus
Roccus
chrysoos
Perca
M avescens
St Izostedlon
vl treum
vl treum
Coregonus
cluoeaf orals
Field
Study
FL
FL
FL
FL
FL
FL
FL
FL
FL
Toxlclty, Experimental
Active Variables,
Field Ingredient, Controlled
Location Pom or Noted Comments
Mlchl qan,
and Erie
Grpat LaKes 0. OU9 (residue) — same as above
- Superior,
Mlchl qan,
and Erie
Great LaKes 0. 020 (residue) -- same as above
- Sup er lor ,
Mlchl qan, and
Erie
Great LaKes 0. 006 (residue) — same as above
- Superior,
Mlchl qan,
and Erie
Great LaKes 0. 0035 (residue) -- same as above
- Superior,
Mlchl qan,
and Erie
Great LaKes 0 . 025 (res 1 due) — same as above
- Superior,
Mlchl gan,
and Erie
Great LaKes 0 . 098 (residue) -- same as above
- Superior,
Mlchl gan, and
Erie
Great LaKes 0. 007 (residue) ~ same as above
- Superior,
Michigan,
and Erie
Great LaKes 0.098 (residue) -- same as above
- Superior,
Hlchl qan,
and Erie
Moose Lake, 0.09 (residue) — Concentrations of 13 toxic
Can. elements In dressed fish from heavily
Industrialized and non- Industrial Ized
Reference
AHTC-377H
Lucas , et
(1970) ,
AMIC-3778
Lucas, et
(1970) ,
AMIC-3778
Lucas, et
(1970) ,
AMIC-3778
L ucas , et
(1970) ,
AMIC-3778
Lucas, et
(1970) ,
AMIC-3778
Lucas, et
(1970) ,
AHIC-3778
Lucas, et
(1970) ,
AMIC-377S
Lucas, et
(1970) ,
AMIC-3778
Uthe,et al
(1971) ,
AMIC-3819
al
at
al
al
a 1
al
al
al
-------
UJ
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Arsenic
Asulua (K salt)
Coregonus FL
clupeaformls
Esox luclus FL
Esox luclus FL
Esox luclus FL
Osmerus
•ordax
FL
Perca FL
flavescens
Rasbora 8CFA
heteromorpha and
BSA
Lake
Ontario,
Can.
Moose Lake,
Can.
Lake St.
Pierre. Can.
Lake Erie,
Can.
Lake Erie,
Can.
Lake Erie,
Can.
0.7 (residue)
0.0? (residue)
0.09 (residue) —
0.0? (residue)
0.1? (residue) —
0.0? (residue) —
?,260 (Tl,
harduster)
Asulu* (K salt)
Rasbora DCFA —-
heteromorpha and
BSA
1,700 (Tl,
sottwater)
a*,e,e, f,
hard (HW)
or soft
(SH)
synthetic
dl lutlon
water, or
seaHater
tor some
soecles
a",c,e,t,
hard (HW)
or soft
(SH)
synthetic
d 11 u 11 on
water, or
seaHater
areas Here determined. Only mercury
exceeded regulatory limits, and
concentrations ot most elements Here
essentially the same In fish from both
areas.
sane as above
same as above
same as above
same as above
seme as above
same as above
One hundred sixty—four
pesticides* wsttlnq agents, and
miscellaneous water pollutants showed a
wide range o( 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 were most toxic In hard Hater
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
sane as above
Uthe, etal
(1971),
AMIC-3819
Uthe, et al
(1971),AMIC-
3819
Uthe, e.t
AL(1971),
»MIC-3819
Uthe, et al
(19711,AHIC-
3819
Uthe, et al
(1971).ftMIC-
3819
Uthe, et
AL(197l),
AHIC-3819
Alabaster(19
69) ,
AMIC-5',2?
Alabaster(19
69),
AHIC-5->2?
-------
I
UJ
ro
To«lclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Pom or Noted Comments
for some
soec les
Asuntol (sh««o dlo) Rasbor» 8CFA — 0.0T2) a»(contln- same as above
vonfagul uous aer-
ation, see-
water, and
daily
solution
renewal)
Reference
A 1 abaster ,
(1969) ,AHIC-
51.25
Portmann, et
al
(1971) ,»MIC-
7 /Q 1
Portnann, et
al (1971),
AMIC-7701
Portaann, et
al (1971),
AMIC-7701
•tlavar
Rasbora BCFA
heteroworpha and
BSA
1,300 (T2) a*,c,e,f, One hundred sixty-four Alabaster
hard (HW; pesticides, wetting agents, and (1969),
or sort miscellaneous water pollutants showed a AMIC-S
-------
Atrvzlne
Carclous
•aenas
BSA ~
greater than
100 (TZ)
Atrazlne
Cardlum edule BSA
greater than
100 (TZ)
I
(jO
O)
thetlc oT magnitude. Knowing the toxlclty and
dilution percentage of all conoonents 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 Has true.
Testing the actual material as sold Has
found to be essential.
ft*(contin- One hundred-forty surface active Portmann, et
UOU3 aer- agentsf solvent emulslflers< pesticides, at (1971),
ation, sea- Polychlorlnated blphenyls, pure AMIC-7701
water, and Inorganic, and organic cheirlcals Here
daily
ooluWon
renewal)
a»tcontin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
evaluated against as many as ten narlne
organisms* The authors noted that Host
published data of this type deal xlth
toxlclty of chemicals to freshwater
organisms.
sane as above
PortBsnn, et
al (1971),
AMIC-7701
Atrazlne
Crangon
crangon
BSA
10-33 (T2>
a«(contin-
uous aer-
ation, sea.
water, and
i^ily
solution
renewal)
same as above
Portmann, «t
al (1971),
AMIC-7701
Avadex BU
Rasbora
heteromorpha
BCFA
and
BSA
6 (TZ)
a»,c,e,f, One hundred sixty-four
hard (HW) P<*stlcldcsi Hettlnn aqents, nnd
or soft miscellaneous Hater oollutants shoxed a
(3W) ayn- "Me range of toxlclty soannlnq 12 orders
thetic of magnitude. Knowing the toxlclty and
dilution percentage of all components of a
water, or formulation did not result In easy
aeawater 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.
Alabaster
(1969).
AHIC-51.25
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Organism Study Location Pom
«v«d«x Rasbora BCFA — 8.2 synrhe
tic
dl lut Ion
Hater, or
seaioter
for some
species
— Approxlmatetoxlcltlpsof
nuTiprous pesticides commonly used In
flrl'talr Here summarized. An excellent
brief, general discussion of toxlclty
testing Is * 1 so present.
Pef erer.ce
Al abaster
(1969) ,
AMIC-SI^S
Mawrtes 1 ev-
Thomas(19ri)
AMIC-1056
>
-p-
»zlnphos»«thyI
Carclnus
naenas
BSA
*zlnohos>ethvl
Cardlun edule BSA
0.033-0.1 (T2> a-i;-(contln- One hundrert-T or tv surface active
uoua aer- aaents, solvent emulslflers, pesticides,
atian, ae£' no IychlorlnatPd blphenyls, pure
water, and Inorganic, and organic cheirlcals 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.
greater than 10 a«(contin-
(T2) uoug aer-
ation, sea-
water, and
daily-
solution
renewal}
same as above
Portmann, «t
al (1971),
AMIC-7701
Portmann, «t
al (1971),
AMIC-7701
Ailnphos»ethy)
Crangon
crangon
BSA —
0.0003-0.001
(TZ)
a«( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, «t
al U971),
AMIC-7701
Allnphos««thy I
Llaanda
BSA
0.01-0.03 (T2) at(oontin-
same as above
Portaann, «t
-------
llmanda
uous aer-
ation, gea-
water, and
daily
solution
renewal)
at (1971),
AHIC-7701
A*lnDhos«9thyI
Pandalus
montagul
BSA
Azlnphos Methyl
Rasbora BCFA
heteromorpha and
BSA
0.0003-0.001
(T3)
O.D76 (TZ)
same as above
U)
VJ1
Bacterial endotoxlns Salmo
qalrdnerl
(1,00-500 q)
10 (NTEt
Bacterial endotoxlns Oncorhynchus
hlsuteh
(1.00-500 9)
Bal»n
Ganmarus
Tasclatus
BSA
10 (NTE)
1.1 tT
-------
Compound
Drqanlsn
Field Field
Study Location
Toxiclty,
Active
Ingredient,
PDA
Experimental
Variables,
Control Ied
or Noted
Comments
Re ference
Banner OG01
Crangon
crangon
BS* ~
10-33 (T?)
Banner OCO?
Crangon
crangon
BSA
10 (T2)
represent important food chain llnKs.
a«(contin- One hundred-forty surface active
uous aer-- aqents, solvent emulslflers, pesticides,
ation, pea- ool ych lorln<»ted blphenyls, pure
water, and inorganic, and organic chemicals Mere
daily evaluated against as many as ten marine
solution organisms. The authors noted that nost
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
a«(contin-
uous aer-
ation, sea-
wator, and
daily
solution
renowa.3.)
same as above
Portaann, et
al (1971),
AMIC-7701
Portmann,
al (l,c,e,f. One hundred sixty-four Alabaster
ham (HW) pesticides, wetting agents, and (1969),
or miscellaneous water pollutants showed a AMIC-5t?5
SOFT(SM) wide range of toxicity spanning 12 orders
synthetic ot magnitude. Knowing the toxlclty and
dilution percentage of.all components of a
-------
Bar luii
Barlue
8arlu»
Barlua
Barlue
Berlue
BarluB
Paralabrax
clathratus
Papalaf-rax
clathratus
Paralabrax
clathratus
(gravid
females)
FM
Paralabrax FM
clathratus
Paralabrax FM
clathratus
Paralabrax FM
clathratus
Paralabrax FM
clathratus
FM
FM
Scattergood 2 (dorsal
Steam Plant, muscle
LosAngeles, residue)
Cal.
Catallna 1.7 (dorsal
Island, Cal. muscle
reaidue)
Scattergood l.U (ventral
Steam Plant, muscle
LosAnqetes, residue)
Cal.
Catallna 1.3 (ventral
Island, Cal. muscle
reaidue)
Scattergood 7.8 (gonads
Steam Plant, residue)
LosAnqeleSt
Cal.
Catallna Z.6
Island* Cal. (gonads
reaidue)
Catallna 2.2
Island, Cal. (gonads
reaidue)
water, or formulation did not result In easy
seanater predictability of the toxlclty of a
for some mixture of materials. Sometimes
species pesticides Here most toxic In hard water
and sometimes the opposite Has true.
Testing the actual material as sold was
found to be essential.
Fish collected from an effluent
ploe of a stenm plant and from offshore
waters of Catallna Island were analyzed
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, 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.
-- same as above
same as above
same as above
sane as above
same as above
same as above
Staoleton
(1968).
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(196S),AHIC-
5980
Sfaoleton
(1968),
AMIC-5980
Staoleton
(19*8),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
-------
Coaoound
Barlua
Barlua
Barlua
Bar 1 ua
Barlua
Barlua
Barlua
Barlua
Basol A 06
Organism
Paral abr ax
c 1 athr at us
Parat abrax
el athratus
c 1 athratus
c 1 athratus
Par al abr ix
cl athratus
Paral ahrax
el athrafus
Paral abrax
cl athratus
Paral abrex
cl athratus
Cr anqon
cranqon
Field Field
S t udy Locat 1 on
FN <>c»tt*rqood
Steam Plant,
LosAnqeles,
Cat.
FN Cat*l Ina
Island, Cal.
Steam Plant.
Cal.
FN C a t a 1 1 na
Tsl and, Cal .
FN Sea 1 1 arqoorl
rtoam Plant,
LosAnqe les.
Cal.
FN Catallna
Tsl and, Cal.
FN Scatferqood
Steam Plant,
LosAngeles,
Cal.
FN Catal Ina
Island, Cat.
BSA —
Toxlel ty.
Active
Ingredient,
Ppm
I.I, (liver
residue)
1.4
(liver
raaldua)
residue)
It
. Q
(In tegument
reildua)
1.? (heart
residue)
7
(heart
residue)
5.8 (eyeball
residue)
9.1
(eyebal 1
residue)
10-33 (Te)
f xoerlmental
Variables.
Control led
or Noted Comments
-- same as above
same as above
—
— same as above
same as above
same as above
same as above
Qit(contln- "n« hundred-forty surface active
uoua aor- aq»nts, solvent enuls 1 f 1 ers, pesticides.
ation, sea- oo\ ych lorln»t»d blohenyls, our*
wator, and Inorganic, and organic ch«»lcals were
solution organisms. The authors noted that most
renewal) published data of this tyoe deal with
toxlcity of chemicals to freshwater
organisms.
Reference
S tao leton
(1968),
AMIC-S980
S t o o 1 1» t on
(19fiS) .
AMTC-S9DO
S t n o t *t t on
ANIC-1980
(19M) ,
AMIC--5980
S t n D 1 • t on
(116B) ,
AMIC-S980
S taoleton
(196A) ,
AMIC-«;980
S taol eton
(1968) ,
AMIC-59BO
S t a o 1 e t on
(196B),
ANIC-S980
Portmann, at
al
119711, ANIC-
7701
-------
Basol 99
Rasbora BCFA
heteronorpha and
BSA
«.? (T2,
hardwater)
Basol 99
Rasbora BCFA
heteromorpha and
BSA
32 (T2,
softwater)
>
I
VO
Bayer 39007
Rasbora BCFA
heteronoroha and
BSA
14 (TZ,
harduster)
Bayer 39007
Rasbora BCFA
heteromoroha and
BSA
7.5 (T2,
sottwater)
BayI use Ida
Horone
saxatllls
(fIngerlInqs)
BSA
0.78 (T3)
a*,c,e,f,
hard (HW;
or soft
ISV) syn-
thetic
dilution
water, or
seawater
for some
species
a*,c,o,f,
hard (HW)
OP soft
(SW) syn-
thetic
water, or
seawater
for some
apocles
a*,c,e,f,
hard
(HH)or
soft (SHI
synthetic
dilution
water, or
seawater
for some
species
a*,c,e,f,
hard
(HW)or
soft (SW)
synthetic
dilution
water, or
seawater
for some
species
a,c,d,e>t,
P
One hundred sixty-four Alabaster-
pesticides, wetting agents, and (1969),AHIC-
mlsce I laneous water pollutants showed a 5i»?5
wide range 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 were most toxic In hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential*
sane as above
Alabaster
(1969).
sane as above
Alabaster
(1969),
AMIC-5«5
same as above
Alabaster
(1969),
All compounds were Investigated Wellborn
because of their probable usage in (1971),
hatchery production of white bass. 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
slmul ans
Channel
catf Ish
Roecus
saxat 1 1 Is
Oragonf 1 les
( larvae)
Whirl Iglg
beetles
BacksHlmners
Ictalurus
punctatus
Toxlcl ty.
Active
Field Field Ingredient,
Study Location Ppm
FP Pratt, 0.1 (K
Kansas
FP Pratt, 0.1 (Kit)
Kansas
FP Pratt, 0.1 (NTE
-------
Baytex
Beytex
Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Baytex
Ictalurus
•el as
Carasslus
auratus
Cyprlnus
carplo
Pimeohales
promelas
lepomls
naerochlrus
Leoomls
mlcrolophus
Mleropterus
salmoldes
Sal mo
galrdnerl
BSA
BSA
BSA
BSA
BSA
BSA
BSA
BSA —
Salmo trutta BSA
Oncorhynchus BSA
Klsuteh
Perca
flavescens
BSA
1.62 (Tit)
3.1)0 (Tit)
1.16 (Tit)
Z.itlt (Tit)
1.38 (T
-------
Compound
Field Field
Organlsn Study Location
Toxlclty,
Active
Ingredient,
Ppm
Experimental
Variables*
Controlled
or Noted
Comments
Reference
het*ro«orph» and
6SA
Benvzolln
Basbora
heteronorphB
BCF»
end
BS»
325 (T2)
BensulIde
Gannarus
fasclatus
BSA
l.i, (T
-------
>
BHC tolus llndane) Chain
Pickerel
residue (SB)
FRL Misc. states 0.07
residue (SB)
BHC Colus llndane) Hhlte catfish FRL Misc. states O.Z3 residue
(SB)
BHC (plus llndane) White perch FRL Misc. states 0.18-0.26
residue (SB)'
BHC (plus llndane) Goldfish FRL Misc. states 0.51 residue
(SB)
BHC folus llndane) PuwpkInseed FRL Hlsc. states 0.09 residue
(SB)
BHC (plus llndane) Largenouth FRL Misc. states 0.01-0.".7
bass residue (SB)
BHC (plus llndane) Brown FRL Misc. states O.Ol-ti.37
bullhead residue (SB)
BHC (plus llndane) Carp
BHC (plus llndane) Channel
catfish
FRL Misc. states 0.01-0.99
residue (SB)
FRL Misc. states 0.01-1.SO
residue (SB)
BHC (plus llndane) Redhorse FRL Misc. states 0.02-0.10
sucker residue (SB)
sane as above
sane 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
et al
(1971),
AMIC-1I>07
Henderson,
et al
(1971),
AHIC-li.07
Henderson,
et al
AMIC-1U07
Henderson,
et al
(1971) ,
AMIC-l
-------
Compound
Organism
Field Field
Study Locat1 on
ToKlclty,
Active
Ingredient,
Ppm
Exper1menta ?
Variables,
ControI Ied
or Noted
Comments
Refer ence
BHC (plus llndane) Gl77ard shad FRL Misc. states 0.06-0.10
residua (SB)
same as above
Henderson,
et al
(1971) ,
AMIC-11.07
BHC (olus llndane) Spotted
sucker
FRL Misc. states 0.01-0.03
residue (SB)
same as above
H en derson,
e t al
(1971),
AMIC-l"t07
BHC (olus llndane) Bluet)! Ms
BHC (olus llndane) Striped
*ul let
FRL Misc. states 0.01-0.02
resldue(SB)
FRL Misc. states O.ZS-1.1".
residue (SB)
BHC (olus llndane) Rlue catfish FRL Misc. states O.lfc residue
(SB)
BHC (olus llndane) Rock bass FRL Misc. states O.Ol-O.li.
resldue(SB)
BHC (olus llndane) Freshxater FRL Misc. states 0.01 residue
dru« (SB)
BHC (olus llndane) Bloater
BHC (olus lindane) Lake
HhltefIsh
BHC (plus llndane) Lake trout
FRL Misc. states 0.03-0.08
residue (SB)
FRL Misc. states 0.06
resldue(SB)
FRL Misc. states 0.01-0.01
residue (SB)
same as above
same as above
same as above
same as above
sane as above
same as above
same as above
same as above
Henderson,
et al
(1971),
«MIC-1<«07
Henderson t
et al
(1971) ,
AMIC-1<.07
Henderson,
et al
(1971) ,
AHIC-li.07
Henderson,
et al
(1971),
AMIC-1<|07
Henderson,
et al
(1971),
AMIC-H07
Henderson,et
al (1971),
AMIC-1<(07
Henderson,et
al (1971),
AMIC-1«.07
Henderson,
et al
-------
>
BHC (plus llndsne) Hhlte crapple FRL Hlsc. states 0.07-2.19
residue (SB)
BHC (plus lindane) Blqmouth FRL Hlsc. states 0.03-0.07
buffalo residue (SB)
BHC (plus llndane) Small mouth FRL Hlsc. states 0.08 residue
buffalo (SB)
BHC lolus lindane) Ftathead FRL Hlsc. states 0.0? residue
catfish tSB)
BHC (plus llndane) Goldeye
BHC (plus llndane) Halleve
BHC (plus llndane) Sauqer
FRL Hlsc. states 0.03-0.08
residue (SB)
FRL Hlsc. states 0.01 residue
(SB)
FRL Hlsc. states 0.01 residue
(SB)
BHC (plus llndane) Marine I mouth FRL Hlsc. states 0.02 residue
sucker (SB)
BHC (plus llndane) BlacK
bulI head
FRL Hlsc. states 0.01 residue
(SB)
BHC (plus llndane) White bass FRL Hlse. states 0.01 residue
(SB)
BHC (plus llndane) BlacK crapple FRL Hlsc. states 0.01-0.03
residue (SB)
sane as above
same as above
same as above
sane as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
(1971),
ftHIC-K.07
Henderson,
et al
(1971),
AMIC-1V07
Henderson,
et al
(1971),
AHIC-l«t07
Henderson,
et al
(1971),
AMTC-1I.07
Henderson,
et al
(1171),
AMIC-1U07
Henderson,et
al (1971),
AHIC-l
-------
Compound
Field Field
Organise Study Location
Toxlclty.
Active
Ingredient,
Ppm
Exoerlmental
Variables,
Control led
or Noted
C omments
Reference
BHC (Dlus llndane) Largescale FRL Misc. states 0.01-0.12
sucker residue (Sfl)
same as above
Henderson,
et al
(1971),
AMIC-l"i07
BHC (plus llndane) Small mouth
bass
Misc. states 0.01 residue
(SB)
same as above
Henderson ,
et al
(1971) ,.
BHC (Dlu* llndane) Northern FRL Misc. states 0.01 residue
squa»»lsh (SB)
same as above
Henderson,
e t al
(1971) ,
>
I
BHC (Plus llndane) Chisel mouth FRL Misc. states 0.03-0.03
residue (SB)
BHC (plus llndane) Rainbow trout FRL Misc. states 0.01 residue
(SB)
BHC (Dlus llndane) Brldgello FRL Misc. states 0.02 residue
sucher (SB)
BHC (Dlus llndane) Arctic
gray I 1ng
BHC (Dlus llndane) Round
xhltetlsh
FRL Misc. states 0.12 residue
(SB)
FRL Misc. states 0.0,c,d,e, (
same as above
Henderson,
et al
(1971),
AHIC-1I.OT
Of the pesticides Investigated, Bhatls
-------
BHC
Carclnus
maenas
BSA
greater than
100 IT2)
the most toxic Has Klofos followed in (1971),
decreasing order by Sumlthlon, Malathlon, AHIC-5ir23
Formlthlon, Olmecron, Sevln, and BHC. The
author cites the need for more selective
pesticides nontoxlc to fish or
antagonistic agents for reducing fish
toxlclty.
a*(contin- One hundred-forty surface active Portmann, et
uoua aer- agents, solvent emulsiflers, pesticides, al (1971),
ation, sea-Polychlorlnated blphenyls, pure
water, and Inorganic, and organic chemicals Mere
fiaily evaluated against as many as ten marine
solution organisms. The authors noted that nost
renewal) published data of this type deal Kith
toxlclty of chemicals to freshwater
organisms.
BHC
Cardlun edule BSA
greater than 10 a*(contin-
(T2) uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
AMIC-7701
Portmann, et
at (1971),
AMIC-7701
BHC
Crangon
crangon
BSA
0.001-0.003
(T2>
a-K-t contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, et
al (1971).
AMIC-7701
Bis hydroxyaethyl)
phosphlnlc acid
Plmephales
prose las
BSA
Bis (dlKCthyl thlo Phoraldluti
carbonoyl) dlsulflde a«blguu»
.29.0 ITI») a«,d,e,O, Malathlon and Its hydrolysis Bender
and Fe products Here evaluated with the finding (1969),
that one such product (dlethyl fumarate) AHIC-3787
was more toxic than Malathlon to fathead
minnows. Synerglsm occurred between
Malathlon and two products of hydrolysis.
Continuous exposure resulted In
Increased toxlclty.
0.5-10.0 -- Of 7i» chemicals evaluated as Otto (1970),
(f>6percent alglcldes, only 9 were more toxic than AMIC-S92
growth CuSOit. None Inhibited growth of
Inhibited m mat-forming algae for more than 2 weeks.
CuSO
-------
Comoound
Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient,
Ppn
Experimental
Variables,
Control led
or Noted
Comments
Reference
Bis Itrl-n-butyl) Phormldlm
tin oxide aeblguun
Borasceu
>
Salao
galrdnerl
BCFA
and
BSA
Bourbon
Betta
SPlendens
BP 1002
Carcinus
•aenas
BSA ~
more toxic than CuSOii. No wetting aqents
Here found to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 com). Also reported are factors
affectlnq growth of algae In canals to
determine Hhether there were leads to
controlling algae by environmental
management. No practical environmental
means Here found.
0.5-10.0 (100 — same as above Otto (1970),
percent AMIC-892
growth
inhibited 14)
1,800 a*,c,e,f. One hundred sixty-four Alabaster
hard (HH) pesticides, netting agents, and (1969),
or miscellaneous water pollutants showed a ANIC-5<>25
SOFT(SH) wide range of toxlclty scanning 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.
Testing the actual material as sold was
found to be essential.
2850 (SB 6 hr) a' The effects of ethanol and Ravnes, etat
bourbon on the aggressive response of
S4amese lighting fish were determined. (1968),AMIC
Ethanol Increased all I show 5712
(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
-------
BP 1002
Card!urn edule BSA
33-100
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, gea-
wator, and
daily
solution
renewal)
same as above
Portmann, «t
al (1971),
AMIC-7701
BP
Cranqon
cranqon
BSA
3.3-10
as(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (197D ,
AHIC-7701
BP 1002
Llmanda
llmanda
BSA
10-33 (T2)
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portaann, et
al (1971),
AHIC-7701
BP 1002
Ostrea edulis BSA
33-100
a«( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, et
al (1971),
AHIC-7701
BP 1002
Pandalus
montaqul
BSA
3.3-10 (T?)
a*(contin-
uous aer-
ation, sea-
vater, and
daily
solution
renewal)
same as above
Portraann, et
31 (1971),
AHIC-7701
BP 1100X
Agonus BSA
cataphractus
greater than
10,000 (Ti.)
a*(contin-
uous aer-
same as above
Portnann, et
al (1971),
-------
I
VJ1
O
Toxlelty,
Active
Field Field Ingredient,
Compound Organism Study Location Ppm
> 1100X Cardlun edule BSA — greater than
10,000 (T<()
' 1100X Crangon BSA — greater than
crangon 10, 000 (ft)
> 1100 Agonus BSA — 1000-3300
cataphractus
• 1100 Cardlun edule BSA — 1000-3300 (T2)
1 1100 Crangon BSA — greater than
crangon 3300 (T3)
Exper I men ta 1
Var I ahl es,
Con tro 1 led
or Noted Comments
ation, sea-
water, and
daily
solution
renewal )
a*lcontin- same as above
uoua aer-
ation, sea-
water, and
daily
solution
renewal)
a* (con tin- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal)
a*lcontin- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal )
a*(contin- same as above
uous aer-
ation, sea-
water, and
dully
solution
renewal )
a*(contln- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal )
Reference
AHIC-7T01
P or t mann.
al (1971)
AMIC-7701
Por t mann.
al (1971)
AHIC-7701
Por t mann.
al (1971)
AMIC-7701
Por t nann.
al
eT
,
• t
•
et
t
et
(1971) , AMIC-
7701
Port»ann,
al (1971)
AMIC-7701
et
*
-------
BP
Fundulus
heteroclItus
BSA
0.00001-0.00022 a*,c.e,and
(Ti») synthetic
seawater
6P
Brahontrole
Nertls vlrens BSA —
Rasbora 8CFA
heteronorpha and
BSA
0.00001-0.00017 a*,e,e,
) and
synthetic
seanater
62 (T2>
a*,c,e,f,
hard (HH)
or
SOFT(SH)
synthetic
dilution
water* or
seawater
for some
species
Broaln*
Coregonus
ctupeatormls
FL
Great Lakes
- Superior,
Michigan,
and Erie
O.l(rasldua)
Bronlnc
Bro'lne
Coregonus FL
hoyl
Prosoplun FL
cyIIndraeeun
Salvellnus FL
namaycush
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
O.OKresldue)
O.SIresldue)
O.S(resldue)
A laboratory procedure based on
Standard Methods for 96-hr toxlclty
determinations of crude oil and
oll-dlspersant mixtures Has described.
The dlspersants varied considerably In
toxlclty, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr. These did not differ
significantly from 2UO hr values. The
dlspersants Here designated as CX, 00,
Cl, OH, AO, PC, MM, TN, BP, and NA xlth
no further description of their chemical
nature or source. Only a fen bloassays
Here conducted Hlth shrimp. HotlusKs and
echlnoderms Here suggested as suitable
test animals. The authors stated that
the method could be used to test any
product for toxlcity In seaHater.
same as above
LaRocne, et
al (1970),
AMIC-l»li5
LaRocne.et
al (1970),
AMIC-«.it5
One hundred sixty—four Alabaster
pesticides, netting agents, and (1969),
miscellaneous water pollutants shoned a AMIC-5i»25
Hlrle ranoe of toxlclty spanning 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 opposite was true.
Testing the actual material as sold Has
found to be essential.
Trace element content of fish Lucas, et al
from Lakes Superior, Michigan, and Erie (1970),
was determined by activation analysis. AMIC-3778
Whole body and liver residues were
determined. Concentrations varied Hlth
species and lake. Other elements found
Here? antimony - 5 to 100 ppb, barium -
0.? pom, cesium - 3 ppb, lanthanum - 1 to
20 oob, mercury - 10 ppb, rhenium - 0.5
to 5 ppb, rubidium - 0.06 to 6 ppm,
scandium - 2 ppb, selenium - 0.1 to 2
ppb, sliver - 0.001 opb.
same as above Lucas, et al
(1970),
AMIC-3778
same as above
same as above
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
-------
I
vn
ro
Compound
BroB Ine
BrOBlne
Broalne
BroBophos
BroBoxynll (K salt)
Broaoxynll (K salt)
Toxlclfy,
Active
Field Field Ingredient,
Organism Study Location Ppm
Hlrhl qan,
end Erie
Caresslus FL Great Lakes 0.3(resldue>
auratus - Superior,
M Ich 1 qan.
and Erie
Roccus FL Great Lakes O.o(resldue)
ehrysops - Superior,
W Ichl qan, and
Erie
StlTostedlon FL Great Lakes O.s(rasldue)
vltreu* - Superior,
vltreun Michigan,
and Erie
Rasbora BCFA ~ 0.62 CTZ)
heteronorpha and
BSA
Rasbora DCFA — 60 112,
heteromorpha and hardwater)
BSA
Rasbora BCFA — 5.0 (T2,
heteromorpha and softwater)
8SA
Experimental
Variables,
Con troll ed
or Noted Comments
__
a»,o,o,f,
hard IHW)
or soft
ISW) syn-
thetic
dilution •
water, or
aeawater
for sono
opeoloa
a»,c,o,f ,h
ard (HH)
or soft
(SM)
synthetic
dl lut Ion
Mater, or
for some
species
a",c,e,f ,
hard (HH)
or soft
same as above
sama as above
same as above
One hundred sixty-four
pesticides, wpttlnn aqents, and
Mile ranqo of toxlclty spanning 12 orders
of maqnltude. Knowlnq thm toxlclty and
percantagn 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 Mater
and sometimes the opposite Mas true.
Testing the actual material as sold Mas
found to be essential*
same as above
same as above
Reference
IMIC-377B
Lucas, et al
(1970) ,
AMIC-377S
Lucas, .et al
(1970) .
AMIC-177S
Lucas, et at
(1970) ,
AMIC-3778
Al abaster
(1969) ,
AMIC-51,?
A labaster
(1969), AMIC-
51.25
Alabaster
(1969) ,
AM.IC-5i.2S
-------
Busan 881
Rasbora BCFA
heteronorpha and
BSA
0.65 (TZ)
Busan 90
Rasbora
heteronoroha
I
\fl
U)
BCFA
and
BSA
1.8 (Tl,
hardwater)
Busan 90
Rasbora BCFA
heteronorpha and
BSA
1.2 (Tl,
soltwatar)
Cadalu* chloride (as Agonus
cadalua) cataphractus
BSA —
33 (T*)
(SM)
synthetic
dl lotion
water, or
seawater
for some
soecles
a»,c,e,f,
hard
-------
Toxlclty,
Active
Field Field Ingredient,
Coaoound Organism Study Location Ppm
Cadvluii chloride (as Cardlun edule BSA — 3.3 (T<»)
«<1"lu"»
Cadalua chloride (as Crangon BSA — - 1.0 (T2)
cadmium} crangon
Experimental
Variables.
Control 1 ed
or Noted Comments
a*(oontln- same as above
uoua aer-
ation, sea-
water, and
daily
solution
renewal )
at (con tin- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal )
Pef er ence
Portmann, «t
al (1971),
AMIC-7701
Portmann, et
al (1971),
AMIC-7701
Cad'luB chloride
Fundulus L
heterocl1tus
50 (SB2)
Cadnlun sulfate (as Acroneurla BSA
Cd)
Csd«lu« sulfate (as Fohenerelta BSA
Cd)
Cadulu* *ulf»fe (as Hydropsycne BSA
Cd)
32 (Tl,c,d,e,f
same as above
al(1969),
AMIC-3767
HarnlcK, et
al(1969),
AMIC-3767
Warnlck, et
al(1969),
AMIC-3767
-------
CadnluB
CadBlun
Cadilui
Cadmium
vn
vn
Alosa FL Great Lakes 0.00006
paeudo- - Superior, residua)
harengua Michigan,
and Erie
Coregonus FL
artedil
Coregonus FL
elupeaformls
Coregonus FL
hoy I
Great Lakes
- Superior,
Mlchlgan,
and Frle
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
O.OOlS(residue) —
0.0002(resldue)
O.OOOS(resldue) —
Trace element content of fish
from Lakes Superior, Michigan, and Erie
was determined by activation analysis.
Whole body and liver residues were
determined. Concentrations varied with
species and lake. . Other elements found
were! antimony - 5 to 100 pob, barium -
0.2 oom, cesium - 3 ppb, lanthanum — 1 to
20 pob, mercury - 10 opb, rhenium - 0.5
to 5 ppb, rubidium - 0.06 to 6 opn,
scandium - 2 cpb, selenium - 0.1 to 2
ppb, silver - 0.001 ppb.
same as above
same as above
same as above
Lucas, et
(1970),
AMIC-377S
al
Lucas, et at
(1970).
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Cadtlufi
CadBlun
Prosoolum FL
cyIIndraceun
SalvelInus FL
namaycush
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Mlchlgan,
and Erie
O.OOOMresldue) —
0.003(resldue)
same as above
same as above
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Cadnlun
Cadmium
Osmerus FL
mordax
Carasslus FL
auratus
Great Lakes 0.00007
- Superior, residua)
Michigan,and
Erie
Great Lakes
- Superior,
Michigan,
and Erie
O.OOlUresldue) —
same as above
same as above
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Notropls FL
hudsonlus
Great Lakes
- Superior,
Michigan,
and Erie
O.OOOl(resldue) —
same as above
Lucas, et al
(1970),
AMIC-3778
-------
ON
Compound
Cadalun
Cadm 1 un
CadBlun
C»d»lu«
Cadilu*
CadvluB
Cadnlun
Cadalua
Cadalu*
Organism
Percoosls
cm 1 sc omay cus
Roccus
chrysops
Perca
f 1 avescens
St I 7oster)lon
v 1 t reum
v 1 t reum
Coregonus
clupea formls
Coregonus
c 1 upea f orn 1%
Esox luclus
Esox luclus
Esox luclus
Field
Study
FL
FL
FL
FL
FL
FL
FL
FL
FL
Toxlclty, Experimental
Active Var lab) es,
Field Ingredient, Controlled
Location Pom or Noted Comments
Great Lakes 0 . 0 0 0 1 (r es 1 due ) — same as above
- Suoerlor,
Hlchl qan.
and F r le
Great Lakes 0 . 0 0 0? (r es Idue) — same as above
- Superior,
H i ch 1 qan, and
Erie
Great Lakes 0 . 0 0 05 ( r es 1 due) — same as above
- cuo «*r 1 or ,
Hlchi qan.
and Erie
Great Lakes 0. 00 0? (residue) — same as above
- Suoerlor,
Mlchl gan.
and Erie
Moose LaKe, 0.05 (residue) — Concentrations of 13 toxic
Can. elements in dressed fish from heavily
Industrialized and non- indust ri a 1 ized
areas were determined. Only mercury
concentrations of most elements were
essentially the same In fish from both
areas.
Lake 0.05 (residue) — same as above
Ontario,
Can.
Moose Lake, 0.05 (residue) -- same as above
Can.
Lafce St. 0.05 (residue) -- sane as above
Pierre, Can.
Lake Erie, 0.05 (residue) — same as above
Can.
Refer ence
Lucas, et al
(1970) ,
AMIC-T778
Lucas, et al
(197D) ,
AMIC-3778
Lucas, et al
( 1970) .
AMTC-377*)
Lucas, et al
(1970) ,
AMIC-3778
Uthe.et al
(1971) ,
AMIC-3B19
Uthe.et al
(1971) ,
AMIC-3819
Uthe, et al
(1971) ,AMIC-
3S19
Uthe, et
AL(1971),
AMIC-3819
Uthe, et a!
(1971),AMIC-
3819
-------
Cadmium
Cadmium
Cadmium
VJl
Cadmium
Cadmium
Cadmium
Cadmium
Cadmium
Cadmium
Osmerus
mordax
Perca
flavescens
Paralabrax
clathratus
Paral abrax
clathratus
Paralabrax
cl athratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
(gravid
females)
FL
FL
FM
Lake frit, 0.06 (residue)
Can.
FH
FM
FM
FH
FM
Lake Erie,
Can.
0.05 (residue) —
Scattergood 3 (dorsal
Steam Plant, muscle
Los Angelest residue)
Cal.
Catallna 3 (dorsal
Island, Cal. muscle
residue)
Scatferqood >» (ventral
Steam Plant, muscle
Los Angeles, residue)
Cal.
Catallna ? (ventral
Island, Cal. muscle
residue)
Scattergood 10 (gonads
Steam Plant, residue)
Los Angeles,
Cal.
Catallna 6 (gonads
Island, Cal. residue)
Catallna 3
Island, Cal. (gonads
residue)
same as above
same as above
Fish collected from an effluent
ploe of a steam olant and from offshore
Haters of Catallna Island Here analyzed
for trace element content. Trace element
content of the effluent Mater was at
least 5 times areater than that of normal
sea Hater for cadmium, coooer, nickel,
zinc, and chromium. Livers of fish from
the effluent Here nearly tnlce the sire
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.
same as above
Uthe, et
ALU971),
AMIC-3819
Uthe, et
AL(1971),
AMIC-3819
Staoleton
(196S),
AMIC-5980
same as above
same as above
same as above
same as above
same as above
Staoleton
(116*),
AMIC-5980
Staoleton
(1968),
AMIC-S980
Staoleton
(1968).
AMIC-598!)
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-S980
-------
I
vn
CD
Compound
CadBlu*
CadvluB
C»d»lu«
CadBlua
Cadvlua
CadaluB
CadaluH
CsdnluB
C»lciu« chloride
Organism
Papal abrax
cl athratus
Para 1 abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Lepotils
nacrochlrus
Field Field
Study Location
FM Scattergood
S team P 1 ant ,
Cal.
FM Catal Ina
Island, Cal.
FM Scattergood
Steam Plant,
Los Angeles*
Cal.
FM Catal Ina
Tslandt Cal.
FM Scattergood
Steam Plant,
Los Anqe 1 es ,
Cal.
FM Catal Ina
Island> Cal.
FM Scattergood
Steam Plant*
Los Angel est
Cal.
FM Catal Ina
Island, Cal.
BSA, —
L
Toxlclty,
Active
Ingredient,
Ppm
11 (liver
residue)
?<< (1 Iver
residue)
6 I Integument
residue)
Z (Integument
residue)
it (heart
residue)
2 (heart
residue)
6 (eyeball
residue)
ii (eyebal 1
residue)
10,690 (Ti»)
Experimental
Variables,
Control ted
or Noted Comments Reference
same as above Staoleton
(l«f.?) ,
AMIC-5980
same as above Staoleton
(1968) ,
AMIC-5980
same as above Staoleton
(19SS) ,
AMIC-59BO
same as above Staoleton
11968) ,
SMIC-5980
— same as above Staoleton
(1968) ,
AMIC-5980
same as above Staoleton
(1968) ,
AMIC-5980
same as above Staoleton
(1968) ,
AMIC-5980
same as above Staoleton
(1968) .
AMIC-5980
a»,e, and This study was conducted to Patrick, «t
synthetic determine the relative toxlcltles of ?0 al (1968),
dilution common constituents ot industrial wastes AMIC-57ZO
water to a tish, an alqa, and an Invertebrate.
The experiments were conducted over a
10-year period tor varied purposes. The
authors recommend bloassays Hlth at least
three components of the food neb.
-------
Calcium chloride
Nltzschla
llnearls
BSA,
I
3,130 (T5)
a«,e, and
synthetic
dilution
water
Calciu* hypochlorlte Phormldlus
(as CD amblguum
0.5-10.0
-------
>
Coaoound
CalclviB lulfate
Calcium
Calcium
Calcium
Calcium
CalClUm
Calcium
Organism
Nl tzschle
1 Inear Is
Paral abrax
cl athratus
Paral abrax
clathratus
Paral ahrax
clathratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Field Field
Study Location
8SA, —
L
FM Scattergood
Steam Plant,
Los Angeles,
Cal.
FM Catallna
Island, Cal.
FM Scattergood
Steam Plant,
LosAngeles,
Cal.
FM Catallna
Island, Cal.
FM Scatterqood
Steam Plant,
Los Angeles,
Cal.
FM Catallna
Island, Cal .
Toxlcl ty,
Active
Ingredient,
PDIB
3,200 ITS)
728 (dorsal
muscle
residue)
567 (dorsal
muscle
residue)
1020 (ventral
muscl *
residue)
5
-------
Calclu*
Calclun
Calcium
Calclun
Calclu*
Calciun
Galclua
Calclu*
Calclun
Canal banK
Mcedklller
Paralabrax
clathratus
(gravid
females)
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
FM CatalIna 550 (gonads
Island, Cal. residue)
FM Scattergood 155 (liver
Steam Plant, residue)
Los Anqetes,
Cal.
FM CatalIna 265 (liver
Island, Cal. residue)
FM Scatterqood 1158
Steam Plant, (Integument
Los Angeles, residue)
Cal.
FM CatalIna 1915
Island, Cal. (Integument
residue)
FM Scatterqood 380 (heart
Steam Plant, residue)
Los Anqeles,
Cal.
Paralabrax FM Catal Ina MO (heart
clathratus Island, Cal. residue)
Paralabrax
clathratus
Paralabrax
clathratus
Rasbora
heteromorpha
FM
FM
BCFA
and
BSA
Scattergood 19,000 (eyeball —
Steam Plant, residue)
Los Anqeles,
Cal.
CatalIna 26,200(eyeball —
Island, Cal. residue)
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
610 (T2)
a*,c,e,f,
hard(HW)
or soft
(SW)
synthetic
dl IutIon
water, or
seaHater
for some
species
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water oollutants showed a
wide range of toxicity scanning 12 orders
of magnitude. Knowing the toxicity and
percentage of all comoonents of a
formulation did not result in easy
predictability oT the toxicity of a
mixture of materials. Sometimes
pesticides were most toxic In hard water
and sometimes.the opposite was true.
Staoleton
(1963) ,
AMIC-5980
Staoleton
(1968),
AMIC-5980
Stan I et on
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Stao leton
(1968),
AMIC-5980
Staoleton
(1958),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Alabaster
(1969),AMIC-
-------
Compound
Captan
Captan
Field Field
Organism Study Location
Fish (not
specified)
Brachydanlo t --
rerlo
(1 arvae)
Toxlclty,
Active
Ingredient ,
Ppm
greater than
0.1-1.0 (K)
1.0 (T 30 nln)
Experimental
Variables,
Control led
or Noted Comments
Testing the actual material as sold was
found to be essential.
~ Approximate toxlcltles of
numerous pesticides commonly used In
Britain were summarized. An excellent
brief, qeneral discussion of toxlcity
testing Is also present.
Foloet, Dltolatan, and Captan
were found to be toxic to zebraflsh
larvae within 90 mln. DIfolatan was most
Reference
Mawdesl ey-
Tnomas
(1971) ,AMIC-
1056
Abedl. et al
(1968), AHIC-
0\
K>
Carbaryl
Carbaryl
Fish (not
specified)
SalvelInus
fontInalIs
(1.15 q)
BCFA --
Carbaryl
SalvelInus
font InalIs
<2.0<> g)
BCFA —
greater than
1.0-10.0 (K)
1,070 (Tl.)
1,1,50 (Ti»>
toxlc while Captan w3s least toxic.
Effects observed were cessation of
heartbeat and loss of pigmentation. Tha
authors recommended this as a sensitive,
rapid bloassav tor these and related
compounds.
Approximate toxlcltles of
numerous pesticides commonly used In
Britain were summarized. An excellent
brief, qeneral discussion of toxlclty
testing Is also present.
3717
Ha»desley-Th
o»as(1971)
AMIC-1056
ao,c,d,
e,f,l,o,
oulfate,
copper,
manganese,
Iron, and
chromium
ao.c.d,
e,f,l,o,
aulfate,
coppor,
manganese,
Iron, and
chromium
Four Insecticides were evaluated Post, et al
on four fish species at two body weights. (1971),
Standard method bioassay procedures were AHIC-1812
followed. Symptomoloqv was also
reported. Generally, toxlcity was
significantly different at the two body
weights. I.e., more toxic at the lower
body weight, except for Malathlon.
Well-defined experimental conditions were
said to result In truer measurement of
toxlclty.
sane as above
Post, «t
(1971),
AMIC-1812
at
Carfcaryl
Sal BO clarHi BCFA —
1.5 (Tl.)
a«.c,d.
sane as above
Post, et »l
-------
C»rb»ryl
Carbaryl
Carbaryl
UJ
C»rbaryl
Carbaryl
(D.37 q)
Sal no clarkl
(1.30 g)
SB I mo
qairdnerl
(1.3
Ictalurus
punctatus
8CF» —
2.2 (Tit)
BCFA
1.1.7 (Tfcl
BCFA —
1.3 (Tlf)
BSA
15.SO
Ictalurus
•el as
BSA
20.00 (T
-------
Compound
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbaryl
Carbon dioxide
Toxlcl ty.
Active
Field Field Ingredient,
Organism Study Location Pom
Carasslus BSA -- 13. ?0 IT".)
auratus
Cynrlnus BSA — 5.?8 (T>)
galrdner 1
Salmo trutta BSA — 1.95 (T<«)
Oncorhynchus BSA — 0.76 (Tl»)
klsuteh
Peres BSA — 0.75 (TI.)
f lavescens
Salmo BSA — 35 (SB1)
qalrdnerl
(year! Ing)
Fxppr 1 men tal
Var 1 ab 1 es.
Control 1 ed
or Notpd Comments
a.
synthetic
t PS t Ma ter
a,
syn thp t Ic
t es t Mater
a,
Syn the t Ic
t es t Mater
a.
syn thet Ic
a,
syn thptlc
test Mater
a.
Synthetic
a,
synthetic
test Mater
a,
synthetic
test Mater
a,
Synthetic
test Mater
a,
synthet Ic
test Mater
«.c, bi-
carbon-
ate, and
total
aollda
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
Bicarbonate In blood serum of
brook trout rose to 5 times greater than
that of contro Increase Mas SIOM, being
half complete at 6 hr. Sodium and
Inorganic phosphate Here not affected,
but serum chloride Increased. The
Pe f er pnce
(1970) .
AMIC-5MO
Macek, et
al (1970),
AMIC-SSIO
Mac ek , e t a 1
AMIC-S510
Mac pK , « t a 1
(1970) ,
Macek.et al
(1970) .
AMIC-SMO
Macek, et al
(1970) .
AMIC-5S10
Hacek, etal
(1970) ,
AMIC-SSIO
Hacek, et
al (1970),
AMIC-S510
Macek, et al
(197Q) ,
AMIC-S510
Hacek. etal
(1970),
AMIC-5510
Lloyd, et al
(1967),
AMIC-IT?!
-------
Carbophenothlon
Rasbora BCFA
heterovorpha and
BSA
Z.3 (T2)
Carbyn*
Rasbora • BCFA
heteromorpha and
BSA
0.5 IT2)
o\
a*,c,e,f,
hard (HH)
or
SOFTCSH)
synthetic
dilution
water, or
seawater
for some
species
a*,c,e,f,
hard (HW)
or soft
(SJ) syn-
thetic
water, or
aoawater
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. Hettlnq aqents, and (1969),
miscellaneous water pollutants shotted a AMIC-5l»25
Hide range of toxlclty spanning 12 orders
of maonltude. Knowing the toxfcjty 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 opposite Has true.
Testing the actual material as sold Has
found to be essential.
same as above
Alabaster
(1969),
AMIC-5I.K
Carbyne
Rasbora BCFA
heteromorpha and
BSA
l.i. IT2)
Carbyn*
Asterlas
rubens
BSA
3.3-10 (K 1
HP)
Carbyne
Cardlun edule BSA ~
100 (TZ)
a*,c,e,f,
hard (HWJ
or soft
(SW) syn-
thetic
dilution
water, or
aeawater
for some
species
a«(contin-
uous aer-
ation, aea-
water, and
dally
solution
renewal)
c«(contln-
IUQUS aer-
sane as above
One hundred—fortv surface active
agents, solvent emutslflers< pesticides,
polychlorlnated blphenyls, pure
inorqanlc, 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
Alabaster
119691,
AHIC-SI.35
Portmann, et
al (1971),
AMIC-7701
Portmann, et
al (1971),
-------
>
I
Toxlclty, Exoer I men tal
Active VarlaMes,
Field Field Ingredient, Controlled
Coioound Organism Study Location Port or Noted Comments
etion, sea-
water, or.d
daily
solution
renewal )
Carbyne Crangon BSA — 3.3-10 (T2) a*(contln-
crangon uous aer-
ation, sea-
water, and
daily
solution
renewal)
Casol Plmeohales BSA -- 12. 0 m) c.d.e.T
Drome 1 os
Casol Plmeohales BSA -- 1HSC) c,d,«,f
cromel as
Casol Biochemical L — 610,000 c,d,e,f
oxygen deaand
Cesoron G Rasbora BCFA — 100 (T2) a»,c,o,f,
heteromorpha and hard (KW)
BSA or soft
( QU \ BTrn
V ow i syn—
theUc
dilution
water, or
seawater
for soxa
species
same as above
Toxlcl ty of six oil sol 1 1
dlsnersants Has determined alonq Nlth
BOD values. Pond water HSS used as
diluent and oil Has Included In the
exoerlirent. Oil markedly reduced
toxlclty of all d 1 soersan ts. Oata are
given as "most orobable" "96-hr TL sub «.
same as above
same as above
One hundred sixty-four
pesticides, netting aapnts, and
miscellaneous water pollutants showed a
of magnitude. Knowing the toxlcltv 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 opposite was true.
Testing the actual material as sold was
found to be essential.
Reference
AHIC-77D1
Portmann, et
al (19711,
AMIC-7701
211 1 Ich
(196
-------
Casoron 133
Rasbora
heteromorpha
BCFA
and
BSA
13 (T2)
Casoron
Morone
saxatllIs
IfIngerlInqs)
BSA
6,200
Casoron
Cardlum edule BSA —
qreater than
100
-J
Casoron
Cranqon
crangon
BSA
3.3-10 (T3)
a*,c,e,T,
hard (HM)
or
SOFT(SH)
synthetic
dllutlon
Hater, or
seawater
tor some
species
a,c,d,e,f,
c
same as above
Alabaster
(1969),
AMIC-5i»25
All compounds Here Investigated
because of their orobable usage In
hatchery production of nhlte bass.
Compounds that can be used at recommended
concentrations Here Aquathol, Casaron,
Lindine, and Terramycln concentrate.
Those that should not be used were
Acrlflavlne, (layluscldp. Malachite qreen
oxalate, and Halathlon.
a«-(contln- One hundred-forty surface active
UOU3 aer- aqents, solvent emulslflers, pesticides,
ation, 3ea-POlychlorlnated blphenyls. pure
wator, and inorqanlc, and organic chetlcals Here
dally evaluated against as many as ten varine
solution organisms. The authors noted that nost
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
same as above
a*(oontin-
uoua aer-
ation, sea-
water, and
solution
renowal)
HelIborn
(1971),
AMIC-5571
Portaann, «
al (1971),
AMIC-7701
Port»ann, et
al (1971),
AMIC-7701
Cd CIZ . Z.5 H?0 (as Crangon BSA
Cd 2 plus) septemsplnosa
a*,c,e,
SSH
Although data cited Here taken at Elsler
?0 C and 2.0 percent salinity, varying
temoerature and salinity Here also
studied. Higher temperature (20 C) and
loner salinity (5.0 percent) resulted in
greater susceptibility of mummlchoqs to
cadmiuff. TL sub 25, TL sub 50, and TL
sub 75 for 2<* and *tfl hr are also
presented. Post treatment mortality of
mummlchoqs Has also observed for
considerably prolonned periods (up to SB
days). Teleosts Here less susceptible
than Crustacea. Residue l-evels In
mummicrogs Here also reported, e.g.,
Hhole body residues In excess of Bf> mg
Cd/Kg body ash resulted In death within 5
Hk. A revlen and discussion of results
are also Included.
(1971),
AMIC-1621
-------
1
Cd
Cd
Cd
Cd
Cd
Cd
Cd
Cd
Cd
> Cd
O\
00 Cd
Cd
Cd
Cd
Cd
Cd
Cd
Cd
Cd
Cd
CoMoound
CI2 . 2.5 H20
2 olus)
CI2 . 2.5 H?0
2 olus)
CI2 . 2.5 H20
2 olus)
CI2 . 2.5 H20
2 olus)
CI2 . 2.5 H20
2 olus)
CI2 . 2.5 H21
2 olus)
CI2 . 2.5 H20
2 olus)
CI2 . 2.5 H20
2 olus)
CI2 . 2.5 Vt?.fl
2 olus)
CI2 . ?.5 H20
2 plus)
Field Field
nrq»nl*» Study Locatloi
(as Fundulus BSA
heterocl 1 tus
(as Paqurus BSA —
1 onq 1 carous
(as Palaemonetes BSA
vul gar Is
(as Asterlas BSA
forbesl
(as Mya arpn>irl8 BSA —
(as Carclnus BSA ~
Maenus
(as Urosalolnx BSA
clnerea
(as Fundulus BSA
ma ) a 1 Is
(as My tl lus BSA
edul Is
(ss Cyorlnodon BSA
variegatus
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
l Pom or Noted Comments
55.0 (T<>) a*,c,e, same as above
SSM
0.32 (H.) a*,c,e, same as above
SSM
O.itZ (Ti.) a*,c,e, same as above
SSM
O.S2 a*,c,e, same as above
SSM
2.2 (Ti») a*,c,e, same as above
SSM
ii.l (Ti») a*,c,e, same as above
SSM
6.6 (Ti>) a*,c,e, same as above
SSM
21.0 (Ti>) a*,c,e, same as above
SSM
25.0 (Ti») a*,c,e, same as above
SSM
50.0 (T<») a*,c,e, same as above
SSM
R*f erence
Elsler
(1971),
AMIC-1621
Elsler
(1971) ,
AMIC-1621
Eisler
(1971) ,
AMIC-1621
Elsler
(1971),
AMIC-1621
Elsler
(1971) ,
AMIC-1621
Elsler
(1971) ,
AMIC-1621
Elsler
(1971),
AMIC-1621
Elsler
(1971),
AMIC-1621
Elsler
(1971) ,
AMIC-1621
Elsler
(1971) ,
AMIC-1621
-------
Cd Cl? . 2.5 H20 (as Nassarlus BSA —
Cd 2 olust obsoletus
Cd CIZ . 2.5 M20 (as Nereis vlrcns BSA
Cd 2 plus)
10.5 (T<»)
ll.O(Tit)
Chevron NI-0
Chevron NI-0
Chloral hydrate
Chloramlne
Chlora«lne
Chloraalne
a»,c,e,
SSM
SSM
Steel head
trout
(r ingertInqs)
BSA
Coho salmon BSA Hood Canal
(flngerllnga) in . Hoodsport,
situ Wash.
Neqaprlon. BSA —
brevlrostrls
(1-3 Kg)
0.001 (K)
300 (SB 1 hr>
Gannarus
paeudo-
llmnaeus
BCF
0.22 (T<»)
a*,ofd,e.
Plmephales BCF
promelas
Daphnla nagna BCF
0.15 (T3>
0.09-0.15 (T«f)
0.001 (K 3-5)
a*,c,d,e,
same as above
same as above
Evaluation of 11 oil dlsoersants
resulted In a ranking for each and a
recommendation for use according to the
ranking. Ranking was based on toxlclty
and oil dispersal effectiveness. Corexlt
776it appeared to have the least toxlclty
with fair to good oil dispersion
caoabl11ty.
same aa above
Elsler
(1971),
AMIC-1621
Elsler
(1971),
AMIC-16E1
Tracy, et
al (1969),
AMIC-383*
Data tpom study of drug effects
on young lemon sharks were treated
mathematically to demonstrate
apolIcabl11ty of classical rate theory to
the study of chemical shark deterrents.
IncaoacI tat Ion (narcosis) was the orlitary
parameter timed for effectiveness. This
was usually quite rapid for the more
effective druqs.
Chloramlne toxlclty was very
carefully studied usinq weight reduction
and reor-oduct Ion over 15 to 21 week
exoosure periods. Loss of weight and
ability to reproduce were observed at
concentrations less than that observed
for toxlclty. The lowest chloramine
concentration having no significant
effect was less than 3.
The effect of 52 pesticides on
Davis, et al
-------
Compound
Organise
Field Field
Study Location
Toxic!ty,
Active
Ingredlentt
Ppm
Exper1 mental
Variables,
Controlied
or Noted
Comments
Reference
nercenarls
(eggs)
-J
O
Chlors«oh«nlcol
ChI or•«oh« nIc oI
Nercenar1»
•ercenarla
(Iarvae)
Phormldlun
ambIguum
SO.O (T12)
0.5-10.0 (NTE) —
Cnlorax
Salmo
galrdnerl
BCFA —
and
BSA
1,800 (T2)
etrbryonlc development of clams and
oysters was reported. Synprolsrlc (1969), A1IO
etfects with solvents Here also reported. 5990
Host of the -compounds affected
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 oest control that
would not have serious effect on
shelIfIsh.
same as above Oavls, «t
31(19691,
AMIC-5910
Of 71. chemicals evaluated as Otto(1970),
alglcldes, only q were more toxic than AMIC-S9Z
CuSO<*. None Inhibited growth of
mat-forming alqae for more than ? weeKs.
CuSOU formulated with certain wetting
agents was more toxic than CuSO** alone.
Copper chloramine was also found to be
more toxic than Cu^OW. No wetting agents
were found to be Inhibitory at the
concentrations investigated (0.05 &nd
0.005 com). 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.
a»,o,e,f,
hard (HW)
or soft
(SW) syn-
thetic
dilution
water, or
seawatcr
for some
species
One hundred sixty-four Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a AMIC-5't25
wide 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 ot a
mixture of materials. Sometimes
pesticides were most toxic In hard Hater
and sometimes.the ooposlte was true.
-------
Chiordan*
CMordane
White sucKer FRL Misc. states 0.1Z-0.<»
-------
Field Field
Compound Organism Study Location
Toxlclty,
Active
Ingredient,
Ppm
Exoer 1 menta 1
Variables.
Control led
or Noted Comments Reference
CM or dene
LepOBls
cyanelI us
(Resistant)
BS» —
3.Z8 (TZ)
8»
11.07
Green sunflsh from Relzonl, Miss* Hlnchen, et
Here resistant to Chlordane, Heptachlor, al(1970>,
Llndane, and Strobane, but not to SMIC-5UM
Parathlon. Golden shiners fro«i the same
location were resistant to Llndane and
Strobane, toleranf to Chlordane and
Heotachlor, and susceptible to Parathlon.
Lack of resistance to Parathlon
Indicated lack of aarlcultural usage of
organophosphates In that area. Resistant
fish were compared to susceptible ones
collected at StarNvllle.
Chlordane
Leponls
cyanellus
(Susceptible)
BSA —
0.09 (TZ)
same as above
Mlnchen, et
•1(1970).
-J
fO
Chlordane
Chlordane
Chlordane
Chlordane
Notemlqonus
crysoleucas
(Resistant)
No t em I cj on us
crysoleucas
(Susceptible)
BSA ~
Copopoda
I Cyclops
blcuspidua
Cyclops
varicana,
EucTClops
BSA —
Palaemonetes BSA
Had 1aHensIs
(resistant)
3.33 (TZ)
0.
-------
Chfordan*
CM or dan*
Chi or*a
Chlorfenvlnphos
Chlorfenvlnphos
agilis,
Macrocyclops'
albidus,
Orthocyclopa
modeatus)
Copeoods
(Cyclops
blcusoldus,
Cyeloos
varleans,
Cyclops
vernal Is,
EucyclODS
agilis,
Hacrocvcloos
albidus,
Orthocyclops
modestus)
Tublfex
tubltex
Saliio
galrdnerl
FL
and
BSA
Selzonl,
Hiss
0.30 (96percent —
K2>
FL
and
BSA
BelzonI,
Hiss.
BCFA —
and
BSA
1.50 (NTE)
1,100
-------
Toxiclty,
Active
Field Field Ingredient,
Conoound Organise Study Location Ppn
Experimental
Varlahles,
Con t ro 1 led
or Noted Comments Reference
synthet Ic
dl lut Ion
water, or
seawater
for some
soec les
Chlorine
Plntephales
prone)as
BSA Grand River, 0.07-0.15 (TO
(HL) Wyoming,
Mich.
Chlorln*
Fathead
ml nnoM
BSA Grand »lver, 8.33
(ML) Lansing, percent(Kli
Mich. HWO)
The Indicated toxic levels of Zlllleh, et
chloride occurred In 3.8<< percent and al (1969),
7.fT* percent dilutions of wastewater ANIC-2878
effluent In river mfer. Subtethal
effects were noted at dilutions as low as
1.9? percent. The authors note that this
chewlcel at low concentrations 0.05 mg/l
may seriously degrade fish populations In
r Ivers.
Striking sublethal effects were 71lllch, «t
noted at lower dilutions. OechI or 1na11 on al (1970),
did not remove toxiclty of the wastewater AHIC-7899
since toxic effects were noted at
dilutions of **? and 5(1 percent of
dechtor 1nated waste niter. Cyanide Has
present at 0.2 mq/l and may have had son*
influence on the results. The authors
concluded that the waste water caused
severe deoradatlon of the Grand River.
Chloroflurazol*
Rasbora
he teronorpha
BCFA —
and
BSA
0.13
Chloropropyl ate
Rasbora
neteromorpha
BCFA —
and
BSA
?0 (T2)
a'.c.e.f,
hard (HWI
orsof t
(SH)
synthetic
dl lution
water, or
seawa ter
for some
species
a«,c,e,r.
hard (HW)
or soft
(SW) syi-
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wide r?nqe of toxiclty spanning 1? orders
of magnitude. Knowing the toxiclty and
percentage of all components of a
formulation did not result In easy
predictability of the toxiclty of a
mixture of materials. Sometimes
pesticides were most toxic In hard water
and sometimes the ooposlte was True.
Testing the actual material as sold was
found to be essential.
same as above
Alabaster
(1969),
AMIC-5«,2S
Alabaster
(1969) ,
-------
Chlopthlanld
Rasbora BCFA
heteroiKorpha and
BSA
30
Chroiates (as
chPo«lu«>
Agonus 'BSA
cataohractus
33-100 (T2)
-la
NJl
thetic
dilution
water, or
aeawator
for some
apeeles
a»,c,e,fi
hard (HW)
OP
SOFT(SH)
synthetic
dilution
watep, or
seawatep
fop some
sppcles
a*(contin-
uous aer-
ation, sea
water, and
daily
solution
renewal)
same as above
One hundped-fopty surface active
aqents, solvent emutslfleps, pesticides,
polychloplnated blohenyls, OUPB
Inopqanlct and organic cheirlcals Here
evaluated against as many as ten vaPlnc.
opqanlsms. The authoPS noted that most
published data of this type deal Hlth
toxlclty of chemicals to freshwater
opqanlsns>
Alabaster
(1969),
AHIC-5^21!
Porfmann, et
al (1971),
AHIC-7701
Chpo»ates (as
ChPO«lu»)
Aster las
pubens
BSA
33-100
-------
Conoound
Organism
Field Field
Stud/ Location
Toxlclty,
ActIve
Ingredlentf
Ppm
Experimental
Variables,
Control Ied
OP Noted
Comments
Reference
Chro«lc chloride (as Acroneurla BSA
CP!
Chromic chloride (as Ephemerells BSA
Cr)
32 (T7)
a*,c,d,e,f
Ephemerella (mayfly) Has the nost Vlarnlck, «t
Chromic chloride (as Hydroosyche
Crl
Chro»tu» trloxld* Phornldlun
(as Cr) amblguu*
BSA
a*«c,d,e,f
a*,c.d,e,T
sensitive aauatlc Insect of those
studied, and copper the most broadly
toxic Fetal. The authors suggest that
aquatic Insects may not be as sensitive
to heavy metals as fish.
same as above
0.5-10.0 (NTE) —
ChroMlun
Alosa
psoudo-
hai-engus
FL
Great Lakes
- Superior,
Michigan,
and Erie
1.1 (residue)
same as above
al(1969),
AMIC-3767
Harnlck, «t
al (1969),
AMIC-3767
Marnlck, et
al (1969),
AMIC-3767
Of 71. chemicals evaluated as Otto (1970),
alglcldes, only 9 Here more toxic than AMIC-892
CuSOt*. None Inhibited gronth of
mat-forming algae for more than 2 Heeks.
Cu"50 ppb, rubidium - 0.06 to *> ppin,
scandlun - 2 opb, selenium - o.l to 2
ppb, silver -.0.001 ppb.
-------
Chroalun
ChroMlua
Chroalu*
Chrontu*
Chroalui*
ChroBlu*
Chromium
ChroaluB
Notrools FL
hudsonius
Pereopsls FL
omlscomaycus
Coregonus FL
clupeaformls
Coregonus FL
clupeaformls
Esox luclus FL
Esox luclus FL
Esox luclus FL
Great Lakes 5.5(resldue>
- Superior,
Michigan,
and Erie
Great Lakes ?.
-------
Conoound
Cnroalu*
Chroalu*
Chro«lu«
Chro»Iu«
ChroBluB
Chro»lu»
Chronlum
Chro«lu*
Organism
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral ahrsx
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athraf us
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Field Field
Study Location
FM Scattergood
Steam PI ant ,
Los Anqeles,
Cal .
FM Catallna
Island, Cal.
FM Scatterqood
Steam Plant,
Los Anqeles,
Cal.
FM Catallna
Island, Cal .
FM Catallna
Is 1 and, Cal .
FM Scattergood
STeam Plant ,
Los Anqeles,
Cal.
FM Catal Ina
Island, Cal.
FM Scatterqood
Steam Plant,
Los Angeles,
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted Comments
-------
Chroalun
Chroalua
Chronlun
Chroulu*
Paralabrax FM Catallna 2.3 (gonads
clathratus Island, Cal. residue)
Paralabrax FM Catallna 7.6
clathratus Island, Cal. (gonads
(gravid residua)
females)
Paralabrix FM Scattergood 1 (liver
clathratus Steam Plant, residue)
Los Angeles,
Cal.
Paralabrax FM Catallra 1.5 (liver
clathratus Island, Cal. residue)
same as above
same as above
same as above
same as above
Stapleton
(19*8),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1«68),
AMIC-5980
Staoleton
(1968),
CnroBlun
Chroalum
Citric acid
CI
Ct
Paral abrax
clathratus
Paralabrax
clathratus
Carclnus
•aenas
FM
FM
BSA
Fundulus BSA
heteroelItus
Nereis vlrens BSA
Seatterqood 1.9 (Integument
Steam Plant, residue)
Los Angeles,
Cal.
Catallna l.,c,e,
(Ti») and
synthetic
seawater
same as above
LaRoche,et
al (1970),
-------
Coxoound
Cleanosol
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient,
Ppm
Experimental
Controlled
or Noted
Comments
Reference
Cardlum edule BSA —
Clvanosol
Crangon
crangon
BSA
10-33 (T2) av-(contln- One hundred-forty surface active
uous aer- agents, solvent emuls1flers, pesticides,
ation, sea-P°Ivchtor 1nated 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 nlth
toxlclty of chemicals to freshwater
organisms.
33-100 (T2) a«(oontin- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal)
Portmann, et
al (1971),
AMIC-7701
Portmann, «t
al (1971),
AMIC-7701
Cl«anoxol
Panda I us
•ontaqul
BSA
33
-------
dally
solution
renewal)
Clophen A60
Agonus
cataonractus
BSA —
greater than ID a»(contin-
(TZ) uous aer-
ation, sea-
wator, and
daily
solution
renewal)
sane as above
Portmann,et
at (1971),
AMIC-7T01
Clophen A60
Cardluii edule BSA
greater than 10 a*(contin-
ITZ)
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al(1971),
AMIC-7701
Clophen A60
Crangon
crangon
BSA
greater than 10 a*(contin-
«TZ>
uous aer-
ation, sea-
water, and
dail?
solution
renewal)
same as above
Portnann, et
at(1971),
AMIC-7701
Clophen A «.0
Crangon
crangon
BSA
1.0-3.3
-------
Coaoound
Zn
Field Field
Organism Study Location
Wyoming, Mich
Igan
commersonl (ML) at
Wyoming, Mich
Igan
Toxlclty,
Active
Ingredient,
Ppm
percent (T3)
1.25-3.75
percent (T3)
Experimental
Variables,
Con t ro 1 led
or Noted Comments
Ni,Cu,Cr,
CM, and Zn
ductlvlty,
Nl.Cu.Cr,
CH, and Zn
Reference
AMIC-2906
(1969) ,
AMIC-2906
Cobaltous sulfnt*
(as Co)
Cobaltous sulfate
(as Col
Cobaltous sulfet»
(as Co)
Cobalt
Acroneuria
BSA
Ephemeralla BSA
Hydropsyche BSA
Cobalt
Alosa
psoudo-
harengua
Coregonus
artedll
FL
3? (T8)
16 (Tit)
32 (T7>
8*,c,d,e,f
Ephemerella (mayfly) was the most WarnlcK, 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.
a",c,d,e,f same as above
,c,d,e,t
FL Great Lakes 0.029(resldue)
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Mlchlgan,
and Erie
0.020(residue)
same as above
Trace element content of fish
from Lakes Superior, Michigan, and Erie
was determined by activation analysis.
Whole body and liver residues Here
determined. Concentrations varied with
species and lake. Other elements found
were! antimony - 5 to 1QO ppb, barium —
0.2 opm, cesium - 3 pob, lanthanum - 1 To
20 pob, mercury - 10 ppb, rhenium - 0.5
to 5 ppb, rubidium - 0.06 to 6 ppm,
scandium - 2 ppb, selenium - 0.1 to 2
ppb, silver - 0.001 ppb.
same as above
al(1969),
AMIC-3767
HarnlcK, et
al(1969),
AMIC-3767
Warnlck, et
al (1969),
AMIC-3767
Lucas, et al
(1970) ,
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Cobalt
Coregonus FL
clupeafor»ls
Great Lakes
- Superior,
Michigan,
O.OZ3(resldue) —
sane as above
Lucas, et al
(1970),
AMIC-3778
-------
and Erie
UJ
Cobalt
Cob*It
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Coreqonus FL
hoyl
Prosoplum FL
eylIndraceum
Salv»lInus FL
namaycush
Osmerus FL
•ordax
Notropls FL
hudsonlus
Pereopsl* FL
omlscomaycus
Roccus FL
chrysops
Perca FL
fIaveseens
Stlrostedlon FL
vltreum
vltreun
Paralabrax FH
clathratus
0.026(resldue> —
Great Lakes
- Suoerior,
Michigan,
and Erie
Great LaKes
- Superior,
Mlchlqan,
and Erie
Great LaKes
- Superior,
Michigan,
and Erie
Great LaKes
- Superior.
Mlchlqan,
and Erie
Great LaKes
- Superior,
Mlchlgan,
and Erie
Great LaKes
- Superior,
Michigan,
and Erie
Great LaKes
- Superior,
Michigan,
and Erie
Great LaKes
- Superior,
Mlchlqan,and
Erie
Great LaKes 0.0"t5(resIdue)
Super lor,Mlc
hlgan, and
Erie
Scatterqood l.t (dorsal
Steam Plant, muscle
LosAngeles, residue)
Cat.
0.0<»7(resldue) —
0.033(resldue>
0.013(resldue) —
O.D33lresldue) --
0.023(rasldue) —
0.0>>3(resldue) —
O.lZO(resldue) ~
same as above
sane as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
Lucas, et al
J1170),
AHIO3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
A1IC-377S
Lucas, et al
(1970),
AMIC-377H
Lucas, et al
(1970),
AMIC-377*
Libras, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970) ,
AMIC-3778
Fish collected Trora an effluent Staoleton
pipe of a steam plant and from offshore (1968),
Haters of Catallna Island Here analyzed AMIC-5980
for trace element content. Trace element
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organise Study Location Ppm or Noted Comments Reference
content of the effluent water Mas at
least 5 times qreater than that oj normal
sea water for cadmium, cooper, nickel,
zinc, and chromium. Livers of fish from
the affluent Here nearly twice the sire
of those from thp ocean. Greatest
differences In concentration occurred
with aluminum, cadmium, and nickel.
Sliver, barlurr, lithium, and lead showed
the least differences. The author
conduced that trace element analysis of
tissues could be used to determine th«
effect of pollutants on marine organises.
>
I
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paral abrax
clathratus
Paralabrax
clathratus
Paralanrax
clathratus
(gravid
females)
Paralabrax
elathratus
FH Catallna ?.Z (dorsal
Island, Cat. muscle
residue)
FH Scattergood l.Jventral
Steam Plant, muscle
LosAngeles, residue)
Cal.
FH ratal ina it.3 (ventral
Island, Cal. muscle
residue)
FH Scattergood 3.6 (gonads
Steam Plant, residue)
LosAnqeIes,
Cal .
FM Catatlna
-------
CD
v/i
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Cobalt
Papalabrax
clathratus
Paralabrax
clathratus
Papal abrax
ct athratus
Papal abrax
clathpatus
Papalahrax
clathpatus
Papalabpax
clathpatus
Coeoaaln* dlacetate Phornldlun
amblguun
FM
FM
CatalIna
Island, Cal<
1.9 tllvep
residue)
FM
FM
FM
Papal abpax FM
clathpatus
Coco
nonoethanoI amide
lotus ethylene
oxide, ethoxy
Cardlum edule flSA
Scattergood 1.8 (Integument
Steam Plant, residue)
LosAngetes,
Cal.
CatalIna l,it (Integument
Island, Cal. residue)
Scattepgood 1.7 (heart
Steam Plant, residue)
LosAngeles,
Cal.
CatalIna 1.2 (heart
Island, Cal. residue)
Scattepgood 8.2 (eyeball
Steam Plant, residue)
LosAngeles,
Cal.
CatalIna 5.1 (eyeball
Island, Cal. residue)
0.5-10.0 (NTE) —
qpeater than
100 (T2)
same as above
same as above
same as above
same as above
same as above
same as above
same as above
Of 7
-------
Conoound
• onoe thano 1 ami de)
Toxlcl ty,
act lv«
Field Field Ingredient,
Organise Study Location Pot
Exper 1 menta 1
Van lab lei.
Con t ro 1 led
or Noted Comments
Ret er«nce
Coco
• onoetha no I amide
(Dlus ethylene
oxld»» ethoxy
• onoethanoI amide)
Cranqon
cr angon
BSA
greater than
100 (T2)
solution organisms. The authors noted that most
reneimJ.) published data of this type deal N) th
toxlclty of chemicals to freshwater
organises.
ai-( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (19711,
AMIC-7701
Coco
• onoethJinolamide
(plus ethylene
oxide, ethoxy
•onovthanotanlde)
Carclnus
•aenas
BSA —
greater than
100 (T2)
a«-( contin-
uous aer-
ation, ssa-
uater, and
daily
solution
renewal}
same as above
Portmann, «t
al (1971),
AMIC-7701
Coco
• onoethanoI am 1de
Coco
• onoe thano I »•!
-------
Conpass
Crangon
crangon
BSA
greater than
100 (T2)
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms*
a«-(contin- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal)
Portnann, et
at (1971),
AHIC-7701
Compass
Carclnus
maenas
BSA
greater than
100 (T2>
a«-( contin-
uous aer-
ation, sea-
v:ater, and
daily
solution
renewal)
same as above
Portmann, et
a I (197.1),
AHIC-7701
Cooper"* Fly dip
(new type)
Rasbora BCFA
heteromorpha and
BSA
3.55 (TZ)
Copper chloride (as
Cu)
Leoomls
macrochlrus
BSA,
L
1.Z5
Copper chloride (as
Cu)
Nltzschla
IInearls
BSA,
I
0.81 (T5>
a*,c,R,t, One hundred sixty-four Alabaster,
hard(HW) pesticides, Hettlnq agents, and (ig69),AMIC-
or soft miscellaneous water pollutants showed a 5
-------
Compound
•ethane-ar senate
Toxlclty,
Active
Field Field Ingredient,
Organism Study Location Ppm
anblguu* percent growth
Inhlbl tedlii)
Experimental
Variables,
Contro 1 1 ed
or Noted
Comment s
alqlcides, only 9 Here more toxic than
CuSni.. None Inhibited growth of
Reference
AHIC-S92
Copper salts
Copper sal t of
•ndothalI
Fish (not
specified)
Phormldlum
amblguuit
greater than
0.1-1.0 (K)
0.5-10.0 (NTE) —
Copper aodlum
citrate (as Cu)
Waterslpora
cucullata
(larvae)
0.63 (T 2 hr)
mat-forming alqae for more than ? neehs.
CuSOU formulated with certain netting
agents Has morp toxic than CuSOfc alone.
Copper cMcramlne Has also found to be
more toxic than CuSO1*. No wetting agents
Here found to be Inhibitory at the
concentrations Investigated (0.05 and
0.0115 Dpm). Also reoorted are factors
affecting aronth of algae In canals to
determine Hhether there Here leads to
controlling algae by environmental
management. No practical environmental
means Here found.
Approximate toxlcltles of Nawdesley-
numerous pesticides commonly used In Thomas(1971)
Britain were summarized. An excellent AHIC-1056
brief, general discussion of toxlclty
testing Is also present.
Pf ft chemicals evaluated as Otto (19701,
alqlcides. only 9 were more toxic than AMIC-89?
CuSO
-------
Copper sodium
citrate (aa Cu)
Copper sodium
citrate (as Cu)
Copper sodiun
citrate (as Cu)
Copper sodium
citrate (as Cu)
Cooper sulfate olus
AlKylaryl
oolyoxcthylene
glycols
Bugula
nerltlna
(larvae)
Splrorbls
lamelloaa
(larvae)
Qaleolaria
caespltosa
(larvae)
Kytllus
edulls
planulatus
(larvae)
Phormidium
amblguum
3.90 (T 2 hr)
O.W (T 2 hr)
2.90 (T 2 hr)
23 (T 2 hr)
0.5-10.0 (100
percent growth
inhibited 1
-------
>
I
Compound
Copper sul fat* plus
Calc lorn salt or
polyoxyethylen*
Copoer sul fate plus
Dodecy !• th»r of
polyethylene glycol
Copoer sul fate plus
Emulsl r lable
Dot yethy 1 ene
Copper sul fate plus
Ethoxylafed Isooctyl
phenoxy polyefnoxy
•thano 1
Copper sul fate plus
Ethoxylated nonyl
pheny 1 ether
Copper sut late plus
Po lyoxyeth len« nonyl
ph«nvl«ther
Copper sul fat* (as
copper)
Field Field
Organism Study Location
Phormldlum I
amb 1 quum
Phormldlu* I
amh 1 quum
Phormldlu* L
amblquum
Phor«ldlu« L ~
anblguun
Phormldlum L
amblguum
Phormldlum L
amblguun
Carclnus 8SA —
•senas
Toxlclty,
active
Ingredient,
Ppm
0.5-lfl.O (100
percent qrowth
Inhibited 1".)
O.S-iO.O (50
percent growth
Inhibited 1U)
0.5-10.0 (25
percent growth
Inhibited !<•)
0.5-10.0 (50
oercent qrowth
Inhibited 1".)
0.5-10.0 (50
Percent qrowth
Inhibited l<»)
0.5-10.0 (NTE)
109 (T2>
Exoer-lmenta 1
Variables,
Contro 1 1 ed
or Noted Comments
same as above
— same as above
same as above
same as above
— same as above
— same as above
a«f(contln- One hundred-forty surface active
uous aer- aqents, solvent emulsltlers, Pesticides,
atlon, sea-po 1 ych lor Ina ted blphenyls, pure
water, and Inorganic, and organic chemicals were
daily evaluated aqalnst as many as ten marine
solution organisms. The authors noted that mojt
renewal) published data ot this type deal with
toxlclty of chemicals to freshwater
organisms.
Reference
Otto (1170) ,
4MIC-S92
Otto (1970),
aHTC-892
Otto (1970),
8HIC-99?
otto (i97tn,
SMTC-89?
Otto
(1970) ,AMIC-
893
Otto (1970),
4MIC-89?
Portmann, «t
al (1971),
anIC-7701
-------
Copper sulfate fas
cooper)
Cardlum «dule BSA
1.0 CT2I
a«(contin-
uous aor-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al 11971),
AHIC-7701
Copper sul fate (as
copper)
Cranqon
crangon
BSA —
19 (T
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AHIC-7701
Copper sulfate (as
copper)
Copper sutfate (as
Cu7 plus)
Platlcthys
flesus
Sal mo
galrdnerl
(eggs and
sperm)
BSA —
1.0-3.3 (T2)
LCF
1.0 (NTE)
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
a,c,f
same as above
Portnann, et
al (1971),
AMIC-7701
Data were given In mg/l xhlch Has Shan, et al
taken to be the equivalent of opm. (1971),
Fertilization rates Mere statistically AMIC-l<><»
-------
Coaoound
Field Field
Organls* Study Location
Toxlclty,
Active
Ingredient.
Ppm
Experimental
Variables,
Control led
OP Noted
Comments
Reference
>
ro
Cooper sulfaf* (as Acron«urla BSA
Cul
Copper sultafe (as EDhei»«r«ll» BSA
Cul
Copper sulfaf* (as Hydroosyche BSA
Cul
Copper sulfat• (as Phornldlu* L
Cul aablguum
8.3 (TO
0.3? (T2)
3? ITU.)
0.5-10.0 (83
percent growth
inhlbl T«dl
Increased. The authors concluded that In
hard waters neither Cu nor Nl Is tlhely
to Impair fertilization In rainbow trout.
,c,d,e,f Ephemerella (mayfly) was the most Harnlck, et
sensitive aquatic 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 tlsh.
a*,c,d,e,f same as above
a«,c,d.e,f
same as above
Of 7k chemicals evaluated as
alqlcldes, only 9 were more toxic than
CuSOi.. None Inhibited growth of
mat-tormlnq algae for more than 2 weeks.
CuSOi. formulated with certain wettlnq
agents was more toxic than CuS(H alone.
Coooer chloramlne was also found to be
more toxic than CuST». No wetting agents
were found to be Inhibitory at the
concentrations Investigated (O.O'i and
0.005 com). Also reoorted 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*
al (1969)
AMIC-3767
Marnlck,
etal (l<>f>9>,
AMIC-3767
Harnlck,
etal I19S9),
AMIC-3767
Otto (1970),
AMIC-893
Copper tut fat*
Pseudoplauro LCF
nectes
•mericanus (3
yr)
0.180 (SO)
winter flounder were exposed to
varied concentrations of cooper and
selected tissues examined by light and
electron microscopy. Medium to high
concentrations of cooper resulted In
fatty liver deposits, kidney necrosis,
hemopoetlc tissue destruction, and gill
architectural changes as determined by
light microscopic analysis. Seven
additional organs or structures were
Baker
(1969),
AMIC-3763
-------
Copper sol fat*
Copper sut fate
Ui
Copper' sulfate
Copper sulfare
Copper sulfate
Copper sut fate
Pseudopleuro LCF
noctea
anerlcanus (3
vr>
Plmephales BSA
proneI as
Plmephates
prone I as
Plmephales
promelas
0.560-3.?
IK29)
0.08". (T<»)
BCFA —
BCFCH —
Lepomls I
macrochlrus
Ouvenlle)
Trachlnotus BSA
carolInus
(Juvenile)
0.075 (Tlf)
0.018 (T 1Z
HO)
1-5 (S81)
apparently unaffected* LOH levels of
cooper caused varied anomalies In qlll
lamellae as determined by electron
microscopy.
same as above
a«(o,d,e, Copper at lfl.it oob affected
f, acidity survival, growth, and soaHnlnq. Lexer
conduc- concentrations also reduced qroHth and
tivlty, spanning but apparently not eqq
and Cu hatchabl 11ty. The maximum acceptable
« toxicant concentration (MATC) for the
fathead minnow Mas calculated to be
between 0.13 to 0.?2 of the 96-hr TL sub
m. Some difference In results In hard
and soft Hater was found but the authors
recommend further study. Us* and further
develocment of the application factor
approach was further recommended.
same as above
BaKer
(19f>9»,
AMIC-3763
Mount, et al
(1969),
AMIC-376S
same as above
Mount, et al
(1969),
AMIC-376S
Mount, et al
(1969),
AMIC-3765
a*,o,d,o,
f, acidity,
conduc-
tivity,
and Cu
ao,e,d,e,
I, acidity,
conduc-
tivity,
and Gu
a*,c,e,f CoDoer caused a respiratory 0"Hara
Increase as concentration levels Mere (1971),
Increased. Recovery from Initial stress AHIC-3793
by copcer was delayed at higher
concentrations. The author suggests the
flowing Mater fish resoirometer technique
as a fast and sensitive tool for
evaluating pollutants.
a,c,e,f,I, In this study of pomoano salinity Blrdsonq, et
and Mas controlled at 10, 20, and 30 ppt and al (1971),
sulfate, Investlqated as a variable. tcriflavin, AMIC-5570
sodium, formalin, and potassium permanganate uere
calcium, slightly more toxic at the highest
potassium, salinity, while copper sulfate Mas
magnesium, slightly less-toxic. These compounds are
-------
Co»oound
Field Field
Organlsn Study Location
Toxlelty,
Active
Ingredient,
Ppm
Experimental
Variables,
Control Ied
or Noted
Comments
*?« f erence
carbonate, used as prophylactic bacterial
blcarbon- treatments. All appeared to tie
ate, reasonably safe to use except* possibly
salinity potassium permanganate.
Cooper sulfat*
Copper sulfat*
Cooo«r sulfate
Copper sul fat*
Copper sut fate
Copper sulfate
Copper (« Coooer
sulfat«)
Oncorhynchus
tshawy tscha
(egqs)
Oncorhynchus
tshaxytseha
(93
percent K)
0.62 (Ti>)
3.0 (T",)
a*,c,d,f
same as above
Hazel, et al
(1970) ,
AKIC-5572
Wei Iborn
at,c,d,e, Striped bass flnqerlln^s were
f,p, and apparently much more sensitive to
Iron therapeutic and herbicldal compounds than
many freshwater fish.
a*,c,e,f,a Adult crayfish were found to be Hubschman
more resistant to copper sulfate than the (1967),
young. Several life stages were studied,
and additional exposure variations were
Included In the exoer Irnen tat 1 on.
Mortality of newly-hatched crayfish
occurred at 0.1?5 pom, and growth was
Inhibited at concentrations down to 0.015
ppm over a 30-day period. Sublethal
effects of copper were well established
and the procedure appears to be a good
one.
1.0 (T13)
0.015 (SB)
1.7
a*,c,e,f,q
a*,c,e,f,q
same as above
same as above
Hubschman
(1967) ,
AMIC-598S
Hubschwan
(1967) ,
AMIC-598S
a,c,d,«,f Survival, qroxth, reoroductton, Arthur, et
and feeding were the responses used to al (1970)»
-------
Coooer (as Copper
sulfate)
Coporr (as Copper
sul fate)
Coooer (as Copper
sulfate)
Copper (as Copoer
sulfate)
Copper (as Copper
sulfate)
Cooper (plus
PHENOL)
Campeloma
declsun
Physa Integra
Physa Integra
Gammarus
pseudo~
liranaeua
Gammarus
pseudo-
llanaeua
Sal mo
galrdner1
RCFA —
'and
CH
BCFA —
and
CH
8CFA --
and
CH
BCFA —
and
CH
BCFA —
and
CH
BSA
Copper (plus zinc,
nickel)
Sal mo
galrdnerl
BSA
0.008-0.01
O.OT9
0.008-0.011.8
(NTH 6 wk)
0.030 (T!»)
atctd,et f
,c,d,e,f
a,c,d,e,i
a,c,d,e,(
0.008-0.01
-------
Comoound
Copper (plus zinc.
phenol >
Cooper
Coooer
Copper
Copper
Copper
Copper
Coooer
Organism
Sal mo
galrdner 1
Alosa
paeudo-
harengua
Coregonus
artedll
Coregonus
clupeafornls
Coregonus
hoyl
Prosoolum
cy 1 Indraceum
Sal vel Inus
namaycush
Osmerus
•ordax
Field
Study
8SA
FL
FL
FL
FL
FL
FL
FL
Toxlclty,
Active
Flel d Ingredient,
Locat Ion Ppm
0.6-2.
-------
VQ
Copper
Copper
Copper
Copper
Copper
Copper
Carasslus FL
auratus
Notropis FL
hudsonlus
Percopsls FL
omlscomaycus
Roccus FL
chrysops
Perca FL
fIavescens •
Stlzostedlon FL
vltreum
vltreun
Great LaKes IMresldue)
- Superior,
Michigan,
and Erie
Great LaKes l.O(resldue)
- Superior,
Mlchlgan,
and Erie.
1.8(resldue)
(((residue)
Great LaKes
- Superior,
Mlchlgan,
and Erie
Great LaKes
- Suoerlor,
Mlchlgan,
and Erie
Great LaKes 3(residue)
- Superior,
MlcM gan, and
Erie
Great LaKes i» (residue)
- Superior.
Michigan,
and Erie
same as above
same as above
same as above
same as above
same as above
same as above
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
&MIC-3778
Lucas, et at
(1970),
AMIC-3778
Lucas, et
(1970),
AMIC-3778
Lucas, et
(1970),
AMIC-3778
al
Lucas, et al
(1978),
HHTC-3778
Copper
Coreqonus FL
clupeafornls
Moose LaKe, O.S (residue)
Can.
Copper
Copper
Copper
Coregonus FL
clupeafornls
Esox luclus FL
Esox luclus FL
LaKe
Ontario,
Can.
0.9 (residue)
Moose LaKe, 0.07 (residue)
Can.
LaKe St. 0.9 (residue)
Pierre, Can.
Concentrations of 13 toxic
elements In dressed fish from heavily
Industrialized and non-IndustrialIzed
areas were determined. Only trercury
exceeded regulatory limits, and
concentrations of most elements were
essentially the same In fish fron both
areas.
same as above
same as above
same as above
Uthe, et
AL(1971),
AMIC-3819
Uthe, etal
(1971),
AHIC-3819
Uthe, et at
(1971),AMIC-
3819
Uthe, et al
(1971),AMIC-
3819
-------
Compound
Copper
Copper
Copper
Cooper
Organism
Esox tuclus
Osmerus
mordax
Perca
( 1 avescens
Sal vel Inus
Field
Study
FL
FL
FL
BDFCH
Field
Locat Ion
Lake Erie.
Can.
Lake Erie,
Can.
Lake Erie,
Can.
Toxlclty, experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
0.7 (residue) — same as above
0.8 (residue) — same as above
1,3 (residue) — same as above
Re f erence
Uthe, et al
11971), AMIC-
3819
Uthe, et al
(1971) .AMIC-
3819
Uthe, et al
(1971), AHIC-
3819
McKlm, et al
v£>
CD
Copper
Copper
Copper
1 ontInalIs
(eqgs)
cooper did not adversely affect survival, (1970),
qroHth, or scanning of brook trout. AMIC-3S?!
However, this concentration level had
drastic effect on Juvenile trout. The
cooper also delayed yolk sac absorption
and delayed fry development. The maximum
acceptable toxicant concentration (HATC)
Has calculated to be between 9.5 to 17.^
ppb copper.
SaIvelInus
fontInalis
I )uvenlles)
SaIveIInus
fontInalIs
(adults)
Paralabrax
clathratus
BOFCH
BDFCH —
0.017 (K)
0.1 (T<»)
a*,c ,d,e,f
a'.c.d.e,f
same as above
same as above
FM Scattergood 2 (dorsal
Steam Plant, muscle
LosAngeles, RESIDUE)
Cat.
Fish collected from an effluent
Dloe of a steam plant and from offshore
naters of Catallnn Island were analyzed
for trace element content. Trace element
content of the effluent water was at
least 5 times greater than that of nor«al
sea water for cadmium, copper, nickel,
zinc, and chromium. Livers of fish Iron
the effluent were nearly twice the size
of those from the ocean. Greatest
differences in concentration occurred
with aluminum, cadmium, and nickel.
Silver, barium, lithium, and lead showed
the least differences. The author
HcKlm.et al
(1970).
AHIC-3821
Hc
-------
Cooo«r
Copper
Copper
Copper
Copper
Copper
Copper
Copper
Paralabrax
elathratus
Paralabrax
clathratus
Paralabrax
elathratus
Paralabrax
elathratus
Paralabrax
clathratus
Paralabrax
clathratus
(gravid
females)
Paralabrax
elathratus
Paralabrax
clathratus
FH Catallna 2 (dorsal
Island, Cal. muscle
residue)
FH Scattergood Z (ventral
Steam Plant, muscle
LosAngeles, residue)
Cal.
FH Catallna 2 (ventral
Island, Cal. muscle
residue)
FH Scatterqood 6 (gonads
Steam Plant, residue)
LosAngeles,
Cal.
FH Catallna 5 (gonads
Island, Cal. residue)
FH Catallna 5
Island, Cal. (gonads
residue)
FH Scatterqood 5 (liver
Steam Plant, residue)
LosAngeles,
Cal.
FH Catallna 6 (liver
Island, Cal. residue)
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on marine organlsns.
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-5980
Staoleton
(1968),
AHIC-5980
Stapleton
(1968)»
AMIC-5980
S t a D I e t on
(1968),
AHTC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968) ,
AMIC-5980
Staoleton
(1968) ,
AMIC-5980
Copper
Copper
Paralabrax FH Scattcrgood 3 (Integument
clathratus Steam Plant, residue)
LosAmeles,
Cal.
Paralabrax FH Catallna 3 (Integument
elathratus Island, Cal. residue)
same as above
sane as above
Staoleton
(1968) ,
AMIC-"5980
Staoleton
(1968),
AMIC-5980
Copper
Paralabrax FH Scattergood 15 '(heart
elathratus Steam Plant, residue)
LosAngeles,
same as above
Staoleton
(1968),
AMIC-5980
-------
>
I
Compound
Copper
Copper
Copper
Copper
Corexlt 766%
Corexlt 766%
Corexlt 766%
Corexlt 766%
Toxlclty,
Active
Field Field Ingredient,
Organlsn Study Location Ppm
Cal.
Paralabrax FH Catallna 1? (heart
clathratus Island, Cal. residue)
Paralabrax FH Scattergood 8 (eyeball
clathratus Steam Plant, residue)
LosAngeles,
Cal.
Paralahrax FH Catallna % (eyeball
clathratus Island, Cal. residue)
Sal mo BSA -- 0.75 (T2)
galrdnerl
Plnephales BSA — 3?00 CT%)
promeles
Plmephales BSA — 180 (HSC)
promel as
Biochemical L — 380,000
oxygen deoand
Steelhead BSA — 15.8 (T%)
trout
If Ingerl Ings)
Experimental
Variables,
Control led
or Noted Comments
~ same as above
— - same as above
-- same as above
a,c,e RalnboH trout Here exposed to
coooer* phenol, zinc, or nickel solutions
to determine it8-hour LCSO values for
mixtures of cooper and phenoll coooer.
zinc, and phenol I and copoer, zinc, and
nickel. It Has concluded that acute
lethal toxlcltles of the mixtures could
be adequately described by summations of
the fractional toxlcitles.
c,d,e,f Toxlclty of six oil spill
dlsoersants Has determined along with
BOO values. Pond nater Has used as
diluent and oil Has Included In the
experiment. Oil markedly reduced
toxlclty of all dlsoersants. Data are
given as "most probable" 96-hr TL sub •.
c,d,e,f same as above
c,d,e,f same as above
~ Evaluation of 11 oil dlspersants
resulted in a ranking for each and a
recommendation for use according to the
Ref erence
S tapleton
(1968) ,
AMIC-5980
S t a D 1 e t on
(1968) ,
AMIC-5980
Staol eton
(1968) ,
AMIC-5980
BroHn, et al
(1970>,A»1IC-
599
-------
Corexlt 7661).
Corexlt
Corexlt 766".
Corcxlt 766V
Coho salmon BSA Hood Canal
(flngerllngs) In Hoodsport,
situ Wash.
Pacific
oyster
(larvae)
BSA Hood Canal
In Hoodsport,
situ Wash.
Cardlun edule BSA —
.0 (K)
. 0-80.0 (SB)
3300-10,ODU
(TZ)
Crangon
crangon
BSA
3300-10,000
(TZ)
776i» appeared to have the least toxlclty
tilth fair to good oil dispersion
capablllty.
sane aa above
same 03 above
ae(contln- One hundred-forty surface active
uous eer- agents, solvent emuls1flers, pesticides,
ation, sea-oolychlorlnated blphenyls, pure
water, and Inorqanlc, 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 freshwater
organisms.
at I contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
sane as above
Tracy, et al
(1969).
AKIC-3831*.
Tracy, et al
(1969),
AMIC-3331*
Portmann, et
al (197H,
AMIC-7701
Portmann. «t
al (1971),
ANIC-7701
Corexlt 7664
Limsnda
llmanda
BSA
1000-3300 (TZ)
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AHIC-7701
Corexlt 766*
Salmo salar
(parr)
500 (NTEIt)
Corexlt 766«,
Gammarus
oceanlcus
BSA
1900 (NTE)
a»,e Aroclors l?5it and 1221 were
(mixed tap evaluated for toxic effect with Corexlt
or 766i» (weight ratio 1;19) as an
seawater) emulsifying aqent. Since only two fish
were used for each exoosure, the author
notes that the results are only
preliminary. However, PCR"s appeared to
be less toxic to Atlantic salmon parr
than chlorinated hydrocarbon pesticides.
ZItko
(1970),
AHIC-Z3
a» (weekly Aroclor 125<» solutions or
solution susoenslons with Corexit 766<» at varied
change,
seawater)
Hlldlsh
(1970),
concentrations in seawater resulted In AMIC—69
varying toxlclty of the Aroclor. Corexlt
was not lethal at 1900 ppm but caused
sublethal brnchial edema at
-------
o
ro
Compound
Corcxlt 766".
Cor«Klf 9666
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organist) Study Location pp* or Noted Comments
Ganmarus BSA —
oceanlcus
Crangon BSA ~
crangon
0.19 (SB) a'
(week lysot
ut Ion
change.
seawater)
3300 (TZ) a*(contln-
UOUS &OC-
concentrations down to 0.19 pom. The
author notes a possible synerqlstlc
effect betxeen the two compounds.
same as above
One hundred-t or ty surface active
ag»nts, solvent emu 1 s 1 f 1 ers, pesticides.
ation. aoa-POl yen lorlnated blohenyls, cure
Counaphos
Co-Pal
Co-Pal
Rasbora BCFA —
heteromorpha and
BSA
Morone BSA —
saxat 1 1 Is
( linger! Ings)
Mercenarla I —
nercenarla
(eggs)
water, and
daily
solution
renewal )
0.0<»6 (T2) a»,c,e,f.
hard (HW)
or
SCFT(SH)
synthetic
dl lut Ion
water, or
seaHater
for some
species
62 (Ti.) a,c,d,e,f,
p
9.12 (T3)
Inorqanlc, and organic chemicals Here
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal Kith
toxlclty of chemicals to freshnater
organises.
One hundred sixty-four
pesticides, netting aqents, and
miscellaneous water pollutants showed a
wide range of toxlclty spanning 1? orders
of magnitude. Knowing 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 were most toxic In hard water
and sometimes the ooooslte was true.
Testing the actual material as sold was
found to be essential.
All compounds were Investigated
becausp of their probable usage In
hatchery production of white bass.
Comoounds that can be used at recommended
concentrations were Aauathol, Casaron,
tlndane, and Terramycln concentrate.
Those that should not be used were
Acrlflavlne, Raylusclde, Malachite green
oxalate, and Malathlon.
The effect of 52 pesticides on
embryonic development of clams and
oysters was reported. Synerglstlc
Reference
Wl Idlsh
(1970) ,
»MIC-f.9
Portmann, et
al
(1971), AMIC-
7701
A 1 abaster
(1969) ,
AMIC-51,25
Met (born
(1971),
AMIC-5571
Davis, et al
(1969) ,AHIC-
effects with solvents were also reported. 5990
Most of the compounds affected
-------
fe
U)
Co-Rat
Co-P»l
Co-Rat
Craine OSR
Hercenarla
mercenarla
(larvae)
Crassostrea
vlrglnlea
(eggs)
Crassostrea
virqlnlea
(larvae)
Crangon
crangon
BSA
5.21 (T 12)
D.ll (T2)
greater than
1.0 (T 1U
330-1000 (T2)
Cresols
AgonuS BSA
cataphractus
10-33 (T2)
Cresols
Carelnus
•aenas
BSA
10-100
-------
o
-F-
Field Field
Compound Organic" Study Local lor
Cresols Cardluit edule BS4 —
Crvsol* Pleuronectes 8SA
pi atessa
Crossauard Crnngon BS4
crangon
Crotothan* Pasbora BCFA ~
heteromorpha and
9SA
Crow solvent H Crangon BSA
crangon
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
1 Pom or Noted Comments
greater than ac-(contin- same as above
100
-------
Crt NI> Cut CN, and Plmephales
Zn promelas
Cpt Nit Cut CN> and Catostonus
Zn conmersonl
C3
Wolffla
papulifera
BSACF Grand River between
(ML) at 1.25-3.75
Wyoming,Nlch percent (T3)
Iqan
BSACF Grand River between
tML) at 1.25-3.75
Wyoming,Hlch percent (T3>
Igan
100 (K)
A mobl le' bloassay unit Has
utilized to conduct this study of
municipal wastewater containing the
Indicated toxicants. River water was
a,c,e, used as diluent. The conclusion was
conductlvl reached that synerglstlc or additive
Zllllch
(1969).
ty. Nit toxic effects occurred since toxlclty was AHIC-3906
Cu, Cr, greater than that of any of the Ions
CNt and Zn singly.
a,c,e,
conductivl
ty, Nl,
Cu, Cr,
CN, and Zn
Hunter's
medium
diluted
1:5
same as above
ZllIIch
(1969),
AMTC-Z9C6
All compounds ware harmful to Worthley, at
duckweed to gone degree. Decreased al,(1971),
populations were noted at non-lethal AMIC-3233
concentrations and some compounds
(Halathlon and 2.I4.-D) caused toratogenlc
effects at concentrations as low as 1 ppm.
fe
CuCIZ ZHZO (as Cu) Platymonas L
subcordi-
formis
CuCIZ 2HZO (as Cu) Porphyrldlua L
cruentum
CuCIZ ZH20 (as Cu) SKeletonena L
costatum
CuCIZ ZHZD (as Cu) Amohldlnlu* L
carterl
CuCIZ ZHZO (as Cu) Chaetoceros I
sp
CuCIZ ZHZO (as Cu) Cyclotella L
nana
CuC12 2H20 (as Cu) Dunallella L
tortlolecta
CuC12 2H20 (as Cu) Isochryals L
jelbana
approx.1.0 (K) 5SM and
NSH
approx. 0.5(K) SSH and
NSH
aporox. 0.15 SSH and
(K) NSH
less than 0.05 SSH and
(K) NSH
approx. 0.05 SSM and
(K) NSH
approx. 0.15 SSH and
(K) NSH
^50 (50 percent S3K and
K) N3W
Approx. 0.2 K) SSM and
NSW
NTA stimulated algal growth In Frlckson, et
cultures without added copper and reduced a' (1970),
toxlclty of copper at all levels of AHIC-9
Erlckson, et
al (1970),
AHIC-iti»9
Erlckson, et
al (1970),
AKIC-U49
Erlckson, et
al (1970),
-------
Compound
CuC12 3120 (as Cu)
CuC12 2H20 (as Cu)
CuC12 2H20 (as Cu)
CuC12 21120 (as Cu)
Cunllate RQ 2<>
Cunllat* RQ 2<>
Cunllate RO ?<.
Organism
Monochryals
Lutheri
Nannochloris
oculata
Nitzachia
clogtorium
Ollathodlacug
luteua
Salmo
galPdnepl
RasboPa
heterocnoppha
RasboPa
h«t«Pomoppha
Toxlclty, Experimental
Active Var 1 ab 1 es.
Field Field Ingredient. Controlled
Study Location Ppm op Noted Comments
L
L
L
L
RCFA
and
BSA
BCFA «
and
BSA
BCFA —
and
BSA
Approx. 0.5 SSM and
(K) N3W
Approx. 0.5 SSM and
(K) NSW
Approx. 0.05 SSM and
(K) NSW
Approx. 0.05 SSM and
NSW
0.5 (T2, a'.c.e.f,
hapdwatep) hard
(HH) or
soft (SW)
syn thet Ic
dl lut Ion
water , or
seawa t ep
tor some
species
!.<• (T2, a»,c,e,f.
sottwaleP) hard(HW)
or soft
synthetic
dl lut Ion
water ,
orseawater
f OP some
species
0.9 ( T2 » a*,c,e,f»
naPdwatep) hard(HW)
OP soft
(SH)
synthetic
dilution
watep.
same as above
same as above
same as above
some as above
One hundred sixty-four
pesticides, wetting agents, and
mlscel laneous water ool lutants showed a
wide pange of toxlclty spanning 12 ordePS
of magnitude. Knowing the toxlclty and
percentage of al 1 components of a
formulation did not result In easy
prertictahl 1 1 tv 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
sane as above
Reference
Eriekson, et
al (1970),
Erickgon, et
al (1970),
Erlckaon, et
el (1970),
AMIC-U49
Erickaon, et
tl (1970),
A1--IC-UJ4.9
Al abaster
(1969) ,WIC-
5U21;
A lahastep
(1969) .AMIC-
51.25
Al abastep
(1969) .A1IC-
51.25
-------
CuDPlc ammonium
sulfate (as Cu)
Phormldlum
amblguum
Cuorlc chloramlne
Cuorlc sulfate
Phormldlum
amblguum
i —^
Salve Iinus BCFA
fontlnalIs
(6-9 in.)
Cuorlc sulfate
Cuprlnol
SaIveIInus
font InalIs
(6-8 In.)
Cranqon
crangon
BCFCH —
BSA
orseawater
for some
species
0.5-10.0 (16
percent growth
innlbl tedii»)
0.5-10.0 (100
percent growth
Inhibited lit)
0.038-0.069(58
6 and 21)
0.017-0.033(38
337)
3.3-10 (T2)
a",c,e> f ,
Of 71» chemicals evaluated as
alqlcldes, only 1 were more toxic than
CuSO
-------
Compound Organise
Cut Ni, Cr, CN, and Plmeohales
Zn prome 1 as
Field
Study
BSACF
(ML)
Field
Locat Ion
Grand River
at
Wyoming, Mich
Iqan
Toxlclty,
Active
Ingred lent ,
Ppm
between
1.25-3.75
percent (T3)
Exper Itnen ta 1
Variables,
Control 1 ed
or Noted
a,c,e, con- A
ductivity, utilized
Ni,Cu,Cr, municipal
CN, and Zn Indicated
Comments
mobile bloassay unit was
to conduct this study of
wastewater containing the
toxicants* River Hater Has
Reference
711 1 Ich
(1169) ,
AMIC-2906
Cu, Nl, Cr, CN, and
Zn
Catostomus BSACF Grand River between
commersonl (ML) at 1.35-3.75
Wyoming,Mich percent (T3)
Igan
used as diluent. The conclusion Has
'reached that synerglstlc or additive
toxic effects occurred since toxlclty MBS
greater than that of any of the ions
singly.
a,c,e, con-
ductlvity,
Ni,Cu,Cr,
CN, and Zn
same as above
21 I IIch
(1969),
AMIC-3906
ex
00
Fundulus
heterocl1tus
BSA
0.00051-0.00225 a«,c,e,
(T<>) and
synthetIc.
seawater
A laboratory procedure based on
Standard Methods for qf>-hr toxlclty
determinations of crude oil and
ol l-dlspersant mixtures Has described.
The dlsoersants varied considerably In
toxlclty, ranging from 0.01 to 7.1 m!/l,
TL50 for 96 hr. These did not differ
significantly from 2<«0 hr values. The
dlspersants were designated as CX, 00,
Cl, On, AQ, PC, MM, TN, BP, and NA with
no further description of their chemical
nature or source. Only a few bloassays
were conducted with shrimp. HollusKs and
echlnoderms were suggested as suitable
test animals. The authors stated that
the method could be used to test any
product for toxlclty In seanater.
LaSoche, et
al (1970),
ANIC-i»«tS
CX
Nereis vlrens BSA
0.00074-0.0071 a",c,e,
and
synthetic
seawater
same as above
LaRoche.et
al (1970),
AMIC-"t«t5
Cyanides
Leoomls
•acrochlrus
BSA
0.18
a',e, and
synthetic
dllutIon
water
This study Has conducted to
Patrick, et
determine the relative toxlcitles of 30 al (1968),
common constituents of Industrial Hastes AMIC-5720
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.
-------
Cyanides
Cyclohexlnlde
Physa BSA
heterostrooha
Phornldlum
amblguun
0.1.32
0.5-10.0 (66
percent growth
Inhibited)
Oalacld*
Rasbora
heteromorpha
BCFA
and
BSA
620
greater than
500 (T2,
hardnater)
a',e, and
synthetic
dilution
Hater
same as above
a*,o,e,r,
hard IHW)
or soft
ISW) syn-
thetic
dilution
water, or
seawater
for aorae
species
a»,c,e,f,
hard (HW)
or soft
(SM)
synthetic
dllutIon
Hater, or
seawater
for some
Patrick, et
al (196S),
AMIC-5720
Of fit chemicals evaluated as Otto (1970),
slglcldes, only 9 Mere more toxic than ANIC-S92
CuSOi.. None Inhibited growth of
mat-forming algae for more than 2 Meeks.
CuSO<» formulated Hlth certain wetting
aaents Has more toxic than CuSOi* alone.
Cooper chloramlne 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 pom). 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.
One hundred sixty-four . Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a AMIC—5*»25
Hide range of toxiclty scanning 12 orders
of magnitude. Knowing the toxiclty and
percentage of all components of a
formulation did not result In easy
predictability of the toxiclty of a
mixture ot materials. Sometimes
pesticides were most toxic In hard water
and sometimes the ooooslte Has true.
Testing the actual material as sold was
found to be essential.
Approximate toxlcltles of Hawdesley-
numerous pesticides commonly used In Thomas
Britain were summarized. An excellent (1971),A1IC-
brlef, general discussion of toxiclty 1056
testing is also present.
One hundred sixty-four Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a AMIC-5i»Z5
wide range of toxiclty spanning 12 orders
of magnitude. Knowing the toxicitv and
percentage ot all components of a
formulation did not result In easy
predictability of the toxiclty of a
mixture of materials. Sonetiaes
-------
Compound
Dalapon
Dalapon
Dalaoon
Oalapon
08 P
Toxiclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organise Study Location Ppm or Noted Comments
species pesticides Here most toxic In hard water
and sometimes the opposite Has true.
Testing the actual material as sold was
found to be essential.
Rasbora BCFA -- i»7 uous aor-
ation, sea-
water, and
daily
solution
renewal )
Pal»emoni»tes BCF ~ 0.08 (residue) a* Magnification of DOT and Aldrln
kadi ak ens Is tagged Hlth C-lit occurred rapidly.
R«f erence
A 1 abaster
(1969) ,AHIC-
5i»Z5
Portmann, et
a 1 ( 197 1) t
AMIC-7701
Portmann, et
al (1971).
AMIC-7701
Portnann, «t
al (1971),
AMIC-7701
Johnson, et
al
-------
09 P
ODD (C-lfr labelled)
Palaemonetes, BCF
KadlaKensls
Sorghum
haloense
>
I
ODD CC-li. labelled)
Estlqmene
acrea
L
(Mod-
el
BOOST
stem)
0.0001
1 Ib per A
(NTE)
a,c,g,
standard
reference
water and
sand
L
(Mod-
el
ecosy
a tea)
1 Ibper A
(K-NTE)
standard
reference
water and
sand
Biological magnification factors of 2900
to llitilOO depending on the species were
found for DDT, and 22,800 to I'd,000 for
Aldrln. Marked degradation 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
3820
Johnson,*t
al (1971),
AMIC-3820
This small laboratory model Metcalf, et
ecosystem procedure was developed to al (1971),
study pesticide biodegradabl I i ty and AHIC-11.95
ecoloalcal magnification. The Tood-chaln
pathways In this system Here! (1)
sorrjhuir - caterplller (larva), (2)
caterplller (excreta) - flecloaonlum, (3)
Oedoqonlum - snail, (it) Estiqmene
(excreta) - diatoms, (5) Diatoms -
plankton, (6) Plankton - Culex (larvae),
(7) Culex - Gambusla. The fish is the
top of the Tood chain. Using
Isotoplcally labeled pesticides (1
Ib/acre application rate), residues Here
determined for only selected organisms
(snail, mosquito, and fish) and nater.
ReproducibiI 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
Hetcalf, et
al (1971),
AMIC-l
-------
Compound
000 (C-l<> labelled)
000 (C-l«. labelled)
000 (C-l«. label led)
000 (C-l". labelled)
000 (C-l* labelled)
ODD (C-l«. labelled)
000 IC-lt labelled)
Organlsn
Oaphnla magna
Culex nlplens
qulnque-
faaolatus
Oedogonl UM
cardiacun
Ganbusla
af finis
Diatoms
(Navicula,
Coacinodls-
cus, Dlp-
loness, and
Protozoa
(Jiuclearla,
Coleps,
VoTtlcella,
and
Parameolum)
Rotifers
CAaplanehnop-
ua, Notomat-
ta, Euclaris,
fr^.-prHTrm)
Field Field
Study Location
L
(Mod-
el
« co ays
torn)
L
(Mod.
el
ecosy
stem)
L
(Mod-
el
BOOST
stem)
L
(Mod-
el
ecosy
stem)
L
(Mod-
el
•COST
•tea)
L
(Mod-
el
ecosy
stem)
L
(Mod-
el
ecosy
stem)
Toxlcl ty.
Active
Ingredient,
Pom
1 Ib per A
(K-NTE)
S.a(resldue)
1 Ib per A
(NTE)
39.1 (residue)
1 Ib per A
(NTE)
1 Ib per A
(NTE)
1 Ib per A
(NTE)
Experimental
Variables,
Control led
or Noted Comments
a,c,g, same as above
standard
reference
water and
sand
3,0,9, same as above
standard
ref erence
Mater and
sand
a,c,g, sane as above
standard
ref erence
Mater and
sand
a,c,o, sane as above
standard
ref erence
water and
sand
a,c,a, same as above
standard
ref erence
water and
sand
a,c,g, same as above
standard
reference
water and
sand
a,c,g, same as above
standard
reference
water and
sand
Ref erence
Hetcalt, et
al (1971) ,
AMTC-l«i9S
Hetcalf, et
al (1971),
AHIC-1U95
Metcalf, et
al (1971) ,
AM.IC-li.91;
Hetcalf, et
al (1971),
AHIC-1<»95
Hetcalf, et
al (1971),
AHT.C-1(>95
Hetcalf, et
al (1971),
AMIC-H95
Hetcalf, at
al
(1971), AMIC-
11.95
-------
000-IC-lt labelled) Hater
X.
(Mod.
el
•cosy
n)
0.006
Iresldue)
•.e.g.
standard
reference
water and
sand
sane as above
Hetcalf, et
al (1971),
AMIC-1%95
000 Io,p")
Angui I la
rostrata
FRL
H
M
U)
000 (P»p")
ODD (0,0-1
000 (O.p">
000 (D,p")
ODD
St. John,
N.B.t Can.
0.19 (residue) —
Esox nlger FRL St. John,
N.B., Can.
Sal mo salar FRL St. John,
0.03 (residue) —
0.0? (residue) —
Clupea
harengus
Sconber
scombrus
Llmneohl lus
rhomblcus
(larvae)
FRL
FRL
FS
St. John,
N.n., Can.
St. John,
N.B. , Can.
Knights
Creek, Dun
County,
Hlsc.
0.01-0.0".
(residue)
0.03 (residue)
0.007(Hhole
body residue)
PCB"s Here found In hloher
concentrations than organochlorlne
pesticides In all fish analyzed. The
authors point out that PCB Is less toxic
In an acute sense than organochlorlnes,
that little Is Known of sublethal PCB
effects, and that more Knowledge of PCB
distribution and effects Is needed.
sane as above
sane as above
sane as above
same as above
Zltko(1971),
aMIC-3715
71tKo
(1971),AMIC-
3715
ZltKo
(19711,»MIC-
3715
ZltKo(1971),
AMIC-3711;
Zltko(1971),
ANIC-3715
Samoles ot Hater, silt, bettor, Moubry, et
debris, bottom organisms, and fish Mere al
taken in 1966 from a creek ad)acent to an (1968),AHIC-
orchard which had been treated in 3753
1963-1065 xlth various chlorinated
hydrocarbon pesticides. No residues were
found in water samples. Silt samples
contained 0.002-0.013 ppm endrln and
0-0.005 pom dleldrln. Endrln residues ot
0.011-0.0?5 pom and 0.00?-0.006 ppii
dleldrln were found In debris samoles.
Despite limited control data, residue
analyses Indicated that contamination of
the environment studied was limited.
-------
H
Coaoound
000
DOO
000
000
000
000
000
Oraan 1 sm
Phlnichthys
atratulus
Gammarus so*
Sal vel Inus
fontlnal Is
Semotl lus
atromacul at us
Cottus balrdl
Slal Is so.
(1 nrvael
Carasslus
auratus
Field Field
Study Locat Ion
FS Knlqhts
CreeK, Dun
Count y ,
wise.
FS Knlqhts
Crpek, Dun
Coun t y ,
Wise.
FS Knlqhts
Creek, Dun
Count y,
Hlsc.
FS Knlqhts
Creek, Oun
County,
Hlsc.
FS Kniqhts
Creek, Oun
County,
Hlsc.
FS Knlqhts
Creek, Oun
County,
Hlsc.
I
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted Comments
0.76 -- same as above
(fat
residue)
0.007 (whole -- same as above
bodyresldue)
residue)
0.26-1.0"! -- same as above
(fat
residue)
0 .53-0.67 ( fat -- same as above
residue)
0.<»-0.
-------
000
000
000
000
VJI
000
000
000
oon
000
000
000
000
Palaemonetes 8CF
Ka'llakensls
(adult)
Daphnla maqna BCF
(adult)
Palaemonetes BCF
Kadlakensls
(adult)
0.04 (residue) a*
0.0001 (S83)
0.0001 (SB3)
Archootltes FL Clear Lake. 316 (flesh
Interruotus Cal. residue)
Orthodon FL
mlcrolepl-
dotus
Pomoxls FL
nlgromaeulatu
s
Aechmophorus FL
occidental is
Bucephala FL
cl angula
Larus spp. FL
Larus . FL
delanarensls
Merqus FL
merganser
Plankton FL
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
0.5-7.0 (flesh
residue)
10-2
-------
Comoound
000
000
000
000
ono
ON 000
000
000
000
Organism
Arrhoo 1 1 tes
Interruotus
Ic talurus
catus
Ic tal urus
catus
Lavlnl a
ex 1 1 1 cauda
Lenoml s
cy ane 1 1 us
Leoomls
cy ane 1 1 us
Ml crooterus
sal mol des
Mlcronterus
sal moldes
P»rca
f 1 avescens
Field
Study
FL
FL
FL
FL
FL
FL
FL
FL
FLR
Flel d
Locat Ion
Clear Lake,
Cal.
Clear Lake,
Cal .
C 1 f ar L ak e ,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
Clear Lake,
Cal.
93 sampl Ing
stations In
Toxlclty,
Active
Ingredient,
Ppm
3,97? (fat
residue)
1.3-1U". (flesh
residue)
220-2,350 (fat
residue)
less than 1-2
(flesh
residue)
2 (flesh
residue)
1D3 (fat
residue)
0.2-111 (flesh
residue)
28-1.37 (fat
residue)
0.21.-5.7
(residue)
Experimental
Variables,
Control 1 ed
or Noted 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
Fish Indigenous to Massachusetts
freshwater streams were analyzed for DOT
Reference
Linn, etal
(1969) .
L Inn, e t
AL ( 1 96 9) ,
Linn, et
AMIC-S521
L Jnn.e t al
( 1969) ,
AHIC-5S21
L Inn, et al
(1969) ,«MIC-
L Inn, et al
(1969) .AHIC-
L Inn.et al
(1969) ,
Linn, etal
(1969) ,
AMIC-5521
Lyman, et al
(1968) ,
Mass.
and DOT metabolites during 1965-1967. AMIC-3839
Generally there was an Increase In
oestlclde content during the three year
period.
000
Leoonls
FLR 93 sampling 0-6.7
sane as above
Lyman, et al
-------
000
000
000
000
ODD
000
000
glbbosus
Catostomus
commersonl
Ictalurus
nebulosus
Cyorlnus
carolo
FLR
FLR
FLR
Esox nlger FLR
Notemlqonus
crysoleucas
Semotllus FLR
corporalIs
Leoomls FLR
macrochlrus
stations In
Mass.
93 samollng
stations In
Mass.
93 samollng
stations In
Mass.
93 samollnq
stations In
Mass.
93 sampling
statlons In
Mass.
93 sampling
stations In
Mass.
93 samolIng
stations In
Mass.
93 samel Ing
stations In
Mass.
(residue)
0.03-12.5
{residue)
1.2 (residue)
0.21.-1.9
(residue)
0.30 (residue)
0.15-2.7
(residue)
0.07-1..3
(residue)
0.1.8-7.3
(residue)
same as above
same as above
same as above
same as above
sane as above
same as above
same as above
(1968),
AMIC-3839
Lyman, et •!
(1968),
AMIC-3839
Lyman, et al
(1968),
AMIC-3839
Lyman, et al
(1968),
OMIC-3839
Lyman, etal
(195?).
AMTC-3839
Lymant et al
(1968),
SMIC-3839
Lyiran, et al
(196*) .
&MIC-3839
Ly»an, et al
(1968),
AMIC-3839
000
000
000
000
000
Ambloolltes FLR
ruoestrls
Senotllus FLR
atromaculatus
Mlcrooterus FLR
do)omleul
Alosa
p seudo-
harengua
FLR
Fundulus FLR
heterocl1tus
93 samollng
stations In
Mass.
93 samplIng
stations In
Mass.
93 samolIng
stations In
Mass.
93 samolIng
stations In
Mass.
93 samolIng
stations In
Mass.
0.30-10.8
(residue)
0.18-0.61.
(residue)
0.20-0.5D
(resldue)
0.88 (residue) ~
1.7-3.6
(residue)
same as above
same as above
same as above
same as above
same as above
Lyman, et al
(1968),
AMIC-3839
Lyman, et al
(1968),
4MIC-3839
Lyman, et al
(1968),
AMIC-3839
Lyxan, et al
(1968),
AMIC-3839
Lyman, et al
(1968),
AMIC-3839
000
Notrools
FLR 93 samollng 0.8-2.0
same as above
Lyaan, et al
-------
CD
Compound
ono
000
000
000
000
Orqanl s«
cornu tus
ROCCUS
amer Icanus
Pomox I s
nigro-
maculatus
Leoomls
aur 1 tus
Phlnlchthys
at r a t u 1 us
Cyorlnus
carplo
Field Field
Study Locat Ion
s ta 1 1 ons In
Mass.
FLR 91 samol Inq
stat 1 ons In
Mass.
FLR 93 samol Inq
stations In
Ma-is.
FLR 93 sampl Inq
stat 1 ons In
H3SS.
FLR 93 samollnq
s t a 1 1 ons 1 n
M8SS.
FR St. Laurence
Plver i
Toxlcity,
Active
Inqr ed 1 en t •
Ppm
(residue)
0.1.-1.3
(residue)
ID. 7 (residue)
O.if6 (residue)
0.1,0 (residue)
0. 38 (O.IiO pom
max tissue
Experimental
Variables,
Control 1 ed
or Noted Comments Reference
( 19F.M ,
tMIC-3839
-- same as above Lv"an» et
( 19F.M ,
SMIC-3S39
same as above Lynan, et
(lOftB) .
AMIC-3839
— same as above Lyman, et
(19F.B) ,
AMIC-3J39
same as above Lyman, ot
(196.S) ,
iMIC-3839
— Residues of nnn Here measured In Fredeen*
water, mud, molluscs, and fish durlnq and al (1970)
at
al
al
a 1
et
t
000
000
000
Montreal, residue)
Canada
after ODD aopllcatlon In 1967. Sampling AMIC-53,
«MIC-53
-------
6
000
000
000
ODD
OOE
-------
>
o
Compound
ODE CC-K, labelled)
OOF (C-l", label led)
DOt rC-l
-------
OOF CC-1* labelled)
DOC (C-ld labelled)
DOE to,o-}
Rotifers
(Aaplanchnop-
ua. No to ma t-
ta, Euclaris,
Scardium)
Mater
Anqull la
rostrata
L
(Hod.
el
OOOST
stem)
L
(Hod.
el
eco ays
ten)
FRL St. John,
N.B., Can.
1 Ib per A
(NTE)
0.008
(residue)
0.5 (residue)
a,c, g.
standard
reference
water and
sand
»»o,c.
standard
reference
water and
sand
— —
DOE (0,0-)
DOE (0,0")
Esox nlqer
FRL St. John,
N.B., Can.
Sal mo salar FRL St. John,
N.B., Can.
0.16 (residue)
0.22 (residue) —
OOE (D,p">
OOE (D.p")
OOE (0,D">
DOC (o,p">
OOt Co,p")
DOC fp«p")
Clupea
harenqus
Scomber
scombrus
Mytl lus
edul Is
Gadus morhua
Urophycls
tenuls
Hlppo-
glossoidea
FRL
FRL
FRL
FRL
FRL
FRL
St. John,
N.B., Can.
St. John,
N.B., Can.
St. John,
N.R., Can.
St. John,
N.P., Can.
St. John,
N.B., Can.
St. John,
N.R., Can.
0.06-0.2
Dlatessoldes
Sebastodes FRL St. John,
trace
same as above
same as above
PCR"s Mere found In hlqher
concentrations than organochlorlne
pesticides In all fish analyzed. The
authors point out that PCB Is less toxic
In an acute sense than organochlorlne-s,
that little Is KnoMn of sublethal PCB
effects, and that more Knowledge of PCB
distribution and effects Is needed.
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
Metcalf, «t
al(1971),
AHIC-li.95
Metcalf, et
al (1971),
AHIC-1I.S5
71tKo(1971),
AMIC-3715
7ItKo
(1971) , AMIC-
3715
ZltKo
(1971) ,
3715
21tKo(1971) ,
BMIC-3715
Zlt*oU97U,
A1IC-371S
ZltKo
(1071)
3715
21tko(1971),
AMIC-3715
AMIC-3715
Zltko
(1971) ,
AHIC-371S
ZltKo(1971) ,
-------
Coaoound
OOE
OOF
OOF
fe
ru
DOE
OOE
OOE
OHE
DIE
OOE
OOE
Organlsn
Bar Inus
Caro
Channe 1
catfish
Redhorse
sucker
Gizzard shad
Spotted
sucker
Btueqll Is
Redbreast
sunf Ish
Striped
nul let
Blue catfish
Rock bass
Freshwater
druB
Field Field
S t udy Locat I on
N.n.,
FRL Misc.
FRL Misc.
FRL Misc.
FRL MISC.
FRL Misc.
FRL MISC.
FRL Misc.
FRL Misc.
FRL Misc.
FRL Misc.
FRL Misc.
Can.
states
states
states
states
states
states
states
states
states
states
states
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted
(residue)
0.03-2.93
residue (S3)
0.0<.-<.2.3
residue (SB)
0.03-0.36
residue (SB)
0.27-1.5".
residue (SB)
0.29-0.1.5
residue (SB)
0.01.-0.81
residue (SB)
0.02 residue
(SB)
O.OS-I..55
residue (SB)
1.87 residue
(SB)
0.08-0.60
residue (SB)
0.26 residue —
(SB)
Comments
same as above
sane as above
sane as above
same as above
sane as above
same as above
same as above
same as above
same as above
sane as above
sane as above
Reference
AMIC-371S
Hen^rson,
et al
(1971), AMIC-
11.07
Henderson ,
et al (1971) ,
AMIC-11.07
Hendfson.et
81 (1171),
AMIC-ll.07
Henderson ,
et al (1971) ,
AMIC-11.07
Henderson,
et al (19'1) ,
AHIC-11.07
H enderson,
et al (1971),
AMIC-11.07
Henderson,
et al (1971) ,
AMIC-11.07
Henderson,
etsl (1971).
AMIC-li.07
Henderson,
et al (19'1) ,
AMIC-H.07
Henderson,
et al (1971) ,
AMIC-li.07
Henderson ,
et al (1971) ,
-------
DOE
Bloater
FPL Hlsc. states
1.07-3.52
residue (SB)
same as above
Henderson et
al (1071),
1MIC-1I.07
OOF
ODE
Lake FRL
NhltefIsh
Hlsc. states
Lake trout FRL Hlsc. states
0.3
-------
r
IK
ro
Co*oound
OOF
OOE
OOF
OOE
OOE
OOF
OOE
OOF
OOF
OOE
OOE
Field
Orqanlsm Study
RlaeK crappl* FRL
Larqescale FRL
sucher
Smsl (mouth FRL
bass
Northern FRL
souaxf Ish
Chlselmouth FRL
Klamath FRL
sucher
Rainbow trout FRL
Brldqellp FRL
sucher
Arctic FRL
qray 1 109
Pound FRL
Khltet Jsh
lonqnos* FRL
sucker
Field
Locat Ion
Misc. states
Misc. states
Hlsc. states
Hlsc. states
Hlsc. states
Hlsc. states
Misc. states
Hlsc. states
Hlsc. states
Hlsc. states
Hlsc. states
Toxlelty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted
O.itO-0. 9
-------
OOE
Hhlte sucker FRL Misc. States 0.OS-It.8?
residue (SB)
OOE
Yell OH perch FRL Misc. states 0.03-?.1.1
residue (SB)
The Bureau of Sport Fisheries Henderson,
continued Its fish monitoring program by et al
collecting 147 composite fish samples
from 50 nationwide monitoring stations
during the fall of 1969. Fish were
analyzed for residues of 11
organochlorlne Insecticides, llplds, and
PCB-s.
same as above
(1971),
AMIC-K.07
Henderson,
etal (1971),
AMIC-11.07
r
vn
OOE
OOE
OOE
OOE
DOE
DOC
OOE
OOE
Chain
PlcKerel
FRL Misc. states 0.06 residue
(SB)
White catfish FRL Misc. states 0.38-0.86
residue (SB)
White perch FRL Misc. states O.Sit-10.9
residue (SB)
Goldfish FRL Misc. states l.tk residue
(SB)
Pumpklns«?ed FRL Misc. states O.Z3 residue
(SB)
Largemouth FRL Misc. states 0.10-5.85
bass residue (SB)
Brown
bulI head
FRL Misc. states 0.01-1.65
residue (SB)
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),
AMIC-11.87
Henderson,et
al (1971),
AMIC-lf.07
Henderson,
et al(1971),
AMIC-11.07
Henderson,
et al
(1971),AMIC-
11.07
Henderson,
et al
(1971),AHIC-
11.07
Henderson,et
at (1971),
AMIC-11.07
Henderson,
et al(1971),
AHTC-H.07
Llmneohllus FS Knights 0.006 (whole
rhombleus Creek, Dun body residue)
(larvae) County,Hlsc.
Samoles of Hater, silt, bottom Moubry, et
debris, bottom organisms, and fish were al (1968),
taken In 1966 from a creeh adjacent to an AMIC-3753
orchard which had been treated In
1963-1965 with various chlorinated
hydrocarbon pesticides. No residues were
found In water samples. Silt samples
contained 0.007-0.013 ppm endrln and
0-0.005 ppm dteldrln. Endrln residues of
-------
Compound
Field Field
Organlsn Study Location
Toxlclty,
Active
Ingred 1 en t *
Ppm
Experimental
Variables,
Control 1 ed
or Noted Comments
Reference
k
DOE
DOC
OOF
OOF
DOE
OOF
DOE
Slal Is so. FS
( 1 arvae)
Ganmarus so. FS
Sal vel Inus FS
font Insl Is
Semot 1 lus FS
atr omacul a tus
Knlqh ts
Creek, Dun
Count y ,
Wise.
Knlqhts
Crpok, Dun
Count y,
Wise.
Knlqhts
Crnpk , Dun
Coun f y ,
Knlqhts
Creek, Dun
Coun t y ,
Wise.
o.oos
( who t ebody
residue)
0.01 (whole
bodyresldue)
raaldue )
0.3-l.Mfat
residue)
1. 03-1. 53f fat
residue)
Cottus balrdl FS
Rhinlchthys FS
stratulus
Enqraulls FM
mordax
Knlqhts D.6-0.7 (fat
Croek, Dun residue)
County,
Wise.
Knights
Creek, Dun
County,
Hlsc.
1.92(fat
residue)
Pacific 0.06-0.17(res
Northwest idue)
Coast, Grays
Harbor,
Hash.
0.011-0.025 ppm and 0.002-5.006 ppm
dleldrln were found In debris samples.
Respite limited control data, residue
analyses indicated that contamination of
the environment studied Has limited.
same as above
same as above
sane as above
same as above
same as above
same as above
Pesticides from the Columbia
River Into Puget Sound apparently
contaminated fish constltutlna commercial
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.
Moubry
al
Moubry, et
al (1968),
Moubry, et
al (196S),
Moubry, et
al (1366),
AMIC-3753
Moubry, et
al (1066) ,
AMIC-3TS3
Koubry, ef
al (136(1),
AMIC-3753
Stout
(1968),
AMIC-3781,
-------
DOE
OOF
DOE
ODE
ODE
DOE
ODE
DOE
DOE
Sohastodes FM
fIavldus
Sehastories FM
I I avldus
Platichthys FM
stelIatus
Gadus FM
macroceohalus
Cancer FM
maglster
Cancer FM
maqlster
Paroohrys FM
vetuI us
Merlucclus
eroductus
Merlucclus FM
oroductus
Hash.
Pnclf Ic
Northwest
Coast,
Hecate
Strait, B.C.
Pacl( 1C
Northwest
Coast,
Tlwaco,Hash.
Paclf Ic
Northwest
Coast,
Blalne,
Hash.
PacITIc
Northwest
Coast,
Blalne,
Pacific
Northwest
Coast,
Destruction
Island,
Hash.
Pacif Ic
Northwest
Coast,
II waco,
Hash.
PacU Ic
Northwest
Coast,
Rlaine,
Hash.
Paclf ic
Northwest
Coast,
Sarasota
Passage,
Hash.
Pacific
Northwest
0.1)2-0.OA
(residue)
0.09-0.<»2
(residue)
0.02(resldue)
0.01 (residue) —
0.039(resldue> —
0.03-0.0<»
(residue)
0.01-0.05
(residue)
0.08) ,
AMIC-378«i
Stout
(1968),
AHIC-3781*
Stout
(1968) ,
AMIC-378i»
Stout
(1968),
AMIC-378U
Stout
(1968),
»MIC-378
Stout
(1968) ,
AMIC-378'f
Stout
(1968).
-------
k
CD
Conoound
DOE
DOE
DOE
DOE
DOE
DOE
DOE
Organism
Her lucelus
produc tu5
Mer 1 ucclus
produc tus
(f Ishmeal )
Sebastodes
al utus
Carasslus
auratus
TrI turus
cr Istatus
Sana
temporarla
Daphnla nagna
(adult)
Field Field
Study Location
Coast, Fort
Susan, Hash*
FM Pacific
Northwest
Coast, Cape
Foul weather.
Ore.
FM Pacific
Northwest
Coast ,
Aberdeen,
Mash.
FM Pacific
Northwest
Coast ,
Hecate
Strait, B.C.
t
I
I
BCF —
Toxlclty,
Active
Ingredient,
Pom
0. 07 (residue)
0.37 (residue)
0.01 (residue)
I..7-8.2
(resl due)
0.23-0.6^
(residue)
0.001-0.01
mlcroqram
(residue)
1.8 (residue)
Experimental
Variables,
Control 1 ed
or Noted Comments
same as above
— - sa..ie as above
— same as above
a* Goldfish were exposed to
Increasing concentrations of DOT and
residues determined after 21 days of
exposure. Most DDT had been converted to
DDE. PhenobariTal had no significant
effect on Insecticide residues.
DDT caused hyperac t 1 vl ty In
exposed tadpoles. This caused Increased
caoture lunges of newts thus Increasing
the predatory efficiency of the newts.
DDT had no apparent effect on the newts.
— same as above
a» Magnification of DOT and Aldrln
tagged with C-14 occurred rapidly.
Pef *>r ence
4MIC-S781.
Stout
(19f>8) .
4MIC-37*!.
Stout
(19681 ,
AHIC-378<.
Stout
(1968) ,
AMIC-378
-------
DOE
ODE
DOE
OOF
OOE
DOE
OOE
DOE
OOE
OOE
OOE
Gammarus
faseiatus
l t)
Palaemonetes
kartlakensls
(adult)
Hexaqenla
bl I ineata
(nymph)
Ischnura
vertical Is
(naiad)
BCF —
BCF ~
BCF
BCF
Libellula sp. BCF
(naiad)
Chlronomus BCF
sp. (larva)
Daohnla waqna BCF
(adult)
Gannarus
1aselatus
(adult)
Palaemonetes
karilakensls
(adult)
Hexaqenla
bitIneata
(nymoh)
Ischnura
vertical Is
(naiad)
BCF
BCF
BCF —
BCF
O.it (rasldue) a*
0.7 (residue) a>
.it (residue) a"
0.2 (residue) a*
O.OZ (residue) a*
0.1 (residue) a*
0.0001 (SB3) a*
0.0001 (SB3) a*
0.0001 (SB3) a*
0.0001 (SB3) a*
0.0001 (SB3) a*
conclude that aquatic Invertebrates
Influence Quality and quantity of
Insecticide residue passed via the fish
food chain.
sane as above
same as above
sane as above
same as above
same as above
same as above
sane as above
same as above
same as above
sane as above
same as above
Johnson, et
81
(1971), AHIC-
38ZO
Johnson, et
al (1971),
OMIC-38JO
Johnson, et
a I
(19?!) .AMIC-
38?0
Jchnson, et
al
3830
Johnson, et
al (1971),
Johnson, et
al
(1971) ,aiic-
3830
Johnson, et
al (1971),
AHIC-3821
Johnson, et
al (1971),
AMIC-3820
Johnson, et
al (1971),
AMIC-3820
Johnson, et
al (1971),
AMIC-3823
Johnson, et
al (1971),
AMIC-3820
-------
Compound
DOE
DOE
Field Field
Organism Study location
Libel lul a sp. BCF
(naiad)
Chlronomus BCF
sp. (larva)
Toxlclty,
Active
Inqred 1 en t ,
Pom
0.0001 (SB3)
0.0001 (SB3)
Exper 1 men tal
Variables,
Control 1 ed
or Noted Comments
a* same as above
a* same as above
Pet erence
Johnson , e t
al (1971) ,
AMIC-3870
J ohns on, e t
Bl (1971) ,
AMIC-3820
ODE
C
O
ODE
Mlcropterus FL Clear Lake, 0.3-9 (flesh
salnolcles Cal. residue)
Hlcropterus FL
saImoldes
Clear Lake, 82 (fat
Cal. residue)
Residue analysis results mainly Linn, et
tor TDF In fish, birds, and plankton from ALI1969),
19^9 throuqh 1965 were reoorted. The AMIC-SS21
residues ortmarlly resulted from
apollcatlon of DOT to farmland and for
qnat control. In somf* cases, data for a
slnqle animal In one year wore qiven.
Primary emphasis was on larqemouth bass
and whltp catfish. The qeneral level of
TDE contamination In birds and fish
declined markedly from 195R to 1961;.
This decline correlated directly with
strict limitation by permits of DOT
applications durlnq the latter years.
same as above
L Inn, et al
( 1969) , AHIC-
DOE
DOE
ODE
DOE
Aechmophorus FL
occIdentalIs
Larus sop. FL
Larus FL
delawarensls
Perea FLR
flavescens
Clear Lake, 33-2,360 (tat
Cal. residue)
Clear Lake, 300-<»02
Cal. (residue)
Clear Lake, 92-2700 (fat
Cal. residue)
93 sampling 0.25-3.6
stations In (residue)
Mass.
same as above
same as above
same as above
Fish indigenous to Massachusetts
freshwater streams were analyzed for DOT
and DOT metabolites during 1965-1967.
Generally there was an Increase In
pesticide content during the three year
period.
L Inn, e t
AL(iq ,
AMIC-5S21
Linn, et al
(1969) ,
AMIC-55?!
Linn, et al
( 1969) .AHIC-
5521
Lyman, et al
(1968) ,
AMIC-3S39
-------
H
U)
DOE
ODE
OOF.
DOE
ODE
DOE
OOE
DOE
OOE
OOE
Lepomls
glbbosus
Catostomus
commersonl
Ictalurus
nebul osus
Cyprlnus
earplo
Esox nlqer
FLR
FLR
FLR
FLR
FLR
Notemlqonus FLR
crysolsue as
Semotllus FLR
corporal Is
Leoomls FLR
macrocMrus
Ambloplltes FLR
rupestrls
Semotllus FLR
atromaculatus
93 samplIng
stations In
Mass.
93 sampling
stations In
Mass.
93 sampl1ng
stations In
Mass.
93 sampling
stations In
Mass.
93 sampl1ng
stations In
Mass.
93 samplIng
stations In
Mass.
93 samplIng
stations In
Mass.
93 samplIng
stations In
Mass.
93 sampling
stations In
Mass.
93 sampling
stations In
Mass.
D.16-3.5
(residue)
0.16-14.6
(residue)
0.9 (residue)
1.6-i».8
(residue)
(resldue)
0.39-U.2
(residue)
0.17-7.1.
(residue)
0. la-it.d
(residue)
0.76-1,.3
(residue)
0.i»6-3.i»
(residue)
sane 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
Lyman, et al
(1968) t
AMIC-3839
Lyman, et al
(1968) .
AMIC-3R39
Lyman, et al
(1968) .
AMIC-3839
Lyman, et al
(1968) ,
AMIC-3839
Lyman.et al
(1968) ,
A1IC-3839
Lyman, et al
(1968),
AMIC-3S39
et al
(1958) ,
Lyman, et al
(196P) ,
AMIC-3839
Lyman, et al
(1968) ,
AMIC-3839
Lyman, et al
(1963) ,
AMIC-3839
OOE
OOE
DOE
Mlcropterus FLR
dot om1eul
Al osa
pseudo-
harengua
FLR
Fundulus FLR
het*roclItus
93 samplIng
stations In
Mass.
93 samplIng
stations In
Mass.
93 samplIng
stations In
Mass.
0.3-0.82
(residue)
1.08 (residue) —
1.16-it.l
(residue)
same as above
same as above
same as above
Lyman, et al
(1968) ,
AMIC-3839
Lyman, et al
(1968) ,
AMIC-3839
Lyman, et al
(19681,
AMIC-3839
-------
H-
U»
Compound
DOE
OOE
DOE
DOC
OtK
OOE
DOE
OOF
Orqanls*
Notropls
cornutus
Poccus
anerlcanus
Pomoxls
nlgro-
maoulatua
Fundu 1 us
a] aphanu
No tropl s
anatostanus
Lepomls
aur 1 tus
Phlnlchthys
atratulus
Cyorlnus
carolo
Field
Study
FLR
FLR
FLR
FLR
FLR
FLR
FLR
FR
Field
Locat Ion
93 samp! Inq
stations In
Mass.
93 sampl Inq
stations In
Mass.
93 sampl ing
stations In
Mass.
93 saflipllnq
stat 1 ons In
Mass.
93 sampling
stations In
Mass.
93 sampl Inq
static ns in
Mass.
93 samol Ing
stations In
Hass.
St. Lawrence
Plwer,
Montreal >
Canada
Toxlclty,
Active
Inqredlenti
Ppm
0.50-2.6
(residue)
0. 3it-l.it
(residue)
1.9
-------
DOE
DOE
DOE
OOE
Esox luelus FR
Ambloolltes
rupestrls
PlsMlum sp. FR
Campelona sp. FR
St. Lawrence 0.38 (O.i»3
River, ppmmax tissue
Montreal, residue)
Canada
St. Lawrence 0.38(0.05 Dpm
River, max tissue
Montreal,
Canada
residue)
St. Lawrence 0.38 (0.03t>
Fredeen, et
al (1970),
AMIC-531,
Fredeen, et
al (1970),
AMTC-S34
OOE
Catostomus
commersonl
FR
DOT .(C-l<> labelled) Oaphnla maqna BCF
(adult)
UJ
CO
DOT labelled) Gammarus
tasclatus
(adult)
BCF
DOT CC-1* labelled) OPCOnPCtes BCF
nals (adult)
DOT (C-l«t label lei) Palaemonetes BCF
hadlakensls
(adult)
DOT
same as above
Maqnltlcatlon of DOT and Aldrln
taqqed with C-1U occurred rapidly.
Bloloqlcal magnification factors of 2900
to 11>»,100 depending on the species were
found tor DOT, and ?2,BOO to l«.l,00fl tor
Aldrln. Marked degradation of DDT 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
same as above
same as above
same as above
same as above
same as above
Fredeen, ei
al
(1970>,»1tC-
Johnson, «T
al (1971),
AMIC-3820
Johns on,et
al (1971),
AMIC-3830
Johnson,et
al (1971),
AMIC-3630
Johnson,et
al (197D,
AMTC-7S20
Johnson,et
al (1971),
AMIC-3820
Johnson, et
al (1971),
AMIC-3820
Johnson,et
al (1971),
-------
Field Field
Compound Organism Study Location
(nymph)
DOT (C-l* labelled) Slphlonurus BCF
sp (nymph)
DOT (C-l t
al (1971),
Johnson , e t
al (1971),
AMIC-38?0
Johnson, et
al (1971) ,
ANIC-38'O
J ohnson,p t
al (1971),
AMIC-38?0
Johnson, et
al (1971),
AHIC-38ZO
-------
H
UJ
VJ)
DOT l labelled) Slphlonurus BCF
sp. (nvmoh)
DOT
-------
r-1
UJ
ON
Compound
DOT (C-f. label led)
OUT (C-t* labelled)
DOT (C-l". label led)
DOT (C-l* label led)
DOT (C-l<> labelled)
DOT fC-lt labelled)
DOT CC-1* labelled)
DOT CC-1% labelled)
rtrqanism
Protozoa
(Huclearla,
Coleps,
Vorticella,
and
Faramecium)
Rotifers
(Asplanchnop-
us , No toma t-
ta, Euclarls,
Scardlum)
Hater
Physa spp
Oaphnia msqna
Culex plplens
qulnquo—
fascia tua
Oedogonlu*
cardlacuD
Ga«nusla
• f finis
F 1 P t d Field
S tudv Locat 1 on
L
(Mod-
el
eoosy
stem)
L
(Hod-
el
eoosy
stem)
L
(Mod-
el
ecosy
atom)
L
(Mod-
el
ecosy
a tern)
L
(Mod-
el
ecosy
stem;
L
(Mod-
el
ecosys
tern)
L
(Mod-
al
acosy
st«B)
L ~~
(Mod.
el
ecosr
•t«m)
Toxlcity, Experimental
Active Variables.
Ppm or Noted Comments
1 Ib per A afCt<)t same as above
(NTE) standard
r pf erpnce
water and
sand
1 Ib per A a,c,q, same as above
(NTF.) standard
r ef erpnce
Hater and
sand
0«OQJ* atc,gy same as above
(residue) standard
reference
water and
sand
27.9 (residue) a.c.q, same as above
standard
ret erence
Hater and
sand
1 Ib per A a,c,q, same as above
(K-NTEI standard
reference
Hater and
sand
8.9(resldue) 3,c,q, same as above
standard
reference
nater and
sand
1 Ib Per A a,c,q, same as 'above
(NTE) standard
reference
Hater and
sand
5i».2 (residue! a.c.q, sane as above
standard
reference
Hater and
sand
Re f erence
Metcalf, et
al (1971) ,
ANIC-l<.9c;
MetcalT, et
al (1971),
AMTC-1<.9";
Metcalf, et
31 (1971),
AMIC-f.95
Metcal f , et
al (1971),
AMIC-li.95
Hetcalf, et
al (1971),
AHic-nto1;
Metcalf, et
al (1971),
AHIC-K.95
Metcalf, et
nl (1971),
AMIC-1I.9S
Metcalf, et
al (1971),
AMIC-lfc95
-------
DOT (C-ld labelled)
DOT (C-ld labelled)
H
UJ
DOT (C-li. labelled)
DOT (0,0")
DOT (olus DOT
analogs)
Diatoms
(Navicula,
Coscinodis-
cua, Dip-
loness, and
Oiatomella)
Salvel Inus
font InalIs
SalvelInus
tontlnalIs
Rasbora
heteromorpha
Llmnephllus
rhomblcus
(I arvae)
L
(Hod-
el
BOOST
stem)
BCFCM —
BCFCH —
BCFA
and
BSA
FS
1 Ib per A
(NTE)
0.000003
(0.0256ppm
accumulation
120 d)
Knights
Creek, Dun
County,Wise.
a,c,q,
standard
reference
Hater and
sand
0.01.5 mg per kg a
(l.SZppm
accumulat ion
120 d)
0.03 (Tl)
a*,c,e,f,
hard (HH)
or
SOFT(SH)
synthetic
dilution
Hater, or
seawater
for some
species
0.021. (whole
body residue)
Metcalf, et
al (1971),
same as above
This study Has an attempt to WaceK, et al
evaluate, under laboratory conditions, (1970),
the relative Importance of food and Hater »MIC-Si.<.
as sources of ODT for fish and to relate
these observations to natural
environments. To simulate conditions In
Lake Michigan, fish Here exposed to Hater
containing 3 olus or minus 0.3 opt DOT,
and others Here fed 3 plus or minus 0.15
pom DOT (D-Oif*: mo/kq/day) for 120 days.
Whole body accumulations were determined
throughout the test by measuring C-l**
radioactivity In fish. The results shoH
that fish accumulated 3.5 percent of the
DDT available In the Hater and 35.5
percent of that available In food. It Is
concluded that the food chain is the
major source of DDT in fish.
same as above
Hacek, et al
(1970) ,
AMIC-8i.it
One hundred sixty-four Alabaster
pesticides, netting aqents. and (1969),
miscellaneous nater pollutants showed a AMIC-5U75
Hide range of toxlcity soannlng 12 orders
of magnitude. KnoHinq 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 Here most toxic in hard nater
and sometimes the opooslte Has true.
Testing the actual material as sold Has
found to be essential.
Samples of water, silt, bottom r"oubry, et
debris, bottom organisms, and fish Here al (1968),
taken In 19fi6 from a creek adjacent to an AMIC-3753
orchard Hhlch had been treated In
iges-ioes Hltn various chlorinated
hydrocarbon pesticides. No resloues Here
-------
Conoound
OOT (olus OOT
analoqs)
'if OOT (olus OOT
' analogs)
OOT (olus DOT
ana 1 oqs)
OOT (olus OOT
•nal OTS)
OOT (olus DOT
analoqs)
DOT (olus OOT
•nal 091)
OOT (olus DTT
•nal O9s)
OOT (olus OOT
•nal oqs)
DOT (olus DDT
•naloqs)
nrqanls*
Slal Is sp.
( 1 arvae)
Gammqrus sp.
Sal VP| Inus
f on t Inal I s
Sei»ot 1 lus
atr omaru t a tus
Cottus balrdl
Phlnlchthys
atratulus
Sa 1 ve 1 Inus
f on t Ina 1 Is
Semot 1 tus
atronaeul atus
Cottus balrdl
Field Field
Study Locat Ion
FS Knlqhts
Creek , Dun
Count y.
Wise.
FS Knlqhts
Crppk , Dun
Count y,
HI sc.
FS Knlqhts
Creek , Dun
Count y,Hlsc.
FS Knlqhts
Crpek , Dun
Count y.Wlsc.
FS Knlqhts
OunCoun ty ,
Wise.
FS Knlqhts
Creek, Dun
Count y, Wise.
FS Knlqhts
CrppK , Dun
Count y, Wise.
FS Knlqhts
Creek, Dun
County, Misc.
FS Knlqhts
CreeK,
Toxiclty,
Active
Tnqr ed lent ,
Pp«
0.016 (whole
body res 1 due )
0.003-0.013
(whole body
residue)
0.0 ppm
dleldrin were found In debris samples.
analyses Indicated that contamination of
the environment studied was limited.
same as above
same as above
same as above
same as above
-- same as above
-- same as above
same as above
same as above
sane as above
Reference
Houbry, R t
8 1 ( iafl) ,
SMIC-3753
Moubry, et
al (145M ,
AMIC-3751
MouBry, et
a 1 (l<9f>.t) ,
AHIC-3753
Houbry, et
al (1968),
AHIC-3753
Moubry, et
al (1968),
-------
G
vo
DOT (olus DOT
analogs)
Phlnlchthys
atratulus
DunCounty,
Misc.
FS Knights ?.» (fat
Creek, Oun residue)
County,Misc.
DOT (plus ?0 porcont Rasbora
non-Ionic heteromorpha
••ulslfler, 60
percent naphtha)
BCFA --
and
BSA
0.11 (T2)
DOT (olus ?0 percent Rasbora
non-lonlc heteromorpha
•nulslIler, 60
percent naphtha. In
•cetone)
BCFA
and
BSA
0.02 (T2)
a*,c,o,f,
hard (KW)
or soft
ISW) syn-
thetic
dilution
water, or
seawater
for some
species
a*,e,e,f,
hard (HW)
or soft
(SW) syn-
thetic
water, or
aeawator
for some
species
same as above
One hundred sixty-four
pesticides, wettlnq aqents, and
miscellaneous Hater oollutants showed a
wide ranqe of toxlclty scanning 12 orders
of msqnltude. Knoxlnq 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 water
and sometimes the opposite was true.
Testlnq the actual material a^ sold was
found to be essential.
same as above
AMIC-3753
Moubry, et
al (1963),
AHIC-37ST
Alabaster
(19f>9> ,
Alabaster
(1969),
AMIC-51.25
DOT (olus 2<> percent Rasbora
suspending agents) heteromorpha
BCFA
and
BSA
10.7 (Tl)
DOT (plus 3 percent
eaulslfier, d«
percent naphtha)
Rasbora
heteromorpha
BCFA
and
BSA
0.11 (T2)
a»,c,e,f,
hard (HH)
or soft
(SW)
synthetic
d iIu 11 on
water, or
seawater
for some
species
a»,c,e,f,
hard (HH)
or soft
(SW)
synthetic
dilution
water, or
seawater
*or some
species
sane as above
Alabaster
(1969),
AMIC-51,25
same as above
Alabaster
(1969) ,
AMIC-SI.25
-------
Field Field
Conoourxl Organism Study Location
DOT (plus 77 percent Pasbora BCFA —
China clay. 3 he terororpha andBS
0«rc»nt calcium A
sulfat*)
OOT (nlus 77 percent Pasbora BCFA
China clay* 1 he teromorpha and
percent calcium QSA
«ul f ate. 1 n
ACETONE)
OOT «p,o~-» Plneohales BSA —
Drome 1 as M
en)
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments Reference
8.0 ,c,e,Tt sane as above Alabaster
hard (HH) ( llfil) ,
or soft AMIC-Si*??
(SW)
synthetic
dilution
water, or
seaw a ter
forsome
soccles
0.001 (T?) &G,c,6,f, sane as above Alabaster
hard (IIW) (l«369i ,
or soft AMIC-SI,?';
(Srf) oyn-
thetie
water, or
soawa ter-
ror sono
species
0.007*» (T2) a*,c,e,f,k Rloas^ays conrluctpd Llncer, et
,l,n,and simultaneously Indicated th^t HOT Has al (1^70),
nagnesluii, considerably more toxic to fathead AMIC-'5509
iron, under continuous T 1 OH conditions.
calcium Decreasing oxyaen and i ncrpas Inq
OOT
-------
calclu*
DOT (0.o">
AnqulIla
rostr»ta
FRL
St. John,
N.6.i Can.
0.39 (residue)
DOT (0,0")
DOT Co,p")
DOT (0,0")
DOT lo.o")
DOT a*
PCR"s were found In Ktqher Zltko(1971),
concentrations than orqanochlorlne AMIC-3715
pesticides In all fish analyzed. The
authors point out that PCP Is less toxic
In an acute sense than orqanochlorlnes,
that little Is known of sublethal PCS
effects, and that more Knowledge of PCB
distribution and effects Is needed.
same as above ' Zltko
(1971),AMIC-
3715
same as above Zltko
(1971),AMIC-
3715
same as above
same as above
AHIC-3715
Zltko(1971l,
ftMIC-3715
Alabaster
(1969),
AHIC-5i»35
Pne hundred sixty-four
pesticides, netting agents, and
nlsee 1 Ianeous Hater oollutants shoned a
Hide ranqe of toxlclty spannlnq 12 orders
of maqnitude. Knowinq the toxiclty and
oercentaqe of all coiioonents of a
fornulation did not result In easy
predictability of the toxlclty of a
mixture of materials. Somptimps
pesticides were most toxic In hard water
and sotretlnes the opposite was true.
Testlnq the actual material as sold was
found to be essential.
DDT-reslstant mosoultoMsh were Murphy
collected from a oond at Salinas, (19711,
California. Smaller fish (100 mq) AMIC-1805
accumulated OOT-Cl
-------
Field Field
Co^oounl Organism Study Location
DOT (0,0", C-1U G»»busla L
labelled) clflnls
(0.1-1.5 g)
DOT (o,o"t plus 20 Rasbora BCFAa --
O«rc«nt o,p"OOT) heteromorphs nd
8SA
OOT (0,0", plus 20 Basbora BCFA
•percent o,p""ODT> he t»rofl*orpha and
BSA
DOT (o,p", plus 30 Salino trutta BCFA
percent o,p"ODT) (alevln) and
BSA
DOT fp,o**t plus 20 Rasbora BCFA —
percent o,p*"DDT) heteromorpha and
BSA
Toxlclty, Experimental
Active Variables,
Pom or Noted
0.00001.1 (0.01-0 a"
.0<* pom Hhole
body residue Z
d)
0.0031 a*,c,p, f ,
(TZ.hardwater) hard (HW)
or soft
(SH)
synthetic
d 1 1 u 1 1 on
water, or
seaw at er
tor some
species
O.OOOSi, a»,c,e,f,
(TZ.softHater) hard (HW)
or soft
(3W) oyn-
thotlc
water, or
soawater
for some
species
0.0035 (T3) a',c,e,t.
hard (HW)
or sort
(SW)
synthetic
dilution
Hater, or
seanater
for some
species
0.017 (T2> a»,c,e,f.
hard (HH)
or soft
(SHI
Comments
same as above
One hundred sixty-four
pesticides, wpttlnq agents, and
miscellaneous water pollutants shoned a
wid* ranqp of toxlcity spanning 1? orders
of maqnltudo. Knowing the toxlcity and
formulation did not result In easy
predictability of the toxlcity of a
mixture of materials. Sometimes
pesticides were most toxic In hard Hater
and sometimes the opposite was true.
Testlno the actual material as sold was
found to be essential.
same as above
same as above
same as above
Pef er ence
Mur oh y
(1971) ,
•MIC-1805
« labaster
(1969) ,
AHIC-51.75
A 1 abaster
(1969) ,
AMIC-t;'.75
Alabaster
(1969) ,
AHIC-5I.35
A 1 abaster
(1969) ,
AMIC-5<.25
-------
DOT (DID", Plus 20
percent o.o"OOT)
Salmo tputta
(alevln)
RCFA —
and
BSA
0.011 (T2)
DDT (18 percent)
£
OJ
Rasbor» BCFA —
heteromorpha and
BSA
0.17 (T2>
DOT
DOT
Fish (not
spec! f le-1)
greater than
0.0001-0.001
White sucker FRL Misc. states 0.05-2.50
residue (SB)
DOT
DOT
DOT
Redhorse
sucker
FRL Misc. states 0.02-0.25
residue (SB)
Gizzard shad FRL Misc. states 0.13-0.15
residue (SB)
Spotted
sucker
FRL Misc. states 0.1
-------
>
H
Conoound
nn T
Du l
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Organise
S t r 1 p*d
nu 1 1 e t
Rlu» cattish
Poch bass
Freshwater
drun
Bloater
Lake
•hi tef Ish
LaKe trout
White criipple
Rlgnouth
buf talo
Snal 1 nouth
bu t f a 1 o
Flathead
eatf Isn
Field Field
Study Location
FRL M 1 sc states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Hlsc. States
Toxlclty, Exoer [rental
Active Variables^
Ingredient, Controlled
Pom or Noted
residue (SB)
0.071) ,
AMtC-ll.07
Henderson ,e t
al (1971),
AMIC-1«.07
Henrierson,et
al (1971),
4MIC-1I.07
-------
DOT
DOT
DOT
Col n>v*
Hal I eye
Sauqer
FPL Misc.
FRL Misc.
FRL Misc.
states 0.0?-0.3<»
residue (SB)
states O.Oit-0.20
residue (SB)
states 0.18 residue
(SB)
same as above
same as above
same as above
Henderson,
*t al (1971) ,
AMIC-li.07
Henderson,
et al (1971) ,
AMIC-li.07
Henderson,et
a! (1971),
AMIC-H.D7
DOT
Flannelmouth FRL
sucker
Misc. states 0.19 residue
(SB)
same as above
Henderson,et
si (1971),
AHIC-li.07
f
DOT
DOT
Black FRL
bulIhead
Misc. states 0.01-0.03
residue (SH)
White hass 'FRL Misc.
states 0.21 residue
(SB)
same as above
same as above
Henderson, et
al (1971),
AMIC-lfcO?
Henderson,
et al (lO'i),
AMIC-li.07
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Black erapole FRL Misc.
states 0.22-0.?•;
residue (SB)
Larqescale FRL
sucker
Small mouth FRL
bass
Northern FRL
sauawf Ish
Ktamath
sucker
Misc. states 0.05-0.<»5
residue (SB)
Misc. states fl.lft-0.20
residue (SB)
Misc. states 0.0-5-0.10
residue (SB)
Chlselmouth FRL Misc.
FRL Misc.
Rainbow trout FRL Misc.
states 0.07-0.09
residue (SB)
states 0.02 residue
(SB)
states 0.03-0.07
residue (SB)
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),
AMTC-1U07
Henderson , et
al (1971),
AMIC-li.07
Henderson, et
al (1971),
AMIC-1U07
Henderson.et
al (1971),
AHIC-1"»07
Henderson,
etal (1971),
AMIC-11.07
Henderson,
etal (1971),
AMIC-l
-------
Co*oound
DOT
DOT
DOT
DOT
DOT
DOT
ODT
DOT
DOT
ODT
DOT
Field
Orqanlsm Study
nrldq»llp FRL
sucHer
Arctic FRL
qr ay 1 1 nq
Pound FRL
whl tef ish
Lonqnose FRL
sucher
Yel 1 ox p»rch FRL
Chain FRL
pickerel
Hhl te catfish FRL
White perch FRL
Goldfish FRL
Bluegllls FRL
Redbreast FRL
sunf Ish
Field
Locat Ion
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Misc. states
Toxlclty, Experimental
Act 1 ve Variab 1 es,
Tnqredlent, Controlled
Ppm or Noted
0.38 residue
(SB)
0 . ?1 residue —
(Srt)
0.31. residue
(sa>
0.01-0.10
residue (SB)
o.os-j.se
residue (S8)
0.08 res 1 due —
(S81
0.21-0.31
residue (SB)
0.63-1.30
residue (SB)
0.65 residue
(SB)
0.0'»-O.Z
-------
DOT
DOT
DOT
DOT
DOT
DOT
DDT
DOT
DOT
Pumoklnseed FRL Misc. states 0.23 residue
Largemouth
buss
Brown
but I head
Cam
ChanneI
catfish
Gambusla
affinis
FRL Misc. states O.Ofi-1.57
residue (SB)
FRL Misc. states 0.06-0.<»2
residue (SB)
FRL Misc. states 0.01-0.96
residue (SB)
FRL Misc. states 0.02-5.07
residue (SB)
BSA
pob (SB)
Wolffla
papullferft
Salvel Inus
fontInalls
(1.15 q)
BCFA —
100 (K)
7.If
Sal vetInus
font InalIs
(2.13 q>
BCFA —
11.9 (T<>)
Hunter1 s
medium
dilutod
1:5
af>,c,d,
e,f,i,o,
aulfato,
copper,
nan^anese,
Iron, and
chroraluai
e,f,l,o,
aulfato,
copper,
same as above
same as above
same as above
same as above
same as above
Hendersont
et al(1971),
AMIC-ll»f)7
Henderson,et
al (1071),
AMIC-1I»!17
Henderson,et
al (1971),
AHIC-H07
Henderson,
et al (1=71),
AHIC-K.07
Henderson,et
al (1171),
AMIC-ll.07
C-l"»- label 1 ed POT was taken uo by Murchy and
mosgultofish irore raoldly over a ?6-hr Hurohy
period at ?n C thin at 5 r. It was shown C1971),A1IC-
that only live fish take UP ODT, that H70
uptake was related to resoiratlon rate
and that srrall fish are more efficient
than laraer fish In removing nnT from
water. One Imotlcatlon of this study is
that at warmer temperatures PDT is taKen
up more rapidly, thus suggesting that
thermal releases be carefully controlled.
All compounds were harmful to Worthley, et
duckweed to aorie degree. Decreased al (1971).
populations wore noted at non-lothul AMIC-3233
concentrations and some compounds
(Halathion and 2,l\.-fi) caused terstogenlc
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 bioassay procedures were AMIC-1812
followod. Symot omol ogy was also
reported. Generally, toxicity was
significantly different at the two body
weights, i.e., more toxic at the lower
body weight, except for Malathlon.
Well-defined experimental conditions were
said to result in truer measurement ot
toxicity.
same as above
Post, et al
(1971),
AMIC-1812
iron, and
chro.-nium
-------
Covoound
ODT
DOT
DOT
DOT
DOT
DOT
Field Field
Organism Study Location
Sal«o cl arkl BCFA —
(0.33 q)
Salrno clarKl BCFA —
(1.?? q)
Salmo flCFA —
galrdner 1
(0.1.1 q)
Oncorhynchus BCFA --
Klsutch 10.5
9>
Oncorhynchus BCFA — -
Hlsutch (1.6S
9>
Artemla spp. L
Toxlclty, ExDerlmental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
0.0001 (T> a«,c,d, sane as above
o,r,i,o.
sulfato,
copper,
nanganoae.
Iron, and
chromium
0.00001 and — - Artemia SDD oooulatlons exposed
0.000001 In 19fi6 to the Indicated DOT
(sublethal) concentrations and studied for up to
-------
OOT
OOT
OOT
OOT
OOT
OOT
OOT
OOT
OOT
OOT
OOT
Sebastodes
sp.
FO
PanulIrua
interruptus
Paralabrax
nebulIfer
Anlsotrenls
davldsonl
FO
FO
FO
Pimelometaoon FO
pulehrun
Haliotls
rufescens
FO
Strongylocent FO
rotus
franciscanus
Hlnnltes FO
miltIruqosis
Hallotls FO
corrugata
Kelletla
helletll
Plants (algae F
and higher
aquatic
Pacific 0.1.6 (liver
Ocean, Cal. residua)
background. Brine shrimp nauolll Here
apparently most sensitive to DOT comoared
to older stages* Cyclic coexistence of
pesticide residue and vulnerable stage of
life cycle Influenced succeeding
generations.
Samples of marine animals Here Munson
collected from three locations off the (1972),
coast of Southern California and analyzed ANIC-3096
for residues of chlorinated hydrocarbons.
The data suggest that Kellefs Hhelk
Houtd be a good Indicator organism for
studying the regional distribution of
chlorinated hydrocarbons.
Pacific 0.037 (muscle
Ocean. Cal. residue)
Pacific
Ocean. Cal.
PacifIc
Ocean. Cal.
PaclfIc
Ocean, Cal.
Pacific
Ocean, Cal.
Pacific
Ocean, Cal.
Pacific
Ocean, Cal.
0.21
(I Iverresldue)
O.it (liver
residua)
0.21 (liver
residue)
less than 0.1
(liver
residue)
0.0*7-0.073
(gonad
residue)
0.032 (gonad
residue)
Pacific 0.0<»2
Ocean, Cal. (digestive
gland residue)
Pacific 0.077
Ocean, Cat. (residue)
Various 0.01 to 0.71.
ponds and (residue)
streamsln
sane as above
same as above
sane as above
same as above
sane as above
same as above
sane as above
sane as above
same as above
Hunson
(1972),
AMIC-T096
Munson(1972).
AKIC-309&
H.unson(197J),
aiIC-3395
Munson(1972).
4SIC-3096
Munson
(1972).
4MIC-3096
Munson
(1972),
SHIC-3096
Munson
(1972).
1MIC-3098
Munson
(1972),
AHIC-3095
Munson
(1972),»MIC-
3096
Plant, Invertebrate, fish, and Dinond, et
nud samples were Pooled, homogenized, and al (1971).
analyzed for OOT. Birds Here analyzed AMIC-3291
-------
I-1
VI
o
Compound
DOT
DOT
DOT
DOT
DOT
Organism
pi ants)
Invcr fobrates
(C=iwh^rus
barton 1 .
f r eshna t er
mussp 1 <;, and
srnal 1 er
an i i"a I s)
Fish
(Sal v«l Inus
font Inal Is
and Semot 1 lus
atr omacul atus
pr Imarl 1 y)
Birds
(MAoacery 1 e
alcyon.
Merous
merqanser,
and
Lophodytes
cucu I 1 atus)
Muds
Llmnephl lus
rhomblcus
(larvae)
Toxlclty,
Active
Field Field Inqredlent,
Study Location Pom
Maine
F Various 0.03 to 2.<»1
ponds and (residue)
streams In
Maine
f Various 0.21 to 9.8
-------
H
VJ1
OOT
DOT
OOT
DOT
OOT
OOT
OOT
Sibils so. FS
(larvae)
Gammarus sp. FS
Salve)Inus FS
rontlnalIs
Semotllus FS
atromaculstus
Cottus balrdl FS
Rhlnlchthys FS
atratulus
Sal vetInus L
fontlnalIs
(15.? cm)
Knights
Creek, Dun
County,
Wise.
Knlqhts
Creek, Dun
County,
Wise.
Knlqhts
Creek, Dun
County,
HIsc.
Knlqhts
Creek, Dun
County,
Misc.
Knlqhts
Creek, Dun
County,
Misc.
Knlqhts
Creek, Dun
County,
Misc.
0.01 (whole
body
(residue)
0.03(whole body
residue)
(fat
residue)
0.1-0.6(tat
residue)
0.5-1.5 (fat
residue)
0.10
(Tat
residue)
0.1-0.3 (SB1) a»
1963-1965 with various chlorinated
hydrocarbon pesticides. No residues were
found In water samples. Silt samples
contained 0.007-0.013 ppm endrln and
0-0.005 ppm dleldrln. Endrln residues of
0.011-0.025 pom and 0.003-0.006 ppm
dl«ldrln were found In debris samples.
Despite limited control data, residue
analyses Indicated that contamination of
the environment studied was limited.
same as above
same as above
same as above
same as above
same as above
same as above
Houbry, et
al (1968),
AHIC-3753
Houbry, et
al (1Q6M,
AMIC-37S1
Houbry, et
al (1963),
AHIC-3753
Moubry, et
a I (1968),
4HIC-3753
Moubry, et
al (1968),
AHIC-3751!
Moubry, et
al (196.5),
AHIC-3753
NeurophyslologlcaI function of
brook trout was affected by ?i*—hr
exposure to DOT as determined by
measurement of electrical activity of
lateral lines. Partially exposed lateral
lines of freshly killed fish were fitted
with electrodes. DOT caused the lateral
line nerve to become hypersensitive to
experimental stimuli and affected
behavioral responses of fish to
temperature.
Anderson
(1968),
AHIC-376S
-------
CO'ooun-J
Field Field
Organism Study Location
Toxlclty,
Active
Tnqredlentt
Ppit
Experimental
Variables,
Control I «d
or Noted
Comments
Ret erence
DOT
r
rv>
DOT
DOT
DOT
DOT
DOT
Oncorhvnchus L —-
kisutch (?.q
9>
0.33 (T31)
Oncorhynchus
klsutch (7.l>
Oncorhynchus
klsutch
(15.0". q)
Salve)Inus
fontInalIs
(110-180 q)
Parophrys
vetulus
Her luce 1 us
producfus
FM
FM
Paclf Ic
Northwest
Coast,
Blalne,
Wash.
PaclfIc
Northwest
1.3 (T65)
2.6 (T106)
0.0? (SB)
0.01 (residue) —
0.01-0.06
(residue)
A diet containing DOT fed to coho Buhler, «t
salmon resulted In median survival times »l
directly proportional to body weight.
Suoplementa I feeding prolonged llfespan,
but mean survival time remained a direct
function of body weight. Smaller salmon
were more susceptible because Hold
content apparently failed to provide for
storage detoxification of DOT.
Considerable additional data are
presented.
same as above
same as above
(1978),
J7M
Buhler, et
al
(1970),AHTC-
37M
Buhler, et
al
(1970).AMIC-
3781
RrooK trout conditioned to light Anderson,et
and shock respond to both by the al (19701,
propel lei—tall reflex. Exposure to DOT AMIC-3782
resulted In markedly delayed ability to
learn. The authors state that DOT
apparently affects the CNS and may cause
adverse effects on such behavioral
activities as territorial defence and
migration.
Pesticides from the Columbia Stout
River into Puget Sound apparently (1968),
contaminated fish constituting commercial AMIC-378"*
catches In Pacific Northwest waters.
Residues in these marine products were
substantially lower than the FDA
tolerance for beef (7 ppm). Fish fro*
locations near the mouth of the Columbia
Plver had higher pesticide content than
ones caught farther away.
same as above Stout
(1968),
-------
r
H
CU
DOT
DOT
DOT
DOT
DOT
Hcrlucclus FH
productus
Her luce Ius FH
productus
Merlucclus FH
croductus
Sebastodes FH
alutus
Platlchthys FH
stellatus
Coastf
Sarasota
Passage,
Hush.
Pacific O.Ot-0.09
Northwest (residue)
Coasti Fort
Susan • Hash*
Paclf le
Northwest
Coast, Cape
Foul weather,
Ore.
Paclfle
Northwest
Coast,
Aberdeen,
Mash.
Pacific
Northwest
Coast,
Hecate
Strait, B.C.
Pacific
Northwest
Coast,
Rtainv,
Hash.
O.OllresIdue)
0.08 (residue) —
0.01 (residue) —
O.OKresldue)
same as above
sane as above
same as above
same as above
sane as above
AHIC-37BI.
Stout
(1968),
AHIC-378<»
Stout
(19681,
AMTC-37SS) ,
»HIC-378«i
DOT
•Gadus FH
•acrocephalus
Paclfle
Northwest
Coast,
Blalne,
Hash.
O.OOit
(residue)
same as above
Stout
(1968),
DOT
DOT
Sebastodes FH
flavldus
Sebastodes FH
f lavldus
Pacific
Northwest
Coast,
Hecate
Strait, B.C.
Pacific
Northwest
Coast,
Ilwaco,Hash.
O.OCK.-0.05
(residue)
0.0i>-0.19
(residue)
same as above
same as above
Stout
(1968),
Stout
(1968),
AHIC-378<»
DOT
Pfmeohales BCFA —
0.018 (T<>)
a»,e
LAS acted synerglstlcally with Solon, etal
-------
>
H
.£-
Coffoound
nn T
UU 1
DOT
00 T
Field Field
Orqanlsm Study Location
orome 1 as
auratus
Carasslus L
auratus
S* 1 mo L -—
qa 1 rdner I
(186-788 q)
Toxlclty,
Active
Ingredient,
Ppm
1*5-180 (SB
5-20)
0-0.1
(resl due)
15 (SB 6 hr )
Exper I men ta 1
Variables,
Con t ro 1 led
or Noted Comments
oarathlon to cause less survival of
fatheds but had an Indeterminate effect
with DDT and no synerqlstlc effect with
Endrln.
f DDT
residues determined after 21 days of
exposure. Most DDT had been converted to
ODE. Phenobarltal had no significant
effect on insecticide residues.
a* same as above
differences In lateral line preparations.
Reference
(1969) ,
AMIC-3785
(1971) ,AMIC-
3791
Younq, et al
(1171) ,
AMIC-3796
fl ahp * o t1 s t
(1971) ,AHIC-
3808
DOT
DOT
DOT
DOT
*>a I mo
qalrdnerl
g)
Trl turus
crl status
Pana
temporarla
Rana
temporarla
0.1-2.0 (NTE,
Intravenous)
0.62-1.1.
(resldue)
0.05 (SB 5-19
hr)
0.5-1.2
mlcroqram
(resldue)
a»
were observed after 1 hr. Neural
dlscharqe was not affected by Intravenous
Injections, but tremors occurred at
concentration levels of 0.5 pom and
above. The authors conclude that
spontaneous activity of the lateral line
Is not a sensitive Index Tor DOT
neurotoxlc effet.
same as above
DOT caused hyperact1vIty In
exoosed tadooles. This caused Increased
capture lunges of newts thus Increasing
the oredatory efficiency of the newts.
DDT had no apparent effect on the newts.
sane as above
same as above
Bahr, et al
(1971),AMIC-
3808
Cooke
(1971),
AMIC-3811.
Cooke
(1971) ,
AMIC-3811.
Cooke
(1971) ,
AMIC-381
-------
DOT
ODT
DOT
tt
VJ1
DOT
DOT
DOT
ODT
Carasslus 8SA
auratus (8-15
9>
1.0 (SB 2.5hr) a,q*
Carasslus BSA
auratus (a-15
q>
Salmo salar
SaIvelInus
fontInaI 1s
(year IInq)
SalvelInus
fontlnalls
£ndomychura
craverl
(egqs)
Fndomyehura
craver l
(eggs)
Western
U.S.,
PaclTIc
Ocean,
Panama,
Mexico,and
Antarctic
Western
U.S.,
Pacific
Ocean,
1.0 (T 10 hr>
0.02-0.20
(sat)
0.03-0.20
(SB1)
O.i» (SB)
a»,q-
39 (residue)
0.31-2.
-------
CoBDound
DOT
DOT
;>
t->
\JI
o\
ODT
DOT
ODT
DOT
Toxlclty. Exoerlnental
Active Variables.
Orqanls" Study Location Po« or Noted Co««ents
Mex i c o, and
antarctic
Tnalasseus F Western 5,0 (residue) — sa»e as above
e t eqans U.r . ,
(eqqs) Pic 11 Ic
Ocean ,
Pan^a,
Kaxlco.and
Larus F Wostern 1,8 (residue) — sa»e as above
heer«anl u.r.. ,
(•igs) Pact 1 Ic
Ocp^n,
Panan ^
H»xlco, and
Antarctic
Po«oxls F western 1.83 ("hole — sa«e as above
Paclt Ic
Oc»an.
''oxlco, and
Antarctic
Po'oxis F Heitsrn 7.10 (*hole ~ sa>e as above
nlgTO- U.S., body residue)
oaculatoa Pacific
Oce*n ,
Panama,
Mexico, and
Antartic
Leooals F western 5.5 (xhole body — save as above
•acrochlrus U.S., residue)
Pacl f Ic
Ocean ,
Mexico, and
Antarctic
Pyqoscells F Western 0.128 — sa«« as above
adcllae U.S., (residue)
Pe f erence
P 1 sebrouqh.
» t al
( 106K) ,
AMIC-31!^
Dls »brough.
e t al
U96M ,
A MIC- 38*,',
"(S.hrou^h.
t t 3 \
(19SS) ,
AHTC-3!«i<.
PlS.hrouqh,
et al
(19M) ,
AHIC-38M.
P 1 sebrouqh,
e t al (iq«>8
AMIC-38M,
Plsebrouqh,
et al
-------
DOT
DOT
DOT
DOT
DOT
ODT
(eqqs)
Aechmorohorus F
occidental Is
Fulmanus
qlacini Is
Put f Inus
creatoous'
PuT f Inus
qrIseus
PuffInus F
tenulrostrls
Oceanodroma
homochroa
Paclf Ic
ncp»n«
Panama,
Mexico, and
Antarctic
Western
U.S.,
PacITIc
Ocean i
Panama,
Maxlco, and
Antarctic
Western
U.S.,
PacltIc
Ocean,
Panama,
Mexico, and
Sntarctic
Western
I).";.,
Paclf Ic
Ocean,
Panama*
Mexico, and
Antarctic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
?6.!> (flesh
residue)
O.itl-17.5
(whole body
residue)
3.0 (whole body
residue)
2.3-12.3 (whole
body residue)
39 (whole body
residue)
59.3 (whole
body residue)
same as above
same as above
same as above
same as above
same as above
same as above
(19R8),
AMIC-38«.i»
Rlsebrouqh,
et al
(1968) ,
AMIC-J8I.".
RIsebrouqht
et at
(1968),
Rlsebrough,
et al
(1968) ,
Rlsebrouoh,
et al
(196S),
AMIC-38lt«,
Risebrou<;h,
et al
(1968) ,
AMIC-38
Rlsebrough,
et al
(1968),
AMIC-38
-------
VJ1
CD
Co*Doun4
DOT
DOT
DOT
DOT
DOT
DOT
Organism
Pe 1 ecanus
occ M»ntal Is
(eqqs)
Fr eqa t a
maqnl f lc«ns
(eqgs)
Sula
leucogaster
Phal acrocorax
penlc I 1 laTus
(eqqs)
Phal acrocorax
Del aglcus
(eggs)
Anas
cyanootera
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Study Location Ppm or Noted Comments
An tar c T ic
F western 10. 0-11.5 — same as above
U.S., (residue)
Pacl ( Ic
Oc«»an ,
Panam a *
Hex 1 c o, and
Antarctic
F Western 0.0087-0.03 -- seme as above
U.S., (residue)
Pad t Ic
Ocpan,
Panam a ,
Mexico, and
Antarctic
F Western 8.Z (residue) — same as above
U.S.,
PaclT Ic
OCP an ,
Panam a ,
Mpxlco, and
An t ar c t Ic
f Western 0.326 — same as above
U.S., (residue)
Pacl f Ic
Dcoin,
Panama,
Hex Ic o, and
Antarctic
F Western 0.128 — sane as above
U.S., (residue)
Pacl f Ic
Ocean ,
Panama,
Mpxlc o, and
An tare tic
F Western 10.9 (whole ~ same as above
U.S., body residue)
Pacific
Ocean,
Reference
R Isebrouqh.
et al
(196S) ,
AHIC-^S")".
P 1 sebrouqn.
et al
(19S8) ,
AMIC-381.'.
Rlsebrouqh,
et al
(196H) ,
AMIC-3«itii
Rlsebrouqh,
et al
(1968) ,
AMIC-38<4«.
Rlsebrouqh,
et al
(1968) ,
AMIC.-3(<,i,
Rlsebrough,
etal (1968),
tHIC-SOM,
-------
DOT
OUT
>
DOT
DOT
DOT
DOT
El anus
leucurus
(«qgs)
Acclolten
cooperll
Aaul la
chrysaetos
(eqqs)
Pandlon
hal laetus
Fa I co
columbarium
Falco
sparverlus
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Paclf Ic
Ocnan,
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.,
PaclfIc
Ocean,
Panama,
Mexico, and
Antarctic
0.3I.-9.0
(residue)
?5.2 (whole
body residue)
2.0 (residue)
sane as above
same as above
same as above
"55.0 (whole
body residue)
2-9 (whole body
residue!
0.0^ (Mho 1 e
body residue)
same as above
same as above
same as above
RIsebrouqh,
et al
(1968),
AMIC-38«»«i
Rlsebrough,
et al
(1068),
AMIC-3SM>
Rlsebrouqh,
et al
(1968),
Rlsebrough,
et al
(1968),
&MIC-38It
-------
Comoound
DOT
DOT
DOT
OUT
DOT
DOT
Organism
Falco
soarver lus
(eqqs)
Nyc t Iconx
nyc 1 1 corax
(eqqs)
Larus
occidental Is
(eqqs)
Sterna
forsterl
(eqqs)
Hydrooroqne
casola
(eigs)
Phalaropus
ful icarlus
Field F !<•! d
S t udy Locat 1 on
F Western
U.S. ,
Pad f Ic
Ocean ,
Panam a.
Mexico, and
Antarctic
F Was tern
U.S.,
Pacific
Ocean,
Panama,
Kexl co , and
Antarctic
F Western
U.S.,
Pacit ic
Ocean ,
Panam a.
Mexico, and
Antarctic
F Western
U.S.,
Paclf Ic
Ocean,
Panama ,
Mexico, and
Antarctic
f Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F western
u.*..
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
0.? (residue) — same as above
n.5*»l-0.869 — same as above
(resl due)
0.385-0.803 ~ same as above
(resl due)
0.665 — same as above
(residue)
1. 269-1. <»30 -- same as above
(residue)
0*78 (whole ~~ sane as above
body residue)
Reference
R I sebrough ,
etal f 1°.<>3> ,
AMIC-3m.<.
R 1 sehrounh.
ef al
(196M ,
AMI03B<.<»
R I sebrouqh.
et al
(l°f>8) ,
AMIC-38UU
R 1 sebrouqh.
et al
I1Q6R) ,
AHIC-38it
-------
DOT
DOT
DOT
DOT
DOT
DOT
Urla aalge
(eqqs)
Ptychoramphus F
aleutlcua
SynthlIborsmo F
hus antlquu*
Ceporhlnca
monocerata
Zenaldura
macroura
Tyto alba
DOT
Sturnella
neglecta
Western
U.S.,
PaclfIc
Ocean,
Panama,
Mexico,
151 (residue)
sane as above
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.,
PaclfIc
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
•5.8 (xhole body
residual
0.75 (whole
body residue)
2.7 (whole body
residue)
0.19 (whole
body residue)
1.3-6.6 (Hhole
body residue)
0.2-3.3 (Hhole
body residue)
sane as above
same as above
same as above
same as above
sane as above
same as above
Rlsebrought
et al
(1968),
AMIC-J8I.I,
Rlsebrouqh,
et al
(1968),
AHIC-38M
R1sebrouon,
et al
(1968) ,
AMIC-7JI.4
Rlsebrouqh,
et al
(1968) ,
AMIC-38i.it
Rlsebrouah.e
t al (1968),
AMIC-38<.I>
Rlsebrough,
et al (1968) ,
Risebrouqh,
et al
(1968),
-------
o\
ro
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Ppin or Noted Comments
DOT
DOT
DOT
DOT
DOT
Ocean,
Panama,
Mexico, and
An tar c t Ic
Falco F Western 0.0? (residue) — —
pereqrlnus U.S.,
(eggs) Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Falco F Western 1.9-Z96 (flesh ~
pereqrlnus U.S., residue)
(Immature) Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Falco f Western 6i.-5.000 (fat
peregrlnus U.*:., residue)
(Immature) Paclf Ic
Ocean,
Panam a.
Mexico, and
Antarctic
Falco F Western BS-137 (flesh
oereorlnus U.S., residue)
(adult) Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Falco F Western 2,600 (fat
pereqrlnus U.S., residue)
and other predator species Mere collected
widely and analyzed for DOT, DDE, PCB,
and * feM other pesticides to a lesser
deqree. PCR and DDT Here found to be
widely dispersed qlobally. PCH was Tound
to be a powerful inducer of heoatic
enzymes that degrade oestradlol.
Reductions In thickness of ego shells.
eqgshell weight, and Mater retention
occurred. All affect hatchlnq success.
The authors state that the oereqrine nay
be the first species entlrpated by global
con tarn Inatlon.
same as above
same as above
same as above
same as above
Reference
AMIc-38<.«.
et al
(1968),
AMIC-SSM.
R Isehrouah,
et al
(196(0 .AMIC-
381. >.
R i sebrouqh.
et al
(196(0,
AMIC-38M.
Rlsebrouqh,
et al
(1968).
AMIC-38
-------
DOT
DOT
fe
U)
DOT
DOT
DOT
(adult)
Podlceps
caspleus
Loooelanla
•elan la
Halocyptena
mlcrosoma
Plzonyx
vlvesl
Ictalurus
punctatus
USA
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
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
0.26-12.1
(whole body
residue)
1.2 (whole body —
residue)
sane as above
same as above
3.2 (whole body
residue)
same as above
0.71 (whole
body residue)
0.016
-------
Co-ooun^
DOT
nr\T
UU I
DOT
DOT
DOT
£ DOT
-p-
OOT
DOT
DOT
DOT
DOT
Fluid Field
Organism Study Location
Salmo trutta OSA
kisutch
Peres BSA
tl avescens
Ictslurus RSA --
n'las
Carasslus BSA
auratus
Cyorlnus BSA — -
carolo
Pltneohales (ISA •*-
prome 1 as
L»oo»Is BSA
macrochlrus
Leoonls BSA --
microlODhus
Mlcropterus BSA —
sal moldffs
Salno BSA
qalrdnerl
Toxlclty,
Active
Ingred 1 en t «
Pom
0.002 (Tit)
0 Q 0 1* (T^t)
0.009 (Tit)
0.005 (Tl,)
0.021 (Tit)
0.010 (Tit)
0.019 (Tit)
0.008 (Tit)
0.005 (Ti,)
0.003 (Tit)
D.007 (Tit)
Experimental
Variables,
Con t ro 1 led
or Noted
a ,
synthetic
test nater
a ,
synthetic
test Hater
a,
synthetic
test Hater
a,
synthetic
test Hater
a,
synthetic
test Hater
a,
synthetic
test nater
a,
synthet Ic
test Hater
a,
synthetic
test Hater
a,
synthetic
test nater
a,
synthetic
test Hater
a,
synthetic
test Hater
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
Reference
MaceK, »T
Bl (1970) ,
AMIC-^510
al (1970),
AMIC-5510
Maceh, et
al (1970),
AMIC-5510
Mncek, et
al <1°70),
AMIC-5510
MaceK, et
si (1970),
Hacek, et
al (1970) ,
AMTC-5S10
Macek, et
al (1970) ,
AMIC-5510
Macek, et
si (1970) ,
AMIC-5510
Macek, et
al (1970),
AMIC-5510
Hacek, et
al (19701 .
AMIC-5510
Macek, et
al (1970),
AMIC-5510
-------
DOT
Palaemonetes BSA
bad lake/is Is
(resistant)
0.0037-0.0068
m>
a»
fe
V/l
DOT
DOT
Pal aemonetes-
kadlakensls
(non-
resistant)
Tctalurus
catus
BSA
Clear LaKef
Cal.
DOT
DOT
DOT
Perca
fIavescens
Lepomls
qlbbosus
Catostomus
comnersonl
FIR
FLR
93 samplInq
stations In
Mass.
93 samolIng
stations In
Mass.
0.0026 (Tl)
less than 1
(flesh
residue)
0.06-13.2
(residue)
0-9.1
(residue)
FLR 93 sampling 0-11.2
stations In (residue)
Mass.
Bloassays Here conducted with
shrimp from three areas of Intensive
pesticide use and from an unexposed area.
Previously exposed shrimp Mere fro* 1 to
?•> times more resistant than unexoosed
shrimp. Both types of shrimp Mere also
exoosed In canes to Maters of the
contaminated areas. Susceptible shrimp
suffered 66 percent more mortality than
did resistant shrimp. The foxlclty ot
the Insecticides ranked In descending
order Mas as follOMsJ most toxic,
Endrln, DDT, Methyl parathlon, Parathlont
medium toxlclty, Guthlon, Llndane,
Toxaohene, Strobanei lease toxic
Chlordane, Sevin, and Heptachlor.
same as above
Naqvl, et at
(1970).
AMIC-SS19
Naovl.et al
(1970),
AMIC-S519
Residue analysis results mainly Linn, et
for THE In fish, birds, and plankton fro» AL(1969),
11S9 through 19f>5 Mere reported. The AMIC-5521
residues primarily resulted from
application of DDT to farmland and Tor
qnat control. In some cases, data for a
single animal In one year were given.
Primary emphasis Mas on larqerrouth bass
and Mhlte catfish. The general level of
TDK contamination In birds and fish
declined markedly from l^R to 1965.
This decline correlated directly Mlth
strict limitation by permits of DDT
applications during the latter years.
Fish Indigenous to Massachusetts
freshwater streams were analyzed for DDT
and DDT metabolites during 1965-1967.
Generally there was an Increase In
pesticide content during the three year
period.
same as above
same as above
(.yuan, et al
(1968),
4MIC-3839
Lyraan, et el
(1968),
AMIC-3839
Lvnan, et al
(19S8) ,
AMIC-3839
-------
Comoound
DOT
DOT
DOT
00 T
DOT
DOT
DOT
DOT
DOT
DOT
DOT
Organism
Tc tal urus
npbu 1 osus
Cyor Inus
carpi o
Esox nlqer
crysol pucas
*ipmo 1 1 1 us
corporal Is
Lpoom 1 s
macrochlrus
Amb 1 OBI I tes
ruoes tr is
S»"iot 1 lus
atroiacul atus
Microoterus
do 1 om 1 PU 1
Alosa
paeudo-
harengus
Fundu 1 us
heterocl 1 tus
Field Field
Study Locat Ion
FLR 93 samollnq
static ns in
MSSS.
FLR 93 samol 1 nq
stat 1 ons In
Mass.
FLR 93 samollnq
stations In
Mass.
stat 1 ons In
Mass.
FLR 93 samol Ing
stat 1 ons in
Mass.
FLR 93 simol Inq
stations in
Mass.
FLR 93 samol Ing
stations in
Mass.
FLR 93 samol Ing
stations In
Mass.
FLR 93 samol Inq
stations In
Mass.
FLR 93 samollng
stations in
Mass.
FLR 93 samot Ing
stations in
Mass.
Toxlclty, Exoerlmental
Active Variables,
Ingredient, Controlled
PD» or Noted
(1.3? (residue) —
0.3-1.0
(res 1 due)
0.0?- 1.0
(resl due)
0-1.1 — —
(residue)
0-3.8
(residue)
0-Z.l.
(residue)
0.1.-8.3
(residue)
O.OZ-0.3
(resl due)
0.2-0.6
(residue)
0.3<» (residue)
0.7-2.8
(residue)
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
Reference
Lynan, et
AHIC-3839
L yman, e t a
AMIC-3839
(1960) ,
A«IC-3S39
(19681 ,
AMTC-3HT9
Lvman, pt
(1968) ,
AMIC-3R39
L yman , et
AHIC-3339
Lyman, et
( 1 96 f ) ,
AMir—3^3Q
Lynan, et
AMIC-3839
L yn an , pt
AMIC-3839
Lyman, et
( 196") ,
AMIC-3839
Ly*»n, et
(1968) ,
AMIC-3839
al
1
1
3 1
al
al
al
al
al
al
al
DOT
FLR 93 samollng 0.1-3.3
same as above
Lyman, et al
-------
DOT
DOT
DOT
DOT
DOT
DOT
DOT
ODT
cornutu*
ROCCUS
amorIcanus
Pomoxls
nigro-
tuoulatua
FundulU5
dlaphams
Notrools
ana tos t anus
Leoomls
»ur 1 tus
Phlnlchthys
atrafulus
SalvelInus
font Inal Is
(caqed)
SalvelInus
fontInalIs
(Mild)
FLR
FLR
FLR
FLR
FLR
FL"
FS
FS
stations In (residue)
Mass.
93 samollnq 0.2-2.2 --
stations In (residua)
Mass.
93 sampling K.k (residue) —-
stations In
Mass.
93 sampling 5.9 (residue) --
stat1ons In
Mass.
93 samollnq O.<»0 (residue)
stations In
Mass.
91 samollnq 0.
Labrador,
Can.
0.1 (NTE)
c,d,e,g
Bohby"s
BrooKf
Labrador,
Can.
0.1 (SB)
Ctd.e.g
sane as above
same as above
same as above
sane as above
same as above
same as above
In studylnq control of black fly,
the Indicated aauatlc soecles Mere
studied at a series of six sanollnq
stations. Water quality was unaffected
hy the DDT gonllC3tlon. No caned fish
dled» but wild on«>s did aooarently
resultinq from Inaestlon of dead
Invertebrate larvae. Invertebrates were
collected by bottom samolinq and by drift
nets, and fish by nettlm and analinq.
Fish mortality could always be related To
at least a ten-fold increase in DDT
residues In the fish. DOT caused high
bottom fauna mortality by direct contact.
Caddisfly larvae were more affected than
stonefly and way fly larvae. The author
stated that DDT larvicidlnq for black fly
control was not successful because of
harm to non-target organisms.
same as above
(1968) ,
AMIC-3839
Lyman, et al
(19S«),
4MIC-3S39
Lyman, et al
(1968),
AMIC-3839
Lynai, et aJ
(19*8),
AMIC-3939
Lyman, «t al
(19
-------
Compound
OOT
OOT
OOT
OOT
OOT
Toxlclty,
Active
Field Field Ingredient,
Organism Study Location Pom
Slmulum FS Robby"s 0.1 (SB)
venustum Brook,
(larvae) Labrador,
Can.
Bottom FS F!obby~s 0.1 (K)
invertebrates Brook,
Labrador,
Can.
Leoomls 1 — 590 (SB)
macrochlrus
(1 Iver
ml t ochondrl a)
Copepods FL State 0.05 (K2)
(Cyclons and College,
blcusnldus, BSA Hiss.
Cvc 1 ODS
var leans.
Cycl ODS
verna 1 Is,
Fucyc 1 oos
agl 1 Is,
Kacrocy clops
al bldus.
Or t hocyc 1 ODS
modestus)
Cooepods FL Belzonl, 0.05 (91
(Cycl ODS and Miss percent K2)
blcusoldus, BSA
Cycl OPS
var leans.
Cycl ODS
vernal Is,
Eucycloos
•gll Is,
Macro Cyclops
Experimental
Variables,
Control led
or Noted Comments Reference
c,d,e,g same as above Hatfleld
1 196") ,
1MIC-5770
c,d,e,g same as above Hatfleld
(1*569) *
AMIC-5770
a* Oxygen uptake by bluegitl liver Hlltlbran
mitochondria was inhibited In the (1971),
presence of DDT and succlnlc acid. AMIC-5975
Increased hydrolysis of ATP also occurred
In the presence of Hg and Mn Ions. The
author states that the primary effect of
OPT npcears to be Inhibition of electron
flow from succlnlc acid to the cyfochrome
chain.
~ The response of Naavl, et al
pesticide-resistant aauatlr organisms to (1969),
various pesticides was compared to the AMIC-5979
Pesticide-resistant species were
collected at Pelzoni and non-resistant
species at State College. Copepods,
clams, snails, and sludqe Horms 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 troohlc levels.
-- sane as above Naavl, et al
(19691 ,
AMIC-5979
-------
DOT
DOT
001
DOT
DOT
ODT
00 T
albldus,
Orthoevelops
nodestus)
Tublfex
tublf»x
Crassostr«a
vlrglnlea
(larvae)
FU
and
BSA
Hiss.
BSA
Gambus la
aftints
(female, (4.3
en, 1.9 q>
Leblstes
retIculatus
(nale, 1.6
cm, 0.2 9)
Tllapla
mossamblca
(3.<> en, 1.3
Kuhlia
sandvlcensls
«>.3 cm, 1.5
9>
Stolephorus BSA
purpurea (3.6
cm, O.it q)
BSA
BSA
BSA
3.0 (NTE)
0.031. (Til.)
0.0?
0.003 (Ti»)
0.007 ITii)
0.0039 (T,ANIC-
5990
Nunogawa,
al (19701,
AHIC-6567
a.o.d.
»,f,i,
(Honolulu
tap
water)
a,o,d,
e.r.l,
(Honolulu
tap
water.)
a,c,d,e,f ,
l,salt
water
a,c,d,e, f
1, salt
Hater
same as above
same as above
same as above
Nunoaaxa, et
al (1970),
AMIC-656T
Nunogaxa, et
al (1970),
AMIC-6567
Nunooaxa, *t
al (1970),
AMIC-6567
Nunoqana, et
al (1970),
AMIC-1567
-------
Toxlclty,
Active
Field Field Ingredient,
Coaoound Organism Study Location Ppn
DOT Carclnus 8SA — 0.3-1.0 (T2)
DOT Cardlum edule 8SA — greater than
(TZ)
Exoer 1 men tal
Variables,
Con t ro 1 1 ed
or Noted Comments
a-fc(contin- One hundred- f or ty surface active
ation 3oa- 3o1 vch lorlnated blohenyls, pure
water and inorganic, and organic chemicals were
solution organisms. The authors noted that most
renewal) published data of this type deal with
toxlclty ot chemicals to freshwater
organ 1 sms.
10 at (con tin- same as above
uous aer-
ation, sea-
weter, ejid
daily
solution
Re f erence
Portmann, et
AMIC-7701
Portmann, et
al (1971),
AMIC-7701
renewal)
DOT
PIeuronec tes
piatessa
asA
0.003-0.01
(T2t
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, et
al (1971),
AMIC-7701
DOT
Freshwater
druti
FL
DOT
Goldfish
FL
Great Lakes 0.6? (whole
(Ontario, body residue)
Huron,
Erie,
Superior,
oupe.LM.u.1-,
Michigan)
Qraat Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.70 (whole
body residue)
Fish from Lake Mlchlaan contained Relnert
2 to 7 times more nRT (and DDT analoqs) (1970),AMIC-
and n 1 f \ dr 1 n rpsMues than f 1 <;h from tho 196
other Great Lakes. Fish from Lake
Superior Invariably had the lowest
accumulations of both chemicals. The
compounds tended to concentrate In fat
lolls). 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),
AMIC-196
-------
OUT
Klyl
FL
Groat Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
3.28 (whole
body residue)
same as above
Relnert
(197D),
AHIC-196
DOT
Lake herring FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
(Hhote body
residue)
sane as above
Relnert
(1970),ftH!C-
196
DOT
Lake trout FL Great Lakes 6.61-7.it"»
(Ontario, (whole body
Huron, residue)
Erie,
Superior,
Michigan)
same as above
Relnert
(1970).AMIC-
196
DOT
Lake
HhltetIsh
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.1*5-5.02
(wholebody
residue)
same as above
Relnert
(1970),»MIC-
196
DOT
Rock bass
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
O.ifO (Hhole
body residue)
same as above
Relnert
(1970) ,
ftMIC-196
DOT
Round
whlteflsh
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.57 (whole
body residue)
same as above
Reinert
(1970),
ftHIC-196
-------
CoBaounl Organism
Field Field
Study Location
Toxlclty.
Active
Ingredient,
PDA
Experimental
Variables,
Control led
or Noted Comments Reference
DOT
Sea lamorey FL
Great Lakes
(Ontario,
Huron,
Erla,
Superior.
Michigan)
1.27 (Mhole
body residue!
same as above
Re 1n«rt
(1970) ,
AMIC-196
DOT
SIIny sculoln FL
(O
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.22-2.33
(whole body
residue)
same as above
Selnert
(1170) ,
AMIC-196
DOT
Spottall
sh 1 ner
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.25 (whole
body residue)
same as above
Relnert
(1970) ,
AMIC-196
DOT
Nlne-splned
stickleback
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
n.i>3 (Hhole
body residue)
sane as above
Relnert
(1970),
AMIC-196
DOT
Stonecat
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.28 (Hhole
body residue)
same as above
Oelnert
(1970).
Anrc-196
-------
DOT
Trout oerch FL Great Lake a 0.9<« (whole
(Ontario, body residue)
Huron,
Erie,
Superior,
Michigan)
same as above
Pelnert
11970),
»NIC-196
DOT
Malleye FL Great Lakes 1.12-6.02
(Ontario, (whole body
Huron, residue)
Brie,
Superior,
Michigan)
sane as above
Relnert
(1970),
AHIC-196
DOT
U)
Hhlte bass FL Great Lakes 1.89-2.76
(Ontario, (whole body
Huron, residue)
Erie,
Superior,
Michigan)
same as above
Relnert
(1970),
ANIC-196
DOT
Hhlte oerch FL
Qreat Lakes
-------
Comoound
Organism
field Flel d
Study Locat Ion
Toxlclty,
Active
Ingredient 1
Pom
Experimental
Variables,
i Control led
or Noted
Comments
Reference
DOT
Fmerald
shiner
Great Lakes
(Ontario,
Huron,
Brio,
Superior,
Michigan)
0.9
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.53-0.63
(whole body
residue)
sane as above
Pelnert
(1970).AMIC-
196
onr
AleMlfe FL Oreat Lakes 0.7?-3.8A
(Ontario, (whole body
Huron, residue)
Erie,
Superior,
Michigan)
same as above
Relnert
(1970),»«IC-
196
DOT
American FL Great Lakes 0.3J-1.5B
sue It (Ontario, (xhotebody
Huron, residue)
Erie,
Superior,
Michigan)
same as above
Pelnert
(1970).AHIC-
196
DOT
81oster
FL
Great Lakes
(Ontario,
1.09-9.83
(•hole body
same as above
Relnert
(1970).
-------
Huron,
Erie,
Superior.
Michigan)
residua)
AHIC-196
DOT
Brown
but I head
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.78 (Hhole
body
residue)
same as above
Relnert
(1970),AMIC-
196
DOT
Carp
5
vn
Great Lakea
(Ontario,
Huron,
Erie,
Superior,
Michigan)
1.9? (whole
body residue)
same as above
Reinert
(1970).
AMIC-196
DOT
Channel
catfish
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
ft.90 (Hhole
body residue)
same as above
RelnerT
(1970) ,
•MIC-196
DOT
Coho salmon
(flesh)
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.72 (Hhole
body residue)
same as above
Relnert
(1970),AMIC-
196
DOT
Coho salmon
(eqgs)
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
2.1? (Hhole
body residue)
same as above
Relnert
(1970),AMIC-
196
-------
Field Flel d
Co«oound Organism Study Location
Lake
M ichl qan)
DOT Cyorlnus FR St. Lawrence
carplo River,
Toxlclty,
Active
Inqr ed 1 en t •
Ppm
0 . 3M 0. 33 ppm
max tissue
Exper 1 men ta 1
Variables,
Con tro 1 1 ed
or Noted
water.
Comments Reference
Residues of ODD were measured in Fredeen, et
mud, molluscs, and ( Ish durlnq and si (1970),
Montreal* residue)
Canada
DOT
DOT
DOT
DDT
DOT
DOT
Catosto»ius FR
commerson1
Amelurus FR
nebulosus
Peres FR
>lavescens
Esox luclus FR
Ambtoplltes FR
rupestrls
Campelona sp. FR
St. Lawrence 0.38(1.33 pom
Rlvor, max tissue
Montreal, residue)
Canada
St. Lawrence 0.38(0,1? pom
Plver, max tissue
Montreal, residue)
Canada
St. Lawrence 0.38 (0.55ppm
River, max tissue
Montreal, residue)
Canada
St. Lawrence 0.38 (0.38
River, ppmmax tissue
Montreal, residue)
Canada
St. Lawrence 0.38(0.02 pom
River, max tissue
Montreal, residue)
Canada
St. Lawrence 0.38 (O.i>0ppn
after DDD aopllcatlon in 196>7. Sampling AHIC-53ii
points were above the point of
apollcatlon and 10 and i»5 ml downstream.
Residues from unknown sources were
detected upstream. nownstpeam residues
were more than twice those obtained
upstream (0.156 versus 0.369 Ppm). The
highest concentration In an Individual
fish was 1.81 ppm*
River,
Montreal,
Canada
same as above
same as above
same as above
same as above
same as above
same as above
Fredeen, et
al
(1970) ,S1IC-
Fredeen, et
81 (1970),
Fredeen, et
si (1970),
max tissue
residue)
Fredeen, et
al (1970),
AMTC-S3<»
Fredeen, «t
al
(1970),«MIC-
531.
Fredeen, et
al (1970),
AMIC-531.
DOT
Cyprlnodon BSA
0.015-0.02 (K) a».
Sensitivity of three generations Holland, et
-------
DOT
OOVP
OOVP
OOVP
OOVP
DDVP
varleqatus
(50-70 mm)
B<»nthlc
Injects
Trout CreeK, 0.012-0.068
Hasatch (K>
County,Utah
Labeo rohlta
(Try)
BSA
11.2 (T7)
Labeo rohlta
(fInqerI Ing)
BSA —
Trlchogaster BSA
fasclatus
(young)
Trlchogaster BSA
fasc1 atus
(adult)
Channa
punctatus
(fry)
BSA
2.* (T7)
1.8 (T7)
Z.It (T7)
0.8 (T7)
seawater of sheepshead minnows to DOT and Endrln
was determined. Sensitivity to DDT
varied seasonally. Fish were bred In
ponds 15m X 5m X 1.25m exposed to
pesticides In aauarla, and survivors used
for breeding. The results for DDT Mere
not entirely clear due to the seasonal
variability. Increased and decreased
sensitivity were recorded for the Fl
generation at different times. Increased
sensitivity for the F2, and decreased for
the F3. The authors stated that
Incorporation of DOT In ova via llnlds
may have caused increased sensitivity.
Endrln toxlclty was decreased in the Fl
and Increased In the F2 generation.
Stream Complete deoopulatlon was found
flow at the collection station ?000 n
downstream from aopllcatlon point,
Insect mortality was Independent of DOT
concentration In areas of turbulent floM,
thus mortality was not directly related
to DOT concentration In this field
situation. Repopulatlon Has Incomplete
after 57 Hk.
a,c,d,e,f DDVP and Phosphamldon were shown
to be selective toxicants that can be
used for eradication of undesirable
animals from ponds without Injuring carp.
OnVP seemed superior since less was
needed, it was not influenced by
turbidity, and It detoxified nore rapidly
than Phosphamldon.
a,c,d,e,f same as above
al (1970) •
AMIC-726
Sonstelle
(1969),
a,Ctd,e,f same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
Konar
(1969),
5i>53
Konar
5US3
Kona
Konar
(1969),A»1IC-
Konar
(1969) ,
OOVP
Puntius
BSA
6.2 (T7)
a,c,d,e,f
same as above
-------
CO
Co«oound
OOVP
OOVP
DOVP
OOVP
OOVP
OOVP
OOVP
OOVP
ODVP
OOVP
OOVP
Toxic! t v
Active
Field Field Inqredlent,
Organism Study Location Pon
soohor«»
(adul t)
tnxbnt BSA — 1J.7 (T7)
tes tudlneus
Heteropneua- BSA -- 17.8 (T7)
tes foasilis
Fsomus BSA — 2.8
till f ormls
(Snlsootera BSA — 0.15 (T7)
(nymphs)
Cyblster sp. BSA — O.?l (T7)
Var 1 ab 1 es«
Control 1 ed
or Noted Comments
a.Cvd.e.f same as above
a,c,d,e,f same as above
a.Cidte*t 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,l same as above
a.c.d.e.f same as above
a,c,d«e,f same as above
a,c,d,e,» same as above
a.c.d.e.f same as above
Refer ence
( 19^.9) ,AHIC-
51.53
Konar
(1969) ,
Konar
( J9S9) .AMIC-
Konar
(1969) .AMIC-
51.51
Kon sr
(1969) ,AHIC-
5«.5J
Konsr
(1969) ,
AHIC-5I.53
Konar
(1969) ,AMIC-
51.53
Konar
(1969) ,4>
-------
OOVP
00 VP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
Neoa sp. BSA
Belostoma BSA
Indies
Hvdrophllus BSA
sp.
Volvox
BSA
Pandorlna BSA
Closterlum BSA
BraclMonus BSA
Gastrotricha BSA
CypPls
Cyclops
BSA
BSA
Naupllus BSA
Oaohnla
BSA ~
Cerlodaphnla BSA
0.27 (T7) a,c,d,e,f
0.28 (T7) a,c,d,e,f
0.3? (T7) a,c,d,e.t
5.0 (NTE)
5.0 (NTE)
1.0 (K)
0.5 (K)
0.5 (K)
0.5 (K)
0.5 (K)
3,c,d,c,f
5.0 (NTE) a,c,d,e,f
5.0 (NTE) 8,c,d,e,t
»,c,d,e, f
5.0 (NTE) a,c,d,e,t
a,c,d
,c,,e,
a,c,d,e,f
a,c,d,e,f
a,c,d,e,f
a,c,d,e,f
same as above
same as above
sane 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
Konar
(1969) •
Konar
(1969),
Konar
(1969) ,
AMIC-5«t53
Konar
(1969) ,
AHIC-';<.53
Konar
(1969) ,
Konar
(19
-------
Compound
OOVP
OOVP
OOVP
DOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
OOVP
Field Field
Organlsn Study Location
Dlapfomus BSA —
Nnndus nandus BSA
Rita rlta BSA
Amnhlonous BSA
cuchla
Mystus BSA
vl tatus
(fry)
Mystus BSA
vl tatus
(adul t)
Puntlus BSA
sophore
(fry)
Channa BSA —
punc f a tus
{f Inqerl Inq)
Channa BSA --
punctatus
(adul t)
Mastocembelus BSA —
pancalus
Macrognathus BSA — -
aculeatu*
Channa I —
pune tatus
Toxlclty,
Active
Ingredient,
Ppm
0.5 (K)
2.6 (T7)
2.8 (T7)
3.1, (T7)
2.3 (T7)
6.6 (T7)
1.0 (T7)
1.8 (T7)
2.9 (T7>
2.6 (T7)
3.6
-------
00 VP
Oecanethonlun
dlbro«ld«
Oelrad
Oelrad
Deaeton vethyl
Ovrnol
(cqqs)
Channa
punctatus
(hatch)inqs)
NeqaprIon
brevlrostris
(1-3 Kg)
BSA
2.5 (T3)
50 (NTE 3.5
HR)
a»
Mercenarla
mercenarla
(larvae)
0.031 (T12)
Crassostrea I
vlrglnlca
(larvae)
Fish (not
specifled)
Cardlum edule BSA
0.072 (Til.)
greater than
1.0-10.0 (K)
100-330 tT2)
than 1.0 ppm, but delayed hatching
occurred at higher concentrations. Yolk
sac absorption was decreased at 1.6-4.0
pom ana stopped at 5.0 pom or more. Eggs
and hatch)Ings survived well at 0.1 Don
OOVP.
sane as above
6388
Konar
(1969),
AMIC-6388
Data from study of drug effects Baldridqe
on young lemon sharks were treated (1969),
mathematically to demonstrate AHIC-3832
apolIcabll1ty of classical rate theory to
the study of chemical shark deterrents.
Incapacltat Ion (narcosis) was the orlmary
parameter timed for effectiveness. This
was usually quite rapid for the more
effective drugs.
The effect of 52 pesticides on Davis, et al
embryonic development of clams and
oysters was reported. Synerglstic (1969),AMIC-
etfects with solvents were also reported. 5990
Most of the comoounds affected
develocment more than survival. Some,
however, drastically reduced larval
growth. The authors ooint out the
necessity of evaluating the effects ot
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 at
a*(coritin-
uou.3 aer-
ation, sea-
water, and
daljy
5990
Approximate toxlcltles of Hawdesley-Th
numerous pesticides commonly used in o«as(1971)
Britain were summarized. An excellent AMIC-1056
brief, general discussion of Toxlclty
testing is also present.
One hundred-forty surface active Portmann, et
agents, solvent emulslflers, pesticides, al (1971),
polychlorlnated blohenyls, pure AMIC-7701
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
-------
>
ro
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Coaoound ipganlsi" Study Location Pp» or Noted Comments
Dercol Crangon BSA —
cranqon
Oeraol Pandalus BSA --
•ontaqul
0« D« Tan* ?5 Rasbora BCFA —
het»ro»orpha and
BSA
0* Oe Tan* (liquid) Rasbora BCFA —
heferomopoha and
BSA
solution
renewal)
100-330 (T2) as(contin-
uoas aer-
ation, sea-
wator, and
daily
solution
renewal }
100-330 (TZ) a»( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal }
0.11 (T?) *»,c,e,f,
hard (HW)
or soft
(SU) syn-
thetic
dilution
water, or
aeavater
for sorae
species
0.11
-------
0* 0« Tane (liquid)
Rasbora
heteromorpha
BCF4
and
BSA
0* Oc Tane (oast*)
Rasbora
heteromorpha
BCFA
and
BSA
U>
0« Of Tane
(••ttable)
Rasbora
heteromorpha
BCFA
and
BSA
Oe De Tane
(nettable)
Pasbora
heteromorpha
BCFA
and
RSA
0.02
a*,e,e,f ,
hard (HH>
or soft
(SH)
synthetic
dilution
Hater, or
seawater
(or some
species
a«,c,e,f.
hard (HW)
or soft
(SW) syn-
thetic
dilution
water, or
aeawater
for some
apecles
3»,e,p,f ,
hard (HH)
or soft
(SW)
synthetic
dilution
water, or
seawater
for some
species
a*.c.e,f ,
hard
(HH)or
soft (SW)
synthetic
dilution
water, or
seanater
for some
species
same as above
01 acetone alcohol
Phormldlun
amblquun
0.5-10.0 (NTE) --
Alabaster,
(1959) ,
AHIC-51,75
same as above
Alabaster,
(19*9),AMIC-
S<.25
same as above
A Iabaster,
(1089),
AMIC-51.25
same as above
Alabaster,
(1969), AMIC-
5W25
Of 7
-------
ConDound
Field Field
Organism Study Location
Toxjclty.
Active
Ingredient,
Ppm
Experimental
Variables,
Control Ied
or Noted
Comments
Reference
OJarlnon
>
I
Dlca«ba
Olca'ba
Basbora
heteromoroha
BCFA
and
nsa
(Tl)
wolffla
papullfera
Gammarus
fasclatus
BS»
100 (K)
greater than
100.0 (TZ)
hard (HW)
or soft
(SW) syn-
thetic
water, or
soawater
for some
speciea
Kuntor'a
medium
diluted
Paleo»onfes BSA
Kadlakensls
greater than
100.0 (T2>
more toxic thar CuSOl*. No wetting agents
were found to be Inhibitory at the
concentrations Investigated (O.OS and
0.005 pom). Also reported are factors
affecting growth of algae In canals to
determine whether therp were leads to
controlling alqae by environmental
management. No practical environmental
means Mere found.
One hundred sixty-four
pesticides, wetting aqpnts, and
miscellaneous waTor oollutants showed a
wlrte ranoe of toxlclty spanning 1? orders
of magnitude. Knowing the foxlclty and
formulation did not result In easy
predictability of the toxlclfy 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.
All compounds were harmful to
duckweed to some degree. Decreased
populations were noted at non-lethal
concentrations and some compounds
(Malathlon and 2,lj.-D) caused toratogenlo
effects at concentrations as low as 1 ppra.
Of the aquatic weed herbicides
evaluated, Olclone was the most toxic,
Daohnla 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. All ol the anlaals
represent Important food chain links.
same as above
A 1 abas t er
Worthier, et
•1 (1971),
AKIC-3233
Sanders
119791,»«IC-
Sanders
Olcauba
Olca'be
As*11 us BSA
brevlcaudus
Orconectes 8SA
nals
greater than
100.0 (T3)
greater than
100.0 (T?)
sane as above
saoe as above
Sanders
(1970>,»MIC-
(.53
Sanders
11970), »MIC-
I.S3
Daohnln aagna 8SA —
greater than
as above
Sanders
-------
100.0
(1970),AMIC-
ES
Olcamba
Cvnrldopsls
vldua
BSA —
greater than
100.0 (T2)
same as above
Sanders
(1970),A>ac-
3.3«, (T2)
a»
same as above Sanders
(1970),
AMIC-i.53
The effect of 52 pesticides on Davis, et al
embryonic development of clams and
oysters Has reported. Synerqistlc 11969),AHIC-
effects with solvents were also reported. 5990
Host of the compounds affected
dpvelocment 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
orqanlsm and note the possibility of
selecting chemicals tor pest control that
Mould not have serious effect on
shell fish.
Olcapthon
DlchlobenlI
Olchlobenll
Mercenarla
mercenarla
(Iarvao)
Rasbora
heteromorpha
8CFA
and
BSA
Cat IIbactls
sp. (nymph,
8-12 mm)
BSA
5.7i» (T12) -- same as above Davis, et al
(1963),4HIC-
599D
5.7 (T2) a',c,e,f. One hundred sixty-four Alabaster
hard (HW) bestlcldes, wetting agents, and (1969),
or miscellaneous water pollutants showed a AHIC-5',25
SOFT(SW) wide range of toxicity spanning 12 orders
synthetic af magnitude* Knowing the toxicity and
dilution percentage of all components of a
water, or formulation did not result in easy
seawater predictability of the toxicity of a
for some mixture of materials. Sometimes
species pesticides were most toxic In hard water
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
10.3 (T*) a«,b*,c,f, The toxicity of herbicides Olquat Wilson, et
1,1, and and Olchlobenll to aquatic invertebrates al (1969),
silica,
calcium,
magnesium, soecles. Dlouat was oulte toxic to H.
and fish was determined in aquaria
containing substrates natural To each
AMIC-5U52
azeteca but not as toxic to otner
sodium,
potassium, organisms. Olchlobenll was less toxic to
H. azetecus but considerably more toxic
-------
>
Toxlclty, Experimental
Active Variables,
Field Field Inqredlent, Controlled
Co»oound Organism Study Location Pom or Noted Comments
blcarbon- to the remaining organism than Olquat
ate, Hurt lessened the toxlclty of both, but
carbonate, more so for Olquat. nichlobenll had a
sulfate, sublethal narcotizing effect on the
Iron, organisms that resulted In
dissolved Immobilization. It was concluded that
solids, both herbicides could adversely aTfect
conduc- certain fish food organisms.
tance
Hchlobanll Calllbnetls BSA — 7.1. (SB".) a«,b», c, T, same as abova
so. (nymph, i,l, ajid
8-1? mm) silica,
calcium,
magnesium.
sodium,
potassium,
bicarbon-
ate.
carbonate,
aulfate,
iron,
dissolved
solids,
conduc-
tance
Hchlobenli Leoonls BSA — l
-------
OlchlobenlI
Libel lu
(naiad.
turn)
la SP- Bs*
qreater thanlOO a»,b»,c,f,
,T !-!,) 1'J}..
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
iron,
dissolved
solids,
conduc-
tance
sane as above
Wilson, et
at (1959),
OlcMobenl I
Libellula sp. BSA
(naiad,. 16-?"t
mm)
greater thanlOfl •*•
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate ,
sulfate,
iron,
dissolved
solids,
conduc-
tance
same as above
Hllson, et
at (1969).
AMIC-5«i52
OleMobenl 1
SD. (larva,
15-20 mm)
BSA
13.0
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
sane as above
Wilson, et
al (1969).
-------
Compound
Orqanlsn
Field Fleld
Study Location
Toxlclty,
Active
Ingredient,
Pom
Experimental
Varlahlest
Control Ied
or Noted
Comments
carbonate,
sulfate.
Iron,
dissolved
solids,
conduc-
tance
DlchlobenlI
Llmneohllus BSA
so. (larva,
1S-?0 mm)
12.00 (SB<.)
a«,b»,c,f,
1,1, and
silica,
calcium,
magnesium,
sodlun,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
Iron,
dissolved
solids,
conduc-
tance
sane as above
Wilson, et
at (1961),
AMIC-51.5?
DlchlobenlI
Mlcrooterus
salnoldes
BSA
12.5 (Tit)
a*,b»,c,r,
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
snlfate,
iron,
dissolved
solids,
conduc-
tance
same as above
Wilson, et
al (1969),
AMIC-S
-------
OlehlobentI
Hyaletlit
az«teca
(adult, l»-S
BSA
8.5 (Tl>)
>
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
iron,
dissolved
solids,
conduc-
tance
same as above
Hllson, et
al (196=1),
OlchlobeniI
Hyalella
azteea
(adult, U-8
BSA
3.8 (SB".)
OlchlobeniI
Cnallaqma sp. BSA
(naiad, l6-2».
•n)
12.3 (SB1)
a«,b«,c,f,
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
Iron,
dissolved
solids,
conduc-
tance
a*,o»,c,f,
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
sane as above
Wilson, et
al(1969),
AMlC-51,53
same as above
Wilson, et
al (1969),
-------
I
H
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Coooound Organism Study Location Ppra or Noted Comments
carboiiate,
snlfate.
Iron,
dissolved
solids,
conduc-
tance
Dlchlobenll Enallaqma sp. BSA — 20.1 (T
3«..0 (TZ)
2.0 (T2)
Of the aquatic weed herbicides
evaluated, Dlclone Has the most toxic,
Oaohnla Has generally the most sensitive
organism. All of the Crustacea Here
affected by much loner concentration
levels of herbicides than Indicated by
the TL sub 50 values. All of the animals
represent Important food chain links.
same as above
Sanders
same as above
same as above
Sanders
(1970),
AMIC-'.SJ
Sanders
AMIC-i.53
Sanders
AMIC-l.53
-------
DlchlobenlI
Dlchtobenl I
DlchlobenlI
OlcMone
OlcMone
Olchlone
Dlchlone
Oichlone
Olchlone
Oaohnla nagna BSA
Cyprldopsls BSA
vldua
Leoomls BSA
macrochlrus
Salmo
galrdnerl
BCFA
and
BSA
Gammarus
fasciatus
BSA
Paleomontes BSA
kadlakensls
Asellus BSA
brevlcaudus
Orconectes BSA
nals
Oaphnla magna BSA
10.0 (T2>
7.8 (T2)
20.0 (T21
0.09 (T2)
a*,c,e,f,
hard IHW;
or soft
(SWJ syn-
thetic
dilution
water, or
seawator
for sone
apecies
0.2U (T2), 0.10 a*
0.1.5 (T2)
0.20 (T2)
3.2 (T2)
0.025 1T2)
a»
a»
same as above
sane as above
same as above
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous Hater pollutants showed a
Hide range of toxiclty spanning 12 orders
of magnitude. Knowing the toxiclty and
percentage of all components of a
formulation did not result in easy
predictability of the toxiclty of a
mixture of materials. Sometimes
pesticides were most toxic in hard water
and sometimes the opoosite was true.
Testing the actual material as sold was
found to be essential.
Of the aquatic weed herbicides
evaluated, Olclone was the most toxic,
Oaphnla was qenerally the most sensitive
organism. All 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 Important food chain links.
same as above
Sanders
(1970) ,
AMIC-1,53
Sanders
(1970),
A1IC-ii53
Sanders
(1970),
AMIC-25
same as above
same as above
same as above
Sanders
(1970),
AHIC-
-------
>
Compound
01 en lone
Dlchlorfenthion
Olchlorfenthlon
Olch(orf«nlhlon
Olchloropnen (Na
•alt)
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Pom or Noted Comments
vldua
Lepomls BSA —
•acrochlrus
Pasbora BCFA —
heteroworpha and
BSA
Rasbora BCFA —
heteroiorpha and
BSA
Pasbora BCFA —
heteroBorpha and
BSA
Sal BO BCFA —
galrdnerl and
BSA
0.12 (T2) a*
1.9 (T2) a»,c,e,f.
hard (HW)
or soft
(SW) syn-
tbetlo
dilution
water, or
aeawater
for : some
species
2.1 (Tl) a*,c,e,f,
hard (HW)
or soft
(SW) syn-
thetic
water, or
aeawater
for aone
•peolea
0.73 (T2) a«,c,e,f,
hard (HW)
or soft
(SW) syn-
thetic
dilution
water, or
•eawater
for' some
0.22 (TZ) a'.c.e.f.
hard
(HH)or
same as above
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wide range of toxlclty scanning 1? orders
of magnitude. Knowing the toxlclty and
percentage of all cotioonents 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 sometlnes the opposite was true.
Testing the actual material as sold was
found to be essential.
sane as above
sane as above
saac as above
Reference
(1970) ,
4MIC-I.S3
Sanders
( 1970 ) *
AM.IC-1.S3
Alabaster
(1969) ,
A HI C— 5*»25
Alabaster
(1969),
AHIC-SU25
Alabaster
(19691,
A«C-5<»2S
Alabaster
(1969),
ANIC-SdZS
-------
Dlchlorophen (Na
salt!
Rasbora
heteromoroha
BCFA
and
BSA
0.15 (T2)
soft (SW)
synthetic
dilution
Hater, or
seawater
lor some
species
a»,o,e,r,
hard (HW)
or soft
ISW) syn-
thetic
water, or
sea water
for some
•pecleg
same as above
Alabaster
(1989),AMIC-
5<.2"5
Olchlorvos
Rasbora
heteromorpha
BCFA
and
BSA
6.S (T2>
Oletdrln (15 percent Rasbora
H.O.I heteromorpha
BCFA
and
BSA
1.0 (TZ)
DJeldrln
Oleldrln
Fish (not
specified!
Poecllla
latlplnna
BCFA —
a*,c,e,t,
hard (HM)
or
SOFT(SH)
syn tht>t 1C
dilution
Hater* or
seattater
for some
species
a>,c,e.f,
hardtHH)
or soft
(SHI
synthetic
dilution
Hater, or
seaHater
for some
species
qreater than
0.001-0.01 (K)
0.003 (partial a*
One hundred sixty-four
pesticides, Hottlnq agents, and
miscellaneous Hater pollutants shooed a
nlrte range of toxlclty scanning 1? orders
of magnitude* KnoNlnq tho toxlclty and
percentage of alI 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 Hater
and sorretimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
same as above
Alabaster
(1969),
AHIC-51.25
Approximate toxlcltles of
numerous Pesticides commonly used In
Britain Here summarized. An excellent
brief, general discussion of toxlclty
testing Is also present.
Studies Here conducted Hlth fish
neighing 2-S
-------
Covoound
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient,
Pom
Experimental
Variables,
Control led
or Noted Comments Reference
Oleldrln
Poecl I la
latlolnna
BCFA —
0.006 (70
percent KJ)
temperature oT 27 Plus or minus 1 C. The AMIC-13SJ
purpose of the tests was to determine the
etTect of dleldrln on serum qlutamlc
oxaloacetlc transamInenase activity which
Increased at all exposures. However,
little correlation Has found between
enzyme activity and total mortality.
same as above
Lane, etal
(1970),
AMIC-1283
Oleldrln
01«I dr I n
PoeclI la
latIplnn*
BCFA —
0.01Z (K3)
White sucker FRL Misc. states 0.01-0.35
same as above
The Bureau of Sport Fisheries
continued Its fl«;h monitoring program by
collecting 11)7 composite fish samples
from 50 nationwide monitoring stations
during the fall of 1969. Fish were
analyzed for residues of 11
orqanochlorIne Insecticides, Holds, and
L ane, e t a I
(19701.AMIC-
128?
Hendersor»»et
al (1171),
AMIC-H07
Dleldrln
Oleldrln
Oleldrln
Oleldrln
Oleldrln
Yellow perch FRL Misc. states 0.02-0.20
residue (SB)
Chain FRL Misc. states 0.02 residue
pickerel (SB)
White catfish FRL Misc. states 0.01-0.50
residue (SB)
White perch FRL Misc. states 0.06-0.56
residue (SB)
Goldfish FRL Misc. states 0.071),
ANIC-U07
Henderson,et
al (1971),
AMIC-li.07
Henderson,
et al(1971),
AMIC-11,07
Oleldrln
PuHDKlnseed FRL Misc. states 0.05 residue
sane as above
Henderson,
-------
(SB)
etal (1971),
AMIC-l
-------
Comoound
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Pom or Noted
Comments
Reference
Oleldrln
residue (SB)
Lake FRL Misc. states 0.03 residue
Hhlteflsh (SB)
same as above
al
AMIC-11.07
Henderson,et
al 11971),
AMIC-1U07
Oleldrtn
Oleldrln
Lake trout FRL Misc. states 0.0? residue
(SB)
White craoole FRL Misc. states 0.02-0.27
residue (SB)
same as above
same as above
Henderson,
elal (1971),
Henderson,
et al
BMIC-11.07
0 1 e 1 dr 1 n
Dletdrln
Blgmouth FRL Misc. states 0.Oi.-0.lt?
buffalo residue (SB)
Small mouth FRL Misc. states 0.12 residue
buf f alo
(SB)
same as above
same as above
Henderson,
c t al
(1971),
AMIC-H07
Henderson,*t
•I (1971),
AMIC-11.07
Oicldrln
01 el dr In
0 1 e 1 dr 1 n
Olcldrln
Oleldrln
Dleldrin
Flathead FRL Misc. states 0.03 residue
catfish (SB)
Goldeye FRL Misc. states 0.01-0.08
residue (SB)
Walleye FRL Misc. states 0.01-0.03
residue (SB)
Sauger FRL Hlsc. states 0.01 residue
(SB)
Flannelmouth F9L Misc. states 0.01 residue
sucKer (SB)
Freshwater FRL Misc. states O.Olf. residua
drum (SB;
same as above
same as above
same as above
same as above
same as above
aamo as above
Henderson,et
al (1971),
AMir-li.07
Henderson,et
al (1971),
AMIC-1<.07
Henderson,«t
al (1971),
AMIC-li.07
Henderson,
et al(1971),
AMIC-li.07
Henderson,
et al
(1971),
AMIC-HOT
Henderson, et
al (1971),
AKIC-1407
-------
Oleldrln
Black
bulIhead
FRL Misc. states 0.01-0.03
residue (SB)
same as above
Henderson, et
a I (1971),
t
§
Oleldrln
Dleldrln
Oleldrln
01«1e)rln
Oleldrln
Hhlte bass FRL Misc. states O.OZ residue
(SB)
Black craonle FRL Misc. states 0.02-0.36
residue (SB)
Largescale FRL Misc. states 0.01-0.09
sucker residue (SB)
Smallmouth FRL Misc. states 0.03-0.04
bass residue (SB)
Northern FRL Misc. states 0.01-0.03
souaHflsh residue (SB)
same as above
same as above
same as above
same as above
same as above
Henderson,
et al (1971),
AHic-i
residue (SB)
same as above
same as above
Henderson,et
al (1971),
«MIC-l
-------
Co'Dound
Dloldrln
Dieldrin
Dioldrln
^ Dieldrin
H
00 Dieldrin
Dieldrin
Dieldrin
Oleldrln
Dieldrin
Field Field
Organism Study Location
Icttilurua FrtLO Iowa
punctatus
Ictiobua FHLO Iowa
cyprlnellus
Cyprinua FRLO Iowa
carpio
Hlcropterus FRLO Iowa
sal mo Ides
Carplodes sp FRLO Iowa
Pomoxis FHLO Iowa
nlgroraaculatus
Poraoxls FRLO Iowa
annularl s
Stlzostedlon FRLO Iowa
vl treum
Esox luclus FRLO TOMS
Toxlcity,
Active
Ingred lent,
Ppm
0,034-1.6
( accumula tlon,
SB)
0. 028-0. BU.
(accumulation,
SB)
0.015-0.56
(accumulation,
SB)
0.11-0.08
(accumulation,
SB)
0.313
(accumulation,
SB)
0.012
(accumulation,
SB)
o.o59
(accumulation,
S3)
0.01-0.06
(accumul atlon,
SB)
0.05
(accumul atlon,
SB)
Experimental
Variables,
Control 1 ed
or Noted Comments
iXlible flesh of fish collected from
rivers, lakes, ponds, and reservoirs
waa analyzed. Fish taken in areas
receiving agricultural runoff showed
highest accumulation, especially in
bottom feeding fish.
Same as above
same as above
some as above
same as above
same as above
same as above
— same as above
same as above
Ret erence
Morris, et
al (197D.
AKIC-1U52
Morris, et
al (1971),
AMC-lli.52
Korrls, et
»1 (1971),
AKIC-1452
Morris, et
al U971/,
Morris ot
al (1971),
AKIC-11).52
Korrls, et
al i 1971).
Morris, et
al (1971;.
AKIC-1U52
Morris, et al
(1971) ,
Morris, et
al
(1971), A«IC-
K.52
-------
Dleldrln
Dleldrln
Dieldrln
Dieldrin
Ictalarus FRLO Iowa
. melas
Lepomls FRLO Iowa
macrochirua
Esox luciU3 FRLO Iowa
Roccus
chiysopa
FRLO Iowa
0.098
(accumulation,
513)
0.01lj.-0.03k
(accumulation,
SB)
0.05
(accumulation,
SB)
0.091-0.175
(accumulation,
SB)
same as above
same as above
same as above
same as above
Morris, et
al (1971),
AM1C-1452
Morris, et
al (1971),
AHZC-1US2
Korris, et
al (1971).
AHIC-11^52
Morris, et
al (1971),
1
Oleldrln
Oiefdrln
Oleldrln
Dleldrln
Oleldrln
Anacystls I
nldulans
Agneneltum L
quadrup-
llcatum
Leptodlus L
fIorldanus
(larvae)
Panopenus
nerbstll
(larvae)
Llmnephllus
rhombIcus
(larvael
FS
0.5-1.0 (growth a»,c*«r
Inhibited) SH
0.5-1.0 (growth a»,c*,r
Inhibited) SM
5-10 ppb(K) —
5-10 opb (K)
Knights 0.002(Hhole
Creek, Dun body residue)
County,
Misc.
Metabolic products of Aldrln, Batterton,
Dleldrln, and Endrln can be as toxic as etal (1971),
the oarent comooundSi as shonn by 00 AMIC-l
-------
Conoound
Field Field
Organise Study Location
Toxlclty,
Active
Ingredlentt
Ppm
Experimental
Variables,
Control 1 ed
or Noted Comments
Reference
01«IdrIn
Stalls so. FS
(Iarvae)
Knights
Creek, Oun
Count y,
Misc.
0.013
(Mho Iebody
residue)
0-0.005 pom dleldrln. Fndrln residues of
0.011-0.0?5 pom and 0.003-0.006 ppm
dleldrln Here found In debris samples.
Despite limited control data, residue
analyses Indicated that contamination of
the environment studied Mas limited.
same as above
Moubry, et
al (1168) ,
AMIC-37?3
>
o
Dleldrin
Oleldrln
Oleldrln
Oleldrln
Oleldrln
Oleldrln
Oleldrln
Oleldrln
Gamvarus SD. FS
Salvellnus FS
fontlnalIs
Semotllus FS
atronaculatus
Cottus balrdl FS
Rhinlchthys FS
atratulus
SalvelInus FS
fontlnalIs
Senotilus FS
•troBaeulatus
Cottus balrdl FS
Knights
Creek, Dun
Count y,
Misc.
Knights
Creek, Dun
County,Misc.
Knights
Creek, Oun
County,
Misc.
Knights
Creek, Oun
County,
Misc.
Knights
Creek, Oun
County,Misc.
Knights
Creek, Dun
County,Misc.
Knlqhts
Creek, Oun
County,
Misc.
Knights
Creek, Oun
0.005-0.013
(nholebody
res 1 due)
0. 008-0. 01<»
(whole body
residua)
0.006-0.013
(whole body
residue)
0.007-0.017
(whole body
residue)
0 (Mho Iebody
residue)
0.18-O.Z6(fat
residue)
0.17-0.3". (fat
residue)
0.3-0.7
(fat
residue)
same as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
Moubry, et
al (10611,
AMic-371;:*
Moubry, et
al (lifts) ,
AMIC-3753
Moubry, et
al
<19.AMIC-
37-J1
Houbry, et
al (116M ,
AHIC-375J
Houbry, et
a I (196M,
AMIC-J753
Moubry, et
al (196S),
AMIC-3753
Moubry, et
al (1968),
AMIC-3753
Moubry, et
al (1968),
-------
Oleldrin
Oleldrln
r
8
Dleldrln
Dleldrln
01 eldrin
Rhlnlchthys
atrafulus
Leoouls
cyan*11us
County,
Hlsc.
FS Knights 0 (fat
Creeh, Dun residua)
County,Wise.
I —
Leoouls
cyan*11us
Lepomls
cyanelIus
Falco
peregrlnus
(eggs)
0.006 (K9I
5.7 (blood
residue)
10.3 (brain
residue)
Western
O.S.,
Pacific
, Ocean,
Panama,
Mexico, and
Antarctic
0.11 (residue) —
sane as above
The blood and brains of green
sunflsh that died due to exposure to
Dleldrln were analyzed for this chenlcal.
Surviving fish had less Oleldrln In
blood and brains than dead fish.
Severity of poisoning symptoms also
correlated Hlth Dleldrln concentration.
Extraction efficiency from blood and
brains Has quite good (92-95 percent).
same as above
•MIC-3753
Houbry, et
at (1968),
»MIC-3753
Hogan, et al
(1971),
AHIC-382*
Hogan, et al
(1971),*HIC-
sane as above
Hogan, et al
(1971),AHIC-
3821.
peregrine falcons, falcon nrey, ^iseetrough,
and other predator soecles were collected et al
widely and analyzed for HOT, OOF, PCR, (1968).
and a few other pesticides to a lesser »HIC-38
-------
ro
Conoound Organism
Ol«rorlr> Falco
peregr Inus
( 1 tma t ure)
Oleldrln Falco
rereqr Inus
(adul t)
Dleldrln Falco
oeregrlnus
(adul t)
Field Field
Study Locat Ion
F Western
U.S.,
Pacl f Ic
Ocean,
Panama,
Hex 1 co , and
An tar c t Ic
F Western
U.S.,
Paclf Ic
Ocpan,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Paclf Ic
Panama,
Mexico, and
Antarctic
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
0.07-1.6 (fat — same as above
residue)
0.31-3.7 (flesh -- same as above
residue)
0. ,
AMIC-Jf'i't
Rlsebrouqh,
et al
(1968) ,
AMI C— 3 0**^
Olcldrln
01 eldr In
01«ldrln
Dleldrln
Endomychura
cravepl
(eqqs)
Pelecanus
occidental Is
(eqgs)
Sula
leucoqaster
(eqqs)
Fa I co
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico,and
Antarctic
Western
U.S.,
Paclf Ic
Ocpan,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
0.08 (residue)
same as above
0.06-0.16
(residue)
O.OU-0.18
(residue)
0.0<»-O.U
same as above
sane as above
Rlsebrouqh,
et al
(196M ,
sane as above
Rlsebrouqh,
et al
(1968) ,
AMIC-38Mt
P i sehrouqh,
et al
(llfS) ,
AMIC-381,1.
"Issbrough,
-------
peregrinus
(immature)
Oleldrln
> Oleldrln
*•** Oleldrln
Oleldrln
U.S.,
Pacific
Ocean,
Panama,Hexlc
o, and
Antarctic
(flesh
residue)
Chlamydotheca BSCH —
arcuata and
A
Chlamydotheca 3SCH —
arcuata and
A
Ulothrlx so. BSCH —
Copeoods
(Cycl ops
bicuspidus,
Cyclops
varleans,
Cycloos
vernal Is,
Eucycloos
agllis,
Kacrocyelops
albldus.
Orthocyclops
modestus)
FL State
and College,
BSA Hiss.
0.00001-0.001
(1700-2600 ppb
residue**!! wk)
0.02"»5 (Tl)
0.00001-0.001
(1.9-126 ppb
residue 33-<»8
wk)
0.35 (83
oercentKZ)
The organisms were exposed to
0.01 and 0.1 cob of the toxicants for 35
weeks after Hhlch time the amounts added
each week were Increased ten-fold over
the Initial amounts. Ulothrlx occurred
spontaneously In the test tanks. The
results shoH that chronic accumulations
In ChIamyriotheca exceeded levels which
were toxic In acute tests. Residues in
Chiamyflotheca ranged from 12,000 to
260,000 times greater than the
theoretical concentrations In the watert
those In Ulothrlx were ?3«;-3,000 times
exposure levels.
same as above
same as above
et al
(1968),AMIC-
381.1.
Kawatskl, et
al (1971),
AMIC-5506
Kawatskl, et
al (1<»71),
AMIC-S506
Kawatskl, et
al (1971),
The response of
pesticide-resistant aquatic organisms to
various pesticides was compared to the
response of non-resistant species.
Pesticide-resistant species were
collected at Belzonl and non-resistant
species at State College. Copepods,
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 higher trophic levels.
Naavl, et al•
(1969),
AMIC-S979
-------
>
ro
Compound
Oleldrln
Oleldrln
0 1 e 1 dr 1 n
Oleldrln
Oleldrln
Oleldrln
Organism
Tublfex
tubltex
Physa gyrlna
Physa gyrlna
Copepo>1s
(Cycl ocs
bleusoldus.
Cyr 1 ons
var leans.
Cyc 1 ops
verna II*;,
Eucycl oos
agl 1 Is.
Kacrocj xops
albMur;,
Or t hocyc 1 ops
modestus)
Coooports
(Cyclops
blcuspldus,
Cyc 1 oos
var Ic^ns,
Cyc lops
vernal Is,
Eucycl oos
aql 1 Is,
Macro cy clops
Orthocycl ops
•odestus)
Crassostrea
vlrglnlca
Toxlclty,
Active
Field Field Ingredient,
Study Location Ppm
FL Belzonl, 6.0 (NTE)
and Miss.
BSA
FL State 0.50 (K3>
and College,
BSA Hiss.
FL Belzonl, 0.50 (K3>
and Miss.
BSA
FL Belzonl, 0.35 (20
and Miss percent K2)
BSA
FL Belzonl, O.UO (39
and Miss percent K2>
BSA
L — 0.6<* (T2)
Exper 1 men ta 1
Variables,
Control led
or Noted Comments Reference •
same as above Naavl, etal
( inf>9) ,
•MIC-5979
same as above Naavl, etal
( 1959) ,
AMTC-";979
same as above Naavl, et
Bl(l9ft9),
AHIC-5979
sane as above Naavl, et
al (1969) .
AMIC-S979
same as above Naqvi, et
al (1969),
AMIC-5979
The effect of 52 pesticides on Davis, «t al
embryonic development of clams and
oysters Has reported. Synerglstlc
effects Hlth solvents Mere also reported.
Most of the compounds affected
development more than survival. Some,
however, drastically reduced larval
grOMth. The authors point out the
necessity of evaluating the effects of
pesticides on all life stages of an
organls* and note the possibility of
(1969J.AMIC-
5990
-------
Oleldrln
Oleldrln
Dleldrln
Dleldrln
Dleldrin
Dieldrln
Dleldrln
Oleldrln
Crassostrea I
vlrqinlca
(larvae)
Gambusla
affinis
(female, i».3
cm. 1.9 g)
Lehlstes
retIculatus
(male, 1.8
cm, 0.? g)
Tilaola
mossamblca
(3.<> cm, 1.3
9)
Kuhlla
sandvlcensls
^<^.^ cm, 1.5
9>
Stolephorus BSA
purpurea (3.6
cm, 0.<> q)
BSA
greater than
10.0 (Tl
0.031 (T
selecting chemicals for pest control that
would not have serious effect on
shell fish.
same as above
Davis, etal
(1969) ,
a,c,d,e,
e,f,l,
(Honolulu
tap
water)
a,c,dr
e.f.l,
(Honolulu,
tap
water;
a,c,d,
e,f,i,
(Honolulu
tap
water)
a,c,d,e,f,
l.salt
water
a,c,d,e,f,
1, salt
water
a* (contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
The five fish species are
commonly found In streams and estuaries
In semi-tropical areas. G. afflnls was
the most tolerant. Varied sensitivity to
the toxicants were found. K.
sandvlcensls was the most sensitive fish
studied. The standard method procedure
was followed.
same as above
a«(contin-
uous aer-
ation, sea-
water, and
daily
same as above
same as above
same as above
One hundred-forty surface active
agents, solvent emutslflers, pesticides,
polychlorlnated blohenyls. Pure
Inorqanlc, and organic chemicals were
evaluated against as many as ten itarlne
organisms. The authors noted that nost
published data of this type deal with
toxlclty of chemicals to freshwater
organ Isms.
same as above
Nunoqawa, et
at (19701,
AHIC-6S67
Nunogawa, et
al (1970),
AHIC-6567
Nunoaawa* et
al (1970),
AMIC-6567
Nunoqawa, et
al (1970),
A1IC-6567
Nunogawa, et
al (1970),
AMIC-6567
Portirann, et
al (197D,
AHIC-7701
Portnann, et
al (1971),
AMIC-7701
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Organism Study Location Ppm
Exper 1 men tal
Variables,
Control 1 ed
or Noted Comments
solution
ronewal )
Reference
OlcldrIn
Cardlum edule BSA
greater than 10 a*(contin-
uouo aer-
ation, sea-
wator, and
daily
solution
ronewal)
same as above
Portmann, et
al (1971),
AHIC-7701
01«I dr 1 n
I
ro
Crangon
cranqon
BSA
0.01-0.03 (T?)
a*(contin-
uous aer-
ation, sea-
wator, and
daily
solution
renewal)
same as above
Portwann, et
al (19711,
AMIC-7701
Oleldrln
Freshwater
dru*
FL
Oleldrln
Alexlfe
FL
Orsat Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.0(« (whole
body residue!
Great Lakes 0.05-0.97
(Ontario, (whole body
Huron, residue)
Erie,
Superior,
Michigan)
Fish from Lake Michigan contained Pelnert
2 to 7 times more DDT (and DDT analogs) (1970),AHIC-
and Dieldrln residues than fish from the 196
other Great Lakes. Fish from Lake
Suoerior 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 xith less
persistent materials.
same as above
Relnert
(1970),A1IC-
196
Dl«ldrln
American
snelt
FL
Great Lakes
(Ontario,
O.oz-o.io
(whole body
same as above
Relnert
(1970),AHIC-
-------
Huron,
Erie,
Superior,
Michigan)
residue)
196
DIeldrIn
Bloater
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.03-1.07
(whole body
residue)
same as above
Relnert
(19701,AMIC-
196
DIeldrIn
Brown
bul(head
FL
ro
5
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.00 (wholebody
residue)
sane as above
Relnert
(1970),«MIC-
196
Oleldrln
Channel FL Great Lakea 0.07 (whole
catfish (Ontario, body residue)
Huron,
Erie,
Superior.
Michigan)
same as above
Relnert
(1970),4MIC-
196
Oleldrln
Coho salmon
(flesh)
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
O.OKwhole body
residue)
same as above
Reinert
(1970),Ahic-
196
Oleldrln
Coho salmon
(eqqs)
FL Great Lakea 0.0<» (whole
(Ontario, body residue)
same as above
Reinert
(1970),4
196
-------
Field Field
CoBoound Organism Study Location
Huron,
Erie,
Superior.
Michigan)
Toxlcl ty.
Active
Ingredient,
Pom
Exoer 1 menta 1
Variables,
Control 1 ed
or Noted Comments Reference
Oieldrln
Gizzard shad FL
Great Lakes o.0<»-o.09
(Ontario, (whole body
Huron, residue)
Erlo,
Superior,
Michigan)
sane as above
Reinert
(1970),
196
Oieldrln
Klyl
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0•28 (HhoIe
body residue)
same as above
Reinert
(1970).AMIC-
196
OI«ldrin
LaKe herring FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.02-0.07
(Hhole body
residue)
same as above
Reinert
(19/0),AMIC-
196
Oleldrln
LaKe trout
FL
Great Lakes
(Ontario,
Huron,
Brie,
Superior,
Michigan)
0.05-1.13
(Hhole body
residue)
same as above
Re 1nert
(1970),AHIC-
196
-------
Dletdrln
LaKe
whifetish
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
O.D3-0.<»7
(whole body
residue)
•same as above
Relnert
(1970),ANIC-
196
Dleldrln
Rock bass
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.03 (whole
body residue)
sane as above
Relnert
(1970),AMIC-
196
Oleldrln
Round
whiterIsh
FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.03 (whole
body residue)
sane as above
Relnert
(1970),AMIC-
196
Oleldrln
Sea lamprey FL Great Lakes 0-03 (whole
(Ontario, body residue)
Huron,
Brie,
Superior,
Michigan)
sane as above
Reinert
(1970),AMIC-
196
Oleldrln
SI imy scutoln FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.01 (whole
body residue)
same as above
Relnert
(1970),
196
Oleldrln
Nlne-splned
stickleback
FL
Great Lakes
(Ontario,
0.02
-------
Compound
Field Field
Organism Study Location
Active
Ingredient,
Ppm
Variables,
Control 1 ed
or Noted Comments
Ref erence
Huron,
Brie,
Superior.
Michigan)
196
Oleldrln
ro
5
01«ldrln
Wai lay* FL Great Lakes 0.08-0.13
(Ontario, (whole body
Huron, residue)
Erie,
Superior,
Michigan)
—WhTt« bass FL Great Lakes 0.0<»-0.10
(Ontario, (whole body
Huron, residue)
Erie,
Superior,
Michigan)
same as above
Relnert
(1970),AMIC-
196
sane as above
Relnert
(1970),AMIC-
196
Dleldrln
White perch FL
Great Lakes
(Ontario,
Huron,
Erie,
Superior,
Michigan)
0.10 (dhole
body residue)
same as above
Relnert
(1970),4MIC-
196
Dl«ldrln
White sucher FL
Great Lakes
(Ontario,
Huron,
Brie,
Superior,
Michigan)
0.02 (whole
body residue)
same as above
Relnert
(1970),AMtC-
196
-------
Oleldrln
Ye I low perch FL
Dleldrln
Wolffla
ptpulifara
Olethyt-OL-tartarate Plmephales
promel as
Olethyl fu«arafe
Olethyl lunarate
Olethyl aateate
Olethyl succlnate
Olfolatan
Olfolatan
Plmephales
promt-Ins
Plmephales
promelas
Plmephales
promelas
Plmephates
promelas
Michigan)
Great Lakes
(Lake
Ontario,
LakeHuron,
LaKeErle,
Lake
Superior,
Lake
Michigan)
D. 03-0.07
(Hhole body
residue)
BSA —
100 (K)
650.0 (TJ>)
Hunter'3
medium
diluted
1:5
a'.d.e.o,
and Fe
BSA
8CFA
BSA
BSA
2.8
18.0 (Ti»)
a*,d,e,o,
and Fe
a*,d,e,o,
and Fe
a*,d»e«o,
and Fe
a*,d,e,o,
and Fe
Brachydanlo L
rerlo
(larvae)
1.0 (T 30 nln) —
Rasbora BCFA
heteromorpha and
BSA
0.032 25
Hide range of toxlcity spanning 12 orders
of magnitude. Knowing the toxlcity and
percentage of all components of a
formulation did not result in easy
-------
r
K>
(o
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organise Study Location Ppn or Noted Comments
seawater
for some
species
Olfolatsn Rasbora BCFA — 0.017
-------
Olaethoat*
Salmo
galrdnerl
BCFA
and
BSA
9 «TZ>
OlMthoat*
Carelnus
mamas
BSA ~
(V)
ti
01*«thoat«
Cardlum edule BSA —
greater than
3.3 (TZ)
1.3 (TZ)
ae(c,e,f, One hundred sixty-four Alabaster'
hard (HW) pesticides, wetting agents, and (1969),
or soft miscellaneous Mater pollutants showed a AHIC-5<>25
(SW) syn- wide range of toxlclty spanning 1? orders
thetio of matinlturt*. Knowing the> toxlclty and
wator, or percentage of all components of a
seawater formulation did not result In easy
Tor somo predictability of the toxlclty of a
•poclea 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.
a«(c«ntin- One hundred-forty surface active Portmann, et
UOU3 cer- agents, solvent emulslflers, pesticides, 81(1971),
ation, sea-Polychlorlnated hlohenyls, oure AMIC-7701
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.
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portitann, «t
al (tori),
AMIC-7701
Ol'ethoate
Crangon
crangon
BSA —
0.0003-0.001
(TZ)
a*(contin-
uous aer-
ation, soa-
water, and
daily
solution
renewal)
same as above
Port»ann, et
al (1971),
AMIC-7701
DIaethoate
Panda I us
•ontagul
BSA —
greater than
0.03 (TZ)
at-( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann,
etal (1971),
AMIC-7701
-------
ro
Toxiclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Coitoound Organism Study Location Ppm or Noted Comments
D 1 •« thy 1 ai I ne Cranqon BSA —
cranqon
0 I »e thy 1 phosphorod 1 1 Pimephales BSA --
hole acid promelas
0 1 «e thy 1 phos ohorod 1 1 Plmephales GCFA —
hole acid promelas
Olnethy 1 phosphorothl Plmephales BSA ~
onlc acid cromelas
Dimethyl fornamlde Cranqon BSA ~
cranqon
greater than atf(contln-
100 (T2) uoua aer-
ation, sea-
water, and
daily
solution
renewal )
33.5 (Ti») a*,d,e,o.
and Fe
21.0 (Tlit) a»,d,e,o,
and Fe
1,2.5 (Ti.) a*,d,e,o,
and Fe
greater than a«(contln-
100 (T3) uous aer-
Pne hundr ed- T or t y surface active
agents, solvent emulslflers, pesticides.
po 1 ych 1 or Ina t ed blphenyls, pure
inorganic, and organic cheirlcals were
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
organ 1 sms .
Malathlon and its hydrolysis
products were evaluated with the findinq
that one such product (dlethyl fumarate)
was more toxic than Malathlon to fathead
minnows. Synerqlsm occurred between
Malathlon and two products of hydrolysis.
Continuous exposure resulted In
Increased toxiclty.
same as above
same as above
One hundred-forty surface active
agents, solvent emulsiflers, pesticides.
ation, aea-po 1 ych lor inated blphenyls, pure
water, and
dally
solution
renewal )
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
toxiclty of chemicals to freshwater
organisms.
Reference
Por t m^nn, e t
al (1971),
AnIC-7701
Pender
( 1059) ,
AMIC-3787
Bender
(1969) ,
AMIC-3787
Render
(1959) ,
AMIC-3787
Por t mann, e t
al (1971),
AMIC-7701
Dimethyl phosohate Plmephales BSA —
prone I as
18.0 (Ti») a*,d,o,o, Malathlon and Its hydrolysis Bender (1969),
and Fe products were evaluated with the finding AMIC-3787
that one such product (dlethyl Tumarate)
was more toxic than Malathlon to fathead
minnows. Synerqlsm occurred between
Malathlon and two products of hydrolysis.
Continuous exposure resulted In
Increased toxiclty.
-------
Dimethyl phosphite
PImeohales
prontelas
DI»ethyl Phormldlum
?»3,6-tetrachloroter amblguum
•phthatata
BSA
ro
H
vn
Tublfax
tubifcx
FL
and
BSA
BelzonI ,
Miss.
Olnltrobutyl phenol
Gammarus
fasclatus
BSA
01nltrophenyI ether
Phormldium
amblguum
L —
325.0
0.5-in.o
(33percent
growth
Inhibited 1
a»,d,e,o,
and Fe
same as above
8ender(l969),
0.50 (NTF1
1.8
Of 7it chemicals evaluated as
alqlcldes, only 9 were more toxic than
CuSOit. None Inhibited growth of
mat-forming algae for more than 2 weeks.
CuSO** formulated with certain wetting
aqents was more toxic than CuSOi* alone.
Copner chloramlne was also found to be
more toxic thar CuSOit. No wettlno aqents
were found to be inhibitory at the
concentrations Investlqated (n.05 and
0.005 pom). Also reoorted are factors
affecting qrowth of alqae in canals to
determine whether there were leads to
controlling alcmp by environmental
managerrent. No practical environmental
means were found.
The response of
ppstIcIde-rpslstant aouatic organisms to
various pesticides was comoared to the
response of n on— r e^ I ^ tan t sp*»cie»s.
Pesticide-resistant species were
collected at Flelzonl and non-resistant
species at State College. Copepods,
clams, snails, and sludge worms from
BelzonI 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.
Of the aquatic weed herbicides
evaluated, Dlclone was the most toxic,
Oaohnla was generally the most sensitive
orqanism. AM 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 Important food chain links.
Of 7i» chemicals evaluated as
alqlcldes, only 9 were more toxic than
CuSO<». None Inhibited growth of
mat-forming alqae for more than 2 weeks.
CuSOi* formulated with certain wetting
aqents was more toxic than CuSOii alone.
Copper chloramlne was also found to be
Otto (19701,
AHTC-892
Naavl. et
al(1969),
AMIC-5379
Sanders
(19701,
AMIC-'t'53
Otto (1978),
ANIC-892
-------
Covoound
Organism
Field Field
Study Location
Toxlclty.
Active
Ingredient,
Pom
Fxoer1montaI
Varieties,
Controlied
or Noted
Comments
Reference
I
fO
OInocao
01 noc*o
Fish (not
soeclfled)
Pashora
heteromorpha
HCFA
and
RSA
greater than
0.01-0.1 (K)
0.11 (T3)
OInocao
Rasbora
heteroworpha
BCFA
and
8SA
0.07 (T3)
Dlnos*b
Fish (not
specified)
greater than
0.1-1.0 (K)
a»,c,e,f,
hard (HW)
or soft
(3WJ syn-
thetic
water, or
seawater
tor aome
species
a*,c,e,f,
hard (HW)
or soft
(SW) syn-
thetic
dilution
water, or
seawater
Tor some
species
more toxic than CuSO<». No netting agents
were found to he Inhibitory at the
concentrations InvestIqated (0.05 and
O.OQS Don). Also r»norted are factors
affecting growth of alcae In cinals to
determine whether th«»re Here leads to
controlling algae by environmental
management. No practical environmental
means were found.
Approximate toxlcltles of Hawrtesley-
numerous pesticides commonly used In thotias
Britain were summarized. An excellent (19M)rAMIC-
brief* general discussion of toxlclty 1056
testing is also present.
One hundred sixty-four Alabaster
pesticides, wettlna agents, and (1^69),
miscellaneous water pollutants showed a AMIC-5fc?5
wide range of toxiclty scanning 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. Sometimes
pesticides were most toxic In hard nnter
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
same as above Alabaster
(1969) ,
AHIC-SI.25
Approximate toxlcltles of
numerous Pesticides commonly used In
Britain were summarized. An excellent
brief, general discussion of toxiclty
testing Is also present.
Mawdesley-
Th o»as(19Tl)
AMIC-1056
-------
Olphenanid
Otphena»ld
Olohena»ld
Gammarus
fasclatus
BSA —
Paleomontes BSA
KadlaKensls
Aseltus BSA
brevicaudus
greater than
100.0 (T2>
58.0
ro
Olphenawld
Diphenamld
Orconectes BSA
nals
Oaohnla maqna BSA
greater than
100.0 (T2>
56.0 (T2>
same as above
sane as above
Sanders
Sanders
(1970) ,
Olphenanld
Cyorldopsls BSA
vldua
50.0 (T3)
same as above
Sanders
(1970)t
AMIC-1.53
Dlphenanld
OlPterex
Olouat-dlbromide
Lenomls BSA
macrochlrus
Crassostrea L
virglnlca
(larvae)
Sal mo
galrdner 1
BCFA
and
BSA
80.0 (T2)
1.0 (Tilt)
same as above
Sanders
(1970),
AMIC-<»53
70
~ The effect of 52 pesticides on Oavlst et al
embryonic development of clams and
oysters was reported. Synerqistlc (1969).AMIC-
effects with solvents Here also reported. 5990
Most of the compounds affected
develocment more than survival. Some,
however, drastically reduced larval
growth. The authors point out the
necessity of evaluating the effects of
pesticides on all life staqes of an
orqanlsm and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
shell fish.
a*,c,e,f. One hundred sixty-four Alabaster
hard (HM) pesticides, wetting aqentsi and (19B9),
or mlscel laneous -water pollutants showed a AMIC-5i>25
-------
ro
fe
Toxlclty, Experlmenta
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Ppm or Noted
SOFT(SW)
syn thet Ic
dl lut Ion
water, or
sfawa t er
for some
spec I es
Olquaf Calllbactls BSA — 16. it (Tfc) »».b*,c,f,
sp. (nytiph, i»l« and
8-1Z mm) silica.
calcium.
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
Iron,
dissolved
solids.
conduc-
tance
Olauat Enallagma sp. BSA ~ greater than a»,b»,c,f,
(naiad, 16-2"t 100 (Tit) l,lt and
•*) silica,
calcium,
magnesium.
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
iron,
dissolved
solids,
conduc-
tance
Comments Reference
wide range of toxlclty spanning 1? orders
of maqnltude. Knowlnq the toxlclty and
oercentaqe of alt components of a
formulation did not result in easy
oredlctabl 1 1 ty of the toxlclty of a
mixture of materials. Sometimes
and sometimes the opooslte was true.
found to be essential.
The toxlclty of herbicides Olauat Wilson, e t
and Dlchlobenll to aquatic Invertebrates al (1989),
and fish was determined In aquaria AMIC-5<»5?
containing substrates natural to each
soecles. Olquat was quite toxic to H.
az»teca tut not as toxic to other
organisms. Olchlobenll was less toxic to
H. azetecus but considerably more toxic
to the remaining organism than OlQuat
Mud lessened the toxlclty of both, but
more so for OiQuat. Dichlobenll had a
sublethal narcotlzlnq effect on the
organisms that resulted In
Immobilization. It was concluded that
both herbicides could adversely affect
certain fish food organisms.
sane as above Wilson, et
al (1969),
AMIC-S<»52
-------
Olquat
Hyalella
azteea
(adult, i>-8
mm)
BS» —
0.05 (T<>>
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 (1969),
ANIC-51,52
Olquat
VO
Libel tula sp. BSA
(naiad, 16-2*
mm)
greater than
100
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
sulfate,
iron,
dissolved
solids,
conduc-
tance
same as above
Wilson, et
al (1969).
Olquat
LimneohlI us
so. (larva,
15-?0 DIB)
BSA —
33 (TI,)
a»,b»,c,f,
1,1, and
silica,
calcium,
magnesium,
sodium,
potassium,
bicarbon-
ate,
carbonate,
snlfate,
same as above
Wilson, et
al (1969),
AMIC-5452
-------
Toxiclty,
Active
Field Field Ingredient,
Compound Organism Study Location Pom
Experimental
Variables,
Control 1 ed
or Noted Comments Reference
dissolved
solids,
conduc-
tance
OJquat
Tendlpedldae BSA —
(larvae, 7-10
•n)
greater than
100
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
01 quit
Olauat
Roccus
saxatil Is
(fIngerlIngs)
BSA —
Mya arenarla F
Nomlnl
CreeK, Va.
80 (T
-------
Olouat
Olouat
MyrlophllI urn
splcatum
Cardlun edule BSA
Nomlnl
Creek,
Va.
0.35 (1.0-70
percent K36)
same as above
greater than 10 a«(eontin- One hundred-forty surface active
(T2) uous aer- agents, solvent emulslflers, pesticides,
atlon, asa-pol ychlorlnated blohenyls, pure
water, and Inorganic, and organic chptiicals 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.
solution
renewal)
Diouct
Crangon
crangon
BSA
greater than 10 a»(contin-
(T2> uous aer-
ation, sea-
water, and
daily
solution
renewal)
Oisoersol SO
Agonus
cataphraetus
BSA
100-330
-------
Compound
Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient.
Ppm
Experimental
Variables.
Control led
or Noted
C oilmen t s
Ref erence
>
Oluron
Oluron
Mercenar la
nercenarla
Gammarus
fasclatus
BSA
01-lsobutyl
Ohenoxyethoxyethy I
dl««tnyi benzyl
••noniu* chloride
Phomldlun
aablguun
01-n-butyl tin oxide Crepldosto»u«
farlonls
greater than
5.0 (T13)
0.70 (T
-------
I
U)
Dl-n-butyl tin oxlrfe Salmo
aquabonlta
Ol-Svston
Ol-Svston
Ol-Srston
Oi-Syston
Mercenar la
•ercenarla
(eqqs)
Hercennrla
mercenarla
(larvae)
Crassostrea I
vlrqlnlca
(eqqs)
Cressostrea
vlrqlnlca
(larvae)
01 (N, M dl-nethyl
cocoaolne salt of
endofhall (ethyl
bis) (?-ethylhexyl)
phosphlnate7-oxablcy
clo (?.?.!)
heptane-?,3-d1 carbox
Vile acid)
Phoriitdlu*
anblquun
• — ^
100-600 (oral
dose, NTE)
5.ZB (TZ>
1.39 (Tl?)
5.86 (TZ)
3.67 (Til.)
0.9-10.0 (NTE) —
absorbed by tissue outside th« Intestinal
tract and that the compound Mas rapidly
eliminated. Tissue residue and retention
time studies were recommended for drug
clearance purposes.
same as above
01 IN. N dimethyl Phormldlum
trlcjecyl anlne) salt amblquum
of endothell
0.9-10.0 (0
percent growth
Inhibited l
sane as above
same as above
same as above
same as above
Of 7i» chemicals evaluated as
alnlcldes, only 9 wpre more toxic than
CuSO't. None Inhibited growth of
mat-forming algae for more than ? Meek*.
CuSOit formulated with certain wetting
aqants Man more toxic thsn Cu^Oit alone.
Conoor chlorairlne wa^ also found to be
more toxic than CuSO't. No wottlnq aqents
were found to be Inhibitory at the
concentrations Investigated (C.05 and
0.00"> DDm). Also reoorted are factors
affecting gronth of algae In canals to
determine whether there were leads to
controlling algae by environmental
management. No practical envlronaental
means Here found.
same as above
Mltchum, et
al (1969).
•NIC-57JD
Davis, et al
(1989).»MIC-
5990
Davis, et al
(1969),AMIC-
5990
Davis, et al
(1969),«1IC-
5990
Oavls, et al
(1969),»HIC-
5990
Otto (1970),
Otto (1970).
AMIC-89Z
OMOC
Fish (not
greater than
Approximate toxlcltles of
Mawdesley-
-------
ro
K>
Co«ooun-1
Dobs JN
Dobs JN
Dobs JN
Dobs JN
Dobs 055
Field Field
Organism Study Location
soecl 1 led)
Carclnus BSA —
ffaenas
Cardlum edule BSA
Cranqon BSA
cr anqon
Randal us 8SA —
nontagul
Carclnus BSA
•aenas
Toxici ty.
Active
Ingred 1 en t ,
Pom
1.0-10.0 (K)
greater than
100 (T2>
greater than
100 (T2)
greater Than
100
greater than
100 (T2>
greater than
100 (contln- same as above
uous aer-
ation, sea-
water, and
daily
solution
renewal)
a*(contin- same as above
uous aer-
ation, sc~-
vatcr, and
daily
solution
ff1frfnrf
T M? 1 3 S
(1^71) ,^WIC-
P Or t (- 3nn , e t
al (1971) ,
A*«!C-77r)i
Portrsrn. et
31 ( 1971) ,
ANIC-77C1
Porffisnn, et
al (1-571) ,
AMIC-7701
PortTann,
etal (1971),
AHIC-7701
Port.Taon, et
al ( ig71) ,
AMIC-7701
-------
renewal)
Dobs 055
Cardium edule BSA
3"..3
at(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, et
al U971) ,
A1IC-7701
IS
vn
Dobs 055
Panda 1 us
•ontaqul
BSA
greater than
100 (T2>
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
sane as above
Portnann, et
al(1971),
Dobs 055
Platlcthys
tIPSUS
BSA
10-30 (T2)
a*(contin-
uous aer-
ation, aoa-
wator, and
daily
solution
renewal)
sane as above
al (1971),
ANIC-7701
Dodine acetate
Oowicide A
Fish (not
soeclf le-l)
Mercenarla
mercer, aria
(eqgs)
greater than
0.1-1,0 (K)
greater than
10.0 (T2)
Approximate toxlclties of HawJesley-
numerous oesticides commonly used In rt\o-~-"f>'"
Britain were surofl'a''ized. An excellent fill!
brief, general discussion of toxicity
testing is also present.
The effect of 52 pesticides on Davis, etal
embryonic development of clans and (19^9),
oysters was reported. Synergistic AHTC-5993
effects with solvents were also reported.
Most of the comoounds affected
development more than survival. Some,
however, drastically reduced larval
-------
Field Fiel d
Comoound Organism Stud/Location
Toxic! ty,
flct i ve
Ingredi ent »
Pom
Experimental
Variables,
Con troll ed
or Noted Comments
o e t er pnce
OoMlcide A
Merc^nar1 a
mercenar1 a
(I arvae)
0.75 (T13)
growth. The authors ooint 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
shel I f ish.
same as above
Davis, et aJ
) ,*MIO
Oowiclde G
ro
ON Do»lcMc G
Hercenar1 a
mercenar1 a
(eiqs)
Hercenar1 a
mercenarla
(Iarvae)
less than 0.25
(T?)
I ess than
0.25(T12>
same as above
same as above
nav Isi et
a I ( 1 1 1 g ) ,
Davis, et
a I ( ig^TD ,
4*115-5990
OoMpon
OONPOO
Rashora
he teromoroha
BCFA
and
BSA
(T2)
Sal mo
galrdner 1
BCFA —
and
8SA
179
a*,o,o,f,
hard (Ka)
or soft
ISW) syn-
thetic
dilution
water, or
aeawatcr
Tor sorr.e
species
a*,c,o,f,
hard (IIW)
or soft
(3W) syn-
thetic
water, or
soawater
for some
species
One hundred sixty-four
pesticides, Hetting agents, and
miscellaneous water nollutants showed a
wide range of toxlclty soanolnq 12 orders
of magnitude. Knowing the toxlcitv 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 sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
same as above
e. I abaster
(1969),
AHIC-5I.25
A Iabaster
(19S9),
AMIC-5U25
-------
Doxclde (CIO?)
Carclnus
BSA
500
greater than
500 (T2)
if.5 cm
a*(contin-
uous aer-
ation, sea-
water, and.
daily
aolxitlon
renewal)
a*(contin-
uous acr-
atioii, sea-
water, and
daily
solution
T-oncv.-al)
a»,c,e,
and
synthetic
^eawater
same as above
same as above
P or t :* ann T e t
al (19711,
Portmann, et
al (1971) ,
AMIC-7701
A laboratory procedure based on
Standard Methods for 16-hr toxlcity
determinations of crude oil and
olI-d1spersant mixtures Has described.
The dlspersants varied considerably in
toxlcity, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr. These did not differ
significantly from 2 |
-------
>
ro
CD
Compound
00
00
OSS
OTMC
Field Field
Organise Study Location
Fundulus BSA —
heterocl 1 tus
Nereis vlrens BSA
Nereis vlrens BSA
Pa 1 aemone t»s BCF --
hadl aHensls
(adul t)
Toxlclty.
Act Ive
Inqredi en t ,
Ppm
0.0005 (Tit)
0.0002-0.001
-------
Oylox
O.B. Granular
"occus
saxatllls
(fInqerlIngs)
BSA —
•Sal mo
galrdner1
BCFA
and
BSA
5.2 (T%)
7,050 IT?)
ro
to
vo
Econat 13086
Rasbora BCFA
heteromorpha and
BSA
0.19 (T2)
EC-90
Rasbora
heteromorpha
BCFA
and
BSA
1.2 (T2,
hardnat*r)
Pesticide-resistant species were
collected at Relzonl and non-resistant
species at State Collpqe. Cooepods,
clams, snails, and sludge MOTH'S (TOT
Belzonl were considerably more tolerant
to oestlcldes than the non-resistant
organisms. The authors note that the
effect of Increased tolerance In the
orqanlsms Is an Increase In the amount of
pesticide residues available to animals
of higher troohic levels.
a*,c,d,e,f Strloed bass flnqorllngs Here Wellborn
iD and apoarentlv much more sensitive to (1959)t
Iron therapeutic and herbicldal compounds than AHTC-572'5
many freshwater fish,
a*,c,e,f, One hurdred sixty-tour alabaster
hard (HH) pesticides, wetting agents, and <1?59),
or miscellaneous water pollutants showed a AHIC-5 wide range of toxicity scanning 12 orders
synthetic of magnitude. Knowlnq the toxicity and
dilution percentage of all components of a
water, or formulation did not result in easy
-------
Toxlcity. Experimental
Active Variables.
Field Field Ingredient. Controlled
Conpound Organism Study Location Ppm or Noted Commpnts
EC-90 Rasbora BCFA —
heteronorpha and
BSA
E»col M-JI.6 (SO Rasbora BCFA —
D«rcent pfu? 20 heteronorpha and
percent Fncol HSA
H-SOOXJ
E»col 70? Rasbora BCFA —
heteronorpha and
BSA
seawater
spec 1 es
1.2 (T3, a»,c,e,f.
softxater) hard
(HH)or
soft (SH)
synthetic
dl lut 16n
water* or
seawater
Tor some
snecles
10 (T2) a»,c,e,f,
hard IHWJ
or soft
(SWJ syn-
thetic
dilution
water, or
seawater
for some
species
6.0 (T2) ac.c.e.f,
.hard (HW)
or soft
CSWJ syn-
thetic
dilution
water, or
aeawater
for sorae
species
prertlctabl 1 1 tv of the toxlcity of a
pesticides Here mo-;t toxic In hard Mater
and sometimes the ooooslte was true.
Testing the actual material as sold was
found to b« essential.
same as above
One hundred sixty~four
pesticides, wettlnq agents, and
miscellaneous water pollutants showed a
Hide range of toxlcity soanninq 1? orders
of magnitude. KnoHlnq the toxlclty and
percentage of atl comoonents of a
formulation did not result in easy
predictability of the toxiclty of a
mixture of materials. So-netimes
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
Ref erence
A labaster
11969) ,
AMIC-5!.??
Al abaster
(19
-------
(eqqs)
EH10
Enpilan
Crassostrea L
vlrqlnlca
(Iarvaet
Cranqon
cranqon
Eaton spi I t~wash
CraKqon
cranqon
IV)
LO
6SA ~
30.0 (Til.)
iOfl-330 (fl.)
USA
l.H-3.3 (Tl,)
oysters was reported. Syneraistlc AHIC-5990
effects with solvents wcr^ also reported.
Most of the compounds af fected
development more than survival. Soiret
however, drastically reduced larval
qrowth. The authors point out the
necessity of evaluating the effects of
pesticides on all life stages of an
orqanlsm and note the oossiblllty of
selecting chemicals for pest control that
would not have serious effect on
shell fish.
a*(contin-
uous aer-
ation, aea-
water, arid
daily
solution
renewal)
au(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
One hundred-forty surface active
aqents, solvent emul^lfl^rs, pesticides,
poIychI or Inated blphenyls, pure
Inorganic, and organic chewlcals were
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal with
toxlcity of chemicals to freshwater
orqanlsms.
same as above
Cavls, et al
(1969),»MIC-
5991
Portmann, et
at (197H,
AMIC-7701
«t
al (1971),
AHIC-7701
faulsifler blend 390 Cranqon
crangon
BS»
100-330 (Ti»)
a*(oontin-
uoua aer-
ation, aea-
wator, and
daily
solution
renewal)
same as above
Portnann, et
al (1971),
AMIC-7701
Endosulfan
Fish (not
specified)
qreater than
0.000001-0.0000
1 (K)
Approximate toxicities of Mawdesley-
numerous pesticides commonly used in Thomas (1971
Britain were summarized. An excellent AMIC-1056
brief, general discussion of toxiclty
testing Is also present.
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Pom or Noted Comnpnts Petere^ce
Endosulfan Rasbora 8CFA — 0.000003 (T2) a*,c,e,f. One hundred sixty-four Slabaste'-
heteromoroha and hard (HW) pesticides, wettlna ar^nts, and ^nini 12 orders
synthetic of maqnltud0. Knowing rhp Toxicitv and
dilution oerc-ntaqe of all coTcon«nts of a
Hater, or formulation did not resulT in essy
seawater predictability of tha :o»icir> of s
for some mixture of *fl i tpr i a I i. •^on^tir^';
species pesticides were most toxic l ^ n.3rd water
and sometimes the oooo^itp M^J frue.
Testing the actual material as sold was
found to be essential.
Endosulfan Agonus 8SA — 0.03-1.0 (T3) a«-(contin- "ne hundred-f or ty surface active Dor
cataphractus uous aer- sqenfs, solvent erru I s I T 1 ers, resticidas, al
ation, sea-POIvchI or 1nated biohp^yis, oure AHIC-7701
water, and Inorqanic, and organic cno-ricais wore
daily evaluated aqalnst as many as ten marine
solution orqanisms. The authors noted That most
renewal) published data of this tyoe deal with
toxlclty of chemicals to freshwater
orqanisms.
ro
u>
ro
EndosulIan
Cardlux edule BSA ~
greater than 10 ac-(cor.tin-
UOUS £3T-
ation, sea-
water, and
daily
solution
renewal)
same as above
P or tmann. e t
al I1971) ,
A1IC-77C1
Cndosulfan
Crangon
crangon
BSA
0.01 (T2)
a«(contin-
uous aer-
ation, sea-
water, arid
daily
solution
renewal)
sane as above
et
al (19711,
iMIC-7711
EndothalI
Rasbora
he teronorpha
BCF*
and
BSA
<»60
Alabaster
ft»fC,e,r, une hundred sixty-four
bard (HW) pesticides, netting aqents, and
Or soft miscellaneous water pollutants showed a 4MIC-<5<.2'5
(SW) ayn- Hide range of toxlclty spanning 12 orders
-------
Cndothall
r
tu
u>
u>
Endofhall
EndothalI
EndothalI
Endothal
EndPln
EndPln
Mercenarla
mePcenaPla
(eqqs)
MePcenaPla
morcenar-la
tIapvap)
CpassostPea
vlPqlnlca
(eqqs)
OassostPea
vlrqlnlca
(I arva<*>
Fish (not
specified)
Fish (not
seedfled)
Anacystls
nlrtulans
theUc
dilution
water, or
seavater
for so.T-e
speciea
51.0 (T2)
12,5 (T12)
8,Z (TZ)
R.l (Tld)
qreater than
10-100 (K)
opeatep than
0.0001-0.001
(K)
0.5-1.0 (qpowth a*,c*iP
Inhibited) SH
of maqnltude. Knowing the toxlclty and
oopcantaoe of all comoonenta of a
fopmulatlon did not result in easy
DP-'llctabl I 1 ty of the toxlcity of a
mixture ot materials. Sonptlm»s
pesticides wepe most toxic in hapd watep
and sometimes the ooooslte was true.
Testing the actual m^tpriat as sold was
found to he essential.
The effect of "5? oesticides on Davis, et al
pmbpyonlc development of clairs and
oysters was reported. Svnoraistlc (1969),AMIC-
effects with solvnts wpr<> also repopted. 5990
Most of the compounds aMected
develocment more than survival. Some,
howevpTf dpastlcnlly ppduc»»d larval
qpowth. The authors point out the
necessity of evaluating The effects of
pesticides on all life st^aos of an
OPqanlsm and note tho oossibillty of
selecting chemicals for- oest control that
would not have sePlous effect on
«h«M t Ish.
same as above
same as above
same as above
Apppoximate toxlcitles of
numepous pesticides commonly used in
Bpltain wepe summarized. An excellent
brief, genePal discussion of toxlcity
testing Is also present.
same as above
HetabolIc products of AldPln.
Dleldrln, and EndPln can be as toxic as
the parent compounds, as shown by 00
measurement.
Davis, et al
(1969), AMIC-
5990
Davis, et al
(1969) ,
5990
Davis, «t al
(19S9) ,4MIC-
5990
Mawdesl ey-
Thonas
(1971) .AMIC-
1056
Maxdesley-
Thooas(1971) ,
AMIC-1056
Bat tePton,et
al (1971),
-------
ro
OJ
Compound
En dr I n
Cndr 1 n
Endr In
EnoTln
Endr In
Endrln
Field Field
Organism Study Location
quadrup-
licatun
Sal vel inus BCFA
font Inal Is
(1.15 <3)
Salvellnus BCFA
font Inal Is
(2.01. q)
Salmo clarkl BCFA —
(0.37 a)
Sslmo clarKJ BCFA
(1.30 qt
Salmo BCFA —
qalrdnor 1
(1.?* o.)
Toxlclty, Exoerlmenfal
Act 1 ve Var 1 ables.
Ingredient, Controlled
Pom or Noted Comments
Inhlbl fed) SM
0.355 (Tit) a«-,c,d, Four Insecticides were evaluated
e,r,l,o, °h four fish species at two body weights.
sulTato, Standard method bloassay orocpdures were
copper followed. SytnDt omol ogy was also
manganese, resorted. Generally, toxlcity was
Iron, and significantly different at the two body
chromium 'welqhts. I.e., more toxic at the lower
body weight, exceot for Malathlon.
Well-defined exoerlmental conditions were
said to result In truer measurement of
toxlcl ty.
0.59 (Tif) a»,c,d, same as above
e,r,i,o,
aulfate,
copper.
iron, and
ehro.-ilum
0. 00001 (T
-------
Endrin
Llmneohltus
rhomblcus
(larvae)
FS
J3 (oral a*,c,q
dose per day,SB
<< mo)
Samples of water, silt, bottom Moubry, et
debris, bottom organisms, and fish were al (1958),
taken In 1966 from a creek adlacent to an SNIC-3753
orchard which had been treated In
1963-1965 with various chlorinated
hydrocarbon pesticides. No residues were
found In water samnles. Silt samples
contained 0.002-0.013 opm endrin ana
0-0.On? ppm dleldrln. Endrin residues of
0.011-0.025 ppm and 0.102-0.006 ppm
dleldrln were found In debris samples.
Despite limited control data, residue
analyses Indicated that contamination of
the environment studied was limited.
same as above
same as above
Moufcry, et
al I1GSM,
41IC-37S3
Houbry, et
al (19SB),
4MIC-3753
t*S acted synergistical ly with Salon, et al
oarathlon to cause less survival of
fatheds but had an indeterminate effect (1969),&HIC-
with DDT and no synerglstic effect with 37S5
Endrin.
No effects were noted at lower Grant, et al
concentrations while higher doses caused (1970),
some mortality, lowered growth rat?, ftMIC—3826
decreased thyroid cell helqht, decreased
gametogenes1s• lowered total body fat,
less vacuolIzatlon of liver cells,
elevated serus Na concentrations,
osmo-regulatory disturbance, and other
effects. The-authors note that sublethal
Endrin
Oncorhynchus BCFA —
kisuteh (1.50
g)
0.76 (Ti»)
a»,e,d,
e.f.l.o,
sulfate,
copper,
Iron, and.
chromium
same as above
Post, et al
(1971),
AHIC-1S1?
-------
ro
oo
Comoound
Fndr 1 n
Cndr In
Endr In
Endrln
Endrln
Orqan Ism
Endomychura
cr aver 1
(eqqs)
Pe 1 ec anus
occ Mental Is
(eqqs)
Sula
leucoqast«r
(eqgs)
Pandl on
ha I laetus
(eqqs)
Gaitbusla
af finis
(resistant)
Toxlcl ty.
Active
Field Field Inqredlent,
Study Location Ppm
F Western 0.17 (residue)
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Western 0.07-1.13
O.S., (residua)
Pacl f Ic
Or-ean ,
Panama,
Mexico, and
An tar c tic
F Western 0.01-0.06
U.S., (residue)
Paclf Ic
Panama,
Mexico, and
Antarctic
F Western 0.25 (residue)
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
1 — 0.05-0.
-------
Enrlrin
Fndrln
Gambusla
af finis
(susceptible)
Plmephales
oromelas (3
en)
BSA
0.00001-0.2
(SB 3 hr)
0.00077
K>
U>
Endrln
Plwephales
promelas (1
cm)
BCFA —
0.00057 (T2)
' a*,C,e,f,
k,l,n,
and nag-
nesiura,
gulf a tea,
Iron,
calcium
a#,e,e,f,
k.l.n,
and mag-
nesium,
aulTates,
Iron,
calcium
at higher concentrations. Some mortality
occurred at .02-.075 pom In susceptible
Tlsh and at .<»0 pom In the resistant
strain.
same as above
Bloassays conducted
simultaneously Indicated that DOT Mas
cons IricrabIy more toxic to fathead
minnows under static conditions than
under continuous fI OH conditions.
Decreasing oxyqen and Increasing
metabolites may have enhanced DOT
toxlclty. An identical study Kith Endrln
resulted in only sllqhtly higher toxlcity
under continuous flow conditions.
Average pH, oxyqen, and ammonia nitrogen
were followed throughout the experiments.
The results were comorehenslvely
discussed taking Into consideration many
contributing factors.
same as above
Mclnqvalei
et al
(1968),
AMIC-5I.75
Llncer, et
al
( 1<170> .AHIC-
5509
Lincer, et
al (1970),
AMIC-5509
Endrln
Palaemonetes
KadlaKensIs
(resistant)
BSA
0.0028-0.0137
(Tl)
a»
Bloassays were conducted with Naavl, et al
shrlmo from three areas of Intensive (1970).
pesticide use and from an unexoosed area. AMIC-5519
Previously exposed shrimp were from 1 to
?5 times more resistant than unexoosed
shrimp. Both types of shrlmo were also
exoosefl in caqes to waters of the
contaminated areas. Susceptible shrimp
suffered 66 percent more mortality than
did resistant shrlmo. The toxicity of
the Insecticides ranked In descending
order was as follows? most toxic,
Endrin, DDT, Methyl parathlon, ParathlonJ
medium toxlclty, Guthlon, Llndane,
Toxaphene, Strobanel lease toxic
Chlordane, Sevln, and Heotachlor.
FndrIn
Palaemonetes
0.0009 (Tl)
same as abova
Naavl,et al
-------
Cowoound
Organism
Field Field
Study LocatIon
Toxlclty.
Active
Ingredient,
Pom
Experimental
Variables,
Control Ied
OP Note/d
Comments
Refer ence
Endrln
fU
U)
CD
Endrln
had1akensis
(non-
resistant)
Gambus1 a
affinis
(resistant)
Gambusla
affinis
(resistant)
0.5-? (S86-9)
(whole body
res 1 due)
(1970),
AMIC-5519
Resistant mosquitoflsh were
exoosed to Endrln for varyina periods of
time then fed to susceotlble green
sunflsh. Other experimental variables
were studied. Edible portions of sunflsh
exoosed to sublethal concentrations of
Endrln for short periods of time
contained uo to 26 pom of this chemical.
The authors note that zero tolerances
have been established for Endrln and that
those fish would be rendered unfit for
human consumption In the event of Endrln
spl11 age.
same as above
Ferguson, et
al (1967),
AMIC-5976
Ferguson, et
al (19b7),
AMIC-^976
fndrln
Lenom i s
cyaneIlus
(suscept1ble)
greater than 1
(iti, percent
same as above
Ferquson, et
al (1967),
AMIC-597R
Endr1n
leoomls
cv gne I I us
(susceptible)
O.it-0.9 (whole
body residue)
same as above
Ferguson, et
al (1967) ,
AMIC-5976
Endrln
(Cyclops
blCUSD1dus,
CycI OPS
varleans,
Cyclops
vernal Is•
EucyclODS
aglI Is,
Kacrocyclops
albi dus,
Orthocyclops
modestus)
FL
and
BSA
State
Col leqe,
Miss.
0.08 (85
percent K2)
The reso
pesticide-res ist
various oesticiri
response of ncn-
Pesti c ide-reslst
col Iec ted at Bel
species at State
cIams• snails, a
Re Izon1 were con
to pesticides th
organisms. The
effect of Increa
organisms Is an
pesticide residu
onse of
ant aauatlc organisms to
es was compared to the
resistant soecies.
ant species were
zonl and non-resistant
College. Cooepods,
nd sludge worms from
siderably more tolerant
an the non-resistant
authors note that the
sed tolerance In the
increase in the amount of
es available ro animals
N a a v 1 i e t
(1969),
AMIC-5979
a I
-------
Endrln
ro
OJ
vo
EndPln
Endrln
Endrln
Endrln
Endrln
EndPln
Cooppods
(Cvcl ons
blcuso Idust
Cycl oos
var leans.
Cvcl on";
vernal is.
Eucvcloos
aql Us,
Macro cyclop 3
albldus,
Or thocycl oos
modes t us)
Tublf ex
tublfex
Physa gyrlna
Physa gyrlna
Eupera
slnqteyl
Lepomls
macrochlPus
FL
and
BSn
FL
and
BSA
FL
and
BSA
FL
and
BSA
FL
and
BSA
BSA
Belzonl, 0.08 (20
Miss percent K2)
Belzonl, 6.0 (NTS)
Miss.
State 0.55 (K3>
Col leqe.
Miss.
Relzonl, 0.55 (20
Hiss. percent (K3)
State 0.075 (K3)
Col lege,
Miss.
0.0001 (SB1) a»c,e
Lepomls
macpochlpus
BSA
0.001 (Kl)
of higher trophic levels.
same as above
same as above
same as above
same as above
same as above
Naqvl, et al
(1969),
AMIC-5979
Naavl, etal
(1069),
In * flow-throuqh resoiroweter,
the sublethal dosaqe cause-T increased
oxyqen consumption while the lethal
dosaqe decreased it. Exercise had no
effect on oxyqen consumption but affected
mucus production and hastened death.
Symptomoloqy of Endrin treatment included
hiqh excitability, loss of body col OP,
increased opercutar activity,
convulslonary loss of eaullibrlum, short
quiesclence periods, and body hemorrhage.
Unexercised fish tpeated with 0.001 opra
Endrln began to die two weeks after
treatment.
same as above
Naavl,et al
(19S9),
AMIC-5979
Naavl, et at
(1969),
AMIC-5979
Naavl, et al
(1969),
AMIC-5979
Huner, et
al(1967),
AMIC-5981
Huner, et al
(1967),AMIC-
5981
-------
Endrln
Endr In
Endrln
Crassostrea
vlrqlnlca
(egqs)
Crasso^tre*
vlrqlnlca
(larvae)
Lepomls
•acrochlrus
Field Field
L
1 •—
BSA
Toxlcl ty.
Active
Ingredient,
0.79
greater than
10.0 (Tl«.)
0.001-0.002
(K)
Experimental
Variables,
Control led
same as above Davis, et al
(19f.9> ,AMTC-
F990
-— same as above Davis, et
si ( 1969) ,
AHIC-5991
a Lab. tests Here fol toned by tests HcReynolds
In oonds to eradicate fish. Endrln (1969), AHIC-
r
EndrIn
EndrIn
Endrln
Endr In
Endrln
toxlclty persisted In one pond study Ct6 108
pob) even after thp pond had been emptied
and refilled twice. In ponds, Endrln
toxlclty varied widely. The author
stated that this chemical was too
dangerous for use as a pesciclde except
In extremely Isolated Instances.
Leoomls
•Icroloonus
Leoonls
•acrochlrus
Leoomls
•acrochlrus
Lepools
•acrochlrus
Leoo»Is
•acrochlrus
BSA
FP
FP
FP
Orl f t wood
Far« Ponds,
Indiana
Orlft wood
Farm Ponds,
Indiana
Driftwood
Farm Ponds,
Indiana
BCFA —
0.001-0.002
(K)
0.00<. (KZ)
0.001 (K?l)
0.01.6 (Kl)
0.002 (Tl)
same as above
same as above
same as above
same as above
Endrln absorbed by blueqlll In
lethal and sublethsl exposures xas
determined by electron capture gas
chrom^tograohy. Absorption was measured
at varying times UP to 2,
AMIC-108
Bennett, et
al(1970),
AMIC-195
-------
Endrln
Lepomls BCFA
nacrochlrus
0.0002 (SB1)
same as above
Bennett, et
al
(1970) ,AMIC-
Endrln
Endrin
Et»drln
Endrln
Endrln
Eolchlorhydrln
Lepomls BCFA
macrochlrus
lepomls BCFA
maerochlrus
Lepomls BCFA
macrochlrus
Lepomis BCFA
•fflacroehlrus
Cyprlnodon BSA
varlegatus
(60-70 mm)
Rasbora BCFA
heteromorpha and
BSA
o.ooo?
(0.0
-------
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient,
Pp«
Fxperlmental
Variables,
Control Ied
or Noted
Comments
Reference
Eot»«
Gammarus
f Q^Cla tUS
BSA
23.0 (Tit)
E*«rlne sulfate
>
ro
NeqaprIon
hrevlrostrls
(1-3 K«J>
BSA
11 (NTE 3 hr)
Csxolw«n«
Carclnus
naenas
BSA
10-33 (T2)
Cssolv«n«
Cardluii edule BSA
33-100 (T2>
Testing the actual material as sold Mas
found to be essential,
a* Of the aquatic need herbicides Sanders
evaluafod, nlclonr wns the mo^t toxic* (1^70),
Oaphnla was qenerally the most sensitive AHIC-<*53
organism. All of the Crustacea were
affected by much lower concentration
levels of herbicides than indicated by
the TL sub 50 values. All of the animals
reoresent Important food chain llnKs,
atCfe Data from study of drug effects na!drldge(19
on younq lemon sharks were treated 691t
mathematically to demonstrate AMIC-3832
apoI 1 cab 1 I 11y of classical rate theory to
the study of chemical shark deterrents,
Incaoacltat 1 on (narcosis) was the primary
parameter timed tor effectiveness. This
was usually qulfe rapid for the more
effective drugs.
a«(contln- One hundred-forty surface active Portmann, et
UOU3 oar- agents, solvent emulsiflers, pesticides, al
ation, aea-polychlorInated biphenyls, oure (1971),AMIC-
water, and Inorganic, and organic chetricals were 7701
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»(contin-
uous eer-
ation, 3oa-
water, and
daily
solution
renewal)
same as above
Porteann, et
al
(1971),AMIC-
7701
Cssotvcn*
Crangon
cranqon
BSA
10 (T2>
a»(contin-
uous aer-
ation, sea-
water, and
same as above
Portmann, »t
al (1971),
AM.IC-7701
-------
daily
solution
ronevial)
Essolvene
Ostrea edulls BSA
33-100 (TZ)
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
rcne-.jal)
same as above
Portmann, et
al (1971),
AMIC-7701
Essolvene
Panda I us
montagul
BSA
10 (T2>
a*(contin-
uoua aer-
ation, sea-
wa t
-------
Field Field
Compound .Organism Study Location
Toxlclty,
Active
Ingredient,
Pom
Experimental
Variables,
Control lad
or Noted Comments
Reference
Eth»nol
Betta
spI»ndens
2»50 (SB 6 hr) a»
Ethlon
Pasbora BCFA —
heteromorpha and
BSA
0.52 (T2)
**' ?'?£,*?
hard ™*>
I
(SW) syn-
thetlc
dilution
water, or
aaawater
for'some
opaclea
Ethlon
Tublfex
tublfex
FL
and
BSA
Belzonl,
Miss.
1.50 (NTE)
EtnoB«*n S-25
Rasbora
heferomorpha
BCFA —
and
BSA
0.35 (T2,
hardxater)
a«,c,e.f,
hard (HWj
or soft
(SW)
The effects of ethanol and Raynes, et
bourbon en the aggressive response of al
Siamese flqhtlnq fish were determined. (1968),AMIC
Ethanol Increased qlll show 5712
(aggressiveness) and bourbon and bourbon
congeners decreased It. The authors
tentatively concluded that the delayed
effect of fhe congener resulted f ro*»
involvement of a different physiological
mechanism and that this may be related to
hangover effects in man.
One hundred sixty-four Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a AHTC-5t»25
wide range of toxicitv soanning 1? orders
of magnitude. Knowing the toxlclty and
percentage of all coimonents of a
formutation did not result in easy
predictability of the toxlclty of a
mlxtur» of materials. Sometimes
pesticides were most toxic In hard water
and sometimes the oonoslte was true.
Testing the actual material as sold was
found to be essential.
The response of Naqvl, et
pesticide-resistant aouatic oroanlsms to al(l?69).
various pesticides was corroared to the AMIC-5979
resoonse of non-resistant soecles.
Pesticide-resistant species were
collected at Belzonl and non-resistant
soecles at State Colleoe. Copeoods,
clams, snails, and sludge worms fron
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.
One hundred sixty-four Alabaster
pesticides, wetting agents, and (1969),AMIC-
mlsce I laneous water pollutants showed a 5
-------
Ethomeen S-Z5
Rasbora
heteromorphs
BCTA
and
BSA
0.68 (T2,
sottwater)
Ethylene phosphite
Pimephales
promelas
BSA
3t.O (Tit)
vn
Ethyl parathion
Cardlun edule BSA
3.3-10
-------
Compound
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient,
Ppm
Exper Imenta 1
Varl abl es.
Control led
or Noted Comments
Reference
E-JK.
Fenac (Ha salt)
>
Fenac (Xa salt)
Fenac (Na salt)
Fenac (Na salt!
Fenac (Na salt)
Fenac (Na salt)
Fenac (Na salt)
Fenoprop
Coho salmon SSA Hood Canal, 0.01 (K)
(f 1 nqerI Inqs) Irl Hoodsport,
altu Wash.
Gammarus
fasclatus
USA
Paleomontes BSA
hartl akoni I •:
As»Mus BSA
br evIcaudus
Orconectes BSA
nals
Daohnla magna BSA
Cyorldopsls BSA
vidua
Leooml*: BSA
macrochlrus
Rasbora BCFA
heteromorpha and
BSA
greater than
100.0 (T2)
greater than
ino.o (T?)
greater than
lOO.O(TZ)
greater than
100.0 (TZ)
greater than
100.0 (T3)
greater than
100.0 (T?)
19.0 (T2)
37 (T2)
a»
a*,c,e,r,
hard (HHJ
or soft
(3\i) syn- •
thetic
dilution
water, or
seawater
with fair to good oil dlsoerslon
caoablIIty.
sane as above
Tracy, et al
(19b9).
Of the aauatlc Heed herbicides
evaluated. Dlclone was the most toxic,
DaDhnla was generally the most sensitive
organism. All of the crustaeoa were
affected by much lower concentration
levels of herbicides than Indicated by
the TL sub 50 values. AlI of the animals
reoresent Important food chain links.
same as above
same as above
same as above
same as above
same as above
same as above
Sanders
(1<»TO> ,
AMIC-I.5S
Sanders(1970)
Sande>-s{1970) ,
AHIC-«.53
Sanders
(1970) .AMIC-
1.53
Sanders
(1970) , AHIC-
<»53
Sanders
(1970) ,AMIC-
1.53
Sanders
(1970) ,
AMIC-45J
One hundred sixty-four Alabaster
pesticides, wetting agents, and (19*>9),
miscellaneous w,ater pollutants showed a A1IC-5U25
wide range of toxlclty scanning 1? orders
of magnitude. Knowing the toxlclty and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty ot a
-------
F«ntln acetate
Fenuron
r
Fenuron
Ferric chlorMo
Ferric sulfate
Panda I us
montaqul
Mercenaria
mercenarla
(eqgs)
Mercenarla
mercenarla
(I arvae)
Carasslus
auratus
Carasslus
auratus
BSA —
for some mixture of materials. Sometlnes
species pesticides Here most toxic In hard water
and sometimes the oooosite Has true*
Testing the actual material as sold was
found to be essential.
greater than 33 a*(contln- One hundred-forty surface active
(T2) uoua aer- agents, solvent emulslflers, pesticides,
ation, sea-po'vcn'orinated blohenyls, cure
water, and Inorganic, and organic cheiricals Here
daily evaluated against as many as ten marine
solution organisms. The authors noted that Host
renewal) published data of this type deal Hlth
toxiclty of chemicals to freshwater
organisms.
Portnann, et
al (1971),
ANIC-7701
greater than
10.0 CT2)
Ferrous chloride
Ferrous sulfate (as Acroneurla BSA
Carasslus L
auratus
greater than
5.0 1T12)
5-10 (K<»)
5-10 (K<>>
5-10 (Kit)
16 (T9>
Pavls, et
a I(1969),
AHIC-5990
The effect of 52 pesticides on
embryonic development of clams and
oysters Has reported. Synerglstlc
effects Hlth solvents Here also reoorted.
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 staoes of an
organlsff and note the oosslbillty of
selecting chemicals for pest control that
would not have serious effect on
shell fish.
same as above Davis, et
al(19S9),
AMIC-5990
Iron salts were most harmful Ashlev
Immediately after dissolving, resulting (1970),AMIC-
In gill blockage (reversible), absorption 5<»36
In digestive tract, and iron precipitates
In epithelium and renal tubules.
same as above
same as above
Ashley
(1970),
AMTC-5^36
Ashley(1970),
AMIC-5I»36
a*,c,d,e,f
Ephemerella (mayfly) Has the most Harnlck, et
sensitive aquatic insect of those al(1969),
studied, and copper the most broadly AMIC-3767
toxic metal. -The authors suggest that
-------
Field Field
CoBoound Organism Study Location
Ferrous xulfate (as Ephenerella BSA
Ferrous sulfate (as Hydropsyche BSA ~
Fe)
Toxlclty,
Active
Ingredient,
Pom
0.32 (Tli)
16 (T7>
Experimental
Variables,
Control led
or Noted Comments
aquatic Insects may not be as sensitive
to heavy metals as fish.
a',c,d,e,f same as above
a*rc,d,e,f same as above
Reference
Warnlch.
etal (1<<69>,
AHTC-3767
Warnick, et
al (1969) .
AHIC-3767
Ferrous sulfate Caras^lu* L
auratus
8
Flnatol FSK
Cranqon BSA
cranqon
5-10
100-330 (T2>
Flnasol
Cranqon
cranqon
BSA
3300 (T
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AMIC-7701
Fleck o.o. Fly dip "ashore
BCFA —
0.73
a*,c,e,f,
One hundred sixty-four
Alabaster,
-------
heteronorpha and
BSA
Fluoresceln sodium
Sal no
galrdnerl
BSA —
1,372
f
Fluor«seeln sodlun Tctalurus nSA
punctatus
Fluoresceln sodlu* Lepomls BSA
•acrochlrus
Ftuoroklll
Rasbora BCFA
heteromorpha and
BSA
2,267 (T"t)
3,1(33 (T«O
3,500 (T2)
Ftuoroklll
Sal no
galrdnerl
BCFA
and
BSA
1.600 (T2)
hard
(HHIor
soft (SHI
synthetic
dilution
Hater, or
seawater
for some
species
a«
a*,c,e,f,
hard (HH)
or
SOFT(SW)
synthetic
dilution
water, or
seawater
for some
scecles
a*,c,e,f,
hard (HH)
or
SOFT(SH1
synthetic
dilution
Hater, or
seaHater
pesticides, wetting agents, and (19691,AMIC-
mlsceIlaneous water oollutants showed a 5«>25
wide range 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 were most toxic In hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
The dyes Rhodamlne B and Marking
Fluoresceln sodium were found to be (1969),
relatively non-toxic in pom AMJC-5729
concentrations while antlmycln was toxic
at oob levels. The author states that
neither dye at field use concentrations
should significantly Influence the
activity of Antlmycln A against fish.
same as above Mar-King
same as above
Marking
«1969) .AMIC-
One hundred sixty-four
pesticides, wetting aqents, and
miscellaneous water ooltutants showed a
wide range of toxiclty spanning 12 orders
of magnitude. Knowing the toxlcity and
percentage of all conoonents 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 opooslte was true.
Testing the actual material as sold was
found to be essential.
sane as above
Alabaster
(1969),
AHIO5V25
Alabaster
(1969) ,
AMIC-5«t2S
-------
ro
Compound
FluoroM 1 1
Follzoll
Toxlclty, Experimental
Active Varlablest
Field Field Inqredlent, Controlled
Orqanlsm Study Location Ppm or Noted Comments
for some
species
Plstessa BCF4 — 1,300 (T2) a*,c,».'.
vulgarls and hard (HW)
BSA or
SOFT(iM)
synthetic
dl 1 ut Ion
water., or
seawater
for sone
soecles
Cardlui" edule BSA — 33-100 (T2) a*(contln-
uoua aer-
sane as above
One hundred- f or ty surface active
aqents, solvent emulslflers, pesticides.
ation, 3ca- po 1 ych 1 or 1 na t ed blphenvls, pure
Follzol 1
Felper
water, and
daily
solution
renewal )
Cranqon BS4 -- 330-1000 (T2) a«(contin-
cranqoo uous aer-
ation, sea-
wator, and
daily
solution
renewal )
Brachydanlo L — 1.0 (T 30 mini
rerio
( 1 arvae)
inorqanic, and orqanlc chemicals were
evaluated against as many as ten marine
organisms. The authors noted that most
published data ol this type deal with
toxlclty of chemicals to freshwater
orqan 1 sins .
same as above
Folpet, Olfolatan, and Cactan
were found to be toxic to zebraflsh
larvae within 90 mln. Dlfolatan was most
Re f erence
HI abaster
(1969) ,
AHIC-5i*?5
Portnann, et
al (1171),
AMIC-7701
Portmann, et
al
(1971) .AHIC-
7701
Abedi.et al
(195f) ,
AMIC-3717
toxic while Captan was least toxic.
Effects observed were cessation of
heartbeat and loss of oigmentat I on. The
authors recommended this as a sensitive,
rapid bloassay tor these and related
compounds.
For«»ldehyde
Salvo
galrdner1
8CFA
and
BSA
50 (TZ)
a*,c,e,f. One hundred sixty-four Alabaster
hard (HH) pesticides, wetting agents, and (1969!,
or soft mi see I laneous water pollutants showed a AMIC-S'tZS
-------
Formaldehyde
Sat mo trutta
BCFA
and
BSA
50 (T2>
r
ro
Formaldehyde
Crangon
cranqon
BSA —
330-1000 (T2>
Formaldehyde
Platlcthys
flesus
BSA
100-330 (T2)
(3W) ayn- wide range of toxlcity spanning 12 orders
the tic of magnitude. Knowing the toxlcity and
dilution percentage of all components of a
water, or formulation did not result In easy
aeaweter predictability of the toxlcity of a
for some mixture of materials. Sometimes
apec3.es 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
a»,c,e,f,
hard (HH)
or soft
(SW)synthe
tic
dilution
water, or
seawater
for some
species
a-:,(contin- "ne hundred-forty surface active
uous aer- agents, solvent emulslflers. pesticides.
atlon, sea-Do'YcMorlnated blphenyls, pure
wator, 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.
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal}
same as above
A I abaster
(1969),
•MIC-5U25
Portrann, et
al (1971),
AMIC-7701
Portmann, et
al (1971),
AMIC-7701
Formal In
Sal mo
galrdnerl
200-1,00 (SB,
Caudal arterial blood samples Hedeneyer
were taken at selected time Intervals and (1971),AHIC-
evaluated for acid-base balance and for 3287
gill, kidney, and liver function by
measuring 02 consumption, total C02,
HC03, Cl(mlnus), Ca(2 plus), blllrubln,
whole blood pH, and Vitamin C depletion.
Formalin treatments seemed to be a more
severe stress to rainbow gelscff pfela
data and discussion are presented.
-------
vn
ru
Field Field
Compound Organls* Study Locatlor
For.atln Oncorhynchus L —
klsutch
Forvxl In Trachlnotus BSA **•
enrol Inus
(Juvenile)
For.sl In Roccus BSA —
saxat 1 1 Is
(f Ingerl Ings)
Foralc »cld Carclnus BSA
naenas
Toxlclty, Experiments
Active Variables,
Ingredient, Controlled
1 Ppm or Noted
200-itOO (S8, f
-------
Furfural
Rasbora
heferonorpha
BCFA —
and
BSA
Z3 (T2)
CO
\n
-------
Compound
Field Field
Organism Study Location
Toxlclty,
Active
Inqredlent,
Ppm
Exoerlmental
Variables,
Controlled
or Noted
Comments
Peterence
renewal )
Ga'len 0
Cardlum edule BSA
33 (TZ)
ac(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewaj.}
seme as above
Por t nann, e t
al (1171),
AMir-7701
rv>
v/i
Crangon
CPanqon
BSA
10 (T2)
ac-( contin-
uous aer-
ation, sea
water, and
daily
solution
renewal)
same as above
Portmannt et
al (1=171),
AMIC-7701
Pandalus
nontaqul
BSA
10
a«-( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al
(1971),AHIC-
7701
Ganlen OS
-------
solution
renewal)
Gaul en OS*
Crangon
cranqon
BSA
ID (T2)
a«(contin-
uous aer-
ation, soa-
wator, and
daily
solution
renewal)
same as above
Portnann, et
al (1971),
AMIC-7701
Gaslen OS
a*(contin-
uous aer-
ation, sea-
water, ar.d
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AMIC-7701
Ganlen PBX
Cranqon
crangon
3SA
330-1000 (T<»)
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, et
al (1971)i
AMIC-7701
Ganlen H8X
Crangon
crangon
BSA
100-330 (Tit)
a«(consin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portaann, et
al (1971),
AMIC-7701
Gamma BHC
Pasbora
heteromoroha
BCFA
and
BSA
0.0
-------
ToxicI ty ,
Active
Field Field Ingredient,
Compound Organism StudyLocatlon Ppm
G«*apax Randal us BSA — 33
-------
Graooxone (J.F.
Rasbora BCFA
heteronorpha and
BSA
570 (T2,
hardwater)
Granoxone (J.F.
Rasbora
heteromorpha
HCFA
and
BSA
200 (T2,
softwater)
ro
VJl
GrIseofulvln
Mercenarla
mercenarla
(eggs)
water, or
seawater
for some
species
a*,c,e,f,
hard IHW)
or soft
(SW)
syn the tic
dilution
water, or
seawater
for some
species
a»,c,e,f ,
hard (HW)
or soft
(SW)
syn the tIc
dilution
Hater, or
seawater
for some
species
less than 0.25 ——
(T2)
sane as above
Alabaster
same as above
Alabaster
(19691,
The effect of 52 ppstlclaes on
embryonic development of clams and
oystprs was reported. Synerglstlc
effects with solvents were also reported.
Most of the compounds affected
development more than survival. Some,
how»vpr, drastically reduced larval
growth. The authors point out the
necessity of evaluating the effects of
pesticides on all life staqes of an
organism and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
shell fish.
Davis, et
al (1969),
AHIC-5990
Grlseofulvin
Gulf agent 1009
Hercenarla
mercenar1 a
(larvae)
Crangon
crangon
BSA —
less than 1.0
(T12)
330 (T
same as above
Q-»(coritin- nr>e hundred-forty surface active
uous aer- agents, solvent emulsiflers, pesticides,
ation, sea-PO'ychlorlnated blphenyls, pure
water, and Inorganic, and organic checicals were
daily evaluated against as many as ten marine
solution organisms. The authors noted that nost
Davis, et
al (1 = 69),
AMIC-5990
Portmann, et
al (1971),
AHIC-7701
-------
Cowoound
Field Field
Organism Study Location
Toxlclty,
ActIve
Ingredient,
Ppm
Experimental
Variables,
ControI Ied
or Noted
Comments
Reference
Guthlon
>
I
ro
o>
Guthlon
Guthion
Gu thlon
Gu th ion
Guthlon
Guthlon
Ictalurus
punc ta tus
BSA
Ictalurus
•e I as
Carassius
auratus
CynrInus
carplo
RSA
BSA
RSA
Plmeohales BSA
promelas
Leooinls BSA
•acrochlrus
Leoomls BSA
•Icrolophus
3.29 (Tit)
3.50 (Tit)
it.27 (Tit)
0.695 (Tit)
0.295 (Tit)
0.022 (Tit)
0.052 (Tit)
renewal) published data of this type deal with
toxlclty ot chemicals to freshwater
organisms.
a, OrganochI orIne Insecticides were Macek, et
synthetic the most toxic compounds, a)(1970),
testwater organophosphates Intermediate, carbamates AMIC-5510
the least toxic. Brown trout was the
species most susceptible to
orqanochI or 1nes, echo salmon the most
susceptible to carbamates, and goldfish
were the least susceptible of all
species. Safe concentrations established
by bloassays with salmonlds or
centrarchlds would likely be safe for
cyorlnlds and Ictalurlds. Safe levels
for Ictalurlds or cyprlnlds would
probably be hazardous for centrarchlds
and salmonlds. The use ot goldfish In
bloassays was discouraged.
synthetic
test water
a,
synthetic
test water
a,
synthetic
test water
synthetic
test water
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(1970),
AMIC-5510
Hacek, et at
(1970).AMIC-
5510
Macek, rt
al (1970),
AMIC-5510
Macek, et
al (1970),
AMIC-5510
Hacek, et
al (1970).
AMIC-5510
Macek, et
al (1970),
AMIC-5510
-------
Guthlon
Guthlon
Cuthlon
Guthlon
Cuthlon
Cuthlon
Mlcropterus BSA
salmoldcs
ro
VJl
Guthlon
Cuthlon
Sal mo
qalrdnerI
BSA
Salmo tputta BSA —
Oncorhynchus BSA
klsutch
Perca
fIavescens
BSA
Palaemonetes BSA
kadlakensls
(resistant)
0.005
-------
Compound
Field Field
Organism Study Location
Toxlcity,
Active
Ingredient,
Ppm
Exper 1 men tal
Variables,
Control 1 ed
or Noted Comments
Reference
CutMon
Gu thlon
Gu thIon
HeotscMor eooxlde
M»rcenarla
mercenarla
(eqgs)
Hercennrla L —
mercenarla
(Iarvae)
Crassostrea L
vlrqlnlca
(eqgs)
0.86 (T2)
0.86 (T12)
0.6? (T2)
H«ot»chlor eooxide Brown
bulIhead
FRL Misc. states 0.3
S990
Davis, et al
(19*9) ,&HIC-
5990
Henderson t
et al
(1971),
«HIC-1<»07
Henderson,et
al (1971),
AMIC-l"t07
H«nd«pson,
et al
-------
Heptachlor epoxlde
Heptachlor epoxlde
Smal1 mouth
buffalo
Falco
pereqrInus
(Immature)
FRL
Heotachlor eooxlde
Heptachlor
Gizzard shad FRL
Heptachlor
Heptachlor
Misc. states 0.16 residue
(SB)
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
0.09 (Hhole
body residue)
Falco F
Deregrlnus
(adul t)
Hestern
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
0.18-1.0 (whole —
body residue)
Misc. states O.i»5 residue
(SB)
Blue catfish FRL
Rasbora BCFA
heteromoroha and
8SA
Misc. states 0.22 residue
(SB)
0.05 (T2)
11971),
AHIC-11,97
same as above Henderson,
et al
(1971),
4MIC-H.07
Peregrine falcons, falcon crey, Rlsebrough,
and other predator soecies were collected et al
widely and analyzed for DDT, DOE, PCS, (1968),AMIC-
and a few other pesticides to a lesser 38
degree. PCR and DPT were found to be
widely dispersed globally. PCS was found
to be a powerful inducer of hepatic
enzymes that degrade oestradlol.
Reductions In thickness of egg shells,
eggshell weight, and water retention
occurred. fill affect hatching success.
The authors state that the peregrine may
be the first species entlrpated by global
contamination.
same as above
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 1961. Fish were
analyzed for residues of 11
organochlorlne Insecticides, Holds, and
PCB-s.
same as above
PIsebrouoh,
et al
(1968),
•MIC-38**
Henderson,
etal 11971),
AMIC-11.07
a*,c,e,f. One hundre
hard (HW) pesticides, wettin
or soft
(SW) syn-
thetic
One hundred sixty-four
g agents, and
miscellaneous water pollutants showed a
wide range of toxlclty spanning 12 orders
of magnitude. Knowing the toxlclty and
Henderson,
etal (1971),
AMIC-H07
A labaster
(1969),
dilution percentage of all components of a
water, or formulation did not result In easy
seawater predictability of the toxlclty of a
-------
Toxlei ty,
Active
Field Field Ingredient,
Comoound Organise Study Locat Ion Ppm
Experimental
Variables,
Control 1 ed
OP Noted
for some mixture of
Comment s
materials. Sometimes
R e f er ence
Hcotachlor
IV)
H«pt»chlor
LepomIs
cyanelI us
(Resistant)
BSA
Lepomls
cyaneI lus
(Susceptible)
BSA
1.98 (T2>
0.07 (T2)
and sometimes the ooooslte was true.
Testing the actual material as sold was
found to be essential.
Green sunflsh from Belzonl, Miss.
Here resistant to Chlordane, Heptachlor,
Llndane, and Strobane, but not to
Parathlon. Golden shiners from the same
location Here resistant to Llndane and
Strobane, tolerant to Chlordane and
Heptachlor, and susceptible to Parathlon.
Lack of resistance to Parathlon
Indicated lack of agricultural usaae of
orqanochosphates in that area. Resistant
fish Here compared to susceptible ones
collected at Starhvllle.
same as above
M1nchen, et
al (197!3> ,
AMIC-5U71
Mlnchen, et
al(1970),
ANIC-SI.71
Heptachlor
Notemlqonus
crysoleucas
(Resistant)
BSA
2.31. (T3)
same as above
HlncheH,
etal (1=-'0
AMIC-51.71
H«otaehlor
No ternIqonus
crysoleucas
(Susceptible)
BSA
0.<»9 (T2)
same as above
Mlnchex,
etal (1070),
AHIC-51.71
Heotachlor
Palaemonetes
kadlakensls
(resistant)
BSA
0.169-0.273
(Tl)
Bloassays nere conducted nith Naavl, et al
shrlno from three areas of Intensive (1970),
pesticide use and from an unexposed area. AMIC-5519
Previously exposed shrimp Here from 1 to
25 times more resistant than unexposed
shrimp. Both types of shrimp Here also
exposed In caqes to Haters of the
contaminated areas. Susceotlble shrimp
suffered 66 percent more mortality than
did resistant shrimp. The toxlcity ot
the Insecticides ranked In descending
order Has as follons! most toxic,
Endrjn, DDT, Methyl Parathlon, Parathlonl
-------
H«otachlor
Htptachlor
HcptacMor
ON
U)
Heptschlor
Palaemonetes
Kadlakensls
(non-
resistant)
Heteropneus-
tes fossilis
Amphlpnous
cuchla
BSA
0.01.06 (Tl)
1.0 (SB 2 hr,K —
!.<> hr)
medium toxlcltyt Guthlon, LIndanet
Toxaphene, Strobanel lease toxic
Chlordane, Sevln, and HeotacMor.
same as above
Epidermal lesions ot catfish
barbels were moderate to severe after
exposure noted. Barbel curllnq and
Inactlvatlon were associated effects.
BSA
(K3)
atCf
Anabus
testudlneus
BSA
0.5 (K3)
,c*d,e,f
Naovl, et
AMIC-5519
Konar
(19S9),
4HIC-5726
All bloassay animals were
collected locally apparently near
Muzaffarpur, Bihar, India. The bloassay AMIC-U<»8
consisted of a simple ) ar (8-IIter) with
dally solution renewal (except for
plankton studies In which solutions were
not renewed). A safe apallcatlon rate of
0.813 lt>/ acre was suggested for survival
of most aquatic species.
same as above
Konar
(1970) ,
AMIC-M.8
Heptaehlor
Channa
ounctatus
(fry)
BSA
0.001 (KID
same as above
Xanar
AMIC-4I.8
Meptachlor
Heptachlor
Heotachlor
HcptacMor
Channa
punctatus
(adul tt
Esomus
danr lea
Heteropneus-
tes fossllls
1.0
a>c,d,e,(
atctd,eif
a,c,d,e,f
atc,d,e,f
same as above
same as above
sane as above
same as above
Konar
(1970) t
AHIC-Mt8
Konar
(1970) ,
Konar
(1970) ,AMIC-
lti>8
Konar (1978) .
-------
ru
Conoound
Heptachlor
Heptacnlor
Heotachlor
Hept achl or
Heptachl or
Heptachlor
Meptachtor
Heptachlor
Heptachlor
Heotachlor
Heptachlor
Toxlclty,
Active
Field Field Ingredient,
Xlrqanlsm Study Location Pom
Oaohnla BSA -- 0.1 (K)
Olaptomus BSA — 0.1 (K)
Gastrotrlcha BSA — 0.1 (NT)
Naupllu? RSA — 0.1 (K)
Pandorlna BSA — 0.001 (K)
Volvox BSA — 0.001 (K)
Anlsoptera BSA — 0.01 (K5>
(nymohs)
Belostoma BSA — 2.0 (K3>
Indlca
Cybister SP. BSA — 0.1
( 1 arvae)
Dytlscus so. BSA — 0.1 (K3>
(adult)
Exoer 1 men ta 1
Variables,
Control 1 ed
or Noted Comments
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,t same as above
a,c,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,r same as above
a,e,d,e,r same as above
a,c,d,e,f same as above
a,c,d,e,r sane as above
a,c,d,e,f same as above
a,c,d,e,f same as above
Ret erence
AMIO«t<>B
Konar
(1970) .A1IC-
Konsr
(1970) ,
AMIC-
-------
CO
Ov
vn
Heptachlor
HeptacMor
Heptachl or
Heptachlor
Heptachlor
Heptachl or
Heptachlor
Heptaehlor
Heptachl or
Heptachlor
Heptachlor
Heotachlor
HeotacMor
Heptachlor
Heptachlor
Hydrophllus BSA
sp.
Neoa sp. BSA
Notonecta sp. BSA
Ranatra BSA
fillformls
Sohaerodema BSA
annutatum
Hystus
vittatus
BSA
Nandus nandus HSA
Puntlus
sophor*
BSA
Trlchoqaster BSA
f asciatus
(younq)
Tr Ic
f asciatus
ladul t)
BSA
Brachlonus BSA
Cerlodaphnla BSA
Closterlum BSA
Cyclops 8SA
0.08 (K3) a,c,d,e,f
n.OU (K6) a,c,d,e,f
0.006 (K?) a,c,d,e,f
0.006
Cypris
BSA
0.1 (K)
0.1 (K)
a,c,d,e.f
e< f
9tCtdf e, f
(Kl) atc.d.e.f
3,c,d,e,f
0.1 (NTE) a,c,d,e,T
0.1 (K)
0.001 (K) a,c,d,e,t
j.c.d.e,f
a,c,d,e,f
same as above
same as above
same as above
sane as above
sane as above
same as above
same as above
same as above
same as above
sane as above
same as above
sane as above
same as above
sane as above
sane as above
Konar(19TO),
Konar
(1970) ,
AMIC-
-------
Compound
Heotachlor
Meot achior
Hexachl orobenzene
Hexachl orobenzene
Hexachl orobenzene
He xachl orobenzene
He xachl orobenzene
Field Field
Organism Study Location
Labeo rohlta BSA
(earl y
flnqerl ing)
Lab»o rohlta BSA
(1 ate
flnqerl Ing)
Anqul 1 la FRL St. John,
rostrata N.B., Can.
Esox nlqer FRL St. John,
N.B., Can.
Salmo salar FRL St. John,
N.B., Can.
Clupea FRL St. John,
harenqus N.B., Can.
Scomber FRL St. John,
scombrus N.B., Can.
Toxlclty, Experimental
Active Variables,
Inqredientt Controlled
Ppm or Noted Comments
0.0? (Kl) a,c,d,e,f same as above
O.?0 (K2) a,c,d«e,f same as above
0.01 (residue) — PCB"s were found in hlqher
concentrations than organoch 1 or ine
pesticides In all fish analyzed. The
authors point out that PCB is less toxic
In an acute sense than orqanoch I or 1 nes.
that little is known of sublethal PCB
distribution and effects Is needed.
0.03 (residue) — same as above
0.002 — same as above
(residue)
0.003-0.006 — - same as above
(residue)
0.001 — same as above
(residue)
Refer ence
Konar
(1970) , AMIC-
I.I.B
Konar
(1970) ,AHIC-
1.1.9
7. Itko
( iq7i ) ,
AMIC-371^
71 tko(1971) ,
AHIC-371S
71tko(1971>,
AMIC-3711;
71 tko
( 1971) ,
AMIC-3715
?ltko
(1971) ,
AMIC-3715
HexachIorod1 me thy I Phormldlum L
sulfon* amblquum
0.5-10.0 (NTE) —
Of 71* chemicals evaluated as
alqlcioes, only 9 were more toxic than
CuSOi*. None Inhibited growth of
iflat-forminq alqae for more than ? weeks*
CuSOi* formulated with certain wettlnq
aqents was more toxic than CuSOi* alone.
Cooper chloramlne was also found to be
more toxic than CuSCli.. No wetting aqents
were found to be Inhibitory at the
concentrations investigated (0.05 and
0.005 pom). Also reported are factors
affecting growth of algae In canals to
determine whether there Here leads to
controlling algae by environmental
AHIC-892
-------
fO
Hexadecanol
(Praoarat Alfol HV
10)
Hexadecanol
(Praparat Alfol HV
ID)
Hexadecanol
(Praoarat Alfol HV
10)
Hexartecano I
(Praoarat Alfol HV
10)
Cooeoods
BSA
(NTE)
Daohnla
BSA
Tublflclds BSA
leblstes BSA
retlculatirs
(NTE)
(NTE)
(NTE)
management. No practical environmental
means were found.
The formulation Has applied to Hann
the water surface at concentration levels (1971),AMIC-
to yield a more or less continuous 3079
monomo lecular layer. Gerrls and other
surface-oriented aquatic Insects as well
as Insect larvae that surface to breathe
and hatch could not maintain themselves
at the surface and therefore sank and
suffocated.
same as above
same as above
same as above
Hann
(1971),AMIC-
3079
Mann
(1971).AHIC-
3079
Mann<1971),
AMIC-3079
Hexadecanol
(Praoarat Alfol HV
10)
Hexadecanol
(Praparat Alfol HV
10)
HiMvale Fly dip
Salmo BSA
galrdnerl
Gerrls
BSA
Rasbora BCFA
heteromorpha and
BSA
(NTE)
(Suffocation)
2.1 (Tl)
same as above
same as above
Hlstanlne phosphate
Neqaorlon
brevlrostrls
(1-3 Kg)
BSA
i»8 (NTE
hr)
a*,Cj6,f, One hundred sixty-four
hard (HW) pesticides, wetting aqents, and
Or soft miscellaneous water pollutants showed a
(SW) oyn- wide range of toxlclty scanning 12 orders
thetic of magnitude. Knowlnq the toxiclty and
water, or percentaqe of all components of a
seawater formulation did not result in easy
for acme predictability of th» toxlclty of a
Opeclea 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.
a,c,e Data from study of drug effects
on vounq lemon sharks wore treated
mathematically to demonstrate
applicability of classical rate theory to
the study of chemical shark deterrents.
Mann
(1971),AMIC-
3079
Hann
(1971),AMIC-
3079
Alabaster,
(1969),A*IC-
Baldrldge
(196^1,
AMIC-3832
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Organism Study Location Pom
Hobstone OSO Cpangon BSA — 1.0-3.3 (T2)
crangon
Expepimenta
Variables,
Control 1 ed
OP Noted
a«( contin-
uous aer-
ation, sea-
Comments Reference
Incaoacl tat 1 on (narcosis) Has the orlraapy
parameter timed Top effectiveness. This
was usually quite Paoid f OP the mope
effective dPugs.
One hundPed-f opty surface active PoPtnann, et
agents, solvent emulslfleps, Destlcldes, al (1971),
pol ychloplnated biphenyls, pure AHIC-77H1
fO Hoc SC 1700
CPangon
CPanqon
BSA
330-1000 (T2)
Steelhead
tpout
(fIngerlInqs)
BSA —
3.2 CT
Eoll-Chen 622
Houihtosolv*
Cohd salmon BSA
(ringerlings) In
situ
Hood Canal,
Hoodsport,
Wash.
0.1 (K)
CPangon
cPangon
BSA
10-33 (T2>
PoPtmann, et
al <1971),
AMIC-7701
water, and Inorganic, and organic chemicals were
daily evaluated against as many as ten marine
solution opq^nisms. The authors noted that most
renewal) oubllshed data of this tvoe deal with
toxlclty of chemicals to freshwater
organ isms.
a*-(contin- One hundPed-fOPty surface active
uoua aer- agents, solvent emulsifleps, pesticides,
ation, goa-POIvch IOPInated biphenyls, cure
water, and Inorganic, and organic chemicals were
daily evaluated against as many as ten marine
solution opganisms. The authors noted that most
published data of this type deal with
toxlcity of chemicals to fpeshwatep
opgan1sms.
Fvaluatlon of 11 oil disoepsants Tpacy, et
resulted In a ranking fOP each and a al(1969),
recommendation f OP use according to the AMIC-383i(
pankino. Ranking Mas based on toxicity
and oil dispersal effectiveness. CoPexlt
776<» appeared to have the least toxlclty
with faip to good oil dispersion
caoabl11ty.
renewal)
same as above
a«(contin- One hundred-foPty surface active
uous aer- agents, solvent emulslfleps, pesticides,
ation, sea-PO'ychloplnated blphenyls, pupe
water, and Inorganic, and oPganic chemicals xePe
daily evaluated against as many as ten maplne
solution opganisms. The authors noted that most
renewal) published data of this type deal with
toxlclty of chemicals to fpeshwatep
Tracy, et al
(1969),
AKIC-383U
PoPtmann, et
al (1971),
AMIC-7701
-------
organisms.
Hydrochloric acid
Hydrochloric acid
ro
Hydrochloric acid
Brook trout
Brachycentrus BCFA
americanus
(larvae and
nymphs)
Ephemerelta
suhvar la
(larvae and
nymphs)
BCFA —
pH 3.? (SB<»)
pH 1.21-1.8 a,c,d,e
pH a,c,d,e
i».35-S.OS) a,c,d,e
pH 3.07-3.1*8 a
-------
Compound
Hydrochloric acid
Hydrochloric acid
Hydrochloric acid
Field Field
Organism Study Location
( 1 arva* and
nymphs )
Isogwnus BCFA
fronta 1 Is
(larvae and
nymphs)
Pteronarcys BCFA —
dorsata
( 1 *rv*e and
nymphs)
Carclnus BSA -—
i»aenas
Toxicityt Experlmenta
Active Variables,
Ingredlentt Controlled
Ppn» or Noted
DH 3. 30-1.. 0". a.c.d.e
(TU
DH 3. 90-1.. 73 a.c.d.e
IT«.»
ZfcO (T2) a»( contin-
uous aer-
Comments
same as above
same as above
agents* solvent emulslflerst pesticides*
ation. sea- D° 'vch lorlnated blphenyls, pure
Hydrochloric acid
Crangon BSA --
cr anqon
water, and
dally
solution
renewal )
26° (T2) a«(contin-
uous nor-
aticn, sea-
water, and
daily
solution
renewal)
Inorganic, and organic chenlcals Here
organisms. The authors noted that most
published data of this type deal nlth
toxlclty of chemicals to frashxater
organisms.
same as above
Re f er ence
AMIC-S9BB
Bell, et al
(l^&o) ,
AMIC-598H
Bel 1 , et al
(1969) ,
amc-^gss
al (1971),
AMIC-7701
Portmann, et
al (1971),
AMIC-7701
Hydrogen sulflde
Esox luclus
(eggs)
BSCFA —
0.030-0.03?
Laboratory studies were designed Adelnan, et
to test the effect of hydrogen sulflde on al 11970),
plKe eggs and sac try and the effect of AHIC-5516
oxygen concentrations on hydrogen sulflde
toxlclty. Eggs subjected to hydrogen
sulfide produced a higher percentage of
sac fry with anatomical malformations.
Sac fry hatched from eggs held at the
higher hydrogen sulflde concentrations
were smaller than the controls. Sac fry
subjected to hydrogen sulfide showed
decreased gronth rates at the higher
concentrations. The level of dissolved
oxygen Has significant only In relation
-------
Hydrogen suit Me
Hydrothol
Hydrotnol 191
Esox luclus
(sac fry)
Leoomls
•icrolophus
Gammarus
fasclatus
0.009-0.026
BSCFA —
FP Tlshomlnqo, 0.03-0.3
Ok la. (SBli.)
atC.e
8SA
0.1.8
Hydroxyacetle acid
(glycollc acid)
Phormidlu*
amblguum
0.5-10.0 «NTE) —
to mortality of sac fry. Experiments
Hlth Dike eggs Indicate that hydrogen
sulflde and oxygen acted Independently In
causing mortality.
same as above
Adelman, et
at (1970).
AMIC-5516
HZS1F6 (as
FLUORIDE)
Gammarus
pseudo-
llonaeua
BCF
0.08-0.13
-------
ro
Conoound
H2SIF* (at
FLUOPIOE)
TJLI
la line brushvecd
Kl ll«r
I»l|n« qrast growth
r«qul»tor (Regulox)
lallnc verglclde
•••dklllcr 0
Organism
Plmephales
pro He I as
Wolfria
papullfera
Sal mo
galrdnerl
Sal no
galrdnerl
Sal no
galrdnerl
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Study Location Ppm or Noted Comments
BCF
!>
BCFA —
and
BSA
BCFA —
and
BSA
BCFA —
and
BSA
0.8-0.13 (NT) a',c,d,e,f
,r*,s
100 (K) Hunter's
medium
diluted
1:5
?7 (T2) a*,c,e,t.
hard
(HM> or
soft (SW)
syn thetic
dilution
nater, or
seanater
for some
spec ies
66 (T2) a>.c.e,f.
hard (HW)
or soft
(SW)
synthetic
dilution
water, or
aeawater
for some
species
3.3 (TZ) a»,c,e,f.
hard(HH)
or soft
(SW)
synthetic
dilution
nater, or
seawater
for some
species
same as above
All compounds were harmful to
duckweed to somo decree. Decreased
populations wore noted (it non-lethal
concentrations and some compounds
(Halatblon and 2,14,-D) caused teratogenlc
effects at concentrations aa low ai 1 ppn,
One hundred sixty-four
pesticides, wettlnq aqents, and
miscellaneous water pollutants showed a
Hide range of toxlclty spanning 1? orders
of magnitude. KnoHinq the toxlcity 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 water
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to b« essential.
sane as above
sane as above
Reference
Arthuret al
(1971) ,
AMIC-3Z90
Worth! ey, et
al (197D,
MHC-3233
A 1 abaster
(1969) ,A»1IC-
5*»25
Alabaster
(1969) ,
AHIC-5i,?5
Alabaster
(1369), AHIC-
S«.Z5
-------
lodoacetlc acid
Phormldlum
••blquuK
• rT
0.5-10.0 (100
percent growth
Inhibited !<•>
Toxynll Na
Pasbora BCFA
heteromorpha and
BSA
68 (T2.
hardnater)
lexynll Na
Rasbora
heterotiorpha
BCFA
and
BSA
3.3 m,
softnater)
IPC
Gammarus
fasclatus
BSA
19.0 (T<»)
a*,c,e,t f
hard
(HH)or
soft (SHI
synthetic
d11u 11 on
Hateri or
seaHater
Tor some
species
a*,c,e,f,
hard
(HH)or
sott
-------
Conoound
•Organism
Field Field
Study LocatIon
Toxlclty.
Active
Ingredient *
Ppm
Experimental
Variables,
Con trolied
or Noted
Comments
Reference
the TL sub 50 values, ail of the animals
reoresent Important food chain links*
Iron
ro
-J
Iron
Paralabrax
clathratus
Para Iabrax
clathratus
FM Scatterqood <>•> (dorsal
Steam Plant, muscle
Los Angeles, residue!
Cal.
CatalIna 3? (dorsal
Island, Cal. muscle
residue)
Fish col
ploe of a steam
waters of Catall
f or trace elemen
content of the e
least •> times qr
sea Hater for ca
zinc? and chromi
the e T fIuent Her
of those from th
dl f ferences In c
Hl.th aluminum, c
S 11ver, bar I urn,
the I east dl f fer
concluded that t
tissues could be
effect of pollut
lected from an effluent
plant and from offshore
na Island were analyzed
t content. Trace element
ffIuent water was at
eater than that of normal
dmlum, copoer, nlcKel,
u". Livers of fish fron
nearly twice the size
ocean* Greatest
oncentratlon occurred
admlum, and nickel.
lithium, and lead showed
ences. The author
race element analysis of
used to determine the
ants on marine organisms.
same as above
Stapleton
(1968),
AHIC-S980
Stap Ieton
(196fl) ,
AMIC-5980
Iron
Paralabrax FM Scatterqood ^6 (ventral
clathratus Steam Plant, muscle
Los Angeles, residue)
Cal.
same as above
S t aoIP t on
(1968),
SMIC-59B3
Iron
Iron
Paralabrax FM Catal Ina "t* (ventral
clathratus Island, Cal. muscle
residue)
Paralabrax FM Scattergood 83 (gonads
clathratus Steam Plant, residue)
Los Angeles,
Cal.
same as above
same as above
S t a o I e t on
(1968),
AMIC-5910
Staoleton
(196?) ,
AMIC-5980
Iron
Iron
Paralsbrax
clathratus
Paralabrax
clathratus
(gravid
FM
FM
Catatlna 122 (qonads
Island, Cal. residue)
Catal Ina
Island, Cal.
110
(qonads
residue)
sane as above
same as above
S tap Ie ton
(1968),
AMIC-5980
S t a p I e t on
(1968),
AMIC-59SO
-------
females)
fO
-J
VJ1
Iron
Iron
Iron
Iron
Iron
Iron
Paralabrax FM Scatterqood 160 (liver
clathratus Steam Plant, residue)
Los Anqeles,
Cal.
Paralabrax FM natalIna 205 (liver
clathratus Island, Cal. residue)
Paralahrax FM Scatterqood 72 (Integument
clathratus Steam Plant, residue)
Los Angeles,
Cal.
Paralahrax FM CatalIna 72 (Integument
clathratus Island, Cal. residue)
Paralabrax FM Scatterqood <* 80 (heart
clathratus Steam Plant, residue)
Los Angeles,
Hal.
Paralabrax FM CatalIna 6UO (heart
clathratus Island, Cal. residue)
same as above
same as above
same as above
same as above
same as above
same as above
S t a o I e t on
(1968),
AMIC-5980
Staoleton
(lie,!!) ,
AMIC-59SO
Staole.ton
(196S),
AHIC-59SD
Staoleton
(1953),
AMIC-5980
Staoleton
(1968),
AMIC-5980
Staol eton
(196M ,
Iron
Iron
Para Iahrax
ct athratus
Paralahrax
clathratus
Iso-prooyl Rasbora
2,<>,dlnl tro-6-sec-bu heteromorpha
Tylphenyl carbonate
FM
FM
BCFA
and
BSA
Scatterqood 120 (eyeball
Steam Plant, residue)
Los Angeles,
Cal.
CatalIna 165 (eyeball
Island, Cal. residue)
0.02<» (T2)
same as above
same as above
a*,c«e,f. One hundred sixty-four
hard (HH) pesticides, netting agents, and
or soft miscellaneous Hater oollutants showed a
(SW) wide range of toxlclty scanning 12 orders
synthetic of magnitude. Knowing the toxiclty and
dilution percentage of all components of a
water, or formulation did not result In easy
seawater predictability of the toxiclty of a
forsome 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*
S t a o I e t on
(1968) ,
A^IC-5980
Stao I eton
(1968),
AMIC-5950
Alabaster
(1969),
AHIC-51.25
-------
ro
^j
o\
Toxlclty,
Active
Field Field Ingredient,
Coxoound Organism Study Location Pom
I.C.T. 5um«»r sheep Rasbora f)CFA — ii . 1 (T2I
BSA
Jansolv-60 Plmephales BSA — aporox. 56.0
promelas (Ti»)
J»nsolv-60 PImeohales BSA — approx. 7.5
promelas (MSC)
J»nsolv-60 Biochemical L — 350,000
oxygen
demand
Jan-Solv-60 Steelhead BSA — 35.5 (T<>)
trout
(f Ingerl Ings)
Jan-Solv-60 Coho salmon BSA Hood Canal, 0.8 (K)
(finger) ings) In Hoodsport,
Exoer 1 men ta 1
Variables,
Control led
or Noted Comments
a'.c.e, f ,
hard
(HM) or
soft (SH)
syn the t ic
water, or
seawater
for some
species
c.d.e, f
c,d,e,f
c.d.e, f
One hundred sixty-four
pesticides, wettlnq agents, and
miscellaneous water oollutants s h o K e d a
wide rsnoe of toxlclty scanning 1? orders
of magnitude. Knowing the toxlclty and
formulation did not result In easy
oredlctabl 1 1 ty of the toxlclty of a
mixture of materials. Sometimes
pesticides were most toxic In hard water
and sometlires the ooooslte was true.
Testing the actual material as sold was
found to be essential.
Toxlcl ty of six oil spi 1 1
dlsoersants was determined along with
BOO values. Pond water was used as
diluent and oil was Included In the
experiment. Oil markedly reduced
toxlclty of all dlspersants. Data are
same as above
same as above
Evaluation of 11 oil dlspersants
resulted in a rankinq for each and a
recommendation for use according to the
ranking. Ranking was based on toxiclty
and oil dispersal effectiveness. Corexlt
776"t appeared to have the least toxlclty
with fair to good oil dispersion
capabl 11 ty.
same as above
Refer ence
Alabaster,
(1969) .AMIC-
5U25
Zi 1 1 Ich
(1969) ,
7111 Ich
(1969) ,AMTC-
2909
Zil llch
(19P.9) .AHTC-
2909
Tracy, et
al (1969),
Tracy, et al
(1969),
situ Wash.
JugI one
Salmo
qalrdnerl
BSA —
0.0383 (Tit)
bioassays were conducted at 12 C. Harking
The toxlclty of Juqlone to rainbow trout (1970),A1IC-
and bIueglI Is .was not altered 5517
-------
Juglone
Juglone
Juglone
Jugl one
Juglone
Juglone
Juglone
Jugl one
Karnex
Kelthsn*
Esox luelus BSA —
Carasslus
auratus
Cypplnus
capolo
Catostomus
Ictalurus
me I as
IctalUPUS
punctatus
Leooiils
cyanelI us
BSA
BSA
BSA
BSA ~
BSA ~
BSA
Lepomls BSA
macpochlpus
°occus
saxatllls
(f inqerlIngsl
RSA
0.0271
0.060 (TI>)
0.088 (T
0.0367
0.01.69 (Tit)
significantly In waters ot different
temoerature OP haPdness. Standapd (DH
7.<») and buffered (pH 9.0) solutions of
Juglone aqed fop one Heek effectively
killed palnbow tpout although
apopoxlmately thpee times as much Juglone
was required at the hIgheP oH. Juglone
Is ea;lly reduced to less toxic
comooi.ents by factops In the natural
environment. However, Juglone Is
sufficiently persistent to eliminate
target fish.
sane as above
same as above
same as above
same as above
same as above
same as above
sane as above
same as above
Tublfex
tublfex
FL Relzonl,
and Hiss.
3.0
0.50 (NTE)
Harking
Marking
(1970) .
A1IC-5517
Mapklng
«1Q7(!) ,
AMIC-5517
Mapklng
(1970) ,
AMIC-SF17
Marking
(ig70) ,
Marking
(1970) ,
AHIC-5517
Mapklng
(1970),
AHIC-5517
Marking
(1970,
AMIC-S517
a*,c,d,e,f Stploed bass fingeplings wep« Hellbopn
,D and apoapently much more sensitive to (1969),
thepapeutlc and hepblcldal compounds than AHIC-5723
many fpeshwatep fish.
The response of Naavt, et al
pesticide-resistant aquatic organisms to (1969),
-------
Compound
Organic™
Field Field
Study Location
Toxiclty,
Active
Ingredient.
PPIB
Experimental
Variables,
Control Ied
or Noted
Comments
Reference
BS»
Keto«ndrln
Anacystls
nldulans
0.5-1.0 (growth a'.c*
Inhibited) SM
various pesticides was compared to the AMIC-5979
Pesticide-resistant species were
collected at Bclzonl and non-resistant
speclps at State College. Cooepods,
clams, snails, and sludge worms from
Belzonl were considerably more tolerant
to pesticides than the non-resistant
orqanlsms. 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.
Metabolic products of Aldrln, Batterton,
Dleldrln, and Endrln can be as toxic as 8l (1971),
the parent compounds, as shown by 00 AMIC-l
-------
organisms.
Lauryl ether sulfate Cranqon
(plus ethylene crangon
oxide)
BSA
greater thanlOO ae(contln-
(T2) uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmanriiet
a) (1971),
AMIC-7701
L»uryl ether sulfate Carclnus
(olus ethylene maenas
oxide)
BSA —
greater thanlOO a»(oontin-
(T2) uoua aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann.et
al (1971),
AKTC-7701
vo
Lauryl ether sutfate Panda I us
Colus ethytene montagul
oxide)
BSA
greater thanlOO a*(contin-
(T2) uous aer-
ation, sea-
water, and
iaily
solution
renewal)
same as above
Port»ann,et
al <1<171),
AHIC-7701
Lead arsenate
Lead carbonate
Fish
-------
>
ro
Compound
L«ad nitrate (as
lead)
Lead nitrate
Toxiclty, Experiments
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppm or Noted
renewal )
Pandalus BSA — 375 (T2) a*(contln-
montagul uoua aer-
ation, sea-
water, and
daily
solution
renewal )
Carasslus L — 6.6 (T7) a,c
auratus
1
Comments Reference
published data of this type deal with
toxlclty of chemicals to freshwater
organ 1 sms.
same as above Portmann, et
al (1971) .
AMIC-7701
In addition to toxlcity data. Heir, et al
conditioned avoidance response was (1970),
studied at sublethal concentrations. The AMIC-739
lowest concentration of metal resulting
O.lOt |pad, 0.07t mercury, 0.0031 and
selenium, 0.2^. Deleterious effects
occurred at metal concentrations
approximately similar to notable water
s tandards.
Lead sulfate (as
Pb)
Lead sulfate (as
Pb)
Lead sulfate las
Pb)
Lead
Acroneur1a
EohemerelI a
Hydropsyche
Coregonus
clupeafornis
BSA
BSA
BSA —
a*,c,d,e,f
Ephemerella (mayfly) was the most HarnlcKt et
FL
Moose Lake,
Can.
16 (T7)
32 (T7)
0.5 (residue)
sensitive aquatic Insect of those
studied, and copper the most broadly
toxic metal. The authors suggest that
aduatic insects may not be as sensitive
to heavy metals as fish.
a*,Ctd,e,f same as above
a*,c,d,e,f
same as above
Concentrations of 13 toxic
elements In dressed fish from heavily
Industrialized and non-IndustrlalIzed
areas were determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements were
essentially the same In fish froa both
al(1969).
AMIC-3767
HarnlcK, et
al (1969),
AMIC-3767
Harnick, et
al(1969),
AMIC-3767
Uthe, et al
(1971),
AMIC-3819
-------
Lead
L«»d
Lead
Lead
L«»d
Lead
Lead
Coreqonus FL
cluDcaformis
Esox lucius FL
Esox lucius FL
Esox lucius FL
Osmerus
nordax
Perca
f1avescens
Paralabrax
clathratus
Lead
Lead
Papalabrax
clathratus
Paralabrax
clathratus
FL
FL
FM
FM
FM
Lake 0.5 (residue)
Ontario,
Can.
Moose Lake, 0.5 (residue)
Can.
Lake St. 0.5 (residue)
Pierre, Can.
Lake Erie, 0.5 (residue)
Can.
Lake Erie, 0.5 (residue)
Can.
Lake Erie, 0.5 (residue)
Can.
Scattergood 2.1 (dorsal
Steam Plant, muscle
Los Angetes, residue)
Cat.
Catallna 1.3 (dorsal
Island, Cal. muscle
residue)
Scattergood 1.1 (ventral
Steam Plant, muscle
Los Angeles, residue)
Cal.
same as above
same as above
same as above
same as above
same as above
same as above
Fish collected from an effluent
ploe ot a steam plant and from offshore
Haters of Catallna Island were 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 from
the effluent were nearly tnlce the size
of those from the ocean. Greatest-
differences In concentration occurred
Hlth aluminum, cadmium, and nickel.
Silver, barium, lithium, and lead showed
the least differences. The author
concluded that trace element analysis ot
tissues could be used to determine the
effect of pollutants on marine organises.
same as above
Uthe, et al
(1971),
anIC-3819
Uthe, et al
(1971),A«IC-
3819
Uthe, eT
«L(197i),
AMIC-3819
Uthe, et al
(1971).ftMIC-
3819
Uthe, et al
(1971),&MIC-
3819
Uthe, et al
(197J) ,»mc-
7819
Staoleton
(1968),
«HIC-S9»0
same as above
StaoIeton
(1968),
«SIIC-'!9BO
Staoleton
(1968),
AMIC-S980
-------
Cowoound
lead
lead
Lead
> Lead
1
ro
O"»
\JJ
ro
Lead
Lead
Lead
lead
Lead
Lead
Organism
Paral ahr ax
c 1 a thr 8 tus
Paral abrax
cl athratus
Para 1 abrax
cl athratus
Paral abrax
c 1 athratus
(qravlrt
femal ««;)
Paral abrax
cl athrstus
Paral abrax
cl athrafus
Paral ahrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paralabrax
cl athratus
Field
Study
FM
FM
FM
FM
FM
FH
FM
FM
FM
FM
Flel A
Locat 1 on
Catal Ina
Is) and, Cal .
Sea 1 1 ergood
StPam Plant,
Los Angeles,
Cal.
Catal Ina
Is land, Cal .
Catal 1 na
Island, Cal .
Scat t erqood
Steam Plant,
Los Anqeles,
Cal.
Catal ina
Isl and, Cal .
Scat terqood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Scattergood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted
1.3 (ventral
muse 1 e
residue)
2.3 (qonads
residue)
?.? (gonads — •
residue)
1.3
(gonads
residue)
0.7 (liver
residue)
1.5 (liver
residue)
1 (Integument --
residue)
1.6 (Integument — •
residue)
1.3 (heart —
residue)
0.9 (heart
residue)
Comments
same as above
same as above
same as above
sane as above
same as above
same as above
same as above
same as above
same as above
sane as above
Refer ence
S t a o 1 e t on
1 196M ,
AMIC-59M
Stan 1 eton
( 19^8) ,
AMIC-5960
S taol e ton
( 19&P) ,
AMIC-S9BO
Slav t eton
(196S) .
AMIC-5955
S t a D 1 <> f on
(1968) ,
AMIC-'igflO
Staol eton
ilic-Ueo
Staol eton
(1968) ,
AMIC-5980
Staol eton
(1968) ,
AMIC-S980
S t a o 1 e t on
(196S) ,
AMIC-S98Q
Staol eton
(1968) ,
AMIC-5980
-------
L«ad
Lead
Paralabrax FH Scattergood 2.2 (eyeball
clathratus Steam Plant, residue)
Los Angeles,
Cal.
Paralanrax
clathratus
Llndane (gamma BHC) Fish (net
specified)
Llndane
U)
Llndane
Lepomls
cyanellus
(Resistant)
FH Catallna 3.
BSA
1.93 (T2)
a»
Leoomls
cyanellus
(Susceptible)
BSA
0.05 (T2>
same as above
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.
Staoteton
(1968),
AHIC-5980
Stapleton
(19ft*) ,
AHIC-5980
Haxdesley-Th
oaas (1971
ANIC-10S6
Green suntlsh Irom Belzonl, Miss. MInchen, et
were resistant to Chlordane, Heptachlor, 31(1970),
Llnrtane, and Strobane, but not to ANIC-5it71
Parathlon. Golden shiners from the same
location were resistant to Lindane and
Strobare, tolerant to Chlordane and
Heotachlor, and susceptible to Parathlon.
Lack of resistance to Parathlon
Indicated lack of agricultural usaqe of
organochosphates In that area. Resistant
fish were compared to susceptible ones
collected at StarKvllle.
same as above
HInche*, et
al(1970),
AMIC-51,71
Llndane
Llndane
Notemlgonus
crysoleucas
(Peslstant)
Notemlgonus
crysoleucas
(Susceptible)
BSA
BSA
(T2)
0.15 (T2)
same as above
same as above
Mlnchex, et
al(1970),
AHIC-51,71
Hinchew, et
al(1970),
AMIC-51,71
' Llndane
Ictalurus
punctatus
BSA
0.0>fi» (T
-------
ro
Compound
Llndane
Llndane
Llndane
L 1 ndan*
Llndane
Llndane
Llndan«
Llndane
Llndane
Llndane
Field Field
Orqanlsm Study Location
Ictaturus BSA --
"el as
Carasslus BSA
aur a tu^
Cynrlnus ISA ~
carplo
Pl-«ephal«»« RSA
prone 1 as
Lepomls BSA
macrochlrus
Lepomls BSA -—
nlcrol ophus
Mlcropterus BSA —
sal mo Ides
Salmo BSA
qalrdnerl
Salrno trutta BSA
Oncorhynehus BSA —
Klsutch
Toxicl ty.
Active
Ingredient,
Ppn
D.06I.
0.131
0.090
O.OS7
0.068
0.083
0.032
0.027
0.002
0.041
(Ti»)
(Ti.)
IT",)
-------
Llndann
Llndane
QJ Llndane
vn
Llndan*
Llndane
Perea
fIavescens
Pataemonctes
kadlakenils
(resistant)
BSA
BSA
0.068
0.01I.-0.0373
(Tl)
same as above
synthetic
test Hater
Palaenonetes BSA
(non-
re ai stan t)
Moron*
saxatiI Is
(fInqerlIngs)
BSA
0.0051 (Tl)
II.It (Tit)
a,c,d,e, fi
P
Copeoods
(CvcIops
blcuspidus,
Cycloos
var1cans,
Cyclops
vernal is,
EucyclCDS
aql11s,
Macroeyclopa
albldus,
Orthocycloos
fflodestus)
FL
and
BSA
State
College,
Hiss.
0.60 (K2>
Vacek, etal
(1970),
AHIC-5510
Bioassays were conducted with Naavi, et at
shrimp from three areas of Intensive (1970),
pesticide use and from an unexoosed area. AMIC-5519
Previously exposed shrimp were from 1 to
?•; tltres more resistant than unexposed
shrimp. Both type*: of shrimp Here also
exoosed In cages to waters of the
contaminated areas. Susceptible shrimp
suffered 66 percent more mortality than
did resistant shrlmo. The toxlclty of
the insecticides ranked in descending
order was as follows? most toxic,
Endrln, COT, Methyl parathion, Parathlonl
medium toxicity, Guthlon, Lindane,
Toxanhene, Strobanpi lease toxic
Chlordane, Sevln, and Heotachtor.
same as above
Naavi, et al
(197D),
AHIC-5519
fill compounds were Investigated Wellborn
because of their probable usage In (1971),
hatchery production of white bass. AHIC-5571
CoiioouPds that can be used at recommended
concentrations were Aquathol, Casaron,
Llndane, and Terramycln concentrate.
Those that should not be used were
Acrlflavine, Oaylusclde, Malachite green
oxalate, and Malathion.
The response of
pesticide-resistant aquatic orqanlsms to
various pesticides was comoared to the
response of non-resistant species.
Pesticide-resistant scecles were
collected at Belzoni and non-resistant
species at State Colleqe. Cooepods,
clams, snails, and sludqe worms from
Belzoni 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.
Naavi, et at
(19f>9) ,
AMIC-5979
-------
Co»ooun-l
Llndan*
L 1 ndane
Llndane
Organ I sit
Conpoo'ls
(Cy c 1 ons
bicu^oldus.
Cyr 1 oos
var 1 c ans *
Cyc 1 oos
vernal Is.
Eucycl oos
aql 1 Is,
Hacrocyclops
a 1 h 1 rius,
Or thocycl oos
modes t us)
Tub 1 (ex
tubl f ex
Mercenar [ a
mercenar 1 a
(eggs)
Field Field
Study Locat Ion
FL Relzonl,
and Miss
BSA
FL Relzonl,
and Miss.
BSA
I
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted Comments Reference
0.60 (87 — same as above Naavl, et at
Dercent K?) (19fi91 .
ANIC-5979
"t.O embryonic develoompnt of clafns and 81(1^69),
oystprs was reoorted. Synprglstlc AHIC-599H
Lindane
LJndane
Lindane
Mercenarla
mercennr1 a
(Iarvse)
Cf^ssos trea
vlrginlca
(eqgs)
Gamhusla
af fInls
(female,
BSA
greater than
10.0 III?)
9.1 (T2)
0.13 (U)
effects with solvents nerp also reported.
Most cf the compounds affected
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 ppst control that
would not have serious effect on
shel I f ish.
same as above
same as above
a,c,d, The five fish species are
Sjfjly commonly found In streams and estuaries
(Honolulu In seml-troolcal areas. G. afflnls was
Davis, et
al (19159),
AMIC-5991
Davis, et al
(1959) .AMIC-
5990
Nunogaua, et
al (1970),
AMIC-6567
-------
Llndnne
Llndane
Llndane
Llndane
Linear alKylate
sultonate
Linear alKylate
sulfonate
cm, 1.9 q)
Lehlstes BSA
retIculatus
(male, 1.8
cm, 0.2 q)
Tilapia BSA
Boasambic*
(3.14. cm,
1.3 Q)
Kuhlla BSA
sandvicenais
14..3 cm,
1.5 O)
Stolephoru'a BSA
purpurea (3.6
en, O.k G)
Plmeohales
promeI as
BCFA --
0.05
0.06
0.0k
0.001).
(T 12 hr)
U.2-I..5
PImenhales
oromelas
8CFCH —
0.63 (NTE)
tap the most tolerant. Varied sensitivity to
water) the toxicants were found. K.
sandvlcensls was the most sensitive » Ish
studied. The standard method procedure
Has foil owed.
a,c,d, same as above
8,f,i,
(Honolulu
tap
water)
a»c,d,e,f,l game aa above
(Honolulu
tap water)
a,c,d,G,f,i, same aa above
, salt water
a,o,d,e,'f,i, same aa above
salt water
a*,c,d,f*. Acute and chronic toxlclty
l,)»n, studies resulted In a laboratory 1 I sh
maqneslum, Lethality of LAS to newly hatched fry was
sodium, the most critical factor with no effect
potassium, at O.'S ppm on spawnina eqq production, or
sul fate, hatchabllity at this concentration. A
beryllium, funqus infection of mature wales occurred
strontium, and was controlled by means of
Iron, antibiotics. No accumulative mortality
boron, occurred. The application factor Has
barium, calculated to be between li» and 28
aluminum, percent. The concentration of 0.63 com
zinc. Has determined to be the maximum
copper, acceptable concentration of LAS tor
cadmium fatheads.
a»,c,d,f», same as above
1,1 in.
calcium.
maqnesium,
sodium.
potassium.
su! fate,
bery 1 1 ium.
strontium.
iron.
boron.
barium.
aluminum.
zinc.
Nunogawa, et
al (1970),
AHIC-6567
Hunogawa, et
al (1970),
AKIC-6567
Sunogawa, et
al (197C),
AKIC-6567
Nunogawa. et
al (1970),
AKIC-6567
Picker Inq,
et al C197Q),
& H T f*— fi^
M n I L. D~
P icker inq.
etal (1970) •
AHIO65
-------
Compound
Llnuron
Llrostanol
Llssaool I PA
Lltsaool NM
llssaool NX
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppm or Noted Comments
copper,
cadmium
Fish (not — — greater than -- Approximate toxlcltles of
specified) 10-100 (K) numerous pesticides commonly used In
brief, general discussion of toxiclty
testing Is also present.
Rasbora 8CFA -- O.O**1* (T2) a»,c,e,f. One hundred sixty-four
heteroporpha and hard (HH) nest 1 c Ides, wettlnn annnt-:, nnti
BSA or miscellaneous water ootlutants showed a
SOFTISH) wide range of toxiclty scanning 12 orders
synthetic of magnitude. Knowing the toxicity and
dilution percentage of all components of a
water, or formulation did not result In easy
seawafer predictability of the toxiclty of a
species pesticides were most toxic In hard water
and sometimes the opposite Mas true.
Testing the actual material as sold was
found to be essential.
Crangon BSA — 1000-3300 (T2) a«(contin- same as above
crangon uoua aer-
ation, sea-
water, and
dally
solution
renewal }
Crangon BSA — 330-1000
-------
Llssaool NX
Crangon
cranqon
BSA
1000-3300 (T2)
Lithium
Paralabrax
clathratus
FH Scatterqood 6.9 (dorsal
Steam Plant, muscle
Los Angelest residue)
Cal.
Llthiua
Llthiua
Llthlun
LItMu-
Paralahrax
elathratus
Paralahrax
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
FH Catallna 6.2 (dorsal
Island, Cal. muscle
residue)
FH Scatterqood 6.7 (ventral
Steam Plant, muscle
Los Angeles, residue)
Cal.
FH Catallna 5.6 (ventral
Island, Cat* muscle
RESIDUE)
FH Scatterqood 8.6 (qonads
Stea* Plant, residue)
dilution percentage of all components of a
Hater, or formulation did not result in easy
seawater predlctabl11ty of the toxlclty of a
for some mixture of materials. Sometimes
soecles 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«-(contin- One hundred-forty surface active
uous aer- agents, solvent emulslfiers, pesticides.
ation, aea-n°l>'chl lorlnated biphenyls, oure
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.
—- Fish collected from an effluent
pioe of a steam plant and from offshore
waters of Catalina Inland were analyzed
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, copper, nicKel,
zinc, and chromium. Livers of fish from
the effluent were nearly twice the size
oT those from the ocean. Greatest
differences In concentration occurred
with aluminum, cadmium, and nickel.
Silver, barium, lithium, and lead showed
the lesst differences. The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on marine organises.
same as above
sane as above
San* as above
sane as above
Portmann, et
al (1971),
AMIC-7701
Staoleton
(1968),AWIC-
5980
Staoleton
(1958),
AMIC-5980
Staoleton
(1968),
AMIC-S9SO
Stapleton
Staoleton
(1968),
-------
Covoound
LI thlun
LlthluB
Lltnlua
L 1 tf* IUB
Litnlu-
Llthlua
Llthlu"
Llthlua
Llthlua
Llthlua
Organism
Paral abrax
cl athratus
Paral abrax
cl athratus
(qravld
femat es)
Par al ahp^x
cl athrntus
cl athratus
Paral ihrax
cl athratus
Par at abrax
cl athratus
Paralabrax
c 1 athratus
Parat abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
clathratus
Field
Study
FM
FH
FM
F M
FM
FM
FM
FM
FM
FM
Field
Loot Ion
Los «nqeles,
Cal.
Catal ina
Tslandt Cal .
Catal Ina
Is) andi Cal .
Sea 1 1 erqood
Steam PI ant v
Los Anqeles,
Cal.
Catal Ina
Isl andt Cal .
Scat t erqood
S tpam P 1 ant v
Los Angelest
Cal.
Catal Ina
Isl and. Cal .
Scatterqood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Scattergood
Steam Plant,
Los Angeles,
Cal.
Catat Ina
Island, Cal.
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppn or Noted
8.1» (gonads --
residue)
7.7
(qonads
residue)
S.8 (1 Iver
resi due)
7.3 (1 1 wer — —
residue)
6.8 (Intequment —
residue)
7.7 (Integument --
residue)
7.6 (heart
resi due)
8.5 (heart
resi due)
580 (eyeball
residue)
!?<• (eyeball
residue)
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
Reference
AMIC-SqgO
S tao 1 e ton
(1°M) ,
AMIC-S180
S t a o 1 e t on
(196?) ,
AMIC-5980
S t ao 1 e t on
( 19MM ,
AMIC-59BO
S t ao 1 e t on
(19
-------
AMIC-5980
Lubrot APNS
Cardiun edule BSA
10-33 (TZ)
Lubrol APNS
Crangon
crangon
BSA
33-100
uouti aei'-
Qtlon, sea
water, o;id
daily
solution
renewal)
a«(contln-
uoua aor-
Qtlon, 30Q-
wator, and
daily
solution
renewal )
One hundred-f opty surface active
agents, solvent emulsl f lers, pesticides,
pol ych lorlnated biohenyls, DUPC
Inopqanlc, and organic cherrlcals were
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal Mlth
toxlclty ot chemicals to freshwater
organisms.
same as above
Portmann, et
al (1971),
AMIC-7701
Portmann, et
al (ig71),
AHIC-7701
Lubrol I
Rasbora BCFA
heteromoroha and
BSA
16
-------
ro
Compound
Field Field
Oraanlsm Study Location
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted
Comments
given as "most probable"
Magic Poner
MaqlC P0«er
Magnesiu"
Plmephales BSA
promel as
Biochemical L
oxygen demand
Paralabrax FM
cl athratus
—
__
Scatterqood
Steam Plant,
Los Angeles,
Cal.
2.7 (MSC) c.d.e.f
880, 000 c,d,e, f
1670 (dorsal
muscle
residue)
pipe of
waters
same as above
same as above
Fish col 1 ected fr
a steam plant and
of Catal Ina Is land
for trace element content
least 5
96-hr TL sub n.
om an effluent
from of f shore
were analyzed
. Trace element
Reference
71 1 1 Ich
(1969) .AMIC-
21 1 1 leh
(1969) ,
AMIC-Z9D9
S t ao 1 e t on
(1968) ,
A1IC-59BO
times areater than that of normal
the effluent were nearly
differences in concentrat
twice the si ze
ion occurred
with aluminum, cadmium, and nickel.
Sllv-r,
barium, 1 1 thlum.
and lead showed
the least differences. The author
Magnesium
Naqnes 1 un
Maoneslu"
Magneslu"
Para 1 abr ax FM
cl athratus
Par at abrax FM
cl athratus
Paral abrax FM
cl athratus
Paralabrax FM
cl athratus
Cat a 1 1 na
Island, Cal.
Scattergood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Scat t erqood
Steam Plant,
Los Angeles,
?190(rtorsal
muse 1 e
residue)
1820 (ventral
muscle
residue)
2190(ventral
muse 1 e
residue)
1010 (gonads
residue)
tissues
effect
cou 1 d be used t o
determine the
of pollutants on marine organises.
same as above
same as above
same as above
same as above
S tap 1 eton
(1968) ,
A^IC-^980
Stapleton
(1968) ,
AMIC-S980
Staol eton
(195S) ,
AMIC-S9SO
Staol eton
(1968) .
AMIC-S980
Cal.
-------
Magneslun
Paralabrax FH Catallna 2i>20(gonads
ctathratus Island, Cal. residue)
sane as above
S t a o I e t on
(1968).
AMIC-5980
Magnesium
Hagneslu*
Hagneslun
Paralabrax FM Catallna
clathratus Island, Cat. (gonads
(gravid residue)
re«ial es)
Paralabrax FM Scattergood 690 (liver
clathratus Steam Plant, residue)
Los Angeles,
Cal.
Paralabrax FM Catatlna 1 DM) (liver
clathratus Island, Cal. residue)
same as above
same as above
same as above
S t a o I e t on
(1063),
AMIC-5981!
Staoleton
(1968),
AMIC-5980
Staoleton
(1<>68) .
AMIC-5993
U>
Magnesium
Magnesium
Paralabrax FM Scattergood 73D (Integument
clathratus Steam Plant, residue)
Los Angeles,
Cal.
Paralabrax FM Catallna 8i>0 (Integument
clathratus Inland, Cal. residue)
sane as above
same as above
S t a o I e t on
(19681.
AH.IC-5980
Staoleton
(los^l.
AMIC-S93!)
Magnesium
Magnesium
Paralabrax FM Scattergood 1280 (heart
ctathratus Steam Plant, residue)
Los Angeles,
Cal.
Paralabrax FM Catallna 950 (heart
clathratus Island, Cal. residue)
same as above
same as above
Staoleton
(1968),
AMIC-S989
S13 o I e t on
(19631,
AHIC-5980
Magneslun
Magneslua
Malachite green
Paralabrax FM Scattergood 1080 (eyeball
clathratus Stean Plant, residue)
Los Angeles,
Cal.
Paralabrax FM Catallna 1<»70 (eyebal I
clathratus Island, Cal. residue)
Pasbora BCFA —
heteromorpha and
BSA
0.*6 (Tl,
hardHatar)
sane as above
sane as above
Staoleton
(196?),
a*,c,e,f. One hundred sixty-four
hard (HH) pesticides, wetting agents, and
or soft miscellaneous water oollutants showed a
(SH) Hid* range of toxlclty soannlng 12 orders
synthetic of magnitude. Knowing the toxlclty and
dilution percentage of all conoonents of a
water, formulation did not result in easy
Staoleton
(1968),
AMIC-5980
Alabaster(l9
69) .
AMIC-SAZS
-------
Compound
Field Field
flpqanlsm Study Location
Toxlcity,
Active
Ingredient,
Ppm
ExpePI mental
Variables,
Control Ied
or Noted
Comments
Ref erence
or seawatep ppedl c tabl I 1 ty o( the toxlclty of a
for some mixture of matePials* Sometimes
species pesticides were most toxic In hard water
and sometimes the ooooclte Has tpue»
Testinq the actual material as sold Has
found to be essential.
Nal»chlt« areen
"asbora
hetepomoppha
BCFA
and
BSA
ro
Malachite grttn
Sal mo
qa Ipdnopl
BCFA
an-1
BSA
Malachite qreen
PasboPB
hetepomoppha
BCFA
and
BSA
Malachite qrcen
RasboPa
hetepomoppha
BCFA
and
BSA
O.OS (Tl,
sot tHatep)
0.09 (T2,
hapdxater)
0.17 (Tl,
haPdxatep)
0.1
-------
Malachite green
ro
\O
Halathlon
Halathlon
Malathlon
Morone
saxatII Is
M Ingerl Inqs)
BSA
0.3 (Tl>
Fish (not
specified)
LePOmls
macrochlrus
fiCFCH —
greater than
0.1-1.0 (K)
0.028 (K5I.)
Leoomls
macrochlrus
BCFCH —
0.066 (K16)
Mater,
or seaHater
lor some
species
a,c,d,e,f,
a,Cidte,t,
conduc-
tivity
a,c,d,e,f,
conduc-
tivity
All compounds Here Investiqated Wellborn
because of their probable usage In (1971),
hatchery production of white bass. AMIC-5571
Compounds that can be used at recommended
concentrations were fiauathol, Casaron,
Llndane, and Terramycln concentrate.
Those that should not be used were
Acrlflavlne, Baylusclde, Halachlte green
oxalate, and Halathlon.
Approximate toxlcltles of Hawdesley-
numerous pesticides commonly used In Thomas
Britain were summarized. An excellent (lO'l) , AMIC-
brlef, general discussion of toxlclty 1056
testing Is also present.
Plueqills were exposed to seven Eaton
concentrations of Halathlon from 0.00125 (197C),
to 0.08 ppm. Fish soawned under the test AMIC-131?
conditions and the effects were noted In
all life stages. Reoroductlon and early
try survival were unaffected by the
0.007
-------
r
Co«oounrJ
M»l»thlon
Malathlon
Malathlon
Matathlon
Malathlon
Toxlcity, Exoerlmental
Active Variables,
Field Field Ingredient, Controlled
Orqxnlsn Study Location Ppm or Noted Comments
toxlcl ty.
Salvellnus BCFA ~ 170.0 (Ti.) a«,o,d, same as above
fontlnalls *,f,l,O,
I?. IS q) aulfate.
copper.
nnnjjanese.
Iron, and
chromium
Sal mo clarkl BCFA -- 0.15 (Ti») a»,o,d, same as above
(0.73 q) e,f,l,o.
aulfete,
copper,
manganese.
Iron, and
chromium
Salmo clarkl BCFA — 0.20 (T<>> a»,c,d, sane as above
(1.75 q) e,f,l,0,
aulfate,
copper.
manganese.
Iron, and
chroralum
Salmo BCFA — 0.12 (T<») a»,c,d, same as above
qalrdnerl e,i",l,o,
(O.iil q) aulrate.
copper,
manganese,
Iron, and
chromium
Oncorhynchus SCFA -~ 0.265 (T
-------
f
rv>
53
Halathion
Halathion
Halathlon
Malathlon
Hafathlon
Malathlon
Halathlon
Halathlon
Catostomu*
connersonl
P«rca
flavescens
Esox nlqer
Notemlqonu*; L
crysolwjcas
Pineohales BSA
promelas
0.010 (SB)
0.010 (SR)
0.010 (SB)
0.010 (SOI
16.0 (Tit)
a»,d,e,o,
and Fe
PJmephales BCFA
promelas
Puntlus tlcto --
11.0 (TIM
0.007
-------
Toxlclty,
Active
Field Field Ingredient,
Compound Orqanlsm Study Location Ppm
ExPer 1 men ta 1
Varlabl es,
Control 1 ed
or Noted
seawater predlctabil
for some mixture of
species pesticides
Comments
1 tv ol the toxlcl tv of a
materials. Sometimes
were most toxic In hard Mater
R ef er ence
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
Malathlon
ro
Malathlon
Ic talurus
punctatus
BSA
8.97
-------
test water
AHIC-5519
ro
Malathlon
Halathlon
Halathlon
Malathlon
Halathlon
Malsthlon
Halathlon
Malathlon
Halathlon
Hlcrooterus BSA
salmoldes
Sal mo
galrdnerl
8SA
Salmo trutta 8SA
Oneorhynchus 8SA
klsutch
Perca
fIavescens
8SA
Horone
saxat 11 is
(fInqerlInqs)
BSA
0.28?
0.170
0.200 (TI>)
0.101 (TV)
0.263 (Tfc)
0.2<> (T
same as above
same as above
same as above
same as above
same as above
HaceKtet al
(1970) ,
Maceh, etal
(1970),
AMTC-5510
Macek, et
al (1970),
AMIC-S510
Hacek.et al
(1971) ,
AMIC-551B
KaceK, etal
(1970) ,
AMIC-5510
All ccmoounds were investigated Wellborn
because of their probable usage in (197D,
hatchery production of white bass. AMTC-5571
Comnounds that can be used at recommended
concentrations were Aquathol, Casaron,
L Indane, and Terranycin concentrate.
Those that should not be used were
Acrlflavlne, Raylusclde, Malachite qreen
oxalate, and Halathlon.
Malathion residues In carp Bender(1969),
occurred primarily In the liver and flesh AHIC-5731
with lesser amounts in the brain, blood,
and gills. Retention time was relatively
brief with most of the residue passing on
or beinq metabolized within 1-2 days.
Metabolism in the fish foreaut,
degradation biochemically, and lack of
uptake due to low permeability were cited
as possible explanations for the results
obtained. Lack of persistence in fish
coupled with slow hydrolysis In the
environment seem to Indicate that this
compound has desirable characteristics
regarding safety to humans.
same as above Pen
The response of
AMIC-5731
Naavl, et al
-------
Toxlclty. Experimental
Act Ive Van 1ables.
Field Field Ingredient, Control led
Co*Dound Organism StudyLocatlon Ppm orNoted Comtnents Refer en ce
(Cyclops and College* pestle I de-res 1st ant aquatic orqan Isms to (1969),
blcusnldus, BSA Miss. various pesticides was compared to the ANIC-5979
Cvcloos response of non-resistant species.
vnrleans. Pestleide-reslstantsoecles were
Cyclons collected at Relzonl and non-resistant
vern*I 1 s» species at State College. Copepods,
Fucy c loos c!amstsnalts«andslurlae nor ms from
agillSt Belzon 1 Here considerahly more tolerant
Macrocyclops t° Pesticides than the non-resistant
a Ib ldus» organisms. Theauthorsnotethatthe
Orthocyclops etfectoflncreasedtolerancelnthe
modestus) orqanismslsanlncreaselntheamountof
pesticide residues aval(able to animals
of higher trophic levels.
Malathlon
(C VC I ODS
blcuso Mu5t
Cyc I on*.
war 1 c ans v
Cvc I ons
v^rnn I 1 s »
Fucycl oos
aql I is,
Macro cyclopa
FL
and
RSA
Belzonl,
Hiss
0.0Z5 (13
percent KZ
Orthocvcl oos
mod«*s t us)
sane as above
Naavlt et al
(1969),
Nslatnlon
Malathlon
Tubltex
tublTex
FL
and
BSA
Relzonl,
Hiss.
Crassostrea I
vlrqlnlca
(eggs)
3.0 (^4TE)
9.07 (T2>
same as above
Naavl, et
al (1969) ,
AMIC-5979
The effect of 52 pesticides on Davis, et al
embryonic development of clams and
oysters was reported. Synerglstic ( 19f>9) , AMIC-
effects Hlth solvents were also reported. 5990
Most of the compounds affected
development more than survival. Some,
however, drastically reduced larval
qrowth. The authors ooint out the
necessity of evaluating the effects of
pesticides on all life stages of an
orqanism and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
-------
Ha lathi on
Halathlon
Halathlon
Crassostrea
vlrqinica
(larvae)
Cardlum edule BSA
Crangon
crangon
BSA
2.66 (Til.)
3.3-10 (T2>
0.33-1.0
shell fish.
same as above
a»{contln- One hundred-forty surface active
uoua, aor- agents, solvent emuls1flers, pesticides,
atlon, soa-po I yen I orinated blphenyls, pure
water, and Inorganic, and organic chemicals Here
daily evaluated against as many as ten marine
solution organisms. The authors noted that most
ronewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
same as above
*«•( contin-
uous, aer-
ation, sea-
water, and
daily
solution
renewal)
Davis, et at
(1969) ,AMIC-
Portmann, et
al (1971),
AMIC-7701
Portnann, et
al (1
Halathion
M»l«lc acid
papullfera
Hanazon
Hancozeb
Haneb
Haneb
promelas
Fish (not
specified)
Fish (not
specified)
Fish (not
speclfled)
Agonus
BSA
100 (K)
5.0 (Tl.)
Hunter's
medium
diluted
1:5
a*td,evO«
and Fe
BSA —
greater than
100-1000 (K)
greater than
1.0-10.0 (K)
greater than
0.1-1.0 (K)
0.33-1.0 (T2) a»
All compounds were harmful to Worthley, »t
duckweed to some degree. Decreased al (1971),
populations were noted at non-lethal AMIC-3233
concentrations and some compounds
(Malathion and 2,l|.-D) caused teratoganlo
effects at concentrations as low as 1 ppn.
Malathion ana Its hydrolysis Bender
products were evaluated with the flndlnq ( 1969) , A"IC.-
that one such product (diethyl fumarate) 3787
was more toxic than Malathion to fathead
minnows. Synerglsm occurred between
Malathion and two oroducts of hydrolysis.
Continuous exposure resulted in
increased toxlclty.
Approximate toxlclties of Mawdesley-
numerous pesticides commonly used in Thomas ( 1971)
Britain were summarized, in excellent AMIC-1056
brief, general discussion of toxiclty
testing is also present.
same as above
Approximate toxlcities of
numerous pesticides commonly used in
Britain were summarized. An excellent
brief, general discussion of toxicity
testing Is also present.
"awdesley-
Tho*as(1971),
t^TC-1056
Mawdeslev-
Thomas
(1971),AMIC-
1056
One hundred-forty surface active Portnann, et
-------
Coioound
Field Field
Organism Study Location
Toxlclty,
ActIve
Ingredlenti
Ppm
ExperI mentaI
Variables,
Control I ed
or Noted
Comments
Reference
cataohractus
Msneb
Aster las
rubens
BSA
33-100
-------
r
Manganese
Manganese
Manganese
Manganese
Hunganese
Manganese
Manganese
Manganese
cluoeaforuls
FSOX luclus FL
Fsox luclus FL
Esox luclus FL
Osmerus FL
mordax
Peres FL
ftavescens
Paralabrax FM
clathratus
Paralabrax
clathratus
Paralabrax
clathratus
Paralahrax
elathrstus
FM
FM
FM
Ontario,
Can.
Moose Lake, 3.0 (residue)
Can.
Lahe St. 3.2 (residue)
Pierre, Can.
Lake Erie, 0.9 (residue)
Can.
Lake Erie, 0.03 (residue)
Can.
Lax* Erin, O.?l (residue)
Can.
Scatterqood 0.5 (dorsal
Steam Plant, muscle
Los Anqeles, residua)
Cat.
Catallna 0.6 (dorsal
Tsland, Cal. muscle
residue)
Scattergood 0.5 (ventral
Steam Plant, muscle
Los Angeles, residue)
Cal.
Catallna 0.5 (ventral
Island, Cal. muscle
sane as above
same as above
same as above
same as above
same as above
Fish collected from an effluent
ploe of a steam plant and from offshore
Hater-; of Catallna Island nerp analyzed
for trace element content. Trace element
content of the effluent Hater Has at
least 5 times qreiter than that of normal
sea Hater for cadmium, copper, nickel,
zinc, and chromium. Livers of fls* from
the effluent wore nearly tnice the size
of those from the ocean. Greatest
differences In concentration occurred
Hlth aluirinunt, cadmium, and nickel.
Silver, barium, lithium, and lead shoned
the least differences. The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on marine organises.
same as above
same as above
sane as above
(19M) ,
AMTC-3819
Uthe, at al
(1971),AMIC-
3S19
Uthe, et
AL(1971),
A1IC-3S19
Uthe, et al
(1971),AMIC-
3811
Uthe, et al
(1"71),A*IC-
3*19
Uthe, et al
(1971J,AKIC-
3819
S taoIeton
(1968),
AMTC-S980
Staoleton
(196R),
A.MIC-5980
Stan Ieton
(1968),
AMIC-5980
Staoleton
(1968),
-------
U)
Comoound
Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Manganese
Hanganese
Manganese
Manganese
Orqani sm
Paral abrax
cl athratus
Par a 1 ahr ax
cl athratus
Paral abrax
cl athratus
(qravld
f eroa 1 PS)
Paral abrax
cl athratus
Par al abrax
c 1 athratus
Par a 1 abrax
cl athr a tus
Paral ahrax
cl athratus
Paral abrax
cl athratus
Para 1 abrax
cl athratus
Paral abrax
cl athratus
Field
Study
FM
FM
FM
FM
FM
FM
FM
FM
FM
FM
Flel d
Loca t Ion
Sea 1 1 prgood
Stpam Plant,
Los Angel es,
Cal .
Catal Ina
Island, Cal.
Catal i na
Isl and, Cal .
Sea 1 1 ergood
S t pam Pi ant ,
Los A nget es ,
Cal .
Catal Ina
Island, Cal .
Scatt erqood
Stpam Plant,
Los Angeles,
Cal.
Catal Jna
Island, Cal .
^cattergood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Scat t erqood
Steam Plant,
Los Angeles,
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted
residue)
1.1 (gonads --
res 1 due)
1.7 (gonads —
residue)
2.2
(gonads
resl due)
?.<• (1 Iver
res i due)
i».Z (1 Iver
residue)
0.7 (Integument —
residue)
0.8 (Integument --
residue)
1.6 (heart
residue)
1. it (heart
residue)
1.6 (eyeball
residue)
C omme n t s
same as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
sane as above
same as above
Peter ence
AMIC-^0
Stan 1 eton
S taol eton
(1968) ,
AMIC-59SO
S taol eton
(1068) ,
Staoleton
AMIC-5180
S t ao 1 e t on
(19f,8) ,
AHIC-59^0
S ts
-------
Cat,
Hanoanes*
Hanoxol
U)
O
V/l
HOP*
HOP*
Papalabrax
clathratus
FM
CatatIna
Island, Cal,
Rasbora BCFA —
heteromorpha and
BSA
2.6 (eyeball
residue)
16 (T2»
same as above
Sfaoleton
(I960 .
AMTC-S9SO
Fish (not
Specified)
Crassostrea
vlrqlnlca
(eggs)
greater than
10-100 (K>
15.6
a*,c,e,f. One hundred sixty-four Alabaster
hard (HW) pesticides, wettlnq aqents, and (1959),
or soft miscellaneous water pollutants showed a AHTC—52 pesticides on
embryonic development of clams and
oysters was reported. Synerglstlc
effects with solvents were also reported.
Most of the compounds affected
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 staaes of an
organism and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
shellfish.
Oavls, et al
(1969),
AMIC-5990
MCPA
Hecarban
Crassostrea
vlrqlnica
(Iarvae)
Fish (not
specified)
31.3 (Tilt)
greater than
0.001-0.01 (K)
same as above
Approximate toxlcltles of
numerous pesticides commonly used In
Britain were summarized. An excellent
brief, qeneral discussion of toxlcity
testing is also present.
Davis, et al
(1969),AMIC-
5990
Mawdeslev-
Thonas(1971)
AMIC-10'56
-------
o
ON
Field Field
Comoouni Orqanlsm Study Location
Menazon Pa', bora BCFA
he ter omoroha and
BSA
Mtrcurlc chloride Acroneurla RSA —
(as Hg)
Mercuric chloride Ephemerella BSA —
<»s Hi)
Mercuric chloride Hyrtroosyche BSA
(as Hq)
Mercuric chloride Hatersloora L
(asHg) cucu 1 1 a t a
(larvae)
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
15
-------
(larvae)
AHIC-S/OS
Mercuric chloride
(as Hg)
Mercuric chloride
(as Hg)
Mercuric chloride
(as Hq)
Mercuric chloride
(as mercury)
Mercuric chloride
(as nercury)
Mytllus L
edulls
Pianulatus
(Iarvae)
Crassostrea L
commercial Is
(I arvae)
Artemla L
sal Ina
(larvae)
Carclnus
maenas
BSA —
13.1 (T 2 hr)
180.9 (T 2 hr)
1809 tT 2 hr)
1.2 (T2)
Cardlum edule BSA
9.0 (T2>
a,0,1,
and
salinity
a,c.l, and
salinity
and
salinity
a«( contin-
uous, aer-
ation, soa
water, and
dally
solution
renewal)
a»(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
same as above
same as above
same as above
One hundred-forty surface active
aqsnts, solvent etnuls 1 tiers, pesticides,
polychlorinated blphenyls, cure
Inorganic, and organic cherlcals 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
Wisely, et
al (1967),
AHIC-570*
Wisely, et
al (1967),
AMIC-«:70S
Wisely, et
al U067),
AMIC-570*
Portmann, et
al (1971),
AMIC-7701
Portiwann, et
al J1971),
A1IC-7701
Mercuric chloride
(as Mercury)
Mercuric chloride
(as mercury)
Crangon
cranqon
BSA —
0.10-0.33(11.)
Ostrea edulls BSA —
(T2)
a*(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
a»(contin-
uous, aer-
ation, sea-
water, and
dally
solution
renewal}
same as above
same as above
Portmann, et
al (1971),
AMIC-770!
Portmann, et
al (1971),
AHIC-7701
Mercuric chloride
Panda I us
BSA —
0.08 (T2>
same as above
Portmann, et
-------
Toxiclty,
Active
Field Field Inqredlent,
Coaoound Orqanlsm Study Location Ppra
(as mercury) montaqul
Mercuric chloride Platlcthys BSA — 3.3 (T3)
(as nercury) flesus
Fxppr 1 men tal
Variables,
Control 1 ed
or Noted Comments
(cont 1 nuous
aerat Ion,
seawater ,
and dal 1 y
solut Ion
reneHa 1 )
a* same as above
(continuous
aerat ion.
seawater.
and dally
so 1 ut ion
renewal )
Reference
al (19711,
AMIC-7701
Portirann, et
al (1971),
AMIC-7711
H«rcurlc chloride
Carasslus
auratus
8SA
Mercuric chloride Carasslus BSA
auratus
Mercuric chloride Carasslus BSA
auratus
0 . ?5 (SB1)
O.Z5 (15 DPm a*,e
tissue residue
1 d)
0.25 (<»0-SO ppm a*,e
tissue
residue 100 hr)
Mercury accumulated rapidly in
qoldflsh. The hlqher the concentration
up to 1.0 pr>m, the more raoid was the
accumulation. At hlqher concentrations,
heavy mucus formation occurred with most
of the mercury belnq found in the mucus.
The authors noted that bacterial
methylatlon occurs In dead Tlsh but only
If tnuchus is present.
same as above
same as above
McKone, et
a I (l°7il,
AMIC-H9?
McKone, et
al (1171),
AMIC-11.9?
McKone, et
al (1971),
AMIC-11.9?
Mercuric chloride Atnbassls BSA
saf9ha
2.8 (Tl)
a*. Measurement of residual dissolved Pal lard,ot
seawater oxyqen during exposure of fish to al (1969),
Toxlcarts resulted In data similar to AMIC-300
that obtained from 2
-------
Mercuric chloride Carnal us
auratus
0.8? (T7)
Mercury (total)
Mercury (total)
Mercury (total)
Mercury (total)
Mercury (total)
Mercury (total)
Mercury (total)
Mercury (total)
Mercury (total)
Salvetlnus FL
namaycush (1
yr)
SalvelInus FL
namaycush (11
yr)
Salvel Inus FL
namaycush (12
yr)
Salve)Inus FL
namaycush (2
yr)
Salvellnus FL
namaycush (3
yr)
SalvelInus FL
namaycush (3 (residue) —
Tn addition to toxlclty data. Weir, et al
conditioned avoidance response w?s (1970),4HIC-
studled at sublethal concentrations. The 739
lowest concentration of metal resulting
In significant Impairment was! arsenic,
0.101 lead, 0.071 mercury, 0*0031 and
selenium, 0.25. Deleterious effects
occurred at metal concentrations
approximately similar to potable water
standards.
Lake trout stocKed annually as Bache, et al
taqqed flngerllngs were netted and (1971),
analyzed for mercury and me thy I mercury. AMIC-38H
Total mercury and the proportion of
methyl irercury to mercury Increased with
age but not sex.
same as above
same as above
same as above
same as above
same as above
sane as above
same as above
sane as above
Bache, et al
(1971) ,
4HIC-3S18
Bache, et al
(1971),
SHIC-381S
Bache, et al
(1971),
4HIC-3S18
Bache, et al
(1971) ,
4MIC-3S18
Rache, et al
(1971),
4HIC-3811
Bache, et al
Pa che, et al
(1971) ,
SHIC-3818
Bache, et al
(1971),
4MIC-3819
Mercury (total)
SalvelInus
FL
Cayuga LaKe, 0.65 (residue)
same as above
Bache, et al
-------
>
OJ
Compound
Mercury (total)
Mercury
M«rcury
Mercury
Mercury
Mercury
Mercury
Mercury
Metasystox
Organ I sm
namaycush (8
yr)
Sal ve 1 Inus
namaycush (9
yr)
Coregonus
clupeaformls
Coregonus
c 1 unea f or m I s
Esox luclus
Esox luclus
Esox 1 uc i us
OsmeruS
mordax
Perca
f 1 avescens
Rasbora
heteromopoha
Toxlclty,
Active
Field Field Ingredient,
Study Location Pom
Ithaca, N.Y.
FL Cayuga Lake, 0.53 (residue)
Ithaca, N.Y.
FL Moose Lake, 0.07 (residue)
Can.
FL Lake 0.17 (residue)
On t ar 1 o.
Can.
FL Moose Lake, 0.11 (residue)
Can.
FL Lake St. 0.70 (residue)
Pierre, Can.
FL Lake Erie, O.i»9 (residue)
Can.
FL Lake Erie, 0.05 (residue)
Can.
FL Lake Erie, 0.33 (residue)
Can.
BCFA — 6.5 (T2>
and
8SA
Exoer 1 men ta 1
Variables,
Control 1 ed
or Noted Comments
— samp as above
Concentrations of 13 toxic
pigments in dressed T Ish from heavily
industrialized and non- Indus trl al 1 zed
areas were determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements were
essentially the same in fish from both
areas.
same as above
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) oesticldes, netting agents, and
or miscellaneous water pollutants showed a
SOFT(SW) wide range of toxlclty scanning 12 orders
synthetic of magnitude. Knowing the toxlclty and
dilution percentage of .all components of a
Pet erence
(1971) ,
AMIC-lflll
Bache, ft al
(1971) ,
AMIC-3? IS
Uthe, etal
(1971) ,
AMIC-3819
Uthe, e t =i 1
( 1971 ) ,
OMIC- JS11
Uthe, et al
(1971) ,1MIC-
3819
Uthe, et
*L (1971) ,
«MIC-3519
Uthp, et al
(1971) ,AMIC-
3919
Uthe, et al
(1971) ,AMIC-
3519
Uthe, et al
(1971) ,AHIC-
7819
Al abaster
(1969) ,
AMIC-51.35
-------
Hcthanol
igonus
cataphractus
BSA
10,000-33,000
(TZ)
>
u>
H«thanol
Cardlum edule BSA
3300-10,000
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 Mater
and sofretlmes the ooooslte was true,
Testlnq the actual material as sold was
found to be essential.
««(contin- One hundred-forty surface active
uous, aer- agents, solvent emulslfiers, pesticides,
ation, sea-poIychlorinated blohenyls, cure
water, and Inorganic, and organic chemicals were
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
organisms.
same as above
a«( contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
Portmann, et
al (1971),
AMTC-7701
Portaann, et
al (1971),
AHIC-7701
Methanol
Crangon
crangon
BSA
1700
a»lcontin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
same as above
Port-nann, et
al (19711,
AMIC-701
HethoxycM or
(tritium labelled)
Sorghum
halpense
U
(mode
I
ecosy
Stem)
1 Ib per
(NTE)
a,c«g. This small laboratory model
standard ecosystem procedure was developed to
reference study pesticide b lodegradab11 11y and
water and ecological magnification. The food-chain
sand pathways in this system were! (1)
sorghum - caterplller (larva), (2)
caterolller (excreta) - Oedooonlum, (3)
Oedoqonium - snail, (<*) Estigmene
(excreta) - diatoms, (5) Diatoms -
plankton, (6) PlanKton - Culex (larvae),
(7) Culex - Gambusla. The fish is the
too of the food chain. Using
isotoplcally labeled Pesticides (1
Ib/acre application rate), residues were
determined for only selected organisms
(snail, mosquito, and fish) and water.
Hetcalf, et
al (1971),
AMIC-1V95
-------
Compound
Organism
Field Field
Study Location
Toxlclty,
Active
Tnqredient,
Ppm
Experimental
Variables,
Con troI led
or Noted
Comments
Reference
Ne thoxychI or
ttrltlum label led)
EstIgmene
acrea
L
(Mod-
al
e cosy
stem)
1 Ib per A
(K-NTE)
a,c,q,
standard
reference
Hater and
sand
ReproduclblI 1ty appeared to be good. The
authors state that the method qlves a
good estimation of the potential toxlclty
of pesticides and their breakdonn
products to a variety of organisms and is
suitable for computer modeling.
same as above
Metcalf, et
al (1971),
He thoxychlor
ftrltlum Iabell4d)
Physs spp
L
(Mod-
el
ecoay
atemj
15.7 (residue)
a,c,g,
standaro
ref erence
water and
sand
same as above
Metcalf, et
al (1971),
Methoxychlor
(trltlun labelled)
Daphnla xagna L
(Mod-
el
OOOST
atom}
1 lb per A
(K-NTE)
a,c,q,
standard
ref erence
Hater and
sand
same as above
Metcalf, et
al (1971),
Methoxychlor
(trlTlun label led)
Culex plplens L
qulnque- (mode
faaoiatua I
ecosy
stem)
O.itSlresIdue)
a,c,g,
standard
reference
Hater and
sand
same as above
Metcalf, et
al (1971),
AMIC-11.91;
MethoxycM or
(tritium labelled)
Oedogonluii
cardlacun
L
(mode
I
ecosy
stem)
1 Ib per
A(NTE)
a,c,g,
standard
reference
Hater and
sand
sane as above
Metcalf, et
al (1971),
M«thoxychlor
(trlflua labelled)
Cambusla
affinis
L
(mode
I
ecosy
0.33 (residue)
a,c,g,
standard
reference
Hater and
same as above
HetcaM, et
al (1971),
AMIC-11.95
-------
stem)
sand
r
UJ
H«thoxycMor
ftrltlui* labelled)
N«fhoxychlor
ttrltlu* labelled)
Hethoxychl or
Itrltlum labelled)
Methoxychtor
{tritium labelled)
Diatoms I
(Navicula, (mode
Cosclnodis- I
CU3, Dip- ecosy
loness, and stem)
Dlatomella)
Protozoa
(Nuclearia,
Coleps,
Vortlcella,
and
Parameclum)
L
(mode
I
ecosy
stem)
Rotifers Llmod
(Asplanchnop- el
us, Notomat- ecosy
ta, Euclaris, stem)
Scardium)
Hater
L
(mode
ecosy
stem)
1 Ib per A
(NTE)
1 Ib per A
INTE)
1 Ib per A
(NTE)
0.0016
(residue)
a,c,q,
standard
reference
water and
sand
a,c,g,
standard
reference
water and
sand
a,c,g,
standard
reference
Hater and
sand
a,c, q»
standard
reference
water and
sand
same as above
same as above
same as above
same as above
Metcalf, et
al(tori),
AMIC-1*95
Metcalf,
etal
AMIC-l«i95
Metcalf,
etal (1971),
AMIC-1U95
Metcalf, et
al (19711,
MethoxycMor
Methoxychlor
HcthoxycMor
Chlronomus
tentans
(Instar)
BSACF —
5.5 IT*)
Stenonema
candldum
(Instar)
Taenlopteryx
nival is
(Instar)
BSACF —
BSACF —
Z.I IT*)
0.98 (Tt»)
c,d,e This chemical Has evaluated
primarily because it is on*» of the
principal substitutes for DOT. Rapid
breakdown of the chemical occurred Hhen
llvlna orqanlstrs were present. The
half-life of methoxychlor Has 7 days In
Ann Arbor city Hater, but Has much more
raold (less than 1 day) in local creek
Hater and slow (approximately ?00 days)
in distilled Hater. These studies Here
to be continued to determine long term
effects but no data are presented.
c,d,e same as above
c,d,e same as above
Bender,et at
(1971),
AMIC-3379
Bender, et
al (1971),
AMIC-3279
Bender,et al
(1971) ,
AMIC-3J71
Methylene bis
Phormldlua
0.5-10.0 (16
Of 7i» .chemicals evaluated as
Otto (1970),
-------
Conoound
th loeyanate
Toxlcltyi Experimental
Active Variables,
Field Field Ingredient, Controlled
'Organism Study Location Ppm or Noted
amblguum percent alqlc
growth Inhibited CuSCKi
Comme n t s
ides, only 9 were more toxic than
. None Inhibited qrowth of
Ref er ence
AMIC-M7
>
Me thy Imercury
N»thyl«ercury
Methy(mercury
M« thyl«ereury
Nethylaercury
Me thy I«ercury
»«rcury
Sal vel Inus
namaycush (1
yr)
SalvelInus
naiiavcush (2
yr)
SalvelInus
namaycush 13
yr)
SalvelInus
namaycush (it
yr)
SalvelInus
namaycush (5
yr)
SaIveIInus
namaycush (6
yr)
SalvelInus
naiiaycush (7
yr)
FL Cayuqa Lake, 0.07 (residue)
Ithaca, N.Y.
FL Cayuqa Lake, 0.11
Ithaca, N.Y.
FL Cayuga Lake, 0.21
Ithaca, N.Y.
FL Cayuqa Lake, 0.3U
Ithaca, N.Y.
FL Cayuga Lake, 0.35
Ithaca, N.Y.
FL Cayuga Lake, 0«*»?
Ithaca, N.Y.
FL Cayuga Lake, 0.31
Ithaca, N.Y.
(residue)
(residue) --
(residue) --
(residue) --
(residue)
(residue)
mat-forming alqae for more than ? Meeks*
CuSOt* formulated Hlth certain wet t i nq
aqents was more toxic than CuSO«t alone.
Coop»r chloramlne was also found to he
morp toxic than CuSO^. No we 11 ino aqents
Here found to be Inhibitory at the
concentrations investiqated (0.05 and
O.TQ^ DD^)« Also reported are factors
affecting qronth of alqae In canals to
determine whether tht»re wore leads to
control IInq algae hy environmental
manaqerrent. No practical environmental
me^ns were found.
Lake trout stocHed annua!!v as
taqqed finqerllngs were netted and
analv7ed for mercury and methylmercury.
Total mercury and tho proportion of
methylrrercury to mercury Increased *lth
aqe but not sex.
same as above
same as above
sane as above
sane as above
same as above
sane as above
Pache, et al
(ig71),
Pache, et al
(1971) ,
AHIC-381S
Pache, et al
(1971).
AHIC-381*
Bache, et al
do^l) .
A1IC-381*
Bache, et al
(1971) ,
AMIC-1818
Pache, et al
(1971) ,
AMIC-3818
Pache, et al
(1971) ,
AMIC-3818
-------
M«thyl«*rcury
He thy I mercury
Methylmercury
Methyl mercury
Me thy I pentynol
r
U)
Methylpentynol
He thyIpentynof
M»thylpentynol
SalvflInus FL
namaycush 18
yrl
SalvelInus FL
namaycush (9
yrl
Sal vetInus FL
na^ayeush (11
yr)
Salve)Inus FL
namaycush (12
yr)
Salmo
galrdnerl
Ictalurus
punctatus
BSA
Cayuga Lake, 0.51 (residue)
Ithaca, N.Y.
Cayuqa Lake, 0.1)3 (residue)
Ithaca, N.Y.
Cayuga Lake, O."*l (residue)
Ithaca, N.Y.
Cayuga Lake, 0.(»7 (residue)
Ithaca, N.Y.
870-1260 (TU)
a*,c,f
Salmo trutta BSA
Methylpenfynol
Me thy 1 oent ynol
Nethylpentynol
Sal vel Inus
font Ina 1 1 s
Sal vel Inus
namaycush
Esox lucius
BSA
BSA
BSA
680-1100 (T a»,c,f
1100-1200 (Ti.) a»,c,f
660-1160 (Tit) a*,c,f
less than 900 a*,c,f
BSA
Leoomls BSA
macrochlrus
1700-1890 (T<.) a'.c.f
l?60-13i»0 (T4) a»,c,f
same as above
same as above
same as above
same as above
Me thy I pentynoI Has tested in
96-hour bloassays for Its toxicity to
rainbow trout, brown trout, brook trout,
lake trout, northern Dike, channel
catfish, blueqills, larqemouth bass, and
walleyes. Channel catfish 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 larger ones in the
96-hour exposures. The druq was uore
toxic to blueqills and rainbow trout with
elevated temperatures. Toxicity was
barely Influenced by changes In water
hardness.
same as above
same as above
same as above
same as above
same as above
same as above
Pache, et al
(1971),
4MIC-38J1
Pache, et al
(1971),
AMIC-3H1B
Bache, et al
(1971),
AMIC-38H
Pache, et al
(1971),
AMIC-3818
Marking(19S9),
AMIC-5<»77
Harking
(1969) .AM.IC-
51,77
Marking(1959)
MarkIng(19S9) .
&.1TC-5V77
Marking
(1969) ,»MIC-
5g<19691
AMIC-5<»77
-------
Coiaoound
Methyloentynol
M«thylo*ntynol
Organism
Mlcrooterus
sa 1 mo 1 des
St 1 zostedlon
vl treum
Field Field
Study Location
BSA
BSA
Toxlclty,
Active
Ingredient,
Pom
1100-1250 (T
11<»0 (Tit)
Experimental
Variables,
Con tro lied
or Noted Comments Reference
a*,c,f same as above MarK 1 nq ( t PS9
a*»c,f same as above Marking
5t(77
H« thy 1 parathlon
Methyl osrathlon
Leoomls BSA
cyanelI us
(Resistant)
LepomIs
cv aneI I us
(Susceptible)
RSA
greater than
5000
greater than
•5000 (T3)
Green sunflsh trom Belzonl, Miss. Mlnchex, et
were resistant to Chlordane, Heotachlor, al (1970),
Lindane, and Strobsne, but not to AMIC-5'.71
Parathion. Golden shiners fron the same
location Here resistant to Llnrlanc and
Strohane, tolerant to Hhlordane and
Heotachtor, and susceptible to Parathion.
Lack cf resistance to Parathion
indicated lacK o( agricultural usage of
orqanochosphates In that area. Resistant
fish were compared to susceptible ones
collected at Starkvllle.
same as above
MlncheH,
al (1970)
A^IC-51.71
et
Hethyl oarathlon
M«thy1 oarathlon
No tern Ioonus
crysolpucas
(Resistant)
Notemloonus
crysoIPUCSS
(Susceptible)
BSA
BSA
greater than
5000 (T2)
greater
thanSOOO (T2)
same as above
same as above
HInchew, «t
al (197C),
AMI--SI.71
Mlnchew, »t
al (1970),
Methyl oarathlon
Ictalurus
ounctatus
BSA —
5.71 (ft) a, Orqanochlorlne Insecticides were Hacek, et al
synthetic the most toxic compounds, (1970),
test water orqanochosphates Intermediate, carbanates AMIC-5510
the least toxic. Prown trout was the
soecles most susceptible to
organochlorlnes, coho salmon the most
susceptible to carbamates, and goldfish
were the least susceptible of all
species. Safe concentrations established
by bloassays with salmonlds or
centrarchlds would likely be sate for
-------
Hethyl parathlon
Methyl oarathlon
Hethyl oarathlon
Methyl parathlon
Hethyl parathlon
Hethyl oarathlon
Hethyl parathlon
Hethyl oarathlon
Hethyl parsthlon
Ictalurus
net as
Carasslus
auratus
Cyprlnus
carolo
Plmeohales
cromelas
LcDoml<;
macrochlrus
Leoonls
mleroloohus
Mlcropferus
salmoldes
Sal mo
gairdnerl
BSA
RSA
BSA
8SA
BSA
BSA
BSA
8SA
6.6".
99.00 (TU)
7.13 )
5.72
5.17
5.23 tTif)
2.75 (Tit)
Salmo trutta BSA
ft
synthetic
test water
a.
synthetic
test water
a.
synthetic
test water
a,
synthetic
test Hater
synthetic
test nater
a.
synthetic
test Hater
synthet le
test Hater
a.
synthetic
test water
a.
synthetic
test water
cyorlnlds and Ictalurlds. Safe levels
for Ictalurlds or cyprlnlds would
probably be hazardous for centrarchlds
and salnonlds. The use of goldfish In
bloassays was discouraged.
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
PaceK.et al
(19701,
Hacek, et al
(1970) ,
AHTC-5510
Mace*, et at
(1970 ,
AMIC-5510
PaceK, et al
(1=170) ,
AHTC-5510
MaceK, et al
(1970) ,
AMIC-5S10
Kscek, et al
(19^0,
AMIC-5510
Macek, et al
(1970) ,
MaceK, et al
(1970) ,
MaceK, et al
(1970),
Hethyt parathlon
Hethyl parathlon
Hethyl parathlon
Oneorhynchus BSA
kisutch
Perca
1 lavescens
BSA
Palaemonetes BSA
kadlakensls
5.30 (Tfc)
3.06 (T
-------
Compound
Organise
Field Field
Study Location
Toxlclty,
Active
Ingredient,
Ppm
Experimental
Var1ab|es *
Control Ied
or Noted
Comments
Reference
(resistant)
U)
fc
Methyl oarathlon
Methyl parathlon
Pa Iaemone tes
kadlaxensls
(non-
resistant)
Tuhifox
tuhlfex
BSA
FL
and
8SA
Relzonl,
Miss.
0.0037 (Tl»
6.00 (NTF)
a»
Mevlnfos
Rasbora
heteromoroha
BCFA
and
BSA
11.5
a*,c,e,f,
hard (HH)
or
SOFT(SW)
synthetic
dilution
Hater, or
seawater
for
some
pesticide use and from an unexoosed area. AMIC-5519
Previously exposed shrlmo were from 1 to
25 times more resistant than unexoosed
shrimp. Both types of shrimp were also
exposed In caqes to wafers of the
contaminated areas. Susceptible shrimp
suffered £6 percent more mortality than
did resistant shrimp. The toxlcity of
the insecticides ranked in descending
order was as follows" most toxic,
Fndrln, DOT, Methyl parathlon, Parathlonl
medium toxlcity, Guthlon, Llndane,
Toxaphene, Strobanei lease toxic
Chlordane, Sevln, and Heptachlor.
same as above
Naavl, et al
(1970),
AMIC-"i5iq
The response of
pesticide-resistant aauatlc organisms to
various pesticides was compared to the
response of non-resistant soecies.
Pesticide-resistant soecies were
collected at Pelzoni and non-resistant
species at State College. Copepods,
clams, snails, and sludoe worms from
RelzonI 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.
One hundred slxty-fpur
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wide range of toxlcity spanning 1? 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. Sometimes
pesticides were most toxic In hard water
Naavl, et al
(1969),
AMIC-S979
Alabaster
(1969),
-------
HI Ibex
Rasbora
heteromorpha
BCFA
and
8SA
3.5
specie a and sometimes the ooooslte Has true.
Testing the actual material as sold was
found to be essential.
a», e,e,f, one hundred sixty-four
hard (HW) pesticides, netting agents, and
or soft miscellaneous water pollutants showed a
(3WJ 3JH- wide range of toxiclty scanning 12 orders
thetic of magnitude. Knowing the toxiclty and
dilution percentaae of all components of a
water, or formulation did not result In easy
aeawater predictability of the toxiclty of a
Jfor'some mixture of materials. Sometimes
apeclea pesticides were most toxic in hard water
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
alabaster
fl<)69> ,
AMIC-5<.?5
UJ
Fundulus BSA
heteroclltus
Nereis vlrens BSA
0.0003-0.0006 a»,c,e»
(T<») and
synthetic
seawater
0. 00006-0. 0001.3 a*,c,e,
(Ti>) and
synthet ic
seawater
same as above
same as above
Hoasplll
Cranqon
cranqon
BSA
1000-3300 (T
a»(contin-
uous, aer-
ation, soa-
water, and
dally
solution
renewal)
Hollnatc
Gamnarus
fasclatus
BSA
0.39 (T2), 0.30 3*
One hundred-forty surface active
aoents, solvent emulslfiers, pesticides,
polychlorlnated blphenyls, pure
inorganic, and organic cheiricals were
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal with
toxlcity of chemicals to freshwater
organisms.
Of the aauatlc weed herbicides
evaluated, Oiclone was the most toxic,
Oaohnia was generally the most sensitive
organism. AH of the Crustacea were
LaVoche, et
al (1Q701,
LaRoche«et
al 11970),
Portwann, et
al (1971),
AM.IC-7701
Portmann, et
al (1971).
AMIC-7701
Sanders
(19'0),
AHIC-l>53
-------
Co»oound
Orqanlsm
Field Field
Study Location
Toxlcitv,
Active
Ingredient,
Ppm
Exper1 men taI
Variables*
Control Ied
or Noted
Comments
Ref erence
Molln»te
BSA —
kadlaH«ns|s
affected by much lower concentration
levels of herbicides than Indicated by
the TL sub 50 values. All of the animals
represent Important food chain links.
same as above
Sanders
(1970),
AMIC-i.53
ro
o
Mollnate
HoiInste
Mollnatc
Hollnatc
Hollnate
Asellus BSA
brevIcaudus
Orconectes BSA
na 1 s
Oaphnla maqna BSA
Cypridopsls BSA
vllua
BSA
0.1,0 (T2)
5.6 (TZ)
O.fiO (TZ)
0.18
0.
-------
Nolyb
-------
Co«oound
Molybdenum
Holybdenu*
Ho 1 ybdenua
Honoxone
Organism
Par a 1 ahr ax
cl athratus
Paral abrax
cl athpaf us
Paral abrax
cl athratus
Sal no
q>»Irdn*r 1
Field
Study
FM
FM
FM
BCFA
and
BSA
Field
Locat Ion
Catal 1 na
Isl and, Cal .
Scattergood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Is I and, Ca t .
—
Toxlcl ty,
Active
Ingred I en t ,
Ppm
O.Mheart
residue)
1.9 (eyeball
residue)
it.8(eyebal 1
residue)
900 (T2)
Experimental
Variables,
Control 1 ed
or Noted Comments
« same as above
— - same as above
— same as above
a»,c,e,f, 0,,e hundred sixty-four
hard IHWJ pesticides, wettlnq agents, and
OP aoTt mlscel laneous water pol lutants showed a
Pet erence
S tap t eton
(1068) ,
AMIC-5980
Staol eton
(1968) ,
AMIC-5980
S tao 1 eton
(19^8) ,
AMIC-59SO
A 1 abaster
(1069) ,
ANIC-5I.3K
K>
ro
(SMJ syn-
thetic
dilution
water, or
seavrater
for sorae
species
Mono (N, N dimethyl Phornldlun
•IKyl amlne) salt of amblquun
•ndothalI
0.5-10.0 (NTE) —
wide range of toxlclty spanning 12 orders
of magnitude. Knowing the toxicity and
pprcpnfaqe of al I 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 ooposite was true.
Testing the actual material as sold was
found to be essential.
Of 7i» chemicals evaluated as
alqlcides, only 9 were more toxic than
CuSOii. None Inhibited growth of
mat-forming algae for more than ? weeks.
CuSO<» formulated with certain wetting
agents was more toxic than CuSCXt alone.
Coop»r chloramine was also found to be
more toxic than CuSCHt. Ho wetting agents
were found to be Inhibitory at the
concentrations Investigated (0.05 and
0.115 oom). Also reported are factors
affecting growth of algae In canals to
determine whether there were leads to
controlling alcae by environmental
management. No practical environmental
means were found.
Otto
AMIC-69?
Honuron
galrdnerl
8CFA —
and
OSA
80 (TZ>
(HW)
or soft
ISW) syn-
thetic
One hundred sixty-four
One hundred sixty-tour
pesticides^ wetting aqents, and
mlscel laneous water DO! lutants showed a
wide range of toxicity soannlnq 12 orders
of magnitude. . Knowing the toxlclty and
Alabaster
(1969),
-------
Monoron
Mercenarla
mercenar1 a
(eggs)
greater than
5.0 (T21
Monoron
Morphothlon
Mercenarla L
mercenarla
(larvae)
Cardlum edule 8SA
greater than
5.0 (T13)
dilution perc*?ntaoe of all components of a
Hater, or formulation did not result In easy
seanater predictability of the toxlclty of a
for some mixture of materials. Sometimes
species pesticides Here most toxic In hard nater
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
The effect of '*? pesticides on
embryonic development of clams and
oysters Has reported. Synerglsflc
effects nlth solvents Here also reported.
Most of the compounds affected
development more than survival. Some,
* hOHever, drastically reduced larval
gronth. The authors point out the
necessity of evaluating the effects of
pesticides on alt life stages of an
organism and note the possibility of
selecting chemicals for pest control that
HOuld not have serious effect on
she!I fish.
same as above
Davis, et
al<1969).
Davis, et
al(19
-------
Toxlclty, Exper 1 menta 1
Active Variables.
Field Field Ingredient, Controlled
Compound Organism Study Location Pom or Noted Comments
MS-23Z Leoomls BSA —
macrochlrus
Mystox LSC-P Rasbora F»CFA
heteroaorpha and
BSA
Mystox LSC-P Pashora BCFA —
heter onorpha and
OSA
Nystox LSE-L Salno BCFA —
qalrdncrl and
BSA
HysTox LSE-P Sal»o BCFA —
galrdnerl and
BSA
30 (S81) a,»
IK IT?, a'.c.e.f.
hardnater) hard(HH)
or soft
(T2, a',c,e,t.
softwat«r> hptrn(HH)
or so(t
(SH)
synthetic
dl lut Ion
xater.
ors»a«ater
tor some
soecles
36 (TZ) a',c,e,f.
hard (HH)
or soft
(SH) synthe
tie
dl lut Ion
water, or
seaxater
Tor sone
species
2 a'.c.e.f.
hard (HH)
or sott
(SH) synthe
tic
dilution
Hater, or
seaxater
Little difference In nitrogen
excretion rate was found betHeen treated
and control fish. Anaesthesia should
have reduced nitrogen excretion but did
not. The author believed that Increased
mucus secretion Has a possible
explanation for the results obtained.
One hundred sixty-four
pesticides, wettlnq aqpnts. and
miscellaneous water pollutants showed a
wide raoqe of foxlclty spanning 1? orders
of magnitude. Knowlnq 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 Has true.
Testing the actual material as sold Has
same as above
sane as above
same as above
Ref erence
Savltz
(1969) ,A1IC-
5838
A 1 a b a s t er
(1969) .AHIC-
5U?S
Alabaster
(1969) .AHTC-
5«S
Alabaster
(1969) ,
AMIC-51iZS
Alabaster
(1969) ,
AMIC-SI.25
-------
Nystox LSL-L
Sal mo
qalPdnePl
BCFA
and
BSA
180 (T2>
Nystox LSL-P
Sal mo
galPdnePl
BCFA
and
SSA
68
V/l
Nystox LSL
RasboPa BCFA
hetepomoppha and
BSA
6.2 (T2,
hapdwatep)
Nystox LSL
Rasbopa BCFA
hetepomoppha and
BSA
Z.5 (T2,
sottwatep)
H»ba«
Mepcenapia
mepcenapis
(eqqs)
fop some
soecles
a»,c,e,r.
hard (HW)
or soft
(3W) syn-
thetic
dilution
water, or
aeawater
for' some
apeelea
a»,c,e,r,
hard IHW)
or sort
ISWJ syn-
thetic
dilution
water, or
seawater
for sorae
species
u»,c»et ft
hard
(HW) OP
soft (SW)
synthetic
dilution
watep, OP
seawater
fop some
species
a*,c,e, t,
hard(HH)
OP soft
(SH)
synthetic
dilution
«atep, OP
seawater
(or some
species
less than 0.5
mi
same as above
Alabaster
(1969).
4MIC-5I.2S
same as above
Alabaster
(1969),
same as above
Alabaster
(1969) ,A>»IC-
same as above
A Iabastep
(1969),AMIC-
51.25
The effect of 5? pesticides on Davis, et al
embpyonlc development of clams and
oysters was pepopted. Synepglstlc (1969),AMIC-
effects with solvents Mere also reported. 5990
Host of the compounds affected
-------
CoMOOund
Field Field
Orqanls* Study Location
Toxlcltv,
Active
Inqredlent,
Ppm
Experimental
Varlabtest
Control led
OP Noted
Comments
Reference
development more than survival. Some*
however, drastically reduced larval
groHth. The authors oolnt out the
necessity of evaluatlnq 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
shelI fish.
Nabaii
I
U)
ro
ON
Naleo ?01
Hercenar1 a
nercenarla
(larvae)
Grassestrea
virqlnlca
(eqqs)
Pasbors
heteromorpha
I _—
8CFA
and
BSA
1.75 (T12)
less than 0.5
(TZ)
0.76
Hatco
Rasbora
het*ro»orpha
BCF&
and
BSA
7.1, (T2)
a»,c,e,f,
hard IHWj
or soft
(3WJ syn-
thetic
dilution
Mater, or
aeawa tor
for some
ipeclea
a»,c,e,f,
hard (HW)
or soft
(SW) syn-
thetic
dilution
water, or
seawater
for • some
•paclea
same as above
same as above
tine hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants showed a
wlcte range of toxlclty spanning 1? orders
of magnitude. Knowing the toxlclty and
percentage of all comoonents 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.
sane as above
et a)
(1969).
5990
Davis, et 81
(19S9).AMIC-
5990
Alabaster
(1969).
Alabaster
(1969).
AHIC-5I.2S
-------
Nalco
Rasbora BCFA
heteromorpha and
BSA
0.28 (TZ)
Naohthenlc acids Leoomls BSA,
mqcrochlrus L
5.6
a*,c,e,f, same as above Alabaster
hard (HH) (1969),
or AHIC-51.25
SOFT(SH)
synthetic
dilution
water, or
seawater
tor some
species
a«,e, and. This study Has conducted to Patrick, et
synthetic determine the relative toxicltles ot 20 al (1Q6S) ,
dilution common constituents ot Industrial Hastes AMIC-5730
water to a fish, an alqa, and an Invertebrate.
The experiments were conducted over a
10-year period for varied purposes* The
authors recommend bloassays xlth at least
three components of the food neb.
U)
Naohthenlc acids Nltzschla BSA,
II near Is L
Naphthenlc acids Physa QSA,
heterostropha U
Fundulus BSA
heterocl1tus
1.3.1 (T51
7.1 (T«)
same as above
same as above
a*,e, and
synthetic
dilution
water
a»,e, and
synthetic
dilution
water
0.00 018-n. 0005,and A laboratory procedure based on
synthetic Standard Methods for 96-hr toxlclty
seaHater determinations of crude oil and
o11-d1spersant mixtures Has described.
The dlspersants varied considerably In
toxlclty, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr. These did not differ
significantly from 2 and
synthetic
seawater
less than 2.<»
same as above
La9oche,et
al (1970),
AMIC-U1.S
The effect ot 5? pesticides on Davis, et
embryonic development of clams and al(1969),
oysters was reported. Synerglstic AMIC-5990
effects with solvents were also reported.
Most of the compounds affected
development more than survival. Some,
-------
Field Field
Compound Organism Study Location
Toxlcl ty,
Active
Ingredient,
Ppn
Experimental
Variables,
Control led
or Noted Comments
Ref er ence
N«buron
Mercenar 1 a
mercenar1 a
(Iarvae)
Mercenarla L
mercenarla
(eggs)
less than 2.l»
(T12)
10.0
0.5-10.0 (NTE) —
however, drastically reduced larval
growth. 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 chenlcals for pest control that
would not have serious effect on
shelltIsh.
same as above
Davis, et
al(1969),
AMIC-59Q0
The effect of 52 pesticides on Oavls, et al
embryonic development of clams and
oysters was reported. Synerqlstlc (1969),AMIC-
effects with solvents were also reported. 5990
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 of an
organism and note the possibility of
selecting chemicals for pest control that
would not have serious effect on
shelIfIsh.
same as above
Pavls, et al
C19S9),AMIC-
5990
Ottotl970>,
AMIC-892
N«M 6P 1100
Crangon
crangon
BSA
3300-10,000
mi
Of 7k chemicals evaluated as
alqlcldes, only 9 were more toxic than
CuSOij. None inhibited growth of
mat-forming algae for more than 2 weeKs.
CuSCXt formulated with certain wetting
agents was more toxic than CuSO
-------
Michel sulfate (as
nickel)
Carclnus
•aenas
BSA ~
U2)
Nickel sulfate (as
nickel)
Nickel sulfate (as
nickel)
Cardlua edute BSA —
Crangon
eranqon
BSA
greater than
500 (T2)
125 (T2)
water, and Inorganic, and organic chemicals were
daily evaluated against as many as ten uarlne
solution organisms. The authors noted that most
renewal) published data of this type deal with
toxlclty oT chemicals to freshwater
organisms.
a«(oontin- One hundred-forty surface active
UOU3, aer- agents* solvent emulsl t I«-rs« oestlcldes<
atlon, aea-polychlorInated blohenyls. pure
water, and Inorganic, and organic cheirlcals Here
dally evaluated against as many as ten marine
solution organisms. The authors noted that «ost
renewal) published data of this type deal with
toxlclty of chemicals to freshwater
organisms.
same as above
a«(contin-
uous, aer-
ation, soa-
water, end
dally
solution
renewal)
a«(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, et
at (117H,
AHIC-7701
Portmann,
al (is^i)
AHIC-7701
et
Portnann, et
al (1«»71),
AMIC-7701
Nickel sulfate (as
nickel)
Ostrea edulIs BSA
100-150 (T2)
a«(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
Portmann, et
al (1971),
AMIC-7701
Nickel sulfate (as
nickel)
Panda I us
•ontagul
BSA
13.9
-------
Co»oound
Orqanls"
Field Flela
Study Location
Toxlclty,
Active
Ingredient,
Pom
Exoerlmental
Variables.
Control led
OP Noted
C orrtnent s
Reference
Michel sulfatu (»s Sal»o
Ml? plus) qalrdnerl
(eggs and
soer«)
BSA
1.0 (NTE)
U)
(Ti.)
61, (Til.)
0.5-10.0 (16
percent groxth
lnhlbltedl<>)
Data were qlven In mq/l which was Shaw, et at
taken to Be the equivalent ol eon. (1971),
Fertilization rates were statistically AMIC-Hfc".
similar In both test (Cu and NI) and
control Hflter*;. The r^tp of hatching was
significantly different for eqqs exposed
to Cu and the rate of develoorrent was
Increased. The authors concluded that In
hard waters neither Cu nor Nl is likely
to Impair fertilization in rainbow trout.
a*,c,d,e,t EphemereI I a (mayfly) was the nest Warnlck, et
sensitive aquatic Insect of those
studied, and cooper the most broadly
toxic metal. The authors suqqest 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,f
same as above
al (1969),
AHIC-1767
Warnlck, et
al (19*9),
AMIC-376?
Warnlck, et
al (19F.9),
AHIC-376T
Otto (1970),
AHIC-89Z
0.5-1.8 (T3)
Of 7
-------
Nickel
Coreqonus FL Moos« Lake, 0.2 (residue)
clupeaformls Can.
U)
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Fsox luclus FL
Esox luclus FL
Esox lucius FL
Osmerus FL
•ordax
Perca FL
flavescens
Coreqonus FL
clupeaformls
Moos* Lake,
Can.
Lake St.
Pierre. Can.
0.2 (residue)
0.7 (residue)
Lake Erie,
Can.
Lake Erie,
Can.
Lake Erin,
Can.
Lake
Ontario,
Can.
0.2 (residue)
0.2 (residue)
0.2 (residue)
0.? (residue)
mixtures of cooper and phenol I copper,
zinc, and phenol I and copper, zinc, and
nickel. It was concluded that acute
lethal toxlcltles of the mixtures could
be adeauately described by summations of
the fractional toxlcltles.
Concentrations of 13 toxic
elements In dressed fish 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 from both
areas.
same as above
same as above
same as above
same as above
same as above
same as above
lithe,ef al
(1971),
AMIC-3819
Uthe, et al
(1971), AMIC-
3819
Uthe, et
OLH971),
AHIC-.T819
Uthe, et al
(1P71) ,AMIC-
3S19
Uthe, et al
(1971) .AHIC-
3819
Uthe, et al
(1971) .AHIC-
3819
Uthe.et al
(1971) ,
AMIC-3819
Nickel
Paralabrax FH
clathratus
Scattergood
Steam Plant,
LosAnqeles,
Cal.
5 (dorsal
muscle
residue)
Fish collected from an eftt.uent
pipe of a steam plant and from offshore
waters of Catallna Island were analyzed
for trace element content. Trace element
content of the effluent water was at
least 5 times qreater than that of normal
sea water for cadmium, cooner, 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, cadmlun, and nickel.
Staoleton
(1968) ,
AMIC-5980
-------
u>
Co«oound
Nickel
Hick«l
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Nickel
Organism
Paral ahrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Para 1 abrax
cl athratus
Paral abrax
cl Rthra tus
Para 1 ahrax
cl athratus
(gravid
females)
Paral abrax
cl athratus
Paral abrax
cl athratus
Psral abrax
el athratus
Field
Study
FM
FM
FM
FH
FM
FM
FM
FM
FM
Field
Locat 1 on
Ca t al Ina
Island, Cal .
Scatterqood
Steam Plant,
Los Angeles,
Cal.
ratal Ina
Island, Cal .
Scatterqood
Steam Plant,
LosAngeles,
Cal .
Catal Ina
Island, Cal .
Catal Ina
Is) and, Cal .
Scatterqood
Stean Plant,
LosAnqeles,
Cal.
Catal Ina
Island, Cal .
Scatterqood
Stean Plant,
LosAnqeles,
Toxlcl ty.
Active
Tnqred lent ,
Ppm
6. i> (dorsal
muse 1 e
residue)
5.8 (ventral
muscle
residue)
6.1 (ventral
muscle
residue)
l8) ,
AHIC-'IISO
same as above Sfaoleton
(l«f.M ,
AMTC-S-JSIl
— same as above Sfaoleton
(1968) ,
AMic-sgso
-- same as above Staoleton
( l°fiB) ,
AMIC-5980
— same as above Sfapleton
(1968) .
AMIC-5980
~ same as above Staolefon
(19SM ,
AMIC-5980
same as above Staoleton
(196(1) ,
AMIC-5980
-- same as above Staoleton
(1968) ,
AMIC-5980
-------
Nickel
Nickel
Nickel
Puralabrax FM Catatlna in.2
clathratus Island, Cat. (Integument
residue)
Paralabrax FM Scatterqood 6.1 (heart
clathratus Steam Plant, residue)
LosAngetes,
Cal.
Paralabrax FM Catallna 10.8 (heart
clathratus Island, Cal. residue)
same as above
same as above
same as above
S tapIeton
(1966),
AMIC-5910
S t a o I e t on
(1968),
AMIC-59SO
S taoleton
(1968) ,
AMIC-5980
u>
u>
U>
Nickel
Nickel
Nickel
Nicotine
Nicotine
Paralabrax
clathratus
Paralabrax
clathratus
Salno
galrdnerl
Negaprlon
brevlrostrls
(1-3 kg)
FM Scattergood 6.
mixtures of coooer and phenolt copper,
zinc, and phenolt anrt copper, zinc, and
nickel. It was concluded that acute
lethal toxlcltles of the mixtures could
be arteouately described by summations of
the fractional toxlcltles.
Data from study of drug effects
on younq lemon sharks were treated
mathematically to demonstrate
app11 caniI 11y of classical rate theory to
the study of chemical shark deterrents.
IncaoacItation (narcosis) was the primary
parameter timed for effectiveness. This
was usually quite rapid for the more
effective drugs.
This experiment showed that Konar
nicotine could be successfully used to (1970),
llve-csoture fish from reservoirs. Fish AHIC-5
-------
U)
.p-
Conoound
Nicotine
Nicotine
Nicotine
Nicotine
Nitric acid
Nitric acid
Nitric acid
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppm or Noted Comments
Puntlus L ~
soohore
Panatra I —
fl llformls
Dytlscus so. L
Heteropneus- t —
tes foaallls
Agonus BSA —
cataohractus
Aster las BSA
rubens
rarclnus BSA —
naenas
1.0 (SB7) a.d.e.f
<>0 (NTE7) a,d,e,f
<»00 (NTE7) a,d,e,f
3.2 (SB 5 hr), —
K 1« hr)
100-330 (T2> ^(contin-
uous aer-
ation, sea-
vater, and
dally
solution
renewal )
100-330 (T2) a»(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal )
180 (T2) »*( contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal )
same as above
same as above
same as above
Epidermal lesions of catfish
barbels Here moderate to severe after
exposure noted. Barbel curling and
Inactlvatlon Here associated effects.
One hundred- f or ty surface active
aqents, solvent emulslflers, pesticides.
pol yen lorlna ted blohenyls, 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 xlth
toxlclty of chemicals to freshwater
organisms.
sane as above
same as above
Pe f er ence
Kon ar
An-IC-UjS
Konar
(1970) ,
Kon,r
(1970) ,
Koner (1969) ,
AMIC-'57?f)
Port mann.
at (1971)
AMIC-7701
Por t mann.
al (1<>71)
AMIC-7701
Portmann,
al
• t
,
et
(
et
(1971). AMIC-
7701
Nitric acid
Cardlua «dul« BSA
330-1000 (T2> a*(contln-
ssme as above
Portnann, «t
-------
uous, aer-
ation, sea-
water, and
daily
solution
renewal)
at (1971),
AMIC-7701
OJ
vn
Nltrllotrlacetlc
•eld (NTA)
Nltrllotrlacetlc
acid (NTA)
Mlfpllotrlacetlc
acid (NTS)
HItrllotrlacitlc
•Cld (NTA)
Amohldlnlum I
carterl
Chaetoceros I
so
Cvclotella L
nana
Ounnllvll* I
tertlolecta
10 (NTE)
10 (NTE)
10 (NTE)
10 (NTE)
SSH and
NSW
SSM and
NSW
SSM and
NSW
SSM and
NSW
NTA stimulated algal growth In Frlckson, et
cultures without added coooer and reduced a! (1970),
toxlclty of cooper at all levels of AMIC-fcit9
cooour addition. See InTormation on
CuCI2.H20 (as Cu) under authors cited for
further Information.
same as above
same as above
same as above
Erickson, et
al(1970),
AHIC-f.i.9
ErlcK-son, et
al(1970),
AHIC-
-------
Co»ooun1
Field Field
Orqanlsm Study Location
Toxlclty.
Active
Tngredlen t,
Ppm
Experimental
Variables,
Controll«d
or Noted
Comments
Ref erence
Nl trofurazone
>
CO
Nl frof urazone
Mltroqen
(dissolved)
HI troqen
(dissolved)
Nltroqen
(dissolved)
Mercenarla
mercenarla
(eqqs)
greater than
100.0
Hercenarla
•ercenarla
(larvae)
Oncorhynchus
tshawytscha
(Juveniles)
i _^
FR.BS Priest
CH RaPlds Oam,
Hash.
qreater than
100.0 (T12)
Super
saturation
CK5<.)
Salvo
qalrrtnerI
(adults)
Oncorhynchus
klsuteh
(Juveniles)
FR
FR,
BSCH
McNary Oam
Hash.
Priest
RapldsDan,
Hash.
Suoersaturatlon •
(NTE 35)
Super
saturation
(6-16 percent
The effect o( *>Z pesticides on
embryonic development of claws and
oyst»rs Has reported. Synnrqlstlc
effects Kith solvents Here also reoorted.
Most of the compounds affected
develocment more than survival. Some,
hoxever, drastically reduced larval
qrOHth. The authors point out the
necessity of evaluatinq the effects of
pesticides on all life staoes of an
oraanlsn and note the possibility of
setectlnq chemicals for pest control that
HOU I fi not have serious effect on
shell fish.
same as above
Davis,et al
(1969),
AMIC-5990
The nltroq»n qas regime In the
Columbia River Has studied In 1966 In
order to determine whether hlqh levels of
dissolved nltroqen miqht be responsible
for losses of adult salmon and poor
production of younq fish at spawning
channels. Examinations of dead (uvenlle
salmon revealed that most fish had
symptoms of "qas bubble disease".
Juvenile salmon kept at sufficient depth
to compensate tor the supersaturat1 on of
dissolved nltroqen Here free of symptoms
of qas bubble disease. Fish under stress
from the supersaturatIon of dissolved
nitrogen were very Intolerant to
temperature Increases.
same as -above
Davis, et al
(1969).
AHIC-5990
Ebel (1969
AHIC-6198
Ebel (1969),
same as above
Ebel (1969),
AMIC-6198
-------
U)
Nitrogen
(dissolved)
HI, Cu, Cr, CN,
Zn (Mastenater)
and
Oncorhynchus
nerKa
(adults)
Plmeohales
prone las
FR
McNary Dam,
Wash.
BSACF Grand River
(ML) at Wyoming,
Michigan
MI, Cu, Cr, CN, and Catostomus
Zn (Kasteiiater) commersonl
Nonyl phenol 12
(olus ethylene
oxide)
Nonyl phenol 12
(plus ethylene
oxide}
Carcinus
maenas
BSACF Grand River
(ML) atwyomlng,
Michigan
BSA
Cardlum edule BSA
SuoersaturatIon a
(SB35)
same as above
approx. 1.67
percent (T3)
betHeen
1.25-3.75
percent con- A mobile bloassay unit Has
duotlvlty, utilized to conduct this study of
Nl,Cu,Cr, municipal nasteHater containing the
CN, and Zn Indicated toxicants. River nater Has
used as diluent. The conclusion Has
reached that synerglstlc or 8ddltlv«
toxic effects occurred since toxlclty was
greater than that of any of the ions
singly.
Ebel (1969),
AMTC-619S
71111ch
(1969),
AMIC-2906
a,c,e, con-
ductivity,
Nl.Cu.Cr,
CN, and Zn
same as above
Z1111ch
(1969),
AMIC-2906
a«(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
a*(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
One hundred-forty surface active Portmann.et
agents, solvent emulsltlers, pesticides, al (1971),
polychtorlnated blphenyls, oure AMIC-7701
Inorganic, and organic chemicals 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
organls*s.
same as above Portnann, et
al
(1971),AMIC-
7701
Nonyl phenol 12
(plus ethylene
oxide)
Cranqon
cranqon
BSA
S9.5 (T2)
a»(contin-
uous, aer-
ation, sea-
wator, and
dally
solution
renewal)
same as above
Portntann, et
al
7701
Nonyl phenol 12
(plus ethylene
oxide)
Pandalus
•ontaqul
BSA
19.3 (T2J
at (contin-
uous, aer-
ation, saa-
same as above
Portnann, et
*l
(1971),AMIC-
-------
Co«oourv]
Organls"
Field Field
Study Location
Toxlelty,
Active
Ingredient*
Po«
Experimental
Variables,
Control led
or Noted
Comments
Ref erence
water, and
daily
solution
renewal)
7701
Korea
Gamnarus
fasclatus
BSA —
>
CD
Cranqon
crangon
BSA
3.3-10 (Ti,)
NPH 1Z53
Rasbora
heteromorpha
BCFA
and
BSA
O.li. (121
NPH 1313
Rasbora BCF» —
heteronorpha and
BSA
11 (T2I
a* Of the aquatic weed herbicides Sanders
evaluated, Olclone Has the most toxic, (1970),
Oaohnla was generally the most sensitive AHIC-1.5J
organism. fill 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 Important food chain linKs.
a*(contin- One hundred-forty surface active Portaann, Qt
uous aer- agents, solvent emulslflers, pesticides, al 11971),
atlon, sea-polychlorinated blphcnyls, pure AMIC-7701
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 tyoe deal with
toxlcity of chemicals to freshwater
organisms.
a',c,e,f,
hard (HH)
or
SOFT(SH)
synthetIc
dilution
water, or
seawater
for
some
specie s
a*,c,e, f ,
hard (HH)
or soft
One hundred sixty-four Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a AMIC-5«i25
Hide range of toxlcity spanning 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 were most toxic In hard Mater
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
same as above
AIabaster
(1969),
AMIC-51.ZS
synthetic
dilution
Hater, or
-------
NPH 1313
Rasbora BCFA
heteromorpha and
BSA
5.0 (T2)
Noeldo I dlazlnon
sheep dip
Rasbora BCFA
heteromorpha and
BSA
(Tl)
U)
uo
vo
Nystatln
Phormldlui
amblquun
N-«ethyl carbamate
derlvltlve
Rasbora
heteromorpha
BCFA
and
BSA
0.58 (TZ)
seawater
for some
species
a«,c,e,f.
hard (HW)
or soft
(3W) syn-
thetic
dilution
water, or
seawater
' for'some
species
a*,c,e,f,
hard (HW)
or soft
(SWJ syn-
thetic
dilution
water, or
seawater
for some
species
O.S-10.0 (NTE) —
a»,c,e, ft
hard (HH)
or soft
(SW)
synthetic
dilution
Hater,or
seanater
for some
same as above
Alabaster
(1969),
same as above
Alabaster,
C1<)69),AMIC
5112-5
Of Tit chemicals evaluated as
alqlcldes, only 9 were more toxic than
CuSO"t. None Inhibited qronth of
mat-formlnq algae for more than 2 xeeks.
CuSO<» formulated Hlth certain netting
aqents Has more toxic than CuSO<» alone.
Conner chloramlne Has also found to be
more toxic than CuSOit. No Netting aqents
Here found to be Inhibitory at the
concentrations Investigated (0.05 and
O.OOS ppml. Also reported are factors
affecting groHth of alqae In canals to
determine Hhether there were leads to
controlling algae by environmental
management. No practical environmental
means were found.
One hundred sixty-four
pesticides, netting agents, and
miscellaneous Hater pollutants shoned a
Hide range of toxlclty spanning 12 orders
of magnitude. 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. Sometimes
Otto (1970),
AHIC-89Z
Alabaster
(1969),
-------
Compound
Field Field
Organise Study Location
Toxlcl ty,
Active
Ingredient,
Ppm
Experimental
Variables,
Control 1 ed
or Noted
Comments
Ref er ence
species
M-3511,
N-35K.
N-351V
Octyl phenol 11
(olus ethylene
oxide)
Cra*sostr«a
vlrglnlca
(eggs)
Crassostrea
vlrglnlca
(larvae)
Carclnus
•»enas
less than 0.5
Crassostrea
vlrglnlca
(Iarvae)
Mercenar1 a
mercenarla
(eggs)
Mercenarla t-
•ereenarla
(larvae)
Crassostrea L
vlrglnlca
(eggs)
less than 0.5
(Til.)
less than 1.0
BSA —
less than 1.0
less than 1.0
(T2)
less than 1.0
(T1U)
pesticides were most toxic In hard water
and sometimes the oooosite was true.
Testing the actual material as sold was
found to be essential.
The effect of 12 pesticides on Davis, et al
embryonic development of clams and
oysters Has reported. Synerglstlc (1969),AMIC-
effects with solvents were also reported. 5990
Most of the compounds affected
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 staaes 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
sane as above
same as above'
same as above
same as above
Davis, et
al (1969).
Oavls, et al
(1969) , »HIC-
59911
Oavls, et
al (1969) ,
greater thanlOO a' One hundred-forty surface active
(TZI (contlnuou agents, solvent emulslflers, pesticides,
s poIychI orInated biphenyls, pure
aeration. Inorganic, and organic chemicals Here
seawater, evaluated against as many as ten narlne
Oavls, et
al (1969),
AMIC-5990
Davis, et
al (1969),
AMIC-5990
Por t mann, et
al (1971),
AMIC-7701
-------
Oetyl phenol It
(plus •thylen*
oxide)
Car dl urn edule BSA
19.6U2)
and daily organisms. The authors noted that most
solution published data of this type deal tilth
renewal) toxlelty of chemicals to freshwater
organisms*
a»(contin-
uous aer-
ation, sea-
wator, and
dally
solution
renewal)
same as above
Portmann, et
al(1971),
AMIC-7701
Oetyl phenol 11
(plus ethylene
oxide)
Crangon
crangon
8SA —
63(11.)
a«(contin-
uous, aer-
ation, 3oa-
water, and
daily
solution
renewal)
sane as above
Portaann, et
al(19711,
AMIC-7701
Oetyl phenol 11
(plus ethylene
oxide)
Pandalus
montaqul
BSA
10.8 (TZI
a»(contin-
uous, aer-
ation, sea-
water, and
dally
solution
renewal)
same as above
Portiiann, et
al(1971),
AMIC-7701
Oetyl phenol 11
(plus ethylene
oxide)
Platlcthys
flesus
BSA
33-100 CT2)
a«( contin-
uous , aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al
(1971),AMIC-
7701
00
Fundulus
heteroelItus
BSA —
0.0005 (TM a*,c,e, « laboratory orocedure based on
and Standard Methods for 96-hr toxlelty
synthetic determinations of crude oil and
seawater oll-dlspersant mixtures was described.
'The dlspersants varied considerably In
toxlelty, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr. These did not differ
slqnl f Icantl y from ?<»0 hr values. The
dlsoersants were designated as CX, DO,
Cl, 00, AO, PC, MM, TN, BP, and NA with
no further description of their chemical
nature or source. Only a few bloassays
were conducted Kith shrimp. HollusKs and
echlnoderms Here suggested as suitable
test animals. The authors stated that
the method could be used to test any
product for toxlelty In seawater.
LaRoche,«t
al (1970),
AMIC-l.i.5
-------
Co*oound
00
01 1 herder
Oil (crude)
Toxlclty,
Active
Field Field Ingredient,
Organism Study Location Pp»
Nereis vlrens BSA — 0 . 0001)
0.0061 (TI.)
0.00005 (T<»)
o.osi
a*.c,c,
and
synthetic
seawater
a'.c.e,
and
synthetic
seawater
a*,c,e,
and
synthetic
seawater
The dlspersants varied considerably In
toxlclty, ranging from 0.01 to 7.1 ml/I.
Tisn for g& hr. These did not differ
significantly from 2UO hr values. The
dlspersants were designated as CX, 00,
Cl, OH, «Q, PC, MM, TN, BP, and N» with
no further description of their chemical
nature or source. Only a few bloassays
were conducted with shrimp. Mo I Iusks and
echlnoderms were suggested as suitable
test animals. The authors stated that
the method could be used to test any
product for toxlclty In seawater.
same as above
LaRoche, et
al (1970),
AMIC-UUS
LaRoche, et
al (1970),
same as above
same as above
The effect of 52 pesticides on Davis, et al
embryonic development of clams and
oysters was reported. Synerglstlc (1969),AHIC-
effects with solvents Mere also reported. 5990
LaRoche, et
al (1970).
-------
Oaazene
Oaazene
CO
U>
Mercenarla
mercenarla
(larvae)
Crassostrea
vlrglnlcs
(eggs)
Crnssostrea
virqlnlca
I ——
OrthodlcMorobenzene Nercenarla
•ercenarla
(egas)
0.38 (T12)
0.078 (T2)
0.3U (Til.)
greater than
100.0 (TZ>
Orthodlchlorobenzene Hercenaria
mercenarla
(larvae)
Oxlne-copper
Salno
galrdnerl
L —
BCFA
and
as*
greater than
100.0 (T12)
0.1* (TZ)
Most of the compounds affected
development more than survival. Sone,
how«?vert drastically reduced larval
growth. The authors oolnt out the
necessity of evaluating the effects of
pesticides on alt life stages of an
organism and note the possibility of
selecting chemicals for pest control that
Hould not have serious effect on
shellfish.
same as above
same as above
same as ahove
DavlSt et al
(19S9I,*MIC-
5990
Oavis« et al
(1969), »HIC-
5990
Davis, et al
5990
Oavls, ef al
(1969),
AHIC-5990
— The effect of 52 pesticides on
embryonic development of clams and
oysters was reported. Synerqlstlc
effects Hlth solvents Here also reported.
Most of the compounds at fected
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 Oavls, et al
(1969),
AMIC-5990
a»,c,e,f. One hundred sixty-four Alabaster
hard (HH) pesticides, wetting agents, and (1969),
or soft miscellaneous water pollutants showed a AHIC-5«25
(SM)synthe wide range of toxlclty spanning 12 orders
tic of magnitude. Knowing the toxlcitv and
dilution percentage of all components of a
water, or formulation did not result in easy
-------
Toxlclty, Experiments!
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Pom or Noted Comments
seawater predictability of the toxlclty of a
for some 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.
Oxygen Leoonls BCF -- 0 to saturation a,e» Fish 15-20 cm long Mere exposed
macrochlrus to gradual hycoxla stress to determine
the effect on skeletal muscle and liver
Reference
Burton
(1970) ,
AMIC-6385
>
o-dIchIorobenzene
(50 percent plus ?0
percent crescyllc
•eld)
Rasbora
heteromorpha
8CF»
and
BSA
5.0 (T2>
0,0—dlethyl o-?
pyrazlnyl
phosphorothlate
Rasbora
heteromorpha
BCFA
and
BSA
0.05U2I
a*,c,e,f,
hard (HH)
or
SOFT(SH)
synthetIc
dilution
water,
orseawater
for some
species
a*,c,e,f.
hard (HH)
or soft
(SH)
synthetic
dl lutlon
water, or
seawater
for son*
species
lactate and oyruvate. Tests were
conducted at S and 20 C with 00 reduced
from saturation to zero over an 8-hour
period. Low HO Increased lactic acid
concentrations In muscle and liver at
both temperatures! pyruvlc acid levels
remained constant. Lactic acid levels
were higher at 5 C than at 20 C. and fish
were better able to tolerate low oxygen
levels at the lower temperature*
One hundred sixty-tour Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a ANIC*5
-------
Paraquat-dl
f•ethyl) chloride
Rasbora BCFA —>
heteromorpha and
BSA
3? (T2)
Paraquat
Chars so
<£
VJI
Paraquat
Paraquat
Paraquat
Paraquat
Paraquat
Hater FL
(bottom)
Hud
FL
Splrogyra sp FL
Chara sp FL
Splroqyra sp FL
Jefferson
County.t
Colo.
a*,c,e,f,h
ard (HM)
or soft
(SH)
synthetic
dilution
water, or
seawater
for some
species
a,c,d,e,g,
and water
stage
sane as abova
Alabaster
(1969).»HIC-
Jefferson
County.,
Colo.
Jefferson
County.,
Colo.
Jefferson
County.,
Colp.
Jefferson
County.,
Colo.
Jefferson
County.,
Colo.
1.14 (1.9 ppa
max residue?
hr)
1.14 (19.9 ppa
maxresldue 16
residue I6d)
1.14 (K16)
1.14 (2300 ppm
max tissue
residua 8d)
1.14 (1300 ppm
max tissue
residue l|d) >
a>c,d,e,g,
and water
stage
a,c,d,e,q,
and Hater
stage
a,c,d,e,g,
and Hater
stage
a,c,d,e,g,
and Hater
stage
a,c,d,e,g,
and Hater
stage
Paraquat almost eliminated Chara
sp. In 16 days and gave Initial control
of Solroeiyra sp. The latter recovered
.Hlthln 3 mos. Fish deaths and other
effects occurred Hlthln <>B hr. Paraquat
Has recovered from mud 99 days after
application. Indication that this
herbicide can be very persistent. This
study was conducted In 196<>. Llvecar
exposure of some fish Has one technique
employed.
same as above
same as above
sane as above
same as above
same as above
Earnest
(1971J,
AHIC-S96*
Earnest
(1971I,»HIO
9964
Earnest
(1971),
AHIC-5564
Earnest
(1971),
AMIC-S954
Earnest
(1971),
AKIC-5964
Earnest
(1971),
ANIC-9964
Paraquat
Paraquat
Rainbow trout FL
Channel FL
catfish
Jefferson 1.1 (1.9ppm max a,c,d,e,g.
County., tissue Land water
Colo. residua Id) stage
Jefferson 1.1 (1.3 ppm a,c,d,e,g.
County., max and Hater
Colo. tissue 1 stage
residue Id)
sane as above
same as above
Earnest
(1971),AMIC-
9964
Earnest
(1971),
ANIC-9964
-------
Compound
Field Field
Organism Study Location
Toxlcl ty,
Active
Ingred lent.
Pom
Experimental
Varl abl es,
Contro 1 1 ed
or Noted Comments
Ret er pnce
>
Paraquat
Paraquat
Paraquat
Paraquat
Green sunflsh FL Jefferson
Count/. t
Colo.
Hlueqllls FL Jefferson
County.,
Col o.
Hater (top) FL Jefferson
Count y.«
Colo.
Cardlum edule BSA —
Paraquat
Crangon
cr anqon
BSA
same as above
same as above
1.1 (2.1ppm max a*c«d,e,g, same as above
tIssueres1 due and water
16 d) stage
1.1 (1.6 ppmmax a,c,d,e,g,
t Issueresldue 8 and Mater
d) stage
l.l
-------
Parathlon (Sesamex
ppetpeatment at 2
DP")
Parathlon (Sesamex
oretpeatment at 2
ppn)
PsPathlon (Sesamex
ppetpeataent at 2
DO*)
P»rathlon
>
U)
PaPathlon
Papathlon
Parathlon
Papathlon
Papathlon
Notemlgonus L
chrysoleucas
Lepomls
cyaneI I us
Lenomls
macpochlpgs
Leoomls
macrochlrus
(brain
tissue)
Plmephales
promel35
Plmeohales
promelas
BCF» —
BCFA —
Notemlqonus L
chpysoleucas
Lepomls
cyanellus
0.20 (
-------
Compound
Field Field
Organls* Study Location
Toxlclty,
Active
Ingredient v
Pp«
Experimental
Variables,
Control 1 ed
or Noted
Comments
Reference
Parathlon
Lepomls BSA —
cyaneIlus
(Peslstant)
0.28 (T2>
Green sunflsh from Belzonl, Miss. Mlnchen, et
Here resistant to Chlordann, Heptachlor, al(1970l,
Llndane, and Strobane, but not to
Parathlon. Golden shiners from the same
location Here resistant to Llndane and
Strobane, tolerant to Chlordane and
Heptachlor, and susceptible to Parathlon.
Lack of resistance to Parathlon
Indicated lack of agricultural usaae of
organochosphates In that area. Resistant
fish nere compared to susceptible ones
collected at Starhvllle.
Parathlon
Leoomls
eyanel(us
(Susceptible)
BSA
0.21 (T2>
B»
same as above
Hlnchen, »t
al(1970),
Parathlon
Parathlon
Notemlgonus
crysoIeucas
(Resistant)
Notemlqonus
crysoleucas
(Susceptible)
BSA —
BSA
2.80 (T2)
1.90 (T2)
same as above
sane as above
Mlnchen, et
al(1970),
AMIC-51.71
Mlnchex,
etal (1970).
AMIC-51.71
Parathlon
Parathlon
Palaemonetes
kadiakensIs
(non-
real 3 ton t)
Pataemonetes
kadlakensls
(resistant)
BSA —
BS»
0.0071 (Tl)
0.0066-0.0111
(Tl)
8»
same as above
Naovl, et al
(1970),
AMIC-5519
EUoassays Here conducted Hlth
shrlnip from three areas of Intensive
pesticide use and from an unexoosed area.
Previously exposed shrimp Here front 1 to
25 times more resistant than unexposea
shrlmo. Both types of shrimp Here 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
order Has as follows! most toxic,
Cndrln, DOT, Methyl parathlon, Parathlonl
medium toxlclty, Guthlon, Llndane,
Naov/1, et
(19701,
AMIC-5519
• I
-------
ParsthI on
Notemlgonus
crysoleucas
0.5 (SB 1-3)
Parathlen
Tublfex
tub If ex
FL
and
BSA
Belzonlt
Hiss.
2.00 (NTE)
Parathion
Cardlum edute BSA —
3.3-10
Parathion
Crangon
crangon
BSA
0.003-0.01
(T2)
Toxaohene, Strobanel lease toxic
Chtordane, Sevln, and Heotachlor.
— Fish exposed as indicated had Butler, et
significant or highly significant changes al (1969),
In hematocrlt, leucocytest lymphocytes, AHIC-5977
heteroohllst and In body weight. No
significant changes Here noted In body
length, or erythrocyte total and
fragility. The authors state that
effects on hemoooelsls and cell membranes
could produce the results reported.
« The response of Naavl, ctal
pesticide-resistant aquatic organisms to (1969),
various pesticides was compared to the AMIC-5979
response of non-resistant species.
Pesticide-resistant species Here
collected at Selzonl and non-resistant
soecles at State College. Cooeoods,
clams, snails, and sludge worms fro*
BelzonI 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 amount of
pesticide residues available to animals
of higher trophic levels.
a»(contln- One hundred-forty surface active Portnann, «t
uous aer- agents, solvent emulslflers, pesticides, al (1971),
ation, sea-polychlorinated blphenyls, pure AMIC-7701
water, and Inorganic, and organic chemicals Here
dally evaluated against as many as ten marine
solution organisms. The authors noted that nost
renewal) published data of this type deal with
toxiclty of chemicals to freshwater
organisms.
sane as above
a»(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
Portmann, et
al (1971),
AMIC-7701
Parathion
Pleuronectes
platessa
BSA
0.03-0.10 (T2)
a«(contin-
uous aer-
ation, sea-
water, and
same as abova
Portnann, «t
al (1971),
AHIC-7701
-------
Compound
ra thlon
Toxlclty,
Active
Field Field Ingredient,
Organic* Study Location Pon
Ictalurus 8CFA — 0.8-3.0 (K up
Exper 1 men tal
Variables,
Control 1 ed
or Noted Comments Reference
daily
solution
renewal )
a*,c,d,e,f Catfish blood content of Mount, et si
correlatable with water content, AMIC-11
00
VJ1
o
Parathlon
PCB
Ictalurus
nehulosus
BCFA --
10-80 (blood
residue)
Hhlte sucker FRL Misc. states 0.27-l
-------
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
Goldfish
FRL Nlsc. states 9.50 residue
(SRI
Pumoklnseed FRL Misc.
Larqemouth FRL
bass
Brown
bullhead
Carp
Channel
catfish
FRL
FRL
Redhorse FRL
sucker
Spotted
sucker
Blueqllls
Redbreast
sunfIsh
Strloed
•ullet
FRL
states 7.68 residue
(SB)
Misc. states less than
0.10-8.07
residue (SB)
Hlsc. states 0.3<»-it.OD
residue (SB)
FRL Hlsc.
states less than
0.10-11.7
residue (SB)
Misc. states less than
0.10-6.77
residue (SB)
Hlsc. states less than
0.10-0.25
residue (SB)
Gizzard shad FRL Misc.
States 0.22-0.86
residue (SB)
Misc. states less than 0.10
residue (SB)
FRL Misc. states 0.35-1.19
residue (SB)
FRL Misc. states 0.15 residue
(SB)
FRL Misc. states less than
0.10-1.39
residue (SB)
sane 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
same as above
Henderson i
et at
(1971),AMIC-
11.07
Henderson*
et al (1971),
AMIC-K.07
Henderson,
et al
(1971),
AMIC-11.07
Henderson,«t
al (1971),
Anir.-n.o7
Henderson,et
al (1971),
AMIC-li.07
Henderson,
et nl
(1971),
AMTC-ll.07
Henderson,
et al
(1971),
AMIC-11.07
Henderson,et
al (1971),
AMIC-1<(07
Henderson,et
al (1971),
AMIC-Ht07
Henderson,
et al
(1971),AMIC-
11.07
Henderson,
et al(1971),
AMIC-11.07
Henderson,
et at
(1971),
-------
Compound
PCB
PCB
PCB
^" PCB
vn
f\>
PCB
PCB
pcb
PCB
PCB
PCB
PCB
Orqanlsm
Blue cattish
Rock bass
Freshwater
drum
ni oater
Lake
xhltef Ish
Lake trout
Hhlte crapple
Blqmouth
buffalo
Smal 1 mouth
buffalo
Flathead
catfish
Col day*
Field Field
Study Location
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FRL Misc. states
FPL Misc. states
Toxlclty, Experimental
Active Variables,
Inqrertlent, Controlled
Ppm or Noted
less than 0.10
residue (SB)
0.39-
-------
4HIC-1I.07
PCB
PCB
Hal I eye
Sauqer
FRL
Misc. states O.ZZ residue
-------
I
UJ
Coaoound
PCB
PCB
PCB
PCB
PCB
PCD
PCB
PCB
PCB
PCB
PCM
OrqanI s«
Br Idqel ID
sucker
Arctic
gray 1 Ing
Pound
whltef Ish
Longnose
sucker
Sebastodes
SD.
Paral ahrix
nebul 1 fer
An 1 so tremus
davldsonl
Plmel ometaoon
pu 1 chrun
Hal lot Is
ruf escens
Stronqylocent
rotus
franclscanus
HInnI tes
•ul tlrugosls
Field
Study
FRL
FRL
FRL
FRL
FO
FO
FO
FO
FO
FO
FO
Flel d
Locat Ion
Misc. states
Misc. states
Misc. states
Misc. states
Paclf Ic
Ocean, Cal.
Paclf ic
Ocean , Ca 1 .
PacI T Ic
Ocean , Cal.
Paclf Ic
Ocean, Cal.
Paclf Ic
Ocean, Cal.
Paclf Ic
Ocean, Cal.
Pacific
Ocean, Cal.
Toxlcl ty.
Active
Ingredient,
Pom
2.75 residue
(SB)
1.U2 residue
-------
PCB
PC8
PCB
PCB
U)
V/1
vn
PCB
PCB
PCB
PCB
PCB
PCB
PCB
PCB
Ha I Iotls FO Pacific 0.008 (gonad
corruqata Ocean, Cal. residue)
Kelletla FO Pacific 0.23 (residue)
kelletll Ocean, Cal.
PinulIrua FO Pacific 0.16 (muscle
Interruptus Ocean, Cal. residue)
AnqulI la
rostrata
FRL Sr. John, 0.71 (residue)
N.B., Can•
Sabaatodes FRL
marlnus
Esox nlqer FRL
1 mo salar FRL
Clupea FRL
harengus
Scomber FRL
scombrus
Mytllus FRL
edulIs
Gadus morhua FRL
Uroohycls FRL
tenuls
St. John,
N.B., Can.
St. John,
N.R., 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.R.i Can.
trace
(residue)
0.33 (residue) —
0.1.5 (residue) —
0.32-O.Si.
(residue)
0.35 (residue) —
O.I* (residue) —
0.02 (residue) --
0.02 (residue) —
sane as above
same as above
same as above
PCB"s Mere found In higher
concentrations than orgarochlorine
pesticides In all fish analyzed. The
authors point out that PCB is less toxic
in an acute sense than organochlorines,
that little Is Known of sublethal PCB
effects, and that more Knowledge of PCB
distribution and effects Is needed.
same as above
same as above
same as above
same as above
same as above
same as above
same as above
sane as above
Hunson
(1972), AMIC-
3096
Hunson
(19721,
3096
Munson(1972)»
AMIC-3096
ZItKo
(1971»i
AHIC-371S
Zltko
(1971),ANIC-
3715
Zitko
(1971), AMIC-
3715
Zltko
(1971)
3715
71tKo(1971),
AMIC-3715
ZItKo
(1971), AMIC-
3715
ZItKo
(1971), AMIC-
3715
ZItKo
(1971), AMIC-
3715
ZItKo
(1971), AMIC-
3715
-------
UJ
Compound
PCB
PCB
PCS
PC8
PCB
PCS
Toxlclty, Experimental
Active Variables.
Field Field Ingredient, Controlled
Orqanlsm Study Location Ppm or Noted Comments
Hippo- FRL
glossoldes
platessoldes
Falco F
pereqr Inus
(eqqs)
Fslco F
oer»qr Inus
(Immature)
Falco F
pereqr Inus
( immature)
Falco F
pereqr Inus
(adul t)
Falco f
pereqr Inus
(adult)
St. John, 0.03 (residue)
N.R., Can.
Western 10.3 (residue)
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western 0.l6-8<» (flesh —
U.S., residue)
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western 3.?-l,t'>
Rlsebrough,
et al
(1968).
-------
PCB
PCB
r
^3
PCB
PCB
PCB
PCB
Loonelanla
nelanla
Haloeyotena
microsona
PlTOnyx
vlvesl
Enrlomychura
craverl
(eqgs)
Thaiasseus
eleqans
(eggs)
Larus
heernanl
(eggs)
Ocean,
Panama,
Mexico,and
Antarctic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Panama,
Mexico, and
Antarotic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
PaclfIc
Ocean,
Panama,
Mexico,and
Antarctic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
1.0 (xhole body
residue)
0.35 (whole
body residue)
0.03 (Mhole
body residue)
It.5 (residue)
sane as above
same as above
same as above
sane as above
(residue)
sane as above
8.1 (residue)
sane as above
AHIC-381*
Rlsebrouqh,
et at
(1968).
AMIC-38M.
P-lsebrough,
et al
(1968),
AMIC-38**
Rlsebrough.
et al
(1968).
P. Isebrouqh.e
t al (1968),
AMIC-38i.li
Rlsebrougn,
et al
(1968),
RlsebrouQh,
eta! (1968),
AMIC-38W.
-------
(Jj
VJ1
CD
Conoound
PCS
PCB
PCB
PCB
PCS
PCB
Organism
Pomox 1 s
annul srls
Pomoxls
nlgro-
maculetus
Lepomls
macrochlrus
Pyqoscel Is
adotlae
(eqqs)
Ful man us
gl acial Is
Put f Inus
creaf opus
Field Field
Study Locat Ion
F Western
U.S.,
Paclf Ic
Ocean ,
Panam a ,
Hexlco, and
An tare t Ic
f Western
U.S.,
Paclf Ic
Ocean ,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pad t Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S. ,
Pacific
Ocean,
Panama,
Maxlco, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Hexlco, and
Antarctic
F Western
U.S.,
Pacific
Ocean,
Panama,
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
O.DOM ,
AMIC-38'.'.
Rlsebrough,
et al
(196») ,
AMIC-3»ii<.
R I sebrough.
et al
(1968),
AMIC-384*
RIsebrough,
et al
(1968),
AMIC-38". It
RIsebrough, e
t al (1968),
AMIC-38iti»
-------
PCB
PC 8
PCS
U)
VJ1
VO
PCS
PCB
pee
Puff Inus
grlseus
PuffInus F
tenulrostrls
Oceanodroma
honochroa
P*leeanus
occidental Is
(egqs)
Freqata
magnlf Icens
(egqs)
Sula
leucogaster
Mexico, and
Antarctic
Western
U.S.,
Pactf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Mestern
U.S.,
PaclfIc
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Paclt Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico,and
Antarctic
Western
U.S.,
PacltIc
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
PaclfIc
Ocean,
Panama,
Mexico, and
Antarctic
0.9-1.2 (whole
body residue)
2.1 (Hhole body
residue)
9.8 (whole body
residue)
0.010(1-0.0231
(residue)
0.0057-0.08".
(residue)
0.00<»8
(residue)
sane as above
same as above
same as above
same as above
same as above
sane as above
Rlsebrough,
et al
(1968),
ANIC-38
Rlsebrough,
et al
(1968),
AHIC-38I.I.
PIsebrouqht
et al
(1968),
ftMIO38<»<>
Risebrouqh,
et al
(1968),
AHIC-3SM»
Rlsebrough,
et al
(1968) ,
Rlsebrough,
et al
(1968),
AMIC-38<.<»
PCB
Phalacrocorax F
Western
0.113
sane as above
Rlsebrough,
-------
CoBDound
PC 8
PCB
PCB
PCS
PC a
Organism
oenlcl 1 latus
(eggs)
Phalacroeorax
oelaglcus
(eggs)
Anns
cyanoDtera
El anus
leucurus
(eggs)
ice loiter
eoooerl I
Aaul la
chrysaetos
(eggs)
FleM Field
Study Local Ion
U.S.,
Pad f Ic
Ocean,
Panam a*
M*»xl co» and
Antarctic
F Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F W»«:t«>rn
U.S.,
Paclf 1C
Ocean ,
Panam a.
Mexico, and
Antarctic
F Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pacific
Ocean #
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Paclf 1C
Ocean,
Panama,
Mexico, and
Antarctic
Toxlelty, Experimental
Active Variables,
Ingredlentt Controlled
Ppn or Noted Comments
(residue)
0.062 — same as above
(residue)
0.91 (whole — • same as above
body residue)
0.0008 -- same as above
(residue)
6.3 (whole body — same as above
residue)
0.23 (nhole -- same as above
body residue)
Reference
et al
(1968) .
AMIC-J8<.<.
Rlsebrough,
et al
(19>JB),
AMIC-38I.I.
Rlsebrough,
etsl (1968),
AMIC-38<.<>
Rlsebrouqh,
et al
(1968) ,
AHIC-38I><>
Rlsebrouqht
et al
(1968).
AMIC-38i.li
Rlsebrouqh,
et al
(1968) ,
ANIC-38I.I,
-------
PC a
PCB
PCS
U)
ON
PCB
PCB
PCB
PCB
Pandlon
ha I lavtus-
Falco
coI unbar I us
Fa I co
SDarverlus
Falco
SDarverlus
(eqqs)
Nyctleorax
nrctlcorax
(eggs)
Larus F
occidental Is
(eqgs)
Sterna
forsterl
(egqs)
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.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
Wastern
U.S.,
Paciric
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacific
Ocean,
0.003(1-0.103
(xhole body
residue)
0.39 (whole
body residue)
0.31 (Hhole
body residue)
0.09 (residue) —
sane as above
sane as above
sane as above
save as above
0.023-0.33
(residue)
0.023-1.31
(residue)
O.llit
(residue)
same as above
same as above
sane as above
Rlsebrough,
et al
(1968),
AMtC-IBItt
Rlsebrough,
et al
(1968) ,
AMIC-SSV",
Rlsebrough,
et al
(1968),
AMIC-38**
Rlsebrough,
et at
(1968),
AMIC-381,1.
RIsebrouqh,
et al
(1968) ,
AMIC-38I.I.
Rlsebrough,
et al
(1968),
AMIC-38I.I.
Rlsebrough,
et al
(1968).
AMIC-38**
-------
Conoound
PCB
PCS
PCB
PCB
PCS
PCB
Organ 1 sn
Hydrooroqn*
casola
(eggs)
Phalaroous
fut Icarius
Urla aalqe
(eqgs)
Ptychoranohus
al«utlcua
Synthl Iboranp
hus antlauu*
Cerorhlnca
•onocerata
Field Field
Study Location
Panama t
Mexico, and
Antarctic
f Western
U.S.,
PaclT Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
PacH Ic
Ocean ,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Paclf Ic
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Paclf 1C
Ocean,
Panama,
Mexico, and
Antarctic
F Western
U.S.,
Pacific
Ocean ,
Panama,
Mexico, and
Antarctic
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pen or Noted Comments
0.11<*-1.01 -- sane as above
(rest due)
0.10 (whole — sane as above
body residue)
Rlsebrough,
et at-
(1968) ,
AMIC-38«.<»
Rlsebrough,
et al
(1968),
ANIC-SS"*
-------
PCS
PCB
PCB
PC
Zenaldura
•acroura
Tyto alba
(eggs)
Sturnella
neglects
Fundulus
heteroel1tus
PC
Pebulate
Nereis vlrens BSA
Ganmarus BSA
fasclatus
Pan*tone X
Crangon BSA
eranqon
Hestern
U.S.,
Pacific
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
Pacir Ic
Ocean,
Panama,
Mexico, and
Antarctic
Western
U.S.,
PacIT Ic
Ocean,
Panama,
Mexico, and
Antarctic
No residue
same as above
BSA —
0.1)7-0.66
(residue)
0.0035-0.0361
(residue)
O.OOOZl»-O.ODO-hr toxlclty
synthetic determinations of crude oil and
seanater oll-dlspersant mixtures Has described.
The dlspersants varied considerably In
toxlclty, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr. These did not differ
slinl f leant! v from 7
-------
Co*oound
Organism
Field Field
Study Location
Toxicity,
Active
Ingredlen t»
Pom
Experiments!
Variables,
Control Ied
gr Noted
Comments
Reference
P«nt«chloroohenol
Pentachlorophenol
Pentachloroohenyl
acetate
Pentachloroohenyl
acetate
Perolln No. 5
Crassostrea
vlrglnlca
(eggs)
Crassostrea
vlrqinlca
(larvae!
Crassostrea
vlrginica
(eqqs)
Crassostres
vlrginica
(larvae)
Crangon
erangon
I —
8SA —
water, and inorqanlc, and organic chemicals Nere
daily evaluated aqalnst as many as ten marine
solution organisms* The authors noted that most
renewal) published data ot this type deal Kith
toxicity of chemicals to freshwater
organ1sms.
less than 0.25
0.071 (Tilt)
less than 0.25
(TZ)
less than
(Til.)
The effect of •>? pesticides on Oavls.et al
embryonic development of clams and (1969)t
oysters Mas reported. Synerglstlc AHIC-5990
effects with solvents Nere also reported.
Most of the comoounds affected
develocment more than survival. Some!
ho*Heverv drastically reduced larval
growth. The authors oolnt out the
necessity of evaluating the effects of
pesticides on all life stages of an
orqanlsir and note the possibility of
selecting chemicals for pest control that
Mould not have serious effect on
shell fish.
sane as above Davls> et
al11969),
AMIC-5990
Davis, et
al (1969).
AMIC-5990
Davis, et al
(1969),
AMIC--5990
Portnann, «t
al (1971).
AHIC-7T01
same as above
same as above
P»rthane
Tub 1 fax
tublfex
FL
and
Belzonl,
Hiss.
3.3-10 (T2) a
-------
BSA
Petrollte W-
Petrolite W-1U39
Phenkapton
Phenobarbltal
Phenobarltal
PhenolIcs
Steelhead
trout
IfIngerlIngs)
BSA
35.5 (T4)
Coho salmon BSA
(tIngerlIngs) In
situ
Fish (not
specified)
Hood Canal,
Hoodsport,
Wash.
Neqaprion
brewlrostrls
11-3 Kq)
BSA —
1.5 (K)
greater than
1.0-10.0 (K>
300 (NTE3.35
hr)
a,c,«
Carasslus
auratus
Fish (not
specified)
75 (NTE>
greater than
0.1-1.0 (K>
a»
various pesticides was compared to the AHIC-5979
resoonse of non-resistant species.
Pesticide-resistant species Here
collected at BelzonI and non-resistant
species at State College. Cooepods,
clams, snails, and sludge norms from
Betzonl were considerably more tolerant
to pesticides than the non-re-slstant
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.
Evaluation of 11 oil dlspersants Tracy, etal
resulted In a ranking for each and a (1969)»
recommendation for use according to the ANIC-383ii
ranking. Ranking Has based on toxlclty
and oil dispersal effectiveness. Corexlt
776
-------
Field Field
Co»oound Organism Study Location
Phenols (plus Salno BSA —
•••onl* end zlncl galrdnerl
ToxlcltVt
Active
Ingredient,
Pom
0.5-2.51. (T2>
Exner 1 men tal
Variables.
Control 1 ed
or Noted Comments
brief, general discussion of toxlclty
testing Is also present.
a,c*,d,e*t Rainbow trout were exposed to
f,m concentrations of fluctuating levels ot
Ref erence
(1071) .AMIC-
1056
Brown, et •!
(1969) ,
>
OJ
Phenols (olus
copoerl
BSA
0.5-1.75 (T2)
qalrdner1
Phenols (plus
coooer. zinc)
Ph«noI*
Sal no
galrdner1
BSA
Rasnora 8CFA
heteromoroha and
BSA
0.6-2.
-------
Phenols
Phenols
Phenols
Phenols
Phenols
Phenols
Phenols
Rasbora BCFA
heteromorpha and
BSA
r.lf (T2,
sottHater)
Lepomls
•acrochlrus
BSA,
L
13.5 (T<»)
Nl tzschla
linear Is
BSA,
I
Physa BSA,
heterostrooha L
Mercenarla
nercenarla
(eggs)
258 (T5)
(TU)
52.6 (T2>
a*,o,«,f,
hard (UW)
or soft
(SW)
synthetic
dilution
water or
seawater
for some
species
a*,e, and
synthetic
dilution
water
a*,e, and
synthetic
dilution
water
a*,e, and
synthetic
dilution
water
sane as above
Hercenarla
nercenarla
(larvae)
Crassostrea
vlrglnlca
55 (T13)
58.3 (TZ)
Alabaster
(1969),
ANIC-5%25
This study was conducted to
determine the relative toxicltles of 20
common constituents of industrial wastes
to a fish, an alga, and an Invertebrate.
The experiments Here conducted over a
10-year period for varied purposes. The
authors recommend bloassays with at least
three components of the food web.
sane as above
same as above
Patrick, et
al (1968),
ANIC-5720
Patrick, et
a I (1968),
AMIC-57ZO
Patrick, et
at (1968),
AHIC-5720
The effect of 52 pesticides on Davis, et al
embryonic development of clams and
oysters Has reported. Synerglstlc (1969),AM1C-
effects with solvents were also reported. 5990
Most of the compounds affected
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
Mould not have serious effect on
shellfish.
same as above
sane as above
Davis, et al
(1969),A1IC-
5990
Davis, et at
-------
Compound
Field Field
OrqanlsH Study Location
Toxlclty,
Active
Ingredient,
Pom
experimental
Variables,
Control led
or Noted
Comments
Reference
PhenoIs
Phenols
U)
Phenols
Phenols
Phenols
Phenols
Phenols
(eqqs)
Salno BSA
qalrdn»r1
9.* (TZ)
Gambusla
af finis
(female, (,.3
cm, 1.9
Leblstes
ret Iculatus
(male, 1.8
en, n.? q)
Tllapla
nossamblca
(T.i. cm, 1.3
BSA ~
26
BSA —
BS»
31 (Td)
19 (Tl.)
Kuhlla BSA
sandvlcensls
("t.3 en, 1.5
q)
Stoleohorus 8SA
purpurea (3.6
en, 0.
-------
Phenols
Cardlum edule BSA
greater than
500 (TZ)
daily evaluated against as many as ten marine
solution orqanlsms. The authors noted that most
renewal) published data of this type deal with
toxlelty ot chemicals to freshwater
i organisms.
a*(contin- same as above
uoua, aer-
ation, sea-
water, and
dally
solution
,renewal)
Portmann, et
al (1971),
•NIC-7701
Phenols
Crangon
cranqon
BSA —
Z3.5 (TZ)
VO
Phenols
PandaIus
•ontaqul
BSA —
17.5 (TZ)
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
same as above
Portmann, et
al (1971),
AHIC-7701
Portmann, et
al (1971),
AMIC-7701
Phenols
Platlcthys
fIesus
BSA —
33-100 (TZ)
a«(contin-
uous, aer-
ation, aea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AHIC-7701
Phenols
Ambassls
satgha
BSA —
13.5 (Tl) a*, Measurement of residual dissolved Ballard, et
seawater oxyqen during exposure of fish to al
toxicants resulted In data similar to (1969),ANIC-
that obtained from ?i>- and ta-hr 300
bloassays by the standard method. The
residual oxygen method required only 8 hr
to conduct. Variables studied Included
density per unit volume, temperature, and
fish size. The authors conclude that the
residual oxygen method Is a Quick and
-------
Compound
Organism
Field Field
Study location
Toxlclty,
Active
Ingredient,
Pom
Experimental
Variables,
Control led
OP Noted
Comments
Reference
Phenoxylene
Cranqon
crangon
8SA
reliable procedure for routine monitoring
work.
greater than 10 a»(contln- One hundred-forty surface active Portnann, et
Phcnoxyfol
Pasbora
he teroiroroha
BCFA —
and
BSA
135 IT?)
a*,c»e,f. One hundred sixty-four Alabaster
hard (HH) pesticides, wetting agents, and (1969),
or soft miscellaneous water pollutants showed a AMIC-51,25
(SH)synthe wide range of toxlclty spanning 1? orders
tic of magnitude. Knowlnq 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 fnlxture 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.
PhenylmercurIc
acetate
Phenyl mercuric
acetate
Brachydanlo
rerlo
{breeding
adults and
eqgs)
Salmo
galrdnerl
0.2 and 1.0 ppb a'
(0)
BCFA
and
BSA
0.003 (Tl)
Pticnyl ••rcurlc
acetate
Sal BO
galrdnerl
BCFA
and
BSA
0.001.
a*,c,e,f,
hard
(HH)or
soft (SH)
synthetic
dilution
water, or
seawater
(or SOB*
species
a*,c,e, f,
hard
(HH)or
soft (SH)
synthe tic
Eggs were collected dally from
spawning females which were continuously
exoosed to water solutions of the
chemical. Dead and hatched eqgs were
counted dally with daily water renewal
an>J removal of dead eqgs. At 1.0 PPb the
number of eggs released was significantly
less, and at 0.? and 1.0 npb hatching
freauency was significantly reduced.
One hundred sixty-tour
pesticides, wetting agents, and
miscellaneous water oollutants showed a
Hide range of toxlclty spanning 12 orders
of magnitude. Knowing the toxlclty and
percentage of all components of a
formulation did not result In easy
predictability of the toxlclty or a
Mixture ot materials. Sometimes
pesticides were most toxic In hard Hater
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
sane as above
Klhlstrom,
et al
(1971),
AMIC-2707
Alabaster
(1969), AMIC-
Alabaster
(1969), AMIC-
-------
Phorete
Phorden*
Phosalone
>
I
H
Phosdrln
Phosdrln
dilution
watert or
seawater
tor some
species
Fish (not
specified)
Crangon
crangon
greater than
0.01-1.0 (K)
Approximate toxlcltles of
numerous pesticides commonly used In
Britain Here summarized. An excellent
brief, general discussion of toxlclty
testing Is also present.
BSA —
gr«at«r than 10 au(contln- One hundred-forty surface active
(T2I uoua, aer- agents, solvent eiruls 1 f lers, pesticides,
atlon, sea-PO'vchlortnated blohenyls, pure
viator, and Inorganic, and organic chemicals were
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) published data of this type deal Hlth
toxlclty of chemicals to freshwater
organisms.
Mawdesley-
Thonas
(1971),AHIC-
1056
Portmann, «t
al (1971),
AMIC-7701
Rasbora
heteromorpha
BCFA
and
BSA
O.k (T2»
a*,c,e,r,
hard (HW)
or soft
(3W)
synthetic
dilution
water or
seawater
for some
species
Cooepods
(Cyclops
blcusoldus,
Cyclops
varlcans,
Cyclops
vernal Is,
Fucycloos
aglIls,Hacroe
Macrocyclops
albldus,
Orthocyclops
modestus)
FL State
and College,
BSA Hiss.
0.055 (91
percent K2)
Cooepods
(C y c I o PS
blcusnldus,
Cyclops
var leans,
Cyc I ops
vernal Is,
FL
and
BSA
Belzonl,
Hiss
0.055 (5
One hundred sixty-four Alabaster
pesticides, wetting agents, and (1969),
miscellaneous water pollutants showed a AMIC—5%25
wide 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 were most toxic In hard water
and sometimes the ooooslte was true.
Testlna the actual material as sold was
found to be essential.
The response of Naqvl, et at
pesticide-resistant aauatlc organisms to (1969),
various pesticides Has compared to the AMIC-5979
response of non-resistant species.
Pesticide-resistant species were
collected at Belzonl 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 higher trophic levels.
same as above Naqvl, et al
(1969),
AMIC-5979
-------
Compound
Phosdrln
Pnosphamldon
Phvsphamldon
>
ro
PhosphamMon
Phosphamldon
Phosphamldon
Phosphamldon
Photphamldon
Phosphamldon
Phosphamldon
Phosphamldon
Field Field
Organism Study Location
fucycloos
agl Us,
Microcyclopa
albidust
Orthocyclops
•odestus)
Tublfex Fl Belzonlt
tub If ex and Hiss.
BS*
Fish Inot
specified)
Labeo rohltm BS* —
Itry)
Labeo rohlta BSA —
If Ingerl Ing)
Trlehoqaster BS* —
f asclatus
Channa BS* —
punctatus
Ifry)
Channa BS*
punctatus
If Inqerl Ing)
Chunna BS* —
punctatus
tadult)
Hastocembelus BSA —
pence 1 us
Macrognathus BSA —
aculeatum
Nandus nandus BSA —
Toxlclty,
Active
Ingredient,
Pom
1.0 INTE)
greater than
1.0-10.0 IK)
137.7 (T7)
177.0-205.2
IT7)
30.2 IT7)
19.1 ITT)
25.1 ITT)
36.3 (T7)
20. * IT7)
*1.7 ITT)
3*.7 ITT)
Experimental
Variables,
Control led
or Noted Comments
— same as above
Approximate toxlcltles of
numerous pesticides commonly used In
Britain were summarized. An excellent
brief t general discussion of toxiclty
testing Is also present.
a,c,d,e,f DDVP and Phosphamldon were shown
to be selective toxicants that can be
used for eradication of undesirable
animals from ponds Hlthout Injuring carp.
DOVP seemed superior since less was
needed. It Has not Influenced by
turbidity, and It etrxlfied more rapidly
than phosohamldon.
a>CtdfC,f same as above
a,c,d,e,f same as above
a,c«d,e,f same as above
a,c,dte,f same as above
a,Ctd,e,f same as above
a,e,d,e,f same as above
a,c,d,e,f same as above
a,c,d,e,r same as above
Reference
Naavl, et al
11969),
AHIC-5979
HaMdesley-Th
omastl971)
AMIC-1056
Konar
11969), AHIC-
51.53
Konar(1969),
ANIC-51.53
Konar(1969) ,
Konar
11969) ,AHIC-
51.53
Konar(1969),
AHIC-51,53
Konar
(1969), AMIC-
51.53
Konar
51.53
Konar
11969) «»HIC-
51.53
Konar(1969),
AMIC-5*53
-------
Phesphaaldon
Phosphaaldon
Phospnanldon
Phospnanldon
Phosphanldon
Phosphaaldon
Phosphanldon
Phosphaaldon
^j Phosphanldon
Phosphanldon
Phosphaaldon
Phosphanldon
Phosphanldon
Phosphanldon
Phosphanldon
Amphlonous as*
cuchla
(young)
Anphlonous BSA
cuchla
(adult)
(TTI
i,c,d,a,f
Mystus
vltatus
Pun 11 us
sooner*
BSA
BSA
Anabas BSA
tastudlnaus
Hetoropnaus-• BSA
taa fosallis
(«ry»
Hataropnaus- ' BSA
tas toaailia
(fInqerllna)
Esoaus
danrlca
(fry)
BSA
Oytlseus so. BSA
(adult)
Sohaerodeaa BSA
annulatun
Ranatra BSA
ttltforals
Anlsoptara BSA
(nynpns)
Cyblster sp. BSA
N*pa sp. BSA ~
Bvlostoaa BSA
Indlca
22.* (T7) »,e,d,«,T
(T7)
2.6 (T7)
2.9 (T7)
1.5 (T7)
.3 (T7)
2.t
68.1. (T7) a,c,d,a,f
66.8 (T7)
66.1 (T7) a,c(dt*,(
178.2 (T7) a,c,d.a,t
1.3 (T7)
a.c.d.c.T
a>Ctdt«f r
a,c
-------
Compound
PnoiPhanldon
Pnosphenldon
Phospha»ldon
Phosphanldon
>
^ Phospnenldon
-P-
Phospnanldon
Pnosphanldon
Phosphanldon
Phosphanldon
Pnospnanldon
Phospnanldon
Field Field
Organlsn Study Location
Hydroohllus BS* —
SP.
Volvox BS*
Pandorlns BS* ~
Ctosterlun BS*
BracMonus 8S» --
Gastrofrlcha BS* —
Cyorls BS* —
Cyclops BS* ~
NauDlIus BS* —
D*phnla BS* —
Cerlodaphnla 8S* —
Toxlclty,
Active
Ingredient,
Ppn
5.6 (T7)
5.0 (NTE)
5.0 (NTE)
5.0 (NTE)
50 (NTE)
10 (NTE)
10 (NTE)
7.5 (K)
2.5 (K)
2.5 (K)
%.• (K)
Experimental
Variables,
Control led
or Noted
a.c.d.e.r
a.c.d.e, f
a,c,d,e, f
a,e,d,e, f
a,ce,d,e,r
Convents
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 ns above
saae ns above
Reference
•MIC-5»53
Konar
(1969) ,
*1IC-5»53
Konar
(1969),
»NIC-5
-------
Pho»phort»s
P»relabr»x
elathratus
V/l
Phosphorus
Phos phorus
Phosphorus
Phosphorus
Paralabrax
et athrntus
ParaMbrax
clathratus
Paral abrax
clathratus
P»ralabrax
elathratus
FH Scatfergood 63ZO (dorsal
Steea Plant, Muscle
Lo« Angeles, RESIDUE)
Cal.
Fish collected fro« an effluent Stapleton
Oloe of a st»a« olant ao-l fro" offshore (1968),
H8tn-9 of Catallna Island wrre analyzed »MIC-598B
for trace ele»»ot content. Trace element
content of the effluent water was at
lei^t 5 tl««s «>reater than that of nor«»I
sea xater for cad«lu«> cooper, nickel,
zinc, and ehro»lu«. Liver* of fish fro*
the effluent N»re nearly twice the size
of those fro» the ocean. Greatest
differences In concentration occurred
with aluolnua, cadalun, and nickel.
Silver, barlu*, tlthluo, and lead showed
the le»st differences. The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on «arlne organises.
FH CatalIna 7590 (dorsal
Islxnd, Cal. nuscle
realdu*)
FM Scatterqood 6<»«tO (ventral
Steao Plant, ousele
Los Angeles, reildu*)
Cal.
FH CatalIna 6700 (ventral
Island, Cal. nuscte
reildu*)
FH Scattergood Z3,6ZO (gonads
Steav Plant, residue)
Los Angeles,
Col.
yemt as above
sa»e as above
sa»e as above
save as above
Staoleton
(1968),
AMIC-S980
Staoleton
Staoleton
(1968),
AM.IC-5980
Staol eton
(1968),
AMIC-59SO
Phosphorus
Phosphorus
Phosphorus
Phosphorus
Par»labrax
clathratus
Paral abrax
clathratus
(gravid
females)
Paralahrax
clathratus
Paralabrax
clathratus
FM
FM
CatalIna ?3,9ZO (gonads
Island, Cal. residue)
CatalInalsla 10,530(gonads
nd, Cal. residue)
Scattergood 9600 (liver
Steam Plant, residue)
Los Angeles,
Cal.
FM
CatalIna
Island, Cal.
7270 (liver
residue)
sane as above
sane as above
save as above
saae as above
Staoleton
(1968) ,
Staol eton
(1968) ,
AHIC-5980
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
-------
I
Ui
^3
cr\
Phosphorus
Phosphorus
Phosphorus
Phosphorus
Phosphorus
Phosphorus
Ph os t o x
Photoaldrln
Ptiotoaldrln
Organ Isn
Par al ahrax
el athratus
Paral abrax
c 1 athratus
Paral abrax
c 1 wthra tus
Par a 1 ahrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Cr angon
crangon
Anacystls
nldul ans
Agnenel lu«
quadrup-
lloatum
Field Field
Study Locat Ion
FH Scattergood
STflam Plant,
Los Angeles,
Cal.
FH Catal Ina
Isl and, Cal .
FH Scattergood
Strain P 1 ant ,
Los Angeles,
Cat.
FH Catallna
Isl and, Cal .
FH Scattergood
Steam Plant,
Los Angeles,
Cal.
FH Catallna
Island, Cal.
BSA —
L
L —
Toxlclty,
Active
Ingr Adi en t ,
Ppm
7530
< In t egument
resl due)
2520
( Integument
residue)
5800 (heart
residue)
5550 (heart
residue)
7800 (eyeball
residue)
10,1.50 (eyeball
residue)
greater than 10
(TZ)
1.0 IqroHth
Inhibited)
NTE
Experimental
Variables,
Control led
or Noted Comments
sane as above
-- sane as above
~ same as above
same as above
same as above
same as above
a»(oontln- One hundred-forty surface active
uous aer- agents, solvent emulslflers, pesticides.
atlon, sea- pot vch lorlnated blohenyls, pure
water, and inorganic, and organic cheirlcals Mere
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.
a»,c',P Metabolic products of Aldrln,
SH Dleldrln, and Endrln can be as toxic as
the parent compounds, as shonn by 00
measurement.
a*,c»,r sane as above
SH
Ref er ence
AMIC-5980
Stnol eton
(1968) ,
AMIC-5980
Staot eton
(1968) ,
AMIC-5980
S t a o 1 f t on
(1968) .
AMIC-5980
S tap 1 eton
(1968) ,
AMIC-5980
Staoleton
(1968) ,
AMIC-5980
Stapl eton
(1968) ,
AMIC-5980
Portnann, et
al (1971),
AHIC-7701
Batterton,
et al
(1971),
AMIC-Hi71
Battcrton,
• t al
(1971) , AMIC-
-------
1*71
Photodleldrln
Photodieldrln
Phygon
Phygon
Phygon
Phyqon
Plcloran (K salt)
Aqmenellun L
auadruoltcatu
ID
Anacystls
nldulans
Hercenarla
mercenarla
(eggs)
Mereenarla
mercenarla
(I arvae)
Crassostrea
vlrqlnlca
(eqgs)
Crassostrea L
vlrqlnlca
(larvae)
O.S-1.0 (growth a*,c»,r
Inhibited) SM
8.5-1.0 (growth a*t
Inhibited) SN
0.0* (TZ)
Sasbora
heteronorpha
SCFA
and
BSA
1.75 (T12)
0.01". (TZ)
0.01.1 (Til.)
11 (T2)
»*,c,e,f ,
hard
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Conpound Organism Study Location Ppi or Noted
PHA Salno L — 3.0 (S830) a,e,l (1
galrdnerl hr
exposure
dal 1 y for
UD to 11
days)
Comments
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
Single exposures of fish to
orianomercury compounds resulted In peak
concentrations of mercury as follows"
gills, 3 hrl blood, 32 hr 1 liver, 7 da»
kMni>y ?1 For repeated one hr (dally)
exposures peak concentrations were?
Reference
Rucker, et
al (1969),
AMIC-5733
3
CD
Polycell product
Cranqon
cranqon
BSA —
Polye lens
Carclnus
maenas
BSA —
blood, 10 dal liver, 10 da« kidney, 61
dat muscle, 7 da. The concentration of
mercury was always lowest In muscle
tissue. Feeding experiments with PM«
showed mercury could be passed from
flnqerllngs to larger fish. The authors
conclude that either legal size or
finqerllng hatchery fish treated with
orqanoirercur lals could be a public health
hazard.
330-1000 (T<») a«(contin- One hundred-forty surface active Portnann, «t
uous aer- agents, solvent emulslflers, pesticides, al (1971),
atlon, sea- polychlorlnated blphenyls, pure AMIC-7701
water, and Inorganic, and organic chenlcals 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.
10-33 (T?) ao(contin- same as above
a»(contin-
uous, aer-
ation, aea
water, and
dally
solution
renewal)
Portmann, et
al
(1971),AMIC-
7701
Polye I ens
Cardlum edul« BSA
33-100 {T2>
a«( contin-
uous aer-
ation, sea-
water, and
dally
solution
sax as above
Portmann, «f
al (1971),
AHIC-7701
-------
renewal)
PolyeI ens
Crangon
crangon
BSA
10-33
a»(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sa*e as above
Portmann, at
a! (1971).
ANIC-7701
Potyclens
Panda I us
•ontagul
BSA —
10 (TZ)
a»(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
Portnann, et
al
7701
Polycoaolex A-ll
NO
Steelh«ad
trout
(fIngerlIngsl
BSA —
13.0 mi
Polycoaplex A-ll
Polyeonplex A
Coho salmon BSA
(flngerlinga) In
situ
Caretnus BSA
•aenas
Hood Canal,
Hoodsport,
Wash.
1.5 (K)
100-330
Evaluation of 11 oil dlsoersants
resulted In a ranking for each and a
recommendation for use according to the
ranking. Ranking Has based on toxlcltv
and oil dispersal effectiveness. Corexlt
776
-------
Compound
Polycovolex A
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organisn Study Location Pom or Noted Comments
renenal 1
Llnanda BS« -- 33-100 (T2) a«(contln- sane as above
11 »and» uous aer-
ation, sea-
watar, and
dally
solution
renewal)
Reference
Portmann, et
al (1971),
Amc-7roi
Polyotlc
>
I
Roccus
saxatlUs
(fIngerl Ings)
BSA —
Potasslu* chloride Lepomls SS»,
•acrochlrus L
greater than
1,818 (T«.)
?,010 (Ti.)
PoTasslun chloride Nitzsehla BSA,
llnearis I
PotasiluB chloride Physa BSA,
heterostropha L
Petastlua chro«at* Leponls 6SA,
(•s Cr) aacrochlrus I
Potasslu* chronate NitzscMa BSA,
IBS Cr) llnearls I
1,337 (T5)
(T)
7.8(T5)
a*,c,d,e,f Strloed bass flnqerllnqs Here Wellborn
,p and apparently -mucn more sensitive to (1969),
Iron therapeutic and herblcldal compounds than AMIC-57Z3
many treshwat^r fish.
a*,«, and
syn the11c
dilution
water
a*,e, and
synthetic
dilution
water
a*,e, and
synthetic
dilution
water
a*,e, and
synthetic
dilution
Hater
a«,e> and
synthetic
dilution
water
This study nas conducted to
determine the relative toxlcltles of 20
common constituents of Industrial wastes
to a fish, an alga, and an Invertebrate.
The experiments Here conducted «ver a
10-year period for varied purposes. The
authors recommend bloassays with at least
three components of the food neb.
sane as above
sane as above
sane as above
sane as abova
Patrick,
al (19*A> ,
AMIC-5TJO
Patrick, et
al (1968),
PatrlcK, et
al (1968),
AMIC-5T2D
Patrick, et
al (1968),
AMIC-5720
Patrick, «t
al (1968),
AMIC-57ZO
-------
Potassium cyanide
las cyanide)
Carclnus
men as
BSA ~
Potassium Cyanide
las cyanide)
Crangon
crangon
BSA ~
greater than 5 a«(oontin- One hundred-forty surface active
IT2) uoua, aer- agents, solvent emulslfIerst pesticides,
atlon, sea-polychlorlnated blohenyls, pure
water, and Inorganic, and organic chemicals were
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) published data of this type deal Mlth
toxlclty of chemicals to freshwater
organisms.
same as above
greaterthan 25 »*(contln-
1T2) uoua, aor-
ation, sea-
water, and
dally
solution
renewal)
Portmann, et
al
(1971),AMIC-
7701
Portmann, et
al
(1971),AHIC-
7701
>
I
Potassium cyanide
(as cyanide)
Potassium; cyanide
Panda I us
aontagul
Leblstes
retlculatus
(1 mo, 1.1
cm)
BSA —
0.25 CT2)
BCF ~
0.36 (T2)
Potassium cyanide
Leblstes
retlculatus
(1 mo, 1.1
cm)
BCF
tTl)
a«(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
a,e,d,e,f,
. n,q, phos-
phates,
carbon-
ates, bi-
carbon-
ates, sul-
fates, and
conduc-
tance
same as above
a,c,d,e,r,
n»q« phos-
phates.
Toxlclty thresholds and a
dilution mixture threshold Here
calculated from fish bloassay data for
zinc chloride and potassium cyanide.
Threshold concentrations for zinc and
cyanide Here found to be 0.33 and 0.236
mg/l, resoectIveIy. A procedure for
determining toxlclty threshold
concentrations for mixtures of chemicals
was also presented. A zlnc-cyanld»
dilution ratio for toxlclty threshold
(TH09) Has found to be a linear function
of the concentration of the tno Ions
taken separately, and therefore; THOR
equals i.?fi-O.S6CN-1.22Zn. Based on a
multlcomponent equation, mixtures of zinc
and cyanide exhibit an antagonistic
effect. This appears to be a significant
advance in an approach to estimating safe
concentrations for Hater pollutants.
same as above
Portmann, et
al (19711,
AMIC-7701
Chen, «t al
(1969),
AMIC-3831
Chen, et al
(1969),
AMIC-3831
-------
Compound
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient,
Ppa
Experimental
Variables,
Control led
or Noted
Comments
Reference
carbon-
ates, bi-
carbon-
«tes, sul-
fates, and
conduc-
tance
Potasslua dlchroaate Leoouls BSA.
(as Cr) aacrochlrus I
113 (T
I
Potasslua dlchronate NltzscMa BSA,
las Cr) llnearls L
Potasslua dlchroaate Physa BSA,
(as Cr) heterostropha I
Potassium dlchroiiate Phoraldlua L
(as Cr) amblguum
0.21
17.3 (T»l
0.5-10.0 (16
percent
growth
Inhibited 14)
a*,e, and
synthetic
dllutlon
Hater
a»,e, and
synthetic
dilution
water
a>,e« and
synthetic
dilution
nater
This study Has conducted to
determine the relative toxlcltles ot 20
common constituents of Industrial Hastes
to a fish, an alqa, and an invertebrate.
The experiments Here conducted over a
10-year period for varied purposes. The
authors recommend bloassays with at least
three components of the food xeb.
same as above
same as above
Patrick, et
al (1968),
AMIC-5720
Patrick, et
al (1168),
AMIC-57?0
Of 71. chemicals evaluated as
alqlcldesi only 9 were more toxic than
CuSO^. Non«> Inhibited growth of
mat-forming algae for more than 2 Heeks.
CuSni» formulated nlth certain Netting
agents Has more toxic than CuSO<» alone.
Copper chloramlne Has also found to be
more toxic than CuSO)
a,«, and
Feeding behavior Has affected by Cairns, et
-------
rerlo
Pot ass iuii
pantacMorophenate
Oncorhynchus
klsutch (CSE
119 embryo
cells)
L ••
*0-1ZO (SB10) a*
CO
Pot ass luii
permanganate
Trachlnotus
carolInus
(Juvenile)
BS» —
1.6-2.9 (Tli)
Potassium
permanganate
PotassIu«
permanganate
Roccus
saxatltls
(finger IIngs)
Phormldlum
ambiguum
BS» —
synthetlcd zinc, chromium, and ABS In that more tl«e al (1967) t
llutlon MBS reaulred for consuming measured AHIC-5707
•ater amounts of food. Feeding response Has
also affected by aeratlont feeding
schedule, light Intensity, and outside
disturbances. The authors note that much
more HorK is needed to establish the
reliability of this procedure.
Growth of cultured coho salmon Hanes, et al
embryo cells on Eaole"s MEM was partially (1970),
Inhibited at iiO oom, strongly Inhibited AMIC-3753
at 80 pom, and totally Inhibited at Z10
, ppm. The 50 percent Inhibitory dose Has
estimated to be 66 ppm. A linear
relationship between dose and effect Has
noted. Data on cell counts, population
volume, dry welaht, ash, nitrogen,
organic acids, and organic matter are
reported.
a,c,e,f,l. In this study of pompano salinity Rlrdsong, et
and. Has controlled at 10, ?0» and 30 DOT and 81 (1971),
sulfate, Investigated as a variable. Acrlflavln, AMIC-5570
sodium, formal In, and potassium permanganate Here
Calcium, slightly more toxic at the highest
potassium, salinity, while copper sulfate Has
magnesium, slightly less toxic. These compounds are
carbonate, used as prophylactic bacterial
blcarbon- treatments. All appeared to be
ate, reasonably safe to use exceote possibly
salinity potassium permanganate.
a*,c,d,et formulated Hith certain netting
aaents was more toxic than CuSO*» alone.
Cooper chlorairlne was also found to be
more toxic thar CuSOit. No wetting agents
Here found to be inhibitory at the
concentrations Investigated (0.05 and
0.005 ppm). Also reported are factors
affecting growth of algae In canals to
determine whether there Here leads to
controlling algae by environmental
Otto (1970),
AMIC-892
-------
Field Field
Comoound 'Orqanlsm Study Location
Potassium salt of Phormldlum I —
?(<>-chlorotol yl ) amblquum
oxy-N-methoxy-acetam
Toxlclty,
Active
Ingredient,
Ppm
0.5-10.0 (16
percent qronth
Inhibited l
Approximate toxlcitles of Haxdesley-Th
numerous oestlclrtes commonly used In omas
Britain nere summarized. An excellent (19M),A*1IC-
brlef, general discussion of toxlclty 1056
testing Is also present.
Protla
Rasbora
heteronorpha
BCFA
•nd
BSA
10.0 (T?t a*,c,e,f. One hundred sixty-four
hardnater) hard(HW) pesticides, nettlnq agents, and
or soft miscellaneous Mater pollutants shoHed a
(Swt Mlde range of toxlclty spanning 12 orders
synthetic of magnitude. KnoHlnq the toxlclty and
dilution percentage of all components of a
Hater, or formulation did not result In easy
seanater predictability of the toxlclty of •
for SOB* mixture of materials. Sometimes
Alabaster
(1969),
-------
Protln
Pro-Noxf Ish
vn
Pro-Noxf Ish
Pro-NoxfIsh
PVP-Iodine
PVP-Iodln«
Rasbora BCFA
heteromorpha and
BSA
1.8 ITZ,
softuater)
species
a»,c.e,ft
hard 6 F.
Eggs burled In gravel survived better
than those at the gravel surface.
Further field evaluations Here
recommended.
same as above
same as above
Garrison
(1968),
AMIC-5711.
Garrison
Garrison
(196S),AHIC-
57m
The effect of 5? pesticides on Davis, et al
embryonic development of clams and
oysters Has reported. Synergistlc (1969),AHIC-
effects with solvents Here also reported. 5990
Most of the compounds affected
develocment more than survival. Some,
honever, 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.
sane as above
Davis, et at
(1969),AMIC-
5990
-------
Toxlclty, Exoerl mental
•Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Ppit or Noted Comments
Pyra»ln Rasbora BCFA — ?» (T?) a*,c,e,f.
heteronorpha and hard
oca f uy \ nr
O4 1 HH 1 or
soft (SHI
synthetic
dilution
water, or
seanater
for some
soecles
Pyrazon Fish (not — — — • greater than —
specified) 10-100 (K)
Pyrlalthat* Rasbora BCF« — (,.1 (T?) a*,c,e,f.
he teromorpha and hard (HW)
BSA or
SOFTC5H)
synthetic
dilution
water, or
seanater
for so»e
species
One hundred sixty-four
Destlcldes, netting agents, and
I*0" a e°U^ ?' ?r,?° i* %£
of maqnltude. Knonlnq the toxlclty and
percentaop of all co">oonpnts of a
formulation did not result In easy
Dredlctabll 1 ty of the toxlclty of a
mixture of materials. Sometimes
pesticides Here most toxic In hard Hater
and sometimes the ooooslte Has true.
Testing the actual material as sold Has
found to be essential.
Approximate toxlcltles of
numerous pesticides commonly used In
Britain Here summarized. An excellent
brief, general discussion of toxlclty
testing is also present.
One hundred sixty-four
Pesticides, Hotting agents, and
miscellaneous Hater pollutants showed a
Hide range of toxlclty scanning 1? orders
of magnitude. Knonlng 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 Hater
and sometimes the ooooslte Has true.
Testing the actual material as sold Has
found to be essential.
Reference
Al abcster
(1969) ,
AHIC-5<»?5
Mandesley-
Thomas(1971)
AMIC-1056
Alabaster
(1969),
AMIC-5<»Z5
Qulnaldlne
Neqaorlon
brewlrostrls
(1-3 Hq)
BSA —
8.2 (SB 10 a,c,e Data from study of drug effects Paldrldge
MINI on young lemon sharks Here treated (1969),
mathematically to demonstrate AMIC-3832
applicability of classical rate theory to
the study of chemical shark deterrents.
Incaoacl tatl on -(narcosis) Has the prlnary
parameter timed for effectiveness. This
Has usually quite rapid for the more
effective drugs.
R*yn»p Sol B
Crangon
BSA
3.3-10 (T2>
a»(contln-
One hundred-forty surface active Portaann, «t
-------
cranqon
RD 1*639
Rasbora
heteromorpha
BCFA
and
BSA
0.58 (T2)
Regions
Rasbora
heteromoroha and
BSA
37 (T2,
sottwater)
Regions
Sal mo
galrdnerl
BCFA
and
RSA
70 (T2,
hardwater)
Region*
Salmo
galrdnerl
BCFA
and
BSA
27 (T2,
sottHater)
uoua aer- agents, solvent emulslTiers, pesticides, al (1971),
•tion, sea-polychlorinated blphenyls, Dure AMIC-77D1
water, and Inorganic, and orqanlc chemicals 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*,c,e,f. One hundred sixty-four Alabaster,
hard pesticides, wetting agents, and (1969),AMIC-
(HN)or miscellaneous water oollutants showed a 5
-------
Field Field
Compound Organism Study Locatlor
lodanlne B Sal mo BSA —
galrdnerl
ioda*lne B Ictalurus BSA —
punc ta tus
ioda«lne B Leponls BSA ~
macrochlrus
drllk Crangon BSA —
crangon
icc»l Mercenarla u
inercenarla
(eggs)
Toxlclty, Experimental
•Active Variables,
Ingredient, Controlled
i Ppii or Noted Comments
synthetic
dl lutlon
water, or
seawater
tor some
species
217 (TO a* The dyes Rhodamlne 9 and
Fluoresceln sodium Here found to be
relatively non-toxic In ppm
concentrations while antlmycln was toxic
at ppb levels. The author states that
neither dye at field use concentrations
should significantly Influence the
activity of Antlmycln A against fish.
5?6 (Tit) a* same as above
379 (Tl.) a* same as above
330-1000 (T?) a«(contln- One hundred-forty surface active
uous aer- agents, solvent emulslflers, pesticides.
atlon, aea.Pol ychlorlnated blphenyls, pure
water, and Inorganic, and organic chemicals were
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) published data of this type deal with
toxlelty of chemicals to freshwater
organ 1 sms.
0.19 (T2) — The effect of 52 pesticides on
embryonic development of clams and
oysters was reported. Synerglstlc
effects with solvents were also reported.
Reference
Hark Ing
(1969) ,
AMIC-5729
Marking
(1969) ,
AHIC-5729
Harking
(19f>9) ,
AMIC-5729
Portmann, et
al (1971),
AMIC-7701
Davis, et al
(1969), AHIC-
5990
Most of the compounds affected
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 chaaicals for pest control that
-------
Roeeal
Re I a OSD
Hercenarla
•ercenarla
(larvae)
Cranqon
crangon
I —
BSA
0.1
-------
>
I
o
Coaoound
Rot*non«
Rot«none
Ro-n»»t
R-1910
Salicylic acid
«?-hydroxy benzole
Field Field
Organism Study Location
( 1 arvae)
Salmo L
galrdner I
Leo on Is I. ~
•acrochlrus
Gammarus 8SA —
fasclatus
Gammarus BS* —
fasclatus
Phornldlun L --
anblguum
•Toxlclty, Experimental
Active Variables,
Inqredlenti Controlled
Ppn or Noted Comments
0.057 (Tit) a» The Dlsclcldes Antlmvcln A and
Rotenone Mere found to be compatible when
mixed and furthermore appeared to have an
additive effect In cmblnatlon. That Is
both compounds were more toxic In the
presence of the other than alone.
0.11
-------
means Here found.
Seasneep
Scfoll
>
H
Sefoll
Steel head BSA ~
trout
(finger)Ings)
Coho salmon BSA Hood Canal,
(fIngerlings) in Hoodsport,
situ Wash.
20.?
Agonus
cataohractus
BSA
1.5 (K)
1000-3300 (T2I
Evaluation of 11 oil dlspersants Tracy, «t al
resulted In a ranking for each and a
recommendation for use according to the (1969),AMIC-
ranKlng. Ranking Has based on toxlclty 383 lead, 0.071 mercury, 0.0031 and
selenium, 0.25. Deleterious effects
occurred at metal concentrations
approximately similar to potable nater
standards.
Concentrations of 13 toxic
elements In dressed fish from heavily
Industrialized and non-industrialized
areas Here determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements Here
essentially the same In fish fron both
Uthe. etal
(1971),
AMIC-3819
-------
Coeoound Organls*
Selvnlu* Coregonus
cl uoeaf or «ls
Selenlu* Esox luclus
Selenium Esox luclus
1 Selenlu* Esox luclus
ro
Selenlu* Osmerus
•ordax
Selenlu* Perca
f 1 avesceos
Sesaaex Notemlqonus
chrysoleucas
Ses»*ex Leoomls
cyanel lus
Sesa*ex Leoomls
•acrochlrus
toxlclty.
Active
Field Field Ingredient,
Study Location Po«
FL Lake 0.>
a,c,d,e,f Of the pesticides Investigated, Bhstla
the most toxic was Klofos followed In (1971),
decreasing order by Sumlfhlon, Malathlon, AHIC-5i»23
Formlthlon, Olnecron, Sevln, and 6HC. The
»utnor cites the. need for more selective
-------
Savin
Rasbora BCF»
heteronoroha »nd
BS»
(T?l
Sevln
Palaemonefes BS»
KadlaKensls
(resistant)
0.06V-O.Z7Z
CTU
U)
pesticides nontoxlc to fish or
antagonistic agents for reducing fish
toxlclty.
a',c,e,f, one hundred sixty-four Alabaster
hard ?5
(SMI Hide range of toxlclty scanning 1? orders
synthetic of magnitude. Knowing the toxlclty and
dilution percentaae of all comnonents of a
water, or fornulatlon did not result In easy
seawater predictability of the toxlclty of a
for some mixture of material*. 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.
•* Bloassays were conducted with Naqvl, et al
shrlmo from three areas of Intensive (1970),
pesticide use and from an unexoosed area. ANIC-5S19
Previously exposed shrlmo were from 1 to
?5 times more resistant than unexposed
shrlnp. Both fyoes of shrimp were also
exoosed In cages to waters of the
contaminated areas. Susceptible shrimp
suffered 6ft oercent more mortality than
did resistant shrimp. The toxlclty of
the Insecticides ranKed in descending
order was as follows! most toxic,
Endrin, DOT, Methyl oarathlon, Parathlonl
medium toxlclty, Guthlon, Llndane,
Toxaohene, Strobanel lease toxic
Chtordane, Sevln, and Heptachlor.
Sevln
Sevln
Palaeaonetes BS* •—
Kadlakensis
(non-
resiatant)
Tublfex
tub Ifax
FL
and
BSA
Belzonlt
HISS.
0.01,25 (Til
1.50 (NTE>
same as above
Naqvi, et
(1970),
ANIC-5519
al
The response of
pesticide-resistant aquatic organisms to
various pesticides was compared to the
response of non-resistant species.
Pesticide-resistant species were
collected at Retzonl and non-resistant
species at State College. Cooeoods,
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 higher trophic levels.
Naqvl, et
al(1969),
AMIC-5979
-------
Compound
Sevln
Field Field
Organism Study Location
Hercenarla L —
mercenar 1 a
(eggs)
Toxlcl ty.
Active
Ingredient,
Ppm
3.»2 CT2)
Experimental
Variables,
Control led
or Noted
Comments
The effect of
embryonic development
oysters Has reported.
52 pesticides on
of c 1 ams and
Synerq 1st Ic
Reference
Oavls, «t al
(1969) ,AMIC-
5990
I
(jj
\O
-p-
Sevln
Sevln
Sevln
S«vin
Shamash R1885
Snamcsn R1S8S
Hercenar1 a
mercenarI a
I Iarvae)
L ——
Crassostrea 1.
virgin lea
(eggs)
Crassostrea
vlrglnlca
(Iarvae)
woirria
papulifora
Crangon
erangon
BSA
greater than
Z.S (Til.)
3 (T2)
3 (Til.)
1000 (K)
3.3-10 (T2)
Panda I us
•ontaqul
BSA
1.0-3.3 (T2)
Most of the compounds affected
development more than survival. Sone,
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 ot
selecting chemicals for pest control that
would not have serious effect on
shall fish.
same as above
same as above
same as above
Dav Is, et
al H9S9) ,
»MIC-15990
Oavls, et al
Huntor1 a
.•nodlum
diluted
1:5
a»(contin-
uous aer-
ation, 3oa-
water, and
daily
solution
renewal)
a»(contin-
uous, aor-
atlon, sea.
water, and
daily
solution
renewal)
AMIC-5990
Dav Is, et al
(1969) .AMIC-
5990
All compounds wore harmful to Wortliley, et
duckweed to norao decree. Docroaaod al (1971),
populations woro noted at non-lethal AMIC-3233
concentrations and some coripounda
(Kalathion and ,;,l4.-D) cnused teratogenic
offoots at concentrations us low as 1 ppa.
One hundred-forty surface actlv* Portmann, «t
agents, solvent emulslflers, oestlcldes» al (1971),
oolychlorlnated blohenyls, pure AMIC-^701
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
toxlcity of cheeelcals to freshwater
organisms.
same as above
Portmann, e
al (1971),
AMIC-7701
-------
Shell D-50
Salmo
galrdnerl
BCF» —
and
BSA
105
a*,c»e«f, One hundred sixty-four Alabaster
hard pesticides.? wetting agents, and (1969),
(HH)or miscellaneous water pollutants shooed a AMIC-5<»25
solt (SH) wlrte range of toxiclty scanning 12 orders
synthetic o' magnitude. Knowing the toxiclty and
dilution percentage of all comoonents of a
Hater, 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 sometimes the ooooslte was true.
Testing the actual material as sold was
found to be essential.
Sliver
•ethane-arsonate
Phormidlum
amblguum
0.5-10.0 (16
percent growth
Inhibited!!,)
VO
vn
Silver
Paralabrax
clathratus
FM Scattergood 0 (ventral
Steam Plant, muscle
Los Angeles, residue)
Cal.
Otto (1970),
AMIC-89?
Of 7
-------
UJ
o\
Compound
Silver
SI Iver
SI Iver
Silver
Sliver
SI Iver
Silver
Silver
Silver
Sliver
Orqanlso
Para 1 abrax
cl athratus
Paral abrax
cl athratus
Paral ahrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
(qravld
females)
Paral abrax
cl athratus
Paral abrax
cl athratus
Field
Study
FM
FM
FM
FM
FM
FM
FM
FN
FM
FM
Field
Locat Ion
Scat tergood
Steam Plant,
Los Anqeles,
Cal.
Catal 1 na
Island, Cal.
Sent t erqood
Steam PI ant ,
Los Angeles,
Cal.
Catal Ina
Island, Cal .
Catal Ina
Island, Cal .
Scatterqood
Steam Plant,
Los Anqeles,
Cal.
Catal Inn
Island, Cal.
Catal Ina
Island, Cal.
Scatterqood
Steam Plant,
Los Anqeles,
Cal.
Catal Ina
Island, Cal.
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted
0.06 (heart
residue)
0.16
(heart
residue)
0.01 (eyeball
residue)
0.03
(eyebal 1
residue)
0.09 (ventral
muse 1 e
residue)
0 (qonad --
residue)
O.it?
(qonad
residue)
O.lZqonad
residue)
0 (liver
residue)
0.02
(liver
residue)
Comment s
sane as above
same as above
sane as above
saae as above
same as above
same as above
sane as above
same as above
sane as above
same as above
Reference
Sf aol eton
(196M ,
AMIC-595H
S t aol eton
(196)1) ,
AMIC-5980
S t a o 1 e t on
(1968) ,
AMIC-5980
Stapl eton
(1968) ,
AMIC-5980
S t a o 1 e t on
(1968) ,
AMIC-5980
S tap 1 eton
(1968) ,
AMIC-5980
S tap 1 eton
(1968) ,
AHIC-5980
Staoleton
(1968) ,
AMIC-5980
Staoleton
(1968),
AMIC-5980
Stacleton
(1968),
»MIC-S9«0
-------
Silver
Paralabrax FH Scattergood O.ZZ
clathratus Steam Plant, (Integument
Los Angeles, residue)
Cal.
sane as above
Staoleton
(19F.8),
AHIC-5980
Silver
Sllvex (BEE)
OJ
Sllvex (BEE)
Sllvex (BEE)
Paralabrax FH CatalIna 0.1Z
clathratus Island, Cal. (Integument
residue)
same as above
Gammarus
fasclatus
BSA
Paleomontes BSA
Kadlakensls
Asetlus BSA
brev icaudus
0.71. (TZ), O.Z5 a*
tUI
8.0 (TZ)
1.0.0 (TZ)
a*
Of the aquatic weed herbicides
evaluated, Dlclone Has the most toxic,
Daphnla was generally the most sensitive
organism. All of the Crustacea Here
affected by much loner concentration
levels of herbicides than indicated by
the TL sub 60 values. All of the animals
represent Important food chain links.
same as above
Stapleton
(1968),
AHIC-59SO
Sanders
(1970),
AHIC-i.53
same as above
Sanders
(1970) ,
AMTC-<,53
Sanders
(1970),
AHIC-i.53
Sllvex (BEE)
Sllvex (BEE)
Sllvex (BEE)
Sllvex (BEE)
Sllvex (PGBE)
Sllvex (PGBE)
Orconectes BSA
nals
Oaphnla maqna BSA
Cyprldoosls BSA
vldua
Lepomls BSA
macrochlrus
Ganmarus BSA
fasclatus
Paleomontes BSA
kadlakensls
60.0 (TZ)
Z.I (TZ)
d.9 (TZ)
70.0 (TZ)
1.0 (TZ), O.t
-------
>
U)
00
Comoound
SI Ivex (PGBE)
Sllvex (PGBE)
SI Ivex (PGBE)
Si Ivex (PGBE)
Sllvex (PGBE)
Si Ivex
Field Field
Organise Study Location
Asellus BSA
br ev 1 caudus
Orconectes BSA —
nals
Daphnln magna BSA —
Cyorldopsls BSA
vldua
Leoomls BSA —
nacrochlrus
Crassostrea I ~
vlrglnlca
(eggs)
•Toxlclty,
Active
Ingredient,
Pon
0.5 (TZ)
greater than
100.0 IT?)
0.18 IT?)
0.20 (TZ>
16.6 (T2>
5.9 (TZ)
Experimental
Variables,
Control led
or Noted Comments
a* save as above
a* sane as above
a* same as above
a* sane as above
a* same as above
The effect of 5? pesticides on
embryonic development of clams and
oysters nas reported. Syn«»rqlstlc
Reference
Sanders
(1970) ,
AMIC-i.53
Sanders
(1970) ,A1IC-
Sandi>rs(1970
), AMIC-«i5J
Sanders
(1970) ,
AMIC-"tS3
Sanders
(1971) ,
AMIC-i.53
Davis, et al
(1969),
AMIC-5990
SI Ivex
SI'azlne
Crassostrea L
vlrglnlca
(larvae)
Fish (not
specified)
0.7 (TIM
greater than
10-100 (K)
effects xlth solvents were also reported.
Most of the compounds affected
development more than survival. Some,
however, drastically reduced larval
qpoxth. The authors point out the
necessity of evaluating the effects of
pesticides on all life staqes of an
organism and note the possibility of
selecting chemicals for pest control That
would not have serious effect on
shell fish.
sane as above
Approximate toxlcltles of
numerous pesticides commonly used In
Britain Here summarized. An excellent
brief, general discussion of toxlclty
testing Is also present.
Davis, et al
(1969),AMIC-
5990
Maxdesley-
Th omas
(1971),AMIC-
1056
Sl»87|ne
Sal«o
8CF» --
1.3 (T?)
a*,c,e,fi
One hundred sixty-four
Alabaster
-------
galrdneri
and
BSA
Slaazlne
Sal mo
galrdncrl
BCFA
and
BSA
(Tl)
>
I
8
Slnzlne
Slmazlne
Roccus
saxatllls
(fIngerIings)
SS«
Carclnus
naenas
BS» —
0.25 (Ti.)
greater than
100 (T2I
Slaazlne
Cardlum edule BSA
greater than
100 (T2>
hard (HH) pesticides, wetting agents, and (1969),
or soft miscellaneous water pollutants showed a AHIC-5,c,d,e,f Strioed bass flnqerllngs were Mellborn
,p and apparently much more sensitive to (1969),
Iron therapeutic and herblcldal compounds than AMIC-5723
many freshwater fish.
a»(contln- One hundred-forty surface active
uous aer- agents, solvent emulsiflers, pesticides,
atlon, sea-polychlorlnated blohenyls, pure
wator, 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 nith
toxlcity of chemicals to freshwater
organisms.
a-tf(contln- sane as above
uous, aer-
ation^ sea-
wator, and
daily
solution
renewal)
Portmann, et
al (1971),
AHIC-7701
Portnann, et
al (1971),
AMIC-7701
Sl«ailne
Crangon
crangon
BSA
greater than
100 (T2)
a»(contin-
uous, aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AMIC-7701
-------
o
Compound
Slmazlne
Slmazlne
Slmazlne
Slmazlne
Slmazlne
Slmazlne
Slmazlne
Sllchgone 1
Field Field
Organism Study Locatlor
Gammarus BSA —
f asclatus
Paleomontes BSA —
KadlaKensls
Asellus BSA
brevlcaudus
Orconectes BSA —
nals
Oaphnla maqna BSA —
Cyprldopsls BSA —
vldua
Lepomls BSA --
macrochlrus
Carclnus BSA — •
•aenas
Toxlclty,
Active
Ingredient,
> Ppm
greater than
100.0 (TZ>
greater than
100.0 (T2)
greater than
100.0 (T2)
greater than
100.0
3.2 (T2)
greater than
100.0 (T2)
33-100
-------
uoua, aer-
ation, sea.
water, and
daily
solution
renewal)
at (1971),
AMIC-7701
SIlcKgone 1
Crangon
crangon
BSA
3.3-10 (TZ)
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
sane as above
Portvann, et
al (1971),
AMIC-7701
SIlcKgone 1
Panda I us
•ontaqul
BS*
3.3-10 (TZ)
a*(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
sane as above
Portnann, «t
al (1971),
AMIC-7701
SIlcKgone Z
Carclnus
•aenas
BSA
10-33 (TZ)
a«(contin-
uous, aer-
ation, sea.
water, and
dally
solution
renewal)
same as above
Portnann, «t
al (1971),
AMIC-7701
SIlcKgone Z
Cardlun «dule BSA —
3.3 (T2)
a«(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
Portmann, et
al (1971),
AMIC-7701
Sllckgone
Crangon
crangon
BSA
3.3-10 (TZ)
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portmann, et
al (1971),
AMIC-7701
-------
k
ro
Compound
SllcNgon* ?
SUM
SI Ix
SI Ix
Sill
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Organism Study Location Ppn or Noted Comments
renewal )
Panda I us BS» — 3.3-10 (T2) a»(contin- san« as »bov«
•ontaqul uous aer-
ation, sea-
water, and
dally
solution
renewal )
Rasbora 8CF» — 8.3 (TZ) a*,c,e,f. One hundred sixty-four
heterororpha and hard pesticides, netting agents, and
BSA (HU)or miscellaneous water pollutants showed a
soft (SHI Hide range ot toxlcltv scanning 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 materials. Sometimes
species pesticides were most toxic In hard water
• and sometimes the ooposlte was true.
Testing the actual material as sold was
found to be essential.
Carclnus BSA ~ 15 (Ti») a»(contln- One hundred-forty surface active
•aenas uous aer- agents, solvent emulslflers, pesticides,
atlon, sea-col ych lorlnated blohenyls, pure
water, and Inorganic, and organic chemicals were
daily evaluated against as nany as ten marine
solution organisms. The authors noted that most
renewal) published data of this type deal with
ion toxlclty of chemicals to freshwater
renewal) organ Isas.
Cardlu* edule BSA — 33 (TZ> a»(contln- same as above
uoua aer-
ation, sea-
water, and
dally
solution
.'renewal)
Crangon BS» — 100-330 (TZ> a»(contin- sane as above
crangon uoua, aer-
ation, sea.
water, and
dally
P. ef erence
Portsann,
at (19711
AMIC-7701
Alabaster
(1969) ,
AMIC-5«i3S
Portmann,
al (1971)
AMIC-7701
Portnann,
al (1971)
AHIC-7701
Port»ann,
al (1971)
AMIC-7701
• t
,
• t
,
• t
,
• t
t
-------
solution
renowol)
SIU
Ostrea edulls BSA —
100 ITZI
a*(contin-
uous, aer-
ation, sea.
water, and
daily
solution
renewal)
saae as above
Portaann, «t
al 119711,
AMT.C-7701
SI Ix
PandaI us
•ontagul
BSA
10-33 ITZ)
a«(contln-
uoua. aer-
atlon, sea.
water, and
dally
solution
renewal)
sea* as above
Portaann. at
al (1971),
AMIC-7701
UJ
Snowdrift SC98
Crangon
cranqon
BSA —
330-1000 (T?l
Sedlua arsenaTa
Carasslus
auratus
3? (T7)
Sodlu* bicarbonate
Leponls
aacrochlrus
BSA,
I
8,600 (Tt>
a»(contln- One hundred-forty surface active
UOUs aer— aq^ntst solvent etnulsl f ierst pesticides*
atlon, sea-DolycMorlnated blohenyls, pure
water, and Inorqanle, and orqanlc cheiticals 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 chenlcals to freshwater
orqanlsms.
Poptwann, et
al (1971),
4MIC-7701
8,C
In addition to toxlclty data. Weir, et at
conditioned avoidance response was (1970),AMIC-
studled at sublethal concentrations. The 739
loxest concentration of metal resulting
In significant Impairment Has* arsenic,
0.101 lead, 0.071 mercury, 0.0131 and
selenium, 0.25. Deleterious effects
occurred at metal concentrations
aooroxlaately similar to potable water
standards.
a*,e, and
This study Has conducted to
Patrick, et
synthetic determine the relative toxlcltles of Ztt al (1968),
dilution common constituents of industrial Hastes AHTC-5720
•ater to a fish, an alga, and an invertebrate.
The experiments Here conducted over a
10-year period for varied purposes. The
authors recoaaend bloassays with at least
-------
Compound
Sodium bicarbonate
Sodlu* carbonate
Sodlu* carbonate
Sodlu* chlorate
Sodlu* chloride
Sodlu* chloride
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
prganls* Study Location Po* or Noted Comments
Nltzschla BSA, —
llnearls I
Leponis BSA, —
macrochlrus L
Nltzschla BSA,
llnearls L
Rasbora BCFA —
heteronorpha and
BSA
Leoonls BSA,
macrochlrus L
Nltzschla BSA, —
llnearls l
650 (T5> a*,e, and
syn thet 1C
dllut Ion
Mater
3?0 (T<>> a»,e. and
syn thef 1C
dilution
Mater
?<,? (T5) a>,e, and
synthetic
dl lut Ion
8600 (Tl) a»,c,e,f.
hard (HW)
or soft
(SH)
syn thet 1C
dl lut Ion
Mater, or
seaMater
for so*e
species
1?,9<,6 (TO a'.e, and
synthetic
dilution
Hater
?,<,30 (T5) a*,e, and
synthetic
dilution
Mater
three components of the food Meb.
sane as above
same as above
same as above
One hundred sixty-four
pesticides, Mettlng agents, and
miscellaneous Mater pollutants shoMed a
MMe range of toxlclty spanning 12 orders
of magnitude. KnoMlnq the toxlclty and
percenfaae 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 Mater
and sometimes the ooooslfe Mas true.
Testing the actual material as sold Mas
found to be essential.
This study Mas conducted to
determine the relative toxlcitles of 20
common constituents of Industrial Mastes
to a fish, an alga, and an Invertebrate*
The experiments Mere conducted over a
10-year period for varied purposes. The
authors recommend bloassays Mlth at least
three components of the food Meb.
same as above
Ref er ence
Patrick, et
al (1968).
AHIC-57?0
Patrick, ef
al (1968).
AMIC-STZO
Patrick, et
al (1968),
AMIC-57JO
Alabaster
(1969) ,
AMIC-SltZS
Patrick, et
al (1968).
AMIC-57ZO
Patrick, et
• 1 (1968),
AHIC-5720
Sodlua chloride
Agonus
BS*
,000-33,000 a*(contln-
On« hundred-forty surface active Portnann.et
-------
cataohractus
(TZI
Sodium chloride
Carcinus
•aenas
BSA —
Sodlua chloride
Card1u» edule BSA —
11,000-16,500
(TZ)
66,000 (TZ>
uous aer- agents, solvent emulsIflers, pesticides,
ation, sea-polychlorlnated blphenyls, 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 tilth
toxlclty of chemicals to freshwater
organisms.
a«(contin- sane as above
uoua aer-
ation, sea-
water, and
dally
solution
renewal)
a*(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
at (1971),
AMIC-7701
Portmann, et
al (1971),
AMIC-7701
Portmann, et
al (1971),
AMIC-7701
Sodlua chloride
Crangon
erangon
BSA
16,900-33,000
(TZ)
a«(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
Portmann, et
al(19711,
AMIC-7701
•Sodlua cyanide
Neqaprlon
brevlrostrls
(1-3 hq)
BSA —
6.6 (SB10 aln) a,e,e
Sodium fluoracetate
Salao
galrdner 1
BCFA
and
BSA
580 CTZ)
a*,c,e,f,
hard CHH)
or soft
(SH)
synthetic
dilution
Data from study of drug effects Baldrldge
on young lenon sharks Mere treated (1969),
mathematically to demonstrate AMIC-3832
apolIcabl11ty of classical rate theory to
the study of chemical shark deterrents.
Incaoacltatton (narcosis) was the primary
parameter timed for effectiveness. This
was usually quite rapid for the more
effective drugs.
One hundred sixty-four Alabaster
pesticides, wettlnq agents, and (1969),AMIC-
mlscel laneous water pollutants showed a 5<»Z5
wide range of toxlclty spanning 12 orders
of magnitude. Knowing the toxlclty and
percentage of alI components of a
water, or formulation did not result In easy
-------
Toxlcl ty.
Active
Field Field Ingredient,
Compound Organism Study Location Ppm
Exper 1 men tal
Variables,
Control 1 ed
or Noted
seswater predlctabl
for some mixture of
spec les pest Ic Ides
Comments
1 I ty of the toxlcl ty of a
materials. Sometimes
were most toxic In hard water
Reference
Sodium fluoride
Crangon
cranqon
8SA
greater than
300 (T2)
Sodium hydroxide
Aqonus
cataphractus
BSA
33-100 (T?)
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
ao(contln- One hundred-forty surface active
uoua, aor- aqents, solvent emulslflers, pesticides,
ation, sea- PoIychI orInated blphenyls, pure
wator, and Inorganic, and organic cherricals 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.
a»(contin-
uous, aer-
ation, sea-
water, and
daily
solution
renewal)
sam« as above
Por tmann,
etal (1971),
AMIC-7701
Portwann, «t
a I(1971),
AMIC-7701
Sodium hydroxide
Cardlum edule BSA
330-1000 (T?)
a«I contin-
uous, aer-
ation, sea-
water, and
daily
solution
renewal)
same as above
Portnann, »t
al (1971),
AMIC-7701
Sodium hydroxide
Crangon
crangon
BS» — -
33-100 (TZ)
B*(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
Portmann, «t
al (1971),
AMIC-7701
Sodlu* (olybdate
Sal no
qalrdnerl
FL
Casflt Lake, 3.5 Ib p«r A
Cal. (NTE)
Molybdenum fertilization resulted Cordone, «t
In greater standing crops of zooplankton al (1970),
-------
Sodlun molybdate
Sodlun nitrite
SalvelInus
fontInalIs
Rasbora
heteromoroha
FL
BCFA
and
BSA
Castle Lahe, 3.5 Ib per A
Cal. (NTE)
Z10 (T2)
k
Sodium
N-nethyldithio
Phormldluni
amblguum
11 ~~
0.5-10.0(NTE)
Sodlun
pentachlorophenate
Sal mo
galrdner1
BCFA
and
BSA
0.15 (T2>
and bottom fauna and apparently in
Increased yields of ralnboN and eastern
brook trout. Mitigating factors nay have
Influenced the results. A second
experimental fertilization was Initiated.
same as above
AHIC-5750
a*,c,9«f» One hundred sixty-four
hard (HW) pesticides, Netting agents, and
or soft miscellaneous water pollutants showed a
(SH) wide range of toxlclty spanning 12 orders
synthetic of magnitude. Knowing the toxlclty and
dilution percentage of all components of a
water, or formulation did not result In easy
seawater prertlctabl11ty of the toxlclty of a
forsome mixture of materials. Sometimes
species pesticides were most toxic In hard water
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
™ Of 71, chemicals evaluated as
alglcldes, only 9 were more toxic than
CuSOit. None inhibited growth of
mat-forming algae for more than 2 weeks.
CuSOU formulated with certain wetting
agents was more toxic than CuSO** alone.
Cooper chlorarolne was also found to be
more toxic than CuSOit. No wetting agents
were found to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 ODIT). fllso 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.
a',c,e,f, One hundred sixty-four
hard pesticides, wetting agents, and
(HH)or miscellaneous water oollutants showed a
soft (SH) wide range of toxiclty 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 Here most toxic In hard water
and sometimes the opposite Has true.
Cordone, et
al (1970),
AMIC-5750
Alabaster
(1969),
AMIC-51.25
Otto (1970),
AMIC-892
Alabaster
(1969),A«IC-
5V25
-------
COB
idlu
»nt»
. , Field Field
jtouBd Organise Study Location
chlorophenafe amblguum
Toxlclfy,
Active
Ingredient,
Pp«
0.5-10.0
00
Sodlu*
pyrldlne-N-oxlde
Sodlu* sulfate
Phormldlun
amblguu*
Leponls
•acrochlrus
BSA,
I
0.5-10.0 (NIC)
13,500
CuSO
-------
Sodlu* thlocyanate Cardlun edule BSA —
Sodlun thlocyanate Crangon BSA —
cranqon
Sodlun thlocyanate Panda I us BSA
nontagul
£•
vo
Splll-X
Splll-X
Steel head BSA —
trout
IfIngerlIngs)
greater than
500 CT2)
greater than
500 (T2)
greater than
6.2 CTZ)
35.5 (TO
Coho salmon BSA Hood Canal, 1.5
(flngerlings) In Hoodsport,
situ Wash.
a«(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
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
sane as above
sane as above
Portnann, et
al (1971),
AMIC-7701
Portmann,et
al (1971),
AMIC-7701
Portnann, et
al (1971),
AHIC-7701
Evaluation of 11 oil dlsoersants Tracy, et al
resulted In a ranKlnq for each and a
recommpndatlon for use according to the (1969),AMIC-
ranHlng. Ranking was based on toxlclty 383<»
and oil dispersal effectiveness. Corexlt
776ii aooeared to have the least toxlclty
xlth fair to good oil dispersion
caoablllty.
same as above
Tracy, et al
(1969).
Spill recover
Spill renover
Spill renover
Plnephates
Drove I as
BSA —
5.6
Plnephales BSA --
prone I as
Bloehenlcal I —
oxyqen denand
(HSCI
630,000
c,d,e,f Toxlclty of six oil split
dlsoersants Has determined along with
BOO values. Pond water Has used as
diluent and oil Has Included In the
exoerlnent. Oil markedly reduced
toxlclty of all dlsoersants. Data are
given as "most probable" 96-hr TL sub n.
c,d,e,f sane as above
c,d,e,f sane as above
Zllllch
(1969),
AHIC-?909
ZllIIch
(1969),AHIC-
?909
Zllllch
(1969),AHtC-
-------
Compound
Field Field
Organism Study Location
Toxlclty,
Active
Ingredient,
Pp»
Experimental
Variables,
Control led
OP Noted
Comment s
Reference
Streptomycin sulfate Llmnodrilus L —
sp
Streptomycin sulfate Tublfex sp L —•
Streptomycin sulfate Peloscotex sp I —
0.5 (Tl)
0.5 (Tl)
0.5 (Tl)
Tublflcld Norms Here found to be
aporoxlmately 300 times more sensitive
than their own gut microflora. The
authors recommend that streptomycin
should not be Indiscriminately applied In
aquatic ecosystems.
sane as above
same as above
7909
Coler,et at
(1968),
AMIC-5^60
Coler, et al
(1968).AMIC-
Si.60
Coler, et at
(1968),AMIC-
51.60
Streptomycin sulfate Phormldium L
amblguum
0.5-10.0 «NTE) —
Strobane
Leoomls BS»
cyan*11 us
(Resistant)
(T2>
Of 7i> chemicals evaluated as Otto(1970),
alqlcldes, only 9 were more toxic than AMIC-892
Cu5071
Parathlon. Golden shiners from the same
location Here resistant to Lindane and
Strobane, tolerant to Chlordane and
Heptachlor, and susceptible to Parathlon.
Lack of resistance to Parathlon
Indicated lack, of agricultural usage of
organophosphates In that area. Resistant
-------
Strobane
Lepomls
cvanelI us
(Susceptible)
BSA
0.05 (T2)
fish Here compared to susceptible ones
collected at Starkville.
same as above
MInchex,
etal (1970),
AMIC-51,71
Strobane
Strobane
Notemlqonus
crysoleucas
(Resistant)
Notemloonus
erysoleueas
(Susceptible)
BSA
BSA —
Z.22 (TZ)
0.06 CT2)
same as above
same as above
MincheH,
etal (1970),
AMIC-5*7l
Mlnchex,
etal (1970).
AMIC-5«.71
Strobane
>
I
K
Strobane
Strobane
Palaenonetes
KadlaKensls
(resistant)
BSA —
Palaemonetes
kadlaHensls
(non-
resistant)
Cooeoods
(Cycloos
blcusoldus,
Cyclops
varlcans,
CyclOPS
vernal Is,
Eucyclops
agllls.
Macrocyclop3
albldus,
Orthocyclops
•odestus)
0.085S-0.307
IT1)
8*
BSA
FL State
and College,
BSA Hiss.
0.0393(11)
0.10 (KZ)
Bloassays were conducted xlth
shrimp from three areas of Intensive
pesticide use and from an unexoosed area.
Previously exposed shrimp Mere from 1 to
25 times more resistant than unexposed
shrlmo. Both types of shrimp Here also
exposed In caqes 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
order Has as follons: most toxic,
Endrln, DDT, Methyl parathlon, Parathlonl
medium toxlclty, Guthlon, LIndane,
Toxaphene, Strobanel lease toxic
Chlordane, Sevln, and Heptachtor.
same as above
The response of
pesticide-resistant aquatic organisms to
various pesticides Has compared to the
response of non-resistant species.
Pesticide-resistant species Here
collected at Belzonl and non-resistant
species at State College. Copepods,
clams, snails, and sludge Horns 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
Naavl, et al
(1970),
AHIC-5519
Nsgvl, et al
(1970),
AMIC-5519
Naqvl, et al
(1969),
AHIC-5979
-------
Compound
Strobane
Strobane
Strontium
Organism
Cooepods
(Cvc 1 oos
bl cusp IduSt
Cycl oos
var leans,
Cycl oos
vernal Is,
Eucyclops
agl 1 Is.lacroc
Macrocyclops
al bldus.
Orthocycl CDS
•odes tus)
Tublfex
tublfex
Paral abrax
cl athratus
Field Field
Study Locat Ion
FL Belzonl,
and Hiss
BSA
FL Belzonl,
and Hiss.
BSA
FM Scattergood
Steam Plant,
Los Angeles,
Toxlclty,
Active
Ingredient,
Pom
0.10 (KZ)
1.50 (NTE)
2.2 (dorsal
muscle
residue)
Exoerlnental
Variables,
Control 1 ed
or Noted Comments Reference
pesticide residues available to anlvals
of higher trophic levels.
-- sane as above Naovl, et al
(19691 ,»NIC-
5979
— - same as above Naavl, et
al (1969) ,
AHIC-59r9
— • Fish collected from an effluent Staoleton
oloe of a steam olant and from offshore (1968),
Haters of Catallna Island were analyzed AMIC-5980
Strentlui
Strontlu*
Cal.
Paralabrax FM Catallna 1.7 (dorsal
clathratus Island, Cat. muscle
'residue)
Parslabrax FH Scatterqood 3.3 (ventral
clathratus Stea* Plant, auscle
Los Angeles, residue)
for trace element content. Trace element
content of the effluent water xas at
least 5 times greater than that of normal
sea water for cadmium, copoer, nickel,
zinc, and chromium. Livers of fish fro»
the effluent Here nearly txlce the size
of those from the ocean. Greatest
differences In concentration occurred
Hlth aluminum, cadmium, and nlcKet.
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.
same as above
sane as above
Staoleton
(1968),
AMIC-5980
Staoleton
(1968),
AMIC-5980
-------
Cal.
Strontlun
Strontlua
Strontium
Strontium
Strontium
Strontlua
Strontlun
Papalabrax
clathratus
Paral abrax
clathratus
Paral abrax
clathratus
Paralabrax
clathratus
(qravld
females)
Paralabrax
clathratus
ParaIabrax
elathratus
Paralabrax
elathratus
FH CatalIna 1.8 (ventral
Island, Cal. muscle
residue)
FH Scattergood 2 (gonads
Steam Plant, residue)
Los Angelest
Cal.
FH Catal Ina 3.<> (gonads
Island, Cat. residue)
FM
CatalIna
Island, Cal.
3.2
(gonads.
reaidue)
Scatter-good 1.1 (liver
Steam Plant, residue)
Los Angel est
Cal.
FH Catal Ina 2.1 (liver
Island, Cal. residue)
FH Scattergood 5.
-------
Toxlclty,
Active
Field Field Ingredient.
Conoound Organism Study Location Pom
Sfrontlun Paralahrax FM C»tal Ina 16? (eyeball
clathratus Island, Cal. residue)
Strychnine nitrate Neqaprlon BSA — 1.7 (SB 10
brevlrostrls HIN)
fl-J H.q>
Sulf Isoxszole Fundulus L — 0.96 (SB30I
(3 In.)
Sulturlc acid Agonus BSA — 80-90 (T2>
cataphractgs
Sulfurlc acid Carclnus BSA — 70-»0 (TZI
•aenas
Experlmenta
Variables.
Control led
or Noted
».c,e
a'.q
a»( contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal )
a»( contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal )
1
Comments
same as above
Data from study of druq effects
on younq lemon sharks Here treated
mathematically to demonstrate
apol 1 cshl 1 1 fy of classical rat» theory to
the sturty of chemical sharto deterrents.
Incaoac 1 1 a 1 1 on (narcosis) nas the primary
parameter timed for effectiveness. This
was usually quite rapid for the more
effective drugs.
The sulfa druq caused no
testes Height. Iodine uptake, or liver
Height. Varying degrees of adrenal
Inactivity and adrenal degr anul a t 1 on
occurred due to treatment. » significant
Increase In heiratocrlt Has noted. As a
result this chemical has become the sulfa
drug of choice In the fllngham Laboratory
for controlling shin Infection of
Kl 1 11 fish.
One hundred-forty surface active
agents, solvent emulslflers, pesticides.
Pol ych lorlnated biphenyls. pure
Inorqanlc, and organic chemicals Here
evaluated against as many as ten marine
organisms. The authors noted that most
published data of this type deal nlth
toxlclty of chemicals to freshnater
organisms.
sane as above
Ref erence
Stapl eton
(1968) ,
AMIC-5980
Baldrldge
(1969),
AMIC-383?
COHmeadoM.
(1969) .
AMIC-5736
Portmann, et
al (1971),
AHIC-7701
Portaann. et
• 1 (1971),
AMIC-7701
Sulfurlc acid
Cardlu* edule BS* —
700-500
a«(contln-
sn* as above
Portaann, et
-------
uoua aer-
ation, sea.
water, and
dally
solution
renewal)
al (19711,
AMIC-7701
SulfurIc acid
Cranqon
crangon
BS» —
70-8D (TZ)
a»(contin-
uous aer-
ation, sea.
water, and
daily
solution
renewal)
sane as above
Portnann, «t
al (1971),
»MIC-7701
SulfurIc acid
Panda I us
nontaqul
BS» —
it?.5 (T2>
vn
a»(contin-
uous aer-
ation, sea-
water, arid
dally
solution
renewal)
sane as above
Port»ann, at
al (1971).
AMIC-7701
Sulfurlc acid
Platlcthys
flesus
BSA —
100-330 (TZ>
a*(contin-
uous aer-
ation, sea-
water, and
dally
solution
renewal)
sane as above
Portaann, at
al (1971),
AMIC-7701
Sulfur
Sulaet (tinted)
Fish (not
specified)
Mercenarla
mercenarla
(eggs)
greater than
1000 (K)
greater than
100 (TZ)
Approximate toxlcltles of Mawdesley-
numnrous pesticides commonly used In Thomas
Britain were summarized. Arv excel l»nt (1971),AHIC-
brleft general discussion of toxlclty 1056
testing Is also oresent.
The effect of 5? pesticides on Oavls, et al
embryonic development of clams and (1969),
oysters was reported. Synerqlstlc ANIC-5990
effects Hlth solvents Here also reported*
Most of the compounds affected
development more than survival. Some,
hoHever, drastically reduced larval
growth. The authors point out the
necessity of evaluating the effects ol
pesticides on all life stages of an
organism and note the possibility of
-------
I
H
ON
Compound
SulBet (tinted)
SulBet (untlnteri)
Sulvet (untinted)
SulBet (untlnted)
Sulmet (untlnted)
SUB! thlon
Field Field
Organism Study Location
Merc en aria I
mercenar 1 a
1 1 arvae)
Mercenarla L —
mercenar la
(eggs)
Mercenar I a L —
mercenarla
(larva?)
Crassostrea L —
vlrglnlca
(eggs)
Crsssostrea L —
vlrglnlca
(larvae)
Puntlus ticto -- --
Toxlclty,
Active
Ingredient?
Ppm
greaterthan 100
(T13)
greaterthan
1000 (T?)
greater than
1000 (U?>
greaterthan 600
(T2)
greater than
600 (Tli>)
0.005S (Td)
Expert men ta 1
Variables,
Control 1 ed
or Noted Comments Reference
selecting chemicals for oest control that
Mould not have serious effect on
Shell fish.
same as above Davis, et
(1169) ,
AMIC-5990
--> same as above Davis, et
(1969) ,
AMIC-5990
sane as above Davis, et
(1969) ,
AHIC-5990
-- same as above Pavls, et
(1969) ,
AMIC-5990
-- same as above Davis, «t
(1969) ,
AMIC-5990
a,c,d,e,f Of the pesticides Investigated, Bhatla
al
al
al
al
• 1
Sut»n
Gammarus
fasciatus
BSA
10.0 (Td)
the most toxic xas Klofos folloHed In (1971),
decreasing order by Sumithlon, Malathlon, AHIC-5itZ3
Formlthlon, Olmecron, Sevln, and BHC. Th«
author cites the need Tor more selective
pesticides nontoxlc to fish or
antagonistic agents for reducing fish
toxlclty.
Of the aquatic Heed herbicides Sanders
evaluated, Dlclone was the most toxic, (19701,
Daohnla Has generally the inost sensitive AMIC-*53
organism. AM of the Crustacea were
affected by much loner concentration
levels of herbicides than Indicated by
the TL sub 50 values. ail of the animals
represent Important food chain links.
S.O. 35ft?
Rasbora
hetero«orpha
BCF»
and
BSA
greater than
1.000 (T?)
a'.c.e, f,
hard(HH)
or soft
(SH)
synthetic
dl lutlon
natepf or
seaxater
for so»e
One hundred sixty-four
pesticides, netting agents* and
miscellaneous Hater pollutants shOHed a
Hide range of toxlclty spanning 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
•Ixture of materials. Sooetlmes
Alabaster
(1969),AMIC-
-------
S.O. 8211
Rasbora BCFA
heteromorpha and
8SA
3.5 (TZ>
S.O.
>
Rasbora BCFA
hetero«orpha and
BSA
<>.3 (TZt
S.H.
Rasbora BCFA
heteromoroha and
BSA
23 ,e,e,t,
hard (HH)
or
SOFTCSVI)
synthetic
dilution
Hater, or
seanater
for some
species
pesticides were 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
Alabaster
(1969),
AMIC-5<»25
sane as above
Alabaster
One hundred sixty-four
pesticides, netting agents, and
miscellaneous Hater pollutants shoned a
Hide range 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 toxlclty of a
mixture of materials. Sometimes
pesticides Here most toxic In hard nater
and sometimes the opposite Has true.
Testlno the actual material as sold Has
found to be essential.
The effect of 52 pesticides on
embryonic development of clams and
oysters Has reported. Synerglstlc
effects Hlth solvents Here also reported.
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
organism and note the possibility of
Alabaster
(1969),
AMIC-5V25
Davis, et at
t!969),AHIC-
5990
-------
Compound
Field Field
Orqanlsn Study Location
Toxlclty,
Active
Inqredlent,
Pp«
Experluental
Variables,
Control Ied
or Noted
Comments
Reference
TCC
Mercenary a
mercenerla
(Iarvae)
0.037 (T1Z)
selecting chemicals for oest control that
Hould not have serious effect on
shell fish.
sane as above
Davis, et •)
(1969),AMIC-
5990
TCP
I
H
CD
Crassostrea
vlrqlnlca
(eqqs)
0.6 (TZ>
The effect of "52 pesticides on
embryonic development of clams and
oysters xas reoorted. Synerqlstlc
effects with solvents were 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 staqes of an
organism and note the possibility of
selecting chemicals for oest control that
would not have serious effect on
sh«l I f Ish.
Oavls, et
(1989),
AMIC-5990
TCP
Crassostrea
vlrglnlca
11arvae)
I —
greater than
1.0 (Tl«.)
same as above
Davis, et
al(19691,
AMTC-5990
TOE
TOE
TOE
Fish (not
specified)
White sucher FRL
qreafer than
0.01-0.1 (K)
Misc. states 0.05-1.81
residue (SB)
Yellow oerch FRL Misc. states 0.03-H7
residue (SB)
Approximate toxlcltles of
numerous pesticides commonly used In
Britain were summarized. An excellent
brief, general discussion ot toxlclty
testing Is also present.
The Bureau of Sport Fisheries
continued Its fish monitoring program by
collecting I
-------
TOE
White catfish FRL Misc.
States 0.33-0.1(3
residua (SB)
same as above
Henderson,«t
al (1171),
AMtC-U07
TOE
TOE
TOE
White perch FRL Misc.
Goldfish FRL Misc.
PumpKlnseed FRU Misc.
states 0.65-8.07
residue (SB)
states 1.91 residue
(S9)
states 0.39 residue
(SB)
same as above
same as above
same as above
Henderson,
etal (1971),
AMIC-li.07
Henderson,
et al(1971),
AMIC-11.07
Henderson,
et al(1971),
AMIC-11.07
TOE
TOE
Largemouth
bass
Brown
butI head
FRL Misc.
FRL MISC.
states O.Oi»-2.73
residue (SB)
states 0.07-1.76
residue (SB)
sane as above
same as above
Henderson,et
al (1971),
8HIC-1U07
Henderson,et
a I (1971),
AMIC-li.07
TOE
TOE
Carp
Channel
catfish
FRL Misc.
FRL
states 0.07-1.S6
residue (SB)
Misc. states 0.0<»-10.it
residue (SB)
same as above
same as above
Henderson,
et al (1971) ,
AMIC-Ii.07
Henderson,et
al (1971),
AMIC-11.07
TOE
TOE
Redhorse FRL
sucker
Misc. states 0.03-0.i>i»
residue (SB)
Gizzard shad FRL Misc.
states 0.37-0.73
residue (SB)
same as above
same as above
Henderson,et
al (1971),
AMIC-1<>07
Henderson,
etal (1971),
AMIC-11.07
TOE
TOE
TOE
Spotted FRL
sucker
Redbreast FRL
sunfish
Misc. states 0.19-0.32
residue (SB)
Bluegllts FRL Misc.
states 0.03-0.
-------
Coaoound
TOE
TOE
TOE
TOE
1
if TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
Organise.
Striped
Blue catfish
Rock bass
Freshwater
dru»
61 oater
Lake
•hltetlsh
Lake trout
White crapole
Blgnouth
buffalo
SnaMaouth
buffalo
Flathead
catfish
Goldeye
Field
Study
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
FRL
Field
Locat Ion
Hlsc.
Hlsc.
Hlsc.
Misc.
Hlsc.
Hlsc.
HISC.
Hlsc.
HISC.
Hlsc.
Hlsc.
states
states
states
states
states
states
states
states
states
states
states
states
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ron or Noted
n. 20-2. 26
residue (SB)
0.08 residue --
(SB)
0.05-0.59
residue (SB)
0.28 residue
(SB)
0.15-0.71,
residue (SB)
0.12 residue — -
(SB)
0.02-0.15
residue (SB)
0.22-0.27 —
residue (SB)
0.17-0.60
residue (SB)
O.ii6 residue
(Sfl)
0.80 residue --
(SB)
0.02-0.28 —
residue (SB)
Comments
same as above
same, as above
sane as above
same as above
sane as above
save as above
same as above
same as above
sane as above
sane as above
saae as above
saae as above
Reference
Henderson, et
al (1971),
AMIC-11.07
Henderson,
et al (1971),
HMIC-1U07
Henderson ,
et al (1971) ,
AMIC-m07
Henderson ,
et al (1971),
AMIC-11.07
Henderson ,
et al (1971),
AMIC-11.07
Henderson,
et al (1971) ,
AMIC-m07
Henderson,
et al (1971) ,
AMIC-1".07
Henderson, et
al (1971),
AMIC-11.07
Henderson.et
al (1971),
AMIC-11,07
Henderson.et
al (1971),
AMIC-H07
Henderson,
etal (1971),
AHIC-li.07
Henderson,
et al (1971),
-------
AMIC-11.07
fe
H
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
Walleye
Sauqer
FRt
Misc. states 0.03-0.79
residua (SB)
FRL Misc. states 0.10 residue
(SB)
Flannelmouth FRL
sucker
Misc. states
BlacK
bulI head
FRL Misc. states
White bass FRL Misc. states
BlacK crapole FRL Misc. states
Larqescale FRL
sucker
Small mouth FRL
bass
Northern FRL
squaHfIsh
Misc. states
Misc. states
Misc. states
Chlselmouth FRL Misc. states
Klamath
sucker
FRL Misc. states
Pa Inbox trout FRL Misc. states
0.28 residue
(SB)
0.02-0.05
residue (SB)
0.09 residue
(SB)
0.2J-O.I.9
residue (SB)
0.06-0.29
residue (SB)
0.1I.-0.23
residue (SB)
0.03-0."4?
residue (SB)
0.09-0.1.1
residue (SB)
0.01 residue
(SB)
0.03-0.16
residue (SB)
same as above
same as above
sane as above
sane as above
sane as above
sane as above
same as above
same as above
same as above
same as above
same as above
same as above
Menders on,
et al(1971),
AHIC-11.07
Henderson, et
al
(1971), AMIC-
Henderson, et
al (1971),
AMIC-l
-------
CoBDOund
TOE
TOE
TOE
TOE
Organise
sucker
Arctic
grayl Ing
Round
•hltef Ish
longnose
sucker
fnqraul Is
•ordax
Field Field
Study Location
FRL Misc. states
FRL Misc. states
FRL Misc. states
FH Pacific
Northwest
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pp« or Noted Consents
(SBt
D.16 residue — - saae as above
(SB)
0.33 residue — se«e as above
(SB)
0.01-0. 52 — save as above
residue (SB)
0.07-0.2** — — Pesticides from the Columbia
(residue) Plver Into Puqet Sound apparently
Re f erence
e t a 1 ( 1 97 1 ) ,
AMIC-l,
AMIC-378
-------
k
u>
TOE
TOE
TOE
TOE
TOE
TOE
TOE
TOE
Herlucelus FN
eroductus
Her luce I us FH
eroductus
Merlucelus FN
DPOductus
(f IshnesM
Sebastodes FH
alutus
Platlchthys FN
stellatus
Gadus FN
naerocephalus
Sebastodes FN
flavldus
Sebastodes FN
flavldus
Poecllla BCH
retlculata
Pacific 0.03-0.09
Northwest {residue)
Coastt Fort
Susant Mash.
Pacific
Northwest
Coastt Cape
Foulxeather,
Ore.
Pacific
Northwest
Const<
Aberdeen,
Mash.
PacifIc
Northwest
Coast,
Hecate
Strait, B.C.
Pacific
Northwest
Coast^
Rlalne,
Mash.
Pacific
Northwest
Coast,
Blalne,
Mash.
PaclfIc
Northwest
Coast,
Hecate
Strait, B.C.
Pacific
Northwest
Coast,
Ilwaco.Wash.
0.07lr«sldue)
0.03 (residue) —
Trace
(residue)
0.03(r«sldue)
0.01 (residue) —
O.Ol(resldue)
0.02-0.09
(residue)
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
sane as above
Stout
(1968),
ANIC-3781.
Stout
(1968),
»NIC-378I»
Stout
(1961),
4MIC-378I.
Stout
(1968),
»NIC-378«»
Stout
(1968),
»MIC-378S7
vlablly, survival, and reproduction of
-------
Compound
Field Field
Organise Study Location
Toxlclty,
Active
Ingredient,
Pp»
Experimental
Variables,
Control led
or Noted Comments
Reference
TEPA
TEPP
Poecllla 8CH
ret Iculaf a
Tublfex
tublfex
FL
and
BSA
Belzonl,
Hiss.
190 IT<>>
8.00 (NTEI
TEPP
Crassostr«a
vlrqlnlca
(•ggs)
greater than
10.0 (TZ»
the unexposed Fl generation. Hale
fertility was adversely affect-d at
concentration levels that did not
Influence female reproductive capability.
Inhibited brood oroductlon was
associated with atrophied and normal
testes. The effect varied with
concentration and exposure frequency.
Male potency appeared to recover when
exposures were discontinued. No apparent
effects were observed In the Fl
generation. TFPA Is a chemosterlI ant
used to Induce sterility In Insect pests.
a.c.d sane as above
Stoch, et
at U969).
AMIC-5I.S7
Naqvli et
al I19&9).
AMIC-5979
The response of
pesticide-resistant aquatic organisms to
various pesticides was compared to the
response of non-resistant snecles.
Pesticide-resistant species were
collected at Helzonl and non-resistant
species at State College. Cooepods,
clams, snails, and sludge, worms from
Belzonl were considerably more tolerant
to pesticides th^n 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 anlnals
of higher trophic levels.
The effect of 5? pesticides on Davis* «t
embryonic develop*ent of clams and al(1959),
oysters was reported. Synerglstlc AHIC-5990
effects with solvents were also reported.
Most of the compounds affected
development nore 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
organlsn and not* the possibility of
selecting che«leils for oest control that
-------
TEPP
T«rra«ycln
fconcentratet
Crassosfrea
vlrglnlca
(larvae)
Horone
saxatlils
(finger)Ings)
BSA
greater than
10.0 (Tll>)
165 mi
Mould not have serious effect on
shellfish.
sane as above
Davis, et
al (1969),
AMIC-5990
Mel I born
(1971),
AMIC-SS71
Tetradifon
Cardlum edule BSA --
rV
vn
Tetrad If on
Cranqon
crangon
BSA
a,c,d,e,f, All compounds Mere 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,
LIndanp, and Terramycin concentrate.
Those that should not be used Mere
Acrlflavlne, Baylusclde, Malachite green
oxalate, and Malathion.
greater than 10 a«(contln- One hundred-forty surface active Portmann, et
(TZ) UOU3, aer- agents, solvent emulslflers, pesticides, at (1971),
ation, sea-oolychlorlnated blohenyls, pure AMIC-7701
water, and Inorganic, and organic chemicals Mere
dally evaluated against as many as ten marine
solution organisms. The authors noted that most
renewal) oubllshed data of this type deal with
toxlelty of chemicals to Treshwater
organisms.
same as above
greater than 10 a«(contin-
(T?) uoua, aer-
ation, sea-
water, and
daily
solution
renewal)
Portnann, et
al (1971),
AHIC-7701
Tetrahydroturfuryl
alcohol
TFN
Rasbora BCFA —
heteronorpha and
BSA
Petronyzon FUR Marouette
varlnus County,
3,1.00 (TZ) a'.c.e.f,
hard(HH)
or soft
(•5H)
synthetic
d 1 1 u 1 1 on
Mater, or
seaHater
for some
species
3.R-9 (annual a,f,
treatment • conduo-
One
pesticides,
m Isce 1 1 aneo<
Hide range
of m^qn I tudi
percentage i
f ormu 1 at 1 on
predlctabll
mixture of i
pesticides
and sonetlmi
Testing the
found to be
TFN
lervlclde, '
hundred sixty-four Alabaster
Mettlng agents, and (1969),AMIC-
us Hater oollutants shOMed a Si»2S
of toxlelty scanning 12 orders
KnoHlng the toxlclty and
ol all components of a
did not result In easy
Ity of the toxicltv of a
materials. Sometimes
Mere most toxic In hard nater
es the opposite Mas true.
actual material as sold Mas
essential .
TFN, a selective lamprey Hanlon
applied annually over a (1969),
-------
Field Field
Compound Organism Study Location
Toxlclfy,
Active
Ingredient,
Pom
Experiments!
Variables,
Control led
or Noted Comments
Reference
Michigan., 89-96 oercent
Garlic River copulation
and SauxHesd reduction)
Lake
Thaillun
Cranqon
cranqon
8SA
10 (T
Thjnet
Rasbora
he teromorpha
BCF»
and
BSA
less than 10
(Tl)
fhloglycollc acid
Plmeohales
or one I as
BSA —
30.0
Thlolutln
Phormldlu*
8«blguu»
0.5-10.0 (100
percent growth
tivlty 3-year period to the Garlic River whlcn AHIC-3761
flows Into *5aux Head Lake. The final
TFN treatment contained I oercent
flaylusclde as a synerglst and "bottom
toxicant". The two compounds in
combination were considerably more
effective than TFN alone. The author
believed total effectiveness was not
achieved because lampreys avoid lethal
doses by moving to untreated water.
a«(contin- One hundred-forty surface active Porti»ann, «t
uoug aer- agents, solvent emulslflers, pesticides* al (1971),
ation, sea-Do 1 yen. I orl na t ed hlnhenyls, pure AMIC-7701
water, and Inorganic, and organic chemicals were
daily evaluated against as many as ten marine
solution organisms. The authors noted that most
re.ievaj,} published data of this type deal with
toxlelty of chemicals to freshwater
organ Isms.
a*,c,e,f, One hundred sixty-four Alabaster
hard (HH) pesticides, wetting agents, and (1969),
or miscellaneous water pollutants showed a AMIC-54??
SOFT(SH) wide range of toxlelty spanning 1? orders
synthetic of magnitude. Knowing the toxlelty and
dilution percentage of all components of a
water, or formulation did not result In easy
seawater predictability of the toxlelty of a
lor 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.
»',d,e,o, Malathlon and Its hydrolysis Bender(1969),
and ft products were evaluated with the finding AHIC-3787
that one such product (dlethyl fumarate)
was iiore toxic than Malathlon to fathead
minnows. Synerglsm occurred between
Malathlon and two products of hydrolysis.
Continuous exposure resulted In
Increased toxlelty.
Of 71. chemicals evaluated as Otto (1970),
alglcldes, only 9 were «orc toxic than AMIC-89Z
-------
Inhibited !<•)
Thlunet
Rasbora
heteronoroha
BCFA
and
BSA
12 (T?)
Thorlua
Alosa
pseudo-
harengus
FL
Thorlu*
Thorlu*
Coregonus
artedll
FL
Coreqonus FL
clupeaformls
a',c,e,f,
hard (HH>
or soft
(SHI
synthetic1
dilution
water, or
seawater
for some
species
Great Lakes
- Superior,
Michigan,
and Erie
0.006(r*sldue) —
Great Lakes
- Superior,
Hlchlqan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
0.003(resldue) —
0.00<» (residue) —
None Inhibited growth of
mat-forming alnae for more than 2 weeks.
CuSQii formulated with certain wetting
agents Mas more toxic than CuSIH alone.
Conner chloramine Has also found to be
more toxic than CuSO<>. No Mettlna agents
Here found to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 oom). Also reoorted are factors
affecting growth of algae in canals to
determine Hhether there Here leads to
controlling algae by environmental
management. No practical environmental
means Here found.
One hundred sixty-four Alabaster
pesticides, netting agents, and (1969),
miscellaneous Hater pollutants showed a AMIC-5*25
HUP range 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. Sometimes
pesticides were most toxic In hard Hater
and sometimes the opposite was true.
Testing the actual material as sold was
found to be essential.
Trace element content of fish Lucas, «t al
from Ljkes Superior, Michigan, and Erie (1970),
was determined by activation analysis. AMIC-3778
Whole body and liver residues were
determined. Concentrations varied with
species and lake. Other elements found
nere! antimony - 5 to 100 ppb, barium -
0.7 opnt, cesium - 3 ppb, lanthanum - 1 to
ZO pob, mercury - 10 ppb, rhenlutt - 0.5
to 5 pob, rubidium - 0.06 to 6 PD«,
scandium - 2 ppb, selenium - 0.1 to 2
ppb, silver - 0.001 pob.
same as above Lucas, et al
(1970),
AMIC-T778
sane as above
Lucas, et al
(1970),
AMIC-3778
-------
Compound
Thorium
Thorium
Thorium
Thorium
Thorium
Thorium
Thorium
Thorium
Thorium
Orqanlsm
Coreqonus
ho/1
Prosoolum
cy 1 Indraeeum
Sal vel Inus
namaycush
Osmerus
mordax
Carassius
auratus
Notropls
hudsonlus
Percopsls
onlscomaycus
Roccus
chrysops
Perca
f lavescens
Field
Study
FL
FL
FL
FL
FL
FL
FL
FL
FL
Toxlclty, Experimental
Active Variables,
Field Ingredient, Controlled
Location Ppm or Noted
Great Lakes 0.0021 (residue) —
- Superior,
Hlchl qan,
and Erie
Great Lakes 0.0005 (residue) —
- Superior,
Mlchl qan,
and Erie
Great Lakes 0. 00". (residue)
- Superior,
Mlchl qan,
and Erie
Great Lakes ? (residue)
- Superior,
Mlchl g an, and
Frie
Great Lakes 53(resldue) —
- Suoerlor,
Mlchl qan,
and Erie
Great Lakes 0. 0085(resl due) —
- Superior,
Mlchl qin,
and Erie
Great Lakes 0.002
same as above
Lucas, et al
-------
vltreun
vltreum
Thyroxine
Tlasan (ethyl Sal no t
••rcury phosphate) galrdnerl
>
VO
Tin
Coregonus FL
clupeaforals
Tin
Tin
Tin
Coregonus FL
cluDeafomls
Esox luclus FL
Esox luclus FL
- Superior,
Michigan,
and Erie
Gadus norhua L —
0.000001 ISB6)
2.0 (SB 1-2)
Moos* Lake, 3.6 (residue)
Can.
Lake 0.8 (residue)
Ontario,
Can.
Hoos« Lake, 5.* (residue)
Can.
Lake St. 0.7 (residue)
Pierre, Can.
Line-caught Juvenile cod held In
small tanks of seaxater responded to
thyroxlne Injection by a 3"5 percent
Increase In swimming speed* Large
replication resulted in highly
significant (P less than 0.001)
difference between treated fish and
controls.
a,e,f (1 Single exposures of fish to
hr orqanomercur-y compounds resulted in peak
exposure concentrations of mercury as follows!
daily for gills, 3 hrl blood, 3? hri liver, 7 dal
up to 11 kidney 21 For repeated one hr (daily)
days) exoosures peak concentrations were!
blood, 10 d?i liver, 10 dal kidney. 61
dai muscle, 7 da. The concentration of
mercury Has always lowest In muscle
tissue. Feeding experiments with "MA
shoHed mercury could be passed from
flngerllngs to larger fish. The authors
conclude that either legal size or
flngerllng hatchery fish treated Kith
organowercurials could be a public health
hazard.
— Concentrations of 13 toxic
elements In dressed fish from heavily
industrialized and non-industrialized
areas Here determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements Mere
essentially the same In fish fro* both
areas.
sane as above
(1970),
AMIC-37T8
Moodhead
(1970),AHIC-
3825
Rucker, et
at (1969),
AMIC-5733
Uthe, et
AL(1971),
AMIC-3819
same as above
same as above
Uthe, et
ALU971),
AMTC-3819
Uthe, et al
(1971),AMIC-
3819
Uthe, et al
(1971),AMIC-
3819
Tin
Esox luclus FL
Lake Erie, 0.5 (residue) —
sane as above
Uthe, et al
-------
Compound
Tin
Tin
TN
Organlsn
Osmerus
nordax
Peres
f 1 avescens
Fundul us
heterocl 1 tus
Field Field
Study Locat Ion
Can.
FL Lahe Eric.
Can.
FL Lake Erie,
Can.
BSA —
Toxlclty,
Active
Ingredient,
Po«
1.2 (residue)
0.6 (residue)
0.000008-0.0001
9 m»
Experimental
Variables,
Control led
or Noted Comments
sane as above
-- sane as above
a*»c,e» fl laboratory procedure based on
and Standard Methods for 96-hr toxlclty
synthetic determinations of crude oil and
Reference
(1971) ,
AMIC-3819
Uthe, et al
(1971) .AMIC-
3819
Uthe, et al
(1971) ,«MIC-
3819
LaRoche, «t
al (1970),
AMIC-".".?
I
§
TN
TO It
Nereis vlrens BSA
Gamnarus
(asclatus
BSA —
seawater
0.00006-0.00033 a'.c.e,
(T",) and
synthetic
seawater
8.30 a»
o 11-dIspersant mixtures was described.
The discersanfs varied considerably In
toxlclty, ranging from 0.01 to 7.1 ml/1,
TL50 for 96 hr. These did not differ
significantly from 2<»Q hr values. The
dlsoersants were designated as CX, DO,
Cl, On, flO, PC, MM, TN, BP, and NA with
no further descrlotlon of their chemical
nature or source. Only a few bioassays
were conducted with shrimo. MollusKs and
echlnoderms were suggested as suitable
test animals. The authors stated that
the method could be used to test any
product tor toxlclty In seawater.
same as above
LaRoche,et
al (1970).
AMIC-".".?
Of the aquatic weed herbicides
evaluated, Oiclone was the most toxic,
"Oaohnla 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 50 values. AlI of the animals
rcoresent Important food chain links.
Sanders
(1970),
AMIC-«.53
Tordon C
Rasbora
heteronorohs
BCFA
and
BSA
(T3)
One hundred sixty-four
a",c,c,t,
hard (HH) pesticides, wettin
or soft miscellaneous wate
(SH) wide ranqe of fox
synthetic ot magnitude. Kno
dilution percentage of all
water, or formulation did not result In easy
seanater predictability of the toxlclty of a
for some mixture of materials. Sometimes
species pesticides were most toxic In hard wster
agents, and
oollutants showed a
Ity spanning 13 orders
Ing the foxlclty and
omoonents of a
Alabaster
(1969).
AHIC-5I.Z5
-------
Tordon M
Toxephene
Toxaphene
Toxaphene
Toxaphene
Toxachene
Toxaphene
Rasbora 8CFA
heteronorpha and
BSA
(T2)
Ictaturus
punctatus
BSA —
0.013 (Tit)
Ictalurus
me I as
Carasslus
auratus
Cvorlnus
carpi o
BSA
BSA
BS» —
Pimeohales BSA
promelas
Leoomls BSA
macrochlrus
0.009
O.OH, (Tit)
0.00
-------
Compound
Toxaphene
Toxephene
Toxaphene
Toxephene
Toxaphene
Field Field
Organism Study Location
Salmo BS» —
galrdner 1
Sal BO trutta BS» —
Oncorhynchus BS* --
klsutch
Perca BS«
f lavescens
Palaemonetes BSA —
had 1 aliens Is
(resistant)
Toxlcltv,
Active
Ingredient,
Ppm
0.011 (TO
0.003 (Tit)
0.008 tiki
0.012 IT*1
0.0«,«,-0.?Z9
(Tl)
Experimental
Variables,
Control led
or Noted Comments
test water
a,
synthetic
test water
a,
synthetic
test Hater
a,
synthetic
test water
a,
synthetic
testnater
a»
sane as above
sane as above
sane as above
sane as above
Bloassays Here conducted nlth
shrimp from three areas of Intensive
pesticide use and from an unexposed area.
Reference
*nrc-55io
Macek, etal
(1970) ,
AMIC-S510
MaceH, et
al (1<<70).
4MIC-5MO
HaceK.et al
11970) ,
»MIC-S510
Haceh.et al
«1970) ,
»MIC-5510
Naqvl. et al
(1970),
»NIC-5519
Toxaphene
Texaphene
Palaemonetes BSA —
hartlaKensls
(non-
resistant)
0.0709 (Til
shrimp. Both types of shrimp Here 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
order Has as follows: most toxic,
Fndrln, POT, Methyl parathlon, ParatMonl
• edluit toxlclty, Guthlon, Llndane,
Toxaphene, Sfrobanei lease toxle
Chlordane, Sevln, and Heptachlor.
same as above
Naovl, et
(1970),
*HIC-5519
• I
Cooepods
(Cyclops
blcusoldus,
Cyclops
varlcansf
Cycloos
Ft
and
BS»
State
Col lege,
Hiss.
0.01,5 181,
percent K3)
The response of
pesticide-resistant aquatic organisms to
various pesticides Has compared to the
response of non-resistant species.
Pesticide-resistant species Here
collected at Belzonl and non-resistant
Naavl, et al
(1969),
4NIC-59T9
-------
Toxaphene
s
CO
Toxaphene
vernal 1st
Eueyclops
agl tIs.Hacroc
Maerocyelops
albldus,
OrthocvctODS
•odestusl
Cooeoods
(Cvclops
blcusoldust
CvclCDS
varlcsns,
Cyct oos
vernal Is,
Eucycloos
aglIls,laeroc
Kacrocyclops
albldus,
Orthoeyelops
•odestus)
Tub ifex
tublfex
FL
and
BS»
Belzonl,
Hiss
0.0<.5 178
percent K2)
FL
and
BS»
Relzonl,
Miss.
6.0 (NTEI
species at State Colleqe. Copepods>
clams, snalls< and sludge norms Iron
Belzonl were considerably more tolerant
to pesticides than the non-resistant
orqanlsms. The authors note that the
effect of Increased tolerance In the
orqanlsms is an Increase In the avount of
pesticide residues available to anlaals
of higher trophic levels.
saae as above
same as above
Naqvl. et at
(19691,
»HIC-59T9
Naavl, etal
(1<»6S) ,
aniC-5979
Toxaohene
Toxaphene
Toxapnene
Toxaphene
Toxaphene
Physa qyrlna
Physa gyrlna
Eupera
slnqleyl
Eupera
slngleyl
Hercenarla
mercenarla
(eggs)
FL
and
BS»
FL
and
BS»
FL
and
BS»
FL
and
SS*
I
State
Col leqe.
Hiss.
Belzonl,
Hiss.
State
College,
Hiss.
Belzonl t
HISS.
~
O.I.5IK3)
0.1.5 (35
percent K3)
0.70 (K3)
0.70 (tO
percent K3>
1.12 (T?)
same as above
same as above
sane as above
same as above
Naavl, et
(19691,
•MIC-5979
el
Naavl, et al
(1969),
SMTC-5979
Naavl, et
(1969),
4MIC-5979
al
Naavl, et al
(196P),
AHIC-5979
The effect of 5? pesticides on Davis, et al
embryonic development of clams and
oysters was reported. Synerglstlc (1969),AHIC-
effects with solvents Here also reported. 5990
Host of the compounds affected
develoement nore than survival. Some,
however, drastically reduced larval
growth. The authors point out the
-------
CoBOound
Organist
Field Field
Study Location
ToitlcHv,
Active
Ingredient,
Pom
fxoerlmental
Variables.
Control led
or Noted
Comments
Reference
Toxaphene
Toulon
Hercenarla
•ercenaria
(Iarvae)
Carclnus
•aenas
USA
less than 0.25
(T1Z)
163 (T?)
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.
same as above
a»(contin-
uous, aer-
ation, sea
water, and
dally
solution
renewal)
same as above
Davis, et
al <19fi9),
AMIC-5990
Portnann, et
al U971),
AMIC-7701
Toxlon
Cardlu* edule BSA
Toxlon
Crsngon
crangon
8S» —
6.6 ITZ)
a*(contin-
uous, aer-
ation, sea.
wator, and
dally
solution
renewal)
a«(contin-
uous, aer-
ation, sea-
water, and
dally
solution
renewal)
One hundred-forty surface active Portmann, et
agentsi solvent emulslflers, pesticides, al (1971),
polychlorlnated blohenyls. Pure AHIC-7701
Inorganic, and organic che»leals 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.
sane as above
Portmann, et
al (19711,
Anrc-77oi
Toxlon
Panda I us
•ontagul
BS» —
0.98 CTZJ
a«(contin-
uous, aer-
ation, soa-
water, and
daily .
solution
renowal)
same as above
Portmann. at
•I (1971).
AHIC-7701
-------
Trace orgsnlcs Rainbow trout BSA •>-
CCCE»
36 «TU
Trace organlcs Rainbow trout BSCH
(CCE)
Trace organlcs Rainbow trout BSCH
(CCE)
Trace organlcs Golden shiner BSA
(CCE)
Trace organlcs Blue-qreen BS»
ICCEI sunflsh
Trace organlcs (CCE Rainbow trout BS»
and CAE)
Trace organlcs (CCE Rainbow trout BSCH
and CAE)
Trace organlcs (CCE Rainbow trout BSCH
and CAE)
in (T 5-10)
1.0 (T more
than ig)
59 (Tl)
56 (Tl)
8(1-301 (Tl)
10 (T 20-30)
1.0 (T nor*
than 5<>>
The organic mlcrooollutants used
In the study were recovered from soring
and Hell Hater and Missouri River Hater.
Chronic effects were studied by
alternately placing the fish In the test
wolutlon for 5 days followed by a 5-day
period In a recovery solution. Results
of the tests are also given as total
accumulated survival tlmo. Studies were
also conducted to determine the
physiological effects of the nollutants,
and enuatlons Here developed for
accurately estimating the toxlcltv of
trace organlcs. CCE and CAE from soring
water were not generally toxic
Individually, but often showed strong
synerqlstlc behavior when combined at
naturally occurring levels. CCE fro*
river water proved to be »ost toxic ot
alt organlcs.
same as above
Smith, et al
(t970>,A*IC-
993
sane as above
same as above
sane as above
same as above
sane as above
sane as above
Smith, et
al(1970),
AMIC-993
SiHth, etal
(1970),
ftMIC-993
S«lth, et al
(1970),AMIC-
993
Smith, et al
(1970),AMIC-
993
Smith, et al
(1970),
AMIC-993
Snlth.et al
(1970),
AHIC-993
Smith, et al
(1970),
-------
-p-
cr\
Toxiclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Compound Organise Study Location Ppm or Noted Comments
Trace organlcs (CCE Blue-green BSA —
and CAF) sunflsh
Trace organlcs (CCE Red shiner BSA —
and CAE)
Trace organlcs (CCE Red shiner BSCH —
and CAF)
Trace organlcs (CCE Red shiner BSCH —
and CAF)
Trace organlcs (CCE Golden shiner BSA
and CAE)
Trace organlcs (CCE Mosaultoflsh BSA
and CAO
Tr«llan E.C. Rasbora 9CFA —
heteromorpha and
BSA
Treflan E.C. Rasbors BCFA —
heteronorpha and
BSA
137-166(T1)
195 (Tl)
21. (T 20-30)
5.6 (T
-------
species
Trlbutyl tin
chloride
Phormldlum
anblguum
| ^^
0.5-10.0
percent
groMlh
Inhibited
1100
Trlbutyl tin oxide
Sal mo
galrdner1
BCFA
and
BSS
0.027 CM)
Trlbutyl tin oxide
Sal no
galrdnerl
BCFA
and
BS*
0.070 CT2)
TrIcalne
••thanesulfonate
IfInguell
Salve IInus
fontlnal Is
100 CNTE)
a>,c,e,f,
hard (HH)
or
SOFT(SH)
synthetic
dl lutlon
Hater, or
seaHater
for some
species
a'.c.e,f,
hard (HH)
or soft
(SH>
synthetic
dilution
Hater, or
seanater
for some
species
Of 71, chemicals evaluated as Otto (1970),
alglcldes, only 9 Here more toxic than AMIC-892
CuSO
-------
Compound
Tr Icalne
•ethanesul fonate
Toxlclty,
Active
Field FI«ld Ingredient,
Organism Study Location Ppm
Salvellnus I — lOO(NTE)
font Inal Is
Experimental
Variables,
Control 1 ed
or Noted Comments
glucose and lactate content, and In a
number of electrolytes.
a* Study oT the effects of
anesthesia, handling, and experimental
oreoaration of brook trout resulted In
Reference
Houston, et
al (1971),
AMIC-38ZZ
I
uo
00
Tr lent orobenzene
Mercenar1 a
mercenarla
(egqs)
greater
thanlO.O (TZ)
alterations In hematoIoglcaI
characteristics, hyoerqIycemla, changes
In olasms, tissue, cellular Ion
concentrations, and eiu1 IIbrlum
conditions. Short-term (?-*j hr) effects
correlated Hlth clearances of the
anesthetic while persistent effects Mere
believed to be associated Hlth
generalized endocrine response to trauiia.
The effect of 52 pesticides on
embryonic develooment of clams and
oysters Has reported. Synerglstlc
effects with solvents Here also reported.
Most of the compounds affected
development more than survival. Some,
however, drastically reduced larval
gronth. The authors point out the
necessity of evaluating the effects ot
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.
Davis, et
(1969),
AMIC-5990
Tr lehIorobenzene
Tr Ichlorobenzene
Trlfluralln
Trlfluralln
Mercenarla
mercenarI a
(Iarvae)
Crassostrea
vlrglnlca
(eggs)
Asellus
brevlcaudus
Orconectes
rials
BS» —
BS» —
greater than
10.0 (Tie)
3.13 (TZ)
7.0 (TZ)
50.0 (TZ)
same as above
sane as above
Pavis. et
(1969),
AM.IC-5990
Davis, et
81(1969),
AMIC-5990
at
Of the aquatic Heed herbicides Sanders
evaluated, Dlclone Has the most toxic, (197n),
Daohnla was generally the most sensitive AMIC-VS*
organism. All of the Crustacea were
affected by much loner concentration
levels of herbicides than indicated by
the TL sub SO values. Alt of the animals
renresent important food chain links.
sax* as above
Sanders
(1970).
»HIC-».S3
-------
Trifluralln
Tr moral in
TrlfIoral In
Trlfluralln
Oaohnla magna BSA —
Cyorldoosls BSA
vltlua
Leponls BSA
"acrochlrus
Gamnarus
fasclatus
BSA —
0.56 IT2)
0.29 (TZ)
0.019 ITZI
1.8 ITZI
same as above
sane as above
sane as above
sane as above
Sanders
•1970),
*M.IC-,
SMIC-U53
Sanders
(1970),
»KIC-,c,e,f.
One hundred sixty-four
Alabaster
-------
Toxlclty, Experimental
Active Variables,
Field Field Ingredient! Controlled
CovDound Organise Study Location Pp. or Noted Comments Reference
hetero»orpha and hard (HH)
BSA or
SOFT(SH)
synthetic
dl lut Ion
Rater, or
seanater
for some
species
Uranlu* Alosa FL Great Lakes 0.0026
paeudo- - Superior, (residue)
hArangua Michigan*
pesticides, netting agents, and (1969),
miscellaneous Hater pollutants showed a AMIC-5I»25
Hide range of toxlclty spanning 12 orders
of maqnltude. 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 opposite Has true.
Testing the actual material as sold Mas
found to be essential.
from Lakes Suoerlor, Michigan, and Erie (1970),
nas determined by activation analysis. AMIC-3778
and Erie
Uranlu*
Urenlu"
Uranium
Uranlu'
Percopsls FL
omlsconaycus
Roccus
chrysops
FL
Perca FL
flavescens
Stlzostedlon FL
wltreu*
vltreun
Great Lakes 0.0008(resldue) --
- Superior,
Mlchlgan,
and Erie
Great Lakes 0.002(residue)
- Superior,
Mlchlgan,and
Erie
Great Lakes 0.0009(residue) —
- Superior,
Michigan,
and Erie
Whole body and 'liver residues Here
determined. Concentrations varied with
species and lake. Other elements found
were! antimony - 5 to 100 ppb, barlun -
0.? opm, cesluir - 3 ppb, lanthanum - 1 to
70 ppb, mercury - 10 PPb, rhenium - 0.5
to 5 ppb, rubidium - 0.06 to 6 ppn,
scandium - 2 ppb, selenium - 0.1 to 2
ppb, silver - 0.001 ppb.
same as above
Great Lakes
- Superior,
Michigan,
and Erie
0.001
(residue)
same as above
same as above
same as above
Lucas, et al
(1970),
»MIC-377»
Lucas, et at
(1970),
AMIC-3778
Lucas, et al
(1970),
4MIC-3778
Lucas, et al
(1970),
AMIC-3778
-------
fc
Uranlua
UranluB
Uranlua
Uranlua
Uranlua
Uranlua
Uranlua
Uranium
UranluB
Corcqonus FL
ertedll
Coregonus FL
clupeafomls
Corcqonus FL
hoy I
Prosoplua FL
cyllndraceua
Salvellnus FL
namaveush
Osmerus FL
Bordax
CarassIus FL
auratus
Notrools FL
ngdsonlus
Corcqonus FL
eluoeaforals
Great Lakes
- Suoerlor,
Michigan,
and Erie
Great Lakas
- Superior,
Michigan,
and Erie
Great lakes
- Suoerlor,
Michigan,
and Erie
Great Lakes
- Suoerlor,
Michigan.
and Erie
Great LaHes
- ^uoerlor,
Mlchlqin,
and Erie
Great Lakes
- Suoerlor,
Michigan,and
Erie
Great Lakes
- Suoerlor,
Michigan,
and Erie
Great Lakes
- Suoerlor,
Michigan.
and Eric
Moose Lake,
Can.
O.OOZCrcslduet
0.0006(resldue) —
O.OD39(raslduc) —
O.OOtaireslduet
O.OOZIrcsldue) —
0.002Crcslduc) —
O.OOOS(rcsIdue) —
0.0058(resldue) —
Ircsldue)
Uranlua
Coregonus FL
cluoeaforBls
Lake
Ontario,
Can*
(rcslduel
sane as abova
SBBC as abova
saaa as abova
sane as abova
sane as abova
same as above
sane as above
same as above
Concentrations of 13 toxic
elements In dressed tlsh from heavily
Industrialized and non-IndustrialIzed
areas Here determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements were
essentially the same In fish from both
areas.
saac as above
Lucas, et al
(19701,
*MIC-37T»
Lucas, et al
(19701,
•MIC-S77H
et al
Lucas,
(1970),
AMIC-3778
Lucas, et at
(19701,
»NIC-3778
Lucas, et al
(19701,
AMIC-3778
Lucas, »t al
(1970),
•MIC-3778
Lucas, et al
(1970),
4MIC-3778
Lucas, at al
(1970),
AMIC-3778
Uthe, et
AL(1971),
AMIC-3819
Uthe, et
«L(1971),
AMIC-3819
-------
>
£
ro
Conpound
Uranlu*
Urcnlun
Uranlu*
Uraniu"
Ur •» 1
-------
Vanadium
Paralabrax
clathratus
FH
I
U)
Vanadium
Vanadium
Vanadiun
Vanadium
Paralabrax
clathratus
Paralabrax
clathratus
Paralabrax
elathpatus
Paralabrax
clathratus
FH
FH
FM
Scattergood 3.3 (dorsal
Steam Plant, muscle
Los Angeles, residue)
Cat.
Catallna 1.9 (dorsal
Island, Cal. muscle
residue)
Scattergood t.Z (ventral
Steam Plant, muscle
Los Angeles, residue)
Cat.
Catallna 1.7 (ventral
Island, Cal. muscle
residue)
Scattergood 5.7 (gonads
Steam Plant, residue)
Los Angeles,
Cat.
Fish collected from an effluent
ploe of a steam plant and from offshore
Haters of Catallna Island were analyzed
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* copper, 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, cadmium, and nickel.
Silver, barium, lithium, and lead shotted
the least differences. The author
concluded that trace element analysis of
tissues could be used to determine the
effect of pollutants on marine organises.
same as above
sane as above
same as above
same as above
Staoleton
(1968),
AHIC-5980
Stapl eton
AHIC-5980
Staoleton
(1968) ,
AMIC-5980
Staoleton
(19*8),
AMIC-S980
Stapl eton
(19681,
AHIC-S980
Vanadium
Vanadium
Paralahrax
cl athratus
Paralabr*x
clathratus
(gravid
females)
FH Cstatlna <..? (gonads
Island, Cal. residue)
FH Catallna 3.
-------
I
Compound
Vanadium
Vanadium
Vanadium
Vanadium
Vanadium
Vanadium:
Vapam
Vetslcol »R 50G
1(7.2 percent plus 9
percent Emeol M-l*6t
Organism
Par at abrax
el athraf us
paral abrax
c 1 a thru tus
Paral abrax
clathrafus
Paral ahrax
el athratus
Para 1 abrax
el athratus
Paral abrax
cl athratus
Rasbora
heteromorphs
Pasbora
hetero»orph«
Toxlclty, Experimental
Active Variables,
Field Field Ingredient, Controlled
Study Location Pom or Noted Comments
FM
FM
FM
FN
FH
FH
8CF*
and
BS«
BCF«
and
8S»
Scatterqood ?.9 tlntegu»«nt ~
Stpan Plant, residue)
Los 'nielest
Cit .
Catallna 3.9 (lnt«qu»«nt —
Islandi Cal. residue)
Scatterqood 3.2 (heart
Stean Plant, residue)
Los «nqeles«
Cal.
Catal Ina 3.2 (heart
Island. Cal. residue)
Scsttergood 9 (eyeball
Steam Plant, residue)
Los Angeles,
Cal.
Catallna 7.6 (eyeball
Island, Cal. residue)
— 0.13 (T?) a'.c.e.f.
hard(HH)
or soft
(SW)
synthetic
dl lutlon
water, or
seaxater
for SOB*
species
— 7.2 CTZ) a>,c,e.f.
hard
(HH)or
sane as abov*
same as abova
same as abova
same as above
same as above
same as above
One hundred sixty-four
pesticides, Mettlnq agents, and
miscellaneous water pollutants showed a
wMe range of toxlclty spanning 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 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 •
Reference
AMIC-5980
S f a p 1 * t on
( ISAM ,
AHIC-5980
S taol eton
(196R) .
AMIC-'!9«0
S tool eton
tlSf,n> ,
AMIC-SgiO
S t a o 1 e t on
(19SB) ,
AMIC-5980
Staol eton
(196M ,
AHIC-S9SD
S t apt eton
(19S8I ,
AMIC-5980
Alabaster
(1969).
AMIC-5
-------
? percentEmcol
H-500X, 1.2percent
Eplchlorhydrlnl
Velslcol AR 50G (89
percent plus 9
percent Encot H-lii6,
2 percent Emcol
H-500X)
Rasbora
heteronorpha
BCFA
and
BSA
9.2 (T2>
vn
Venzar
Rasbora BCFA
heteromorpha and
BSA
50 IT?)
Vergenaster (lallne Salno
verglclde Heedklller galrdnerl
B)
BCFA
and
BSA
2.2 fT2)
sort
synthetic.
dilution
xater, or
seawater
forsome
species
a»,c.e,f,
hard (HH>
or soft
(SH)
synthetic.
dilution
water, or
seawater
for some
soecles
a>,c,e,f,
hard
(HWIor
soft (SH)
synthetic
dilution
Hater, or
seawater
for some
species
a*,c,e,f,
hard (HH)
or soft
(SH»
synthetic
dilution
nater, or
seaHater
for some
species
Vernolate
Ganmarus
fasclatus
BSA
20.0 (TZ), 13.0 a*
wide range 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 were most toxic In hard Hater
and sometimes the opposite Has true.
Testing the actual material as sold Has
found to be essential.
sane as above
Alabaster
(1969)..
AMIC-5V25
One hundred sixty-four
pesticides, wetting agents, and
miscellaneous water pollutants showed a
Hide range of toxlclty scanning 12 orders
of magnitude. Knowing the toxlclty and
percentage of alI components of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of materials. Some-times
pesticides Here most toxic In hard water
and sometimes the opposite Has true.
Testing the actual material as sold was
found to be essential.
sane as above
Alabaster
(1969),
AMIC-5fc25
Alabaster
(1969),
ANIC-SV2S
Of the aouatlc Heed herbicides Sanders
evaluated, Olclone Has the most toxic, (1970),AMIC-
Daohnla Has generally the irost sensitive
-------
Compound
Vernol ate
Vernol ate
Vernol ate
Vernol ate
Verno late
Vernol ate
Vinyl acetate
Field Field
Organism Study Location
Paleomontes BSA
kadlahensls
Asellus BSA —
brevlcaudus
Orconectes BSA —
nals
Daphnla nagna BSA
Cynrldoosis BSA —
vl dua
Leoomls BSA
•acrochlrus
Asterlas BSA —
rubens
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
1.9 (TZ) a'
5.6 a»
Zfc.O CTZ) »•
1.1 (TZ) 8«
07LIT91 •*
• Ct \ t £ I •
9.Z (TZ) 8»
330-1000 (TZ) a»(contln-
uous aer-
levels of herbicides than Indicated by
the TL sub SO values. All of the animals
represent Important food chain links.
same as above
same as above
same as above
same as above
same as above
One hundred-forty surface active
aqents, solvent emulslflers, pesticides.
ation, sea- Do 1 ych 1 orl na t ed blphenyls, pure
Vinyl acetate
Crangon BSA --
crangon
water, and
daily
solution
renewal )
10-100
-------
Vinyl acetate
Platlcthys
Ilesus
BSA
greater than
100 (T2)
a»(contin-
uous aer-
ation, sea-
water, and
daily
solution
renewal)
sane as above
Portaann, et
al 11971),
AMIC-7701
Heedazol T-L
Crangon
crangon
BSA —
1000-3000 (T?)
a«(contin-
uous aer-
ation, sea*
water, and
dally
solution
renewal)
sent* as above
Portmann, »t
al (1971),
AMIC-7701
Heedazol
Rasbora BCFA
heteromorpha and
BSA
CTZ)
HL
Rasbora 8CFA
heteromorpha and
BSA
0.50 (T7J
a*,e,e, 1,
hard
(HH)or
soft (SM(
synthetic
dilution
Hater, or
seanater
Tor some
species
a*,c,e,f,
hard
(HH)or
SOft (SW)
synthetic
dilution
Hater, or
seaNater
for some
species
One hundred sixty-four
pestlcldes» netting agents, and
miscellaneous nater pollutants shoned a
Hide range of toxlclty scanning 1? orders
of magnitude. Knowing the toxlclty and
percentage of all coiioonents of a
formulation did not result In easy
predictability of the toxlclty of a
mixture of materials. Sonet lutes
pesticides Here most toxic In hard Mater
and sometimes the opposite Has true.
Testing the actual material as sold was
found to be essential.
same as above
Alabaster
(1969),
AHIC-5M5
Alabaster
(1969),
AMIO5«i?S
Yell OH phosphorus
Ye 11 OH phosphorus
re 11 OH phosphorus
Cluoea
harengus
(10-15 cm)
Sal mo salar
(7-13 em)
Homarus
amerlcanus
BCFA —
0.016 (T 12
HR)
BCFA —
BCFA —
0.018
(Indolent
lethal level)
0.01,0 (T10)
a*,c,f The lethal effect of ye 11 OH
phosphorus Has apoarently Irreversible
and Possibly cumulative. This form of
phosphorus nas surprisingly stable In
bottom muds Hhere oxygen content Has low.
The most probable cause of death Has
asphyxiation brought on by massive
hemolysls.
a*,c,f same as above
a*,c,f same as above
Zltko, et al
(1970),
AHIC-3817
ZlfKo, et al
(197Q),
AMIC-3817
Zltko, et
al(1970),
AMIC-T817
-------
Compound
Yellow phosphorus
Yellow phosphorus
Field Field
Organls* Study Location
Gamffiarus BCF* —
ocean Icus
Salvellnus BCF* —
1 ont lo»l Is
Toxlclty,
Active
Ingredient,
Pom
3-1, (Kl)
0.0005 (T ZOO
hr)
Experimental
Variables,
Control 1 ed
or Noted
a'.Ctf same
a The
50 (tlire to
aporox Ima te
Comments
as above
data Mere presented at I_T sub
50 percent lethality). The
TL sub m data cited were
Reference
ZltKo, et al
(1970), AHIC-
3817
Fletcher, et
al (1970).
AMIC-839
Tel I on Dhosohorus
Veil OH phosphorus
Tall OH phosphorus
Ye 11 ON phosphorus
Young's Dally
Zectran
SalvelInus
1ontInalIs
Osmerus
mordax
Osmerus
mordax
Clupea
harengus
BCF* —
BCF* —
BCFA —
BCF* —
Rasbora BCFA
heteromorpha and
BS*
Ictalurus
ounctatus
BS*
1.2 IT 2.J hr)
0.0005 (T 190
hrl
1.0 (T It hr)
0.1 (T 3.6 hr)
2.3 (T2)
Interpolated from plotted TL sub 50
values. Pedness, hemolysls, and reduced
he»atocrlts correlated directly nlth
toxlclty to brooK trout. No redness or
hewolysls occurred In smelt although
reduced hematocrlts occurred. Herring
also turned red xlth hemolysls and
redness around head and fins* In tin*
phosphorus Has toxic at concentrations as
Ion as 0.5 mlcron/l.
sane as above
same as above
sane as above
same as above
Fletcher, et
al (1970),
AHIC-B39
Fletcher, et
al (1970),
AMIC-839
Fletcher, et
al (1970),
AMIC-839
Fletcher, et
al (1970).
AMIC-839
a*,c,e,f,
hard
(HM)or
soft (SH)
synthetic
dilution
water, or
seanater
for soce
species
11.tO
-------
Zectran
Zectran
Zectran
Zeetran
Zactran
Zeetrarr
Ztctran
Zectran
Zeetran
Zcctran
Zectran
Zinc cMorld* (as
llnc>
Ictalurus
••las
Carasslus
auratus
Cyprlnus
carplo
Plmephales
proifetas
Leponls
naerochirus
Leoomls
nlerotophus
Micropterus
sal mo Ides
Salmo
galrdner1
BSA
BSA —
BSA
BSA
BSA
BSA —
BSA
BSA
Sal no trutta BSA
Oncorhynchus BSA
Klsutch
Perca
flavescens
BSA —
Brachydanlo BSA
rerlo
16.70 (Td)
19.11. (Td)
13."to (Td)
17.00 (Td)
11.20 (Td)
16.70 (Td)
d.70 (Tdl
10.20 (TI.I
a.10 (It)
1.73 (Td)
Z.dS (Td)
3.7-6.7 (SBd)
species most susceptible to
organochIoplnes» coho salmon the most
susci>Dtlt> le to carbamntest and goldfish
Here t^e least susceotlble of all
species. Safe concentrations established
by bloassays with salmonlds or
ceitrarchlds would IlKely be safe for
cyprlnlds and Ictalurlds. Safe levels
for Ictalurlds or cyorlnlds would
probably be hazardous for centrarchids
and salnpnlds. The use of goldfish In
bloassays Has discouraged.
sane as above
synthetic
test water
a.
synthetic
test Hater
at
synthetic
test Hater
a.
synthetic
test Hater
a.
synthetic
test Hater
8t
synthetic
test nater
a.
synthetic
test Hater
synthetic
test Hater
af
synthetic
test Hater
at
synthetic
test nater
a,
synthetic
test Hater
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
same as above
HaceK. et
al(1970),
AMIC-5510
Hacek, eta)
(19701,
AMIC-5510
Hacekt et
al(1970),
AMIC-5510
Hacek.et al
(1970),
AMIC-5510
ttacek, etal
(1970)t
AMIC-5510
MaceK, etat
(1970),
AMIC-5510
MaceK, etal
(1970),
AMIC-5510
Macek, et
al(1970),
AMIC-5510
Macek, et
81(1970),
AMIC-5510
Macek, etal
(1970) ,
AMIC-5510
Macek, et
al (1970),
AMIC-5510
a,e, and Feeding behavior Has affected by Cairns, et
synthetic zinc, chromlu*, and ARS In that more tine al
dilution Has reoulred for consuming measured (1967),AHIC-
H8t«r amounts of food. Feeding response Has 5707
-------
Coaoound
Field Field
Organism Study Location
Toxlcl ty.
Active
Ingredient,
PP«
Experimental
Variables,
Con t ro 1 led
or Noted Comments
Reference
line chloride las Leoomlj BS»,
Zn) nacrochlrus I
3.3 (U)
VJ1
O
Zinc chloride las Nltzschla 8SA,
Zn) llnearls L
Zinc chloride (as Physa BSA,
Znl heterostrooha L
1..3 (T5)
0.98 (Ti>)
also attected by aeration, feeding
schedule, llqht intensity, and outside
disturbances* The authors note that nuch
more worh Is needed to establish the
reliability of this procedure.
ae,e, and This study was conducted to
synthetic determine the relative toxlcltles ol 20
dilution common constituents of Industrial Hastes
water to a fish, an alga, and an Invertebrate.
The experiments Here conducted over a
10-year period for varied purposes. The
authors recommend bloassays with at least
three components of the food web.
a«,e, and
synthetic
dilution
water
a*,e, and
synthetic
dilution
Water
same as above
same as above
Patrick, «t
al (19SS),
AMIC-57?0
Patrick, «t
al (1968),
AMTC-5TZO
PatrlcK, at
at (1969) ,
Zinc chloride
Leblstes 8CF
reticulatus
(1 no, 1.1
cm)
0.56 (Tit)
Zinc chloride
Leblstes BCF
retlculatus
(1 »o. 1.1
ci)
1.0 (T 1.51
a,e,d,e,f, Toxlclty thresholds and a
n,q, phos- dilution mixture threshold were
phates, calculated from fish bloassay data for
carbon- zinc chloride and potassium cyanide.
ates* bi- Threshold concentrations for 7lnc and
carbon- cyanide were found to be 0.33 and 0.?36
atesf aul- ma/I, respectively. A procedure for
fates, and determining toxlclty threshold
conduc- concentrations for mixtures of chemicals
tance "3^ also presented. A zinc-cyanide
dilution ratio for toxlclty threshold
(THD1?) Has found to be a linear function
of the concentration of the tno Ions
taken separately, and therefore} THDR
eauals 1.26-0.06CN-1. '2Zn. Based on a
mu I 1 1 component eauatlon, mixtures of zinc
»nd cyanide exhibit an antagonistic
effect. This appears to be a significant
advance In an approach to estimating safa
concentrations for Hater pollutants.
same as above
a,c,d,e,f,
n,q, phos-
phates,
carbon-
ates, bl-
Chen,et al
(1969).
AMIC-3831
Chen, et al
(1969),
AMIC-3831
-------
carbon-
ates, sul-
ratea, and
conduc-
tance
Zinc
dimethyldithlo-
oarbamato
Phornldlun
amblguua
0.5-10.0 (NTE) —
Zinc hydroxyqulnone
Rasbora
heteronorpha
BCFA
and
BS»
0.10 (T2I
Zinc sodiua citrate
las Zn)
Matersloora
cuculI ata
(larvae)
33 (T
hr)
Of 7>t chemicals evaluated as Otto (1970),
alqlcides, only 9 Here more toxic than AMIC-59Z
CuSO<». None Inhibited qronth of
mat-tormlng algae ror more than 2 weeks.
CuSOit formulated Mlth certain netting
agents Has more toxic than CuSO<* alone.
Coooer chloramlne Has also found to be
more toxic than CuSO<«. No wetting agents
Here round to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 DD"i). Also reported are factors
affecting gronth of algae In canals to
determine Hhether there Here leads to
controlling alcae by environmental
management. No practical env Ironnent al
means Here found.
One hundred sixty-four Alabaster
pesticides, netting agents, and (1969), ANIC-
miscellaneous nater pollutants shoned a
Hide range of toxlclty spanning 12 orders
of magnitude. Knonlng the toxlclty and
percentage or 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 Mater
and sometimes the opooslte Has true.
Testing the actual material as sold Has
round to be essential.
a,c,I, and This study Has conducted to Wisely, et
salinity determine species of marine larvae al (1967),
suitable for use in test screening AMIC-5708
antlfoutlng chemicals. A. sallna (brine
shrlno) appeared to have the best
potential for this purpose. A. sallna
larvae sensitivity Has greatest starting
at age 20-80 hr, and tolerated relatively
IOM pH (5.0).
8*,C«e,f|
hard
(HH)or
soft (SHI
synthetic
dilution
Mater, or
seanater
Tor sons
species
Zinc sodiu« citrate
(as Znl
Splrorbl-!
lane)losa
(larvae)
t.9 (T Z hr)
a,c.l, and
salinity
same as above
Wisely, et
al (1967),
AMIC-S708
-------
vn
CoBOOund
Zinc sodluB citrate
Us Zn)
Zinc sulfst*(as Zn)
Zinc sul fat* (as
Zn)
Zinc sul fat* I as
Znl
Zinc sul fat*
Field Field
Orqanls* Study Location
Buqula l —
nerltlna
(1 arvae)
Acroneurla BSA
Ephenerella BSA —
Hydropsyche BSA —
Lepouls BSCF —
Bacrochlrus
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Pp« or Noted Comments
5.1 IT 2 hrl a,e,l, and
salinity
32 (Tl<>) a*,c,d,e,f
16 (T10I a*,c,d,e,f
32 (Till a«,e,d,e,f
r»,t»
sane as above
Ephemerella (mayfly) Has the most
sensitive aquatic Insect of those
studied, and copper the most broadly
toxic metal. The authors suggest that
aquatic Insects may not be as sensitive
to heavy netals as fish.
same as above
same as above
Results of monitoring fish
br»*thlng freauency were primarily
Pef erence
Wisely, et
al (1967),
AHIC-570H
Warnlck, et
al (1969),
AMIC-3767
WarnlcK, et
al
3767
HarnlcK, et
al (1969),
AMIC-3767
Cairns, et
al (1971),
Zinc sulfat*
Zinc sulfat*
Sal no BCF
galrdnerl
0.0056
(avoidance)
,c,f
reoort»rt. The Indicated 7n concentration AMIC-3232
was the lowest detectable. Reoroduct1 on
and qroxth of blueallls were apparently
not affected by 0.025 and 0.075 mq/l. At
a concentration of 0.25 mq/l spanning Mas
inhibited and nenly-hatched fry Here
Killed. The authors suggest ways of
Improving this technique and suggest
simultaneous use nlth fish movement
change (See Cairns and Waller, 1971).
The threshold avoidance limit Has Sprague
essentially the same at 9.5 and 17.0 C. (196R),
The value noted Is 0.01 of the lethal AHIC-3760
threshold concentration, according to th*
author. Improvements In the test
procedure are described.
Sal no
galrdnerl
BCF —
0.56 (threshold a«,c,f
toxlclty)
same as above
Sprague
(1966),
AMIC-3760
Zinc sulfate
Plieohales BCFCH —
0.18 (SBI
a,c,d,e,f,
Hatchlna Has unaffected at the
Brungs
-------
proaalas
10.3-0.* 9)
Zinc sulfate
Xlphoohorus
maculatus m
m)
BS*
12.0 (T*»
I,n,q, Cat Indicated concentration of zlncf but egg (1969)t
N9t Na( Kt croquet I on Has significantly reduced. AM.IC-5<|58
and SO* GroHth Inhibition occurred at 3.8 ppi*.
Egg oroductlon was the most sensitive
parameter studied. The author notes that
an application factor of 0.009 Mould
exist If a ?0 percent reduction ot egg
production Is biologically Insignificant.
&.,*>, C,t, Fathead minnows were more Rachlln, et
m, Fe, Ha, susceptible to zinc than Inbred al 11968)t
Cu,' and Kg platytlsh. Hale olatyflsh were more ANIC-57??
succeotlble than female. The authors
suggest the Inbred Dlatyflsh as a
candidate for bloassay evaluations due to
Its known (31 generations) genetic
background.
CO
Zinc sulfate
Zinc sulfate
Plmephales BS»
promelas (V5
RatnbOK trout
(RT6-? gonad
cell Una)
7.6 (TO
18.0 (SB*)
a*,b,c,f,m
t Fe.Mn,
Cuf and Hg
sane as above
Rachlln, et
al (1968),
»HIC-5722
Rachlln, et
al (1968),
Zinc (plus ammonia
•nd phenol)
Sal mo
galrdnerl
BS»
0.5-2.5MT3)
Zinc (Plus copper,
nickelI
Sal mo
galrdnerl
BS»
Tissue culture study using the
Eagles MEM medium resulted In 70 percent
re-luctlon In mltotlc Index and cytotoxlc
changes In cell morphology.
Concentrations at 0 to 10.0 ppm zinc had
no significant effect. The trout cells
M»re less sensitive than cultured celts
of fathead minnow.
a,c*,d««*« Ralnbox trout were exposed to Brown, et al
f,m concentrations of fluctuating levels of (1969),
ammonia, phenol, and zinc and to constant lMIC-5993
mixtures of the three. Tests tilth
fluctuating levels of toxicants showed
that LC50 values Here similar to those
for constant concentrations as Ionq as
the periodicity of the fluctuation did
not exceed the resistance time for the
poison. Except when zinc predominated In
the mixtures, the fractional toxlcltles
could be summed to give the toxiclty of
the mixture.
0.9-1.6 (T2) a,c,e Rainbow trout Here exposed to Brown,et at
cooper, phenol, zinc, or nickel solutions (1970),
to determine
-------
Compound
"Organlsn
Field Field
Study Location
Toxlclty,
Active
Ingredlenti
Pp»
Experimental
Variables,
i Control t ed
or Noted
Comments
Ret erenco
Tine (plus copper, Saloo
phenol I galrdnerl
Zinc
>
-p-
Zinc
Zinc
Zinc
Zinc
Zinc
Coregonus
artedll
BSA
FL
Coregonus FL
clupeafor«ls
Coregonus Ft
hoyl
Prosoplum FL
cyl Indraceu*
Salvellnus FL
nanaycush
Car ass 1 us FL
auratus
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Mlchlqan,
and Erie
Great Lakes
- Superior,
Mlchlqan,
and Erie
Great Lakes
- Superior,
Michigan,
and Erie
Great Lakes
- Superior,
Michigan,
and Frle
Great Lakes
- Superior,
Michigan,
and Erlt
0.6-3.1,0 (T?)
38(resldue>
?3tresldue)
••".(residue)
ll(resldue)
<.8(resldue)
36lresldue)
be adeauately described by summations of
the fractional toxlcltles.
same as above
Brown,ef al
AMIC-S99",
Trace element content of fish
from Lakes Suoerlor, Michigan, and Erie
Mas determined by activation analysis*
Whole body snd liver residues were
determined. Concentrations varied Hith
species and lake. Other elements found
Nere! antimony - 5 to 100 ppb, barium -
0.? ppm, cesium - 3 PDb, lanthanum - 1 to
?0 ppb, mercury - 10 opb, rhenium - 0.5
to *> pcb, rubidium - O.Ofi to 6 ppn,
scandium - 2 ppb, selenium - 0.1 to Z
pob, silver - 0.001 ppb.
same as above
same as above
sane as above
sane as above
same as above
Lucas, et
(19701 .
AHIC-377*
al
Lucas, et al
(1970) ,
AMIC-3771!
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, et al
(1970),
AMIC-3778
Lucas, ct al
(1970),
HMIC-3778
Zinc
Roccus
FL Great Lakes ?8(resldue)
salt* as above
Lucas, et al
-------
Zinc
Chrysops
Coregonus FL
clupeaformls
VJl
Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Coregonus FL
clupeaformls
Esox luclus FL
Esox luelus FL
Esox luclus FL
Osmerus FL
morrtax
Perca FL
Tlaveseens
- Superior.
Michigan,
and Erie
Moos* Lake, Id (residue)
Can.
Lake
OntarlOt
Can.
Moose Lake.
Can.
Lake St.
Pierre. Can.
Lake
Can.
Lake Erie,
Can.
Lake Erie,
Can.
12 (residue)
19 (residue)
19 (residue)
11 (residue)
20 (residue)
12 (residue)
Concentrations of 13 toxic
elements In dressed fish from heavily
Industrialized and non-IndustrialIred
areas Here determined. Only mercury
exceeded regulatory limits, and
concentrations of most elements Mere
essentially the sane In fish from both
areas.
sane as above
sane as above
same as above
sane as above
same as above
same as above
(1970).
AMIC-3778
Uthe, et
AL(1971),
AHIC-3819
Uthe. et
AL(1971),
AMIC-3819
Uthe, et al
(1971), AMIC-
Uthe, et al
(19711, AMIC-
3819
Uthe, et al
(1971), AMIC-
3819
Uthe, et al
(1971), AMIC-
3819
Uthe, et al
(1971), AMIC-
3819
Zinc
Paratabrax FH
clathratus
Scattergood
Steam Plant,
Los Angeles,
Cal.
26 (dorsal
muscle
residue)
Fish collected from an effluent
ploe of a steam plant and from offshore
Haters of Catallna Island Here analyzed
for trace element content. Trace element
content of the effluent Hater Has at
least 5 times greater than that of normal
sea nater for cadmium, copper* nickel.
zinc, and chromium. Livers of fish fron
the effluent Here nearly twice the size
of those from the ocean. Greatest
differences In concentration occurred
Hith aluminum, cadmium, and nickel.
Silver, barium, lithium, and lead shotted
the least differences. The author
concluded that trace-element analysis of
Stapleton
(1968),
AHIC-5980
-------
Co»oound
Zinc
Zinc
Zinc
1
VJ1 Zinc
ON
Zinc
Zinc
Zinc
Zinc
Zinc
Zinc
Organism
Paral abrax
cl athratus
Paral abrax
cl athratus
Paral abrax
cl athratus
Parat abrax
cl athratus
Paral abrax
clathratus
Paral abrix
cl athratus
(gravid
females)
Paral abrax
cl athratus
Paral abrax
cl athretus
Paral abrax
cl athratus
Paral abrax
clathratus
Field
Study
FM
FH
FH
FH
FH
FM
FH
FH
FH
FH
Field
Locat Ion
Catat Ina
Island, Cal.
Scattergood
S team P 1 ant ,
Los Angeles,
Cal.
Catal Ina
Island, Cal .
Scat t ergood
Steam P 1 ant ,
Los Angeles,
Cal.
Catal Ina
Island, Cal .
Catal Ina
Island, Cal.
Scattergood
Steam Plant,
Los Angeles,
Cal.
Catal Ina
Island, Cal.
Scatf ergood
Steam Plant,
Los Angeles,
Cal.
Catal tna
Island, Cal.
Toxlcl ty.
Active
Ingredient,
Pom
10 (dorsal
muse 1 e
residue)
15 (ventral
muse) e
residue)
9 (ventral
muscle
residue)
17? (gonads
residue)
119 (gonads
residue)
(gonads
residue)
61 (liver
residue)
100 (liver
residue)
2?3 (Integument
residue)
19D (Integument
residue)
£ xoer 1 menta 1
Variables,
Control 1 ed
or Noted Comments
tissues could be used to deternlne the
effect of oollutants on marine organisms.
-- 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
S t a D 1 e t on
(1968) ,
AMIC-5980
S t a D 1 e t on
11968) ,
AMIC-59BO
Staol eton
(1968) ,
AMIC-5980
S t 3D 1 eton
(1968),
AMIC-5980
Staoleton
(1968) ,
AMIC-5980
Staol eton
(1968),
AMIC-5980
Staoleton
(1968) ,
AMIC-59SO
Staoleton
(1968) ,
AMIC-5980
Staoleton
(1968).
AMIC-S980
Staoleton
(1960),
-------
AMIC-59BO
Zinc
Zinc
Psralabrax FN
elathratus
Paralabrax FH
cl athratus
Scattergood 6? (heart
Steam Plantt residue)
Los Angeles,
Cat.
CatalIna 90 (heart
Island, Cat. residue)
sane as above
same as above
Stapleton
(1968),
AMIC-5980
Staoleton
(1968),
ANIC-5980
Zinc
Zinc
Zinc
VJl
Zinc
Zinc
Paralabrax FH
clathratus
Paralabrax
clathratus
Sal no
galrdnerl
FH
BS»
Sal no
galrdnerl
Sal no
galrdnerl
Seatterqood 700 (eyeball
Steam Plant, residue)
Los Angeles,
Cal.
CatalIna 600 (eyeball
Island, Cal. residue)
1.95-5.85
(fluctuating
cone, T
23<»0-2960 Kin)
same as above
same as above
BS» —
BSA —
ZnSO* . 7H20 (as Zn Lepomls BSA
? Dlus) macrochlrus and
CF
Staoleton
(19S8),
AMIC-5980
Staoleton
(1968),
AMIC-5980
a»c*»d,e'« RalnboH trout Here exposed to Brown, et at
(,• concentrations of fluctuating levels of (1969),
ammonia, phenol, and zinc and to constant AtlIC-5993
mixtures of the three. Tests nlth
fluctuating levels of toxicants shotted
that LC50 values Here similar to those
for constant concentrations as long as
the periodicity of the fluctuation did
not exceed the resistance time for the
poison. Except when zinc predominated In
the mixtures, the fractional toxleltles
could be summed to give the toxlclty of
the mixture.
3.9 (T 2400
mln)
4.0 (T2>
8,C«
a,c,e
same as above
Broxn, et
al(1969),
AHIC-5993
?.9
-------
Compound
Field Field
Organise Study Location
Toxlclty,
Active
Ingredient,
Pp«
Experiments!
Variables,
Control led
or Noted
Comments
Reference
ZnSOIt . 7H20 las 2n Notemlgonus
2 plus) crysoleucas
>
-p-
CD
ZnSOfc . 7H20 (as Zn
7 plus)
Zn, Nl.
and Zn
Cr, CN, Cu.
Carasslus
auratus
Catostonus
commersonl
Zn, Nl, Cr, CN, Cu,
and Zn
Plmephales
or one I as
BSA —
BS«
7.5 (SB)
7.5 (K)
BSACF Grand River betxeen
(ML) at 1.35-3.75
Wyoming,Hlch percent (T3)
Igan
BSACF Grand River between
(ML) at 1.25-3.75
Wyoming,Mich percent (T3)
Igan
a,c,d,e,f,
r,t
a,c,d,e,f,
r.t
a,c,e, con-
ductivity,
Nl.Cu.Cr,
CH, and Zn
a,c,e, con.
ductlvity,
Hi.Cu.Cr,
CH, and Zn
lowest detectable concentration causing
significant movement changes. Values (or
golden shiners and goldfish Here obtained
In preliminary studies. At 1/10 the
Indicated concentration, growth and
reoroductlon of bluegllls Here
significantly affected but not at 1/100
dilution. Considerable discussion and
additional data are presented.
sane as above
sane as above
A mobile bloassay unit Has
utilized to conduct this study of
municipal nastewater containing the
Indicated toxicants. River Mater was
used as diluent. The conclusion Has
reached that synerglstlc or additive
toxic effects occurred since toxlclty was
greater than that of any of the Ions
singly.
same as above
Cairns, et
al (19711,
AHIC-^231
Cairns,et al
(19711 ,
AMIC-3Z31
Zlllich
(1969),
AMIC-»906
Zllllch
(1969),
AMIC-2906
l,l--»ethyl»nedl-2- Ptychochellus BSA —
naphthol oregonensls
(71 ••)
0.006-0.015 (K
6-31 hr)
a,c,d,f,
and
conduc-
tivity
The chenlcal studied Has found to HacPhee, et
be selectively lethal to souanflsh at
concentrations 3 to 100 times more toxic
to these species than to salmon Ids.
Potency varied positively Hlth
concentration and temperature.
Concentrations cited are for 10-18 C. A
sheeo and ducKs showed no III effects
over a 7-day period when forced to drink
Hater containing 10 DDK of the naphthol.
A field application In a snail lagoon
containing several species of fish
resulted only In kill of P. oregonensls.
This chenlcal appears to be an effective
oisclclde that Is selective for
souawfIsh.
al
(1969),AMIC-
51.50
-------
-p-
VJ1
t,l"-t»eth.ylenedI-2-
naphthol
1,c,d,«,
and
conduc-
tivity
a*( contin-
uous aer-
ation, sea-
wator, and
daily
solution
renewal)
sane as above
San* as above
sane as above
same as above
same as above
0.5-10.0 (NTEI —
HacPhee, et
al (1969) t
AMIC-5i(50
HaePhee, et
al (1969),
et
al (1969) •
ANIC-5I.SO
HacPheet et
al
( 19691, »HtC-
HacPhee, et
al (1969).
AMIC-5i»50
One hundred-forty surface active
aqents, solvent enulsl Hers, pesticides,
polychlorlnated blphenyls, oure
Inorganic, and organic chemicals Here
evaluated against as many as ten ivarlne
organisms. The authors noted that nost
published data o( this tyoe deal xlth
toxlclty of chemicals to freshwater
organisms.
Of 7i» chemicals evaluated as
alglcldes, only 9 were more toxic than
CuSOit. None Inhibited growth of
mat-forminq algae for more than 2 xeeKs.
CuS1<» formulatPd with certain wetting
agents was more toxic than CuSO<> alone.
Coooer chlorairlne was also found to be
more toxic than CuSO
-------
Compound
Z-aelno-S-chloro-l,*
Organism
Phormldlun
Field Field
Study Location
L
Toxlelty,
Active
Ingredient,
Poi
0.5-10.D(16oer
cent a mirth
Experimental
Variables,
Control led
or Noted
Of
alqlc 1 des.
Comments
7 alone.
Copper chloramlne was also found to be
more toxic than CuSO«t. No wetting agents
were found to be Inhibitory at the
concentrations Investigated (I).05 and
0.005 DDI") • 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 were found.
Of 7. None Inhibited growth of
mat-forming algae tor more than ? weeks.
CuSO. No wetting agents
•ere found to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 PDB). Also reported »re factors
Otto (1970).
AHIC-892
Otto (1970).
AMIC-89?
-------
Z-nercaptodlethyl
succInatv
Plmeohales
proneI as
BS» —
Z-prooenal
(acroteln)
Phormldlum
amblguum
I —
k
V-1
?-prooene-t-ol
(ally! alcohol)
2-tert-butylamIfio
V-ethyl-amlno
(-•ethyl S-trlazlne
Phormldlum
amblguum
Phormldlum
anb1guum
35.0
0.5-10.0 (66
percent growth
Inhibited 1UI
0.5-10.0 (16
percent
growth
Inhibited 114.)
0.5-10.0 (66
percent growth
Inhibited 1M
affecting growth of algae in canals to
determine whether there were leads to
controlling algae by environmental
management. No practical environmental
•cans were found.
a*td««»ot Halathlon and Its hydrolysis
andFe products were evaluated with the finding
that one such product (dlethyl fumarate)
was more toxic than Halathlon to fathead
minnows. Synerglsm occurred between
Halathlon and two products of hydrolysis.
Continuous exposure resulted In
Increased toxlclty.
-- Of 7. None Inhibited growth of
mat-fornlnq algae for more than ? weeks*
CuSO<> formulated with certain wetting
agents was more toxic than CuSO>> alone.
Coooer chloranlne 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 DO"). Also reported are factors
affectlnq growth of algae In canals to
determine whether there were leads to
controlling algae by environmental
management. No practical environmental
means were found.
-• same as above
Bender
(1969),
•HIC-3787
Otto (1970) t
ANIC-892
Otto (1170I,
AMIC-B92
01 7i> chemicals evaluated as
alqleldes* only 9 were more toxic than
CuSOit. None Inhibited growth of
mat-forming algae tor more than Z weeks.
CuSOii formulated with certain wetting
agents was more toxic than CuSO"» alone.
Coooer chloramlne 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 opm). Also reported are factors
affecting growth of algae In canals to
determine whether there Mere leads to
controlling algae by environmental
management. No araetlcal environmental
Otto (1970)>
AHIC-89Z
-------
Compound
?, 3-dlchloro-l,*-
nADhthooulnone
Organism
Phormldlum
amblquum
Field Field
Study Location
L
Toxlclty,
Active
Ingredient,
Ppn
0.5-10.0 (NTE)
Experimental
Variables,
Control led
or Noted
means Here
Of
at qlcldes.
Comment 5
found.
71. chemicals evaluated as
Reference
Otto ( 1 97 0 ) ,
AMIC-89?
>
Z,»-D (acid)
Gammarus
fasclatus
BSA ~
(T?)
?,*-D (acldl
*,*-D (acid)
?t%-0 (BEE)
Z.%-0 (BEE)
Z,«-0 (BEFt
Daphnla magna BS*
LeDomls BSA
•acrochlrui
Gam«aru$
fasclatus
BSA
Paleomontcs BSA
Kadlakensls
Asellus BSA
bravlcaudus
greater than
100.0 (TZt
5.9 (T?l. 5.9
(TV)
!.«. (T2)
3.2 (TZt
CuSO alone.
CoDD-r chlorairlne nas also found to be
more toxic than CuSOii. No wetting aqents
Here found to be Inhibitory at the
concentrations Investigated (0.05 and
0.0OS op"). 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.
Of the aquatic weed herbicides
evaluated. Die I one was the most toxic,
Oaohnla 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 50 values. All of the animals
represent Important food chain links.
sane as above
same as above
same as above
sane as above
same as abeva
Sanders
(1970),
AMIC-1.53
Sanders
119701,ANIC-
i>53
Sanders
(1970),
AH.IC-I.53
Sanders
(1970),A1IC-
«.53
Sanders
(19701,
AHIC-W53
Sanders
(1970),
-------
ANIC-453
Z,»-D (BEE)
Orconectes BSA
nals
greater than
100.0 IT?)
sa»e as above
Sanders
(ig70l,AMIC-
t,k-D (BEE)
Oaphnla magna BSA —
9.6 (TZI
sa«e as above
Sanders
-0 (clay based) Rasbora BCFA
heteromorpha and
BSA
IT1)
a'.e.e.ft
hard (HH)
or soft
(SM>
synthetic
dilution
•ater, or
seaxater
Tor sone
soecles
a*.cteif t
hard(HH)
or soft
synthetic
dilution
•ater, or
seaNater
tor son*
species
2,%-D Idlaethylanlne Crassostraa I
salt) vlrglnlca
(eggs)
ITZ)
sax* as above
sane as above
One hundred sixty-lour
p*«tlcl
-------
Compound
Field Field
Organism Study Location
Toxlcltvt
Active
Ingredient,
Poe
Exoerlmental
Variables,
Control led
or Noted
Comments
Reference
7,*-D (dlmethy lamlne Crassostrea L
salt! vlrglnlca
(larvae)
?.*-0 (dlmethylamlne Gammarus
saltl faselatus
>
k
BSA —
2
-------
5990
2,%-D (ester)
Z,*-0 INa salt)
fc
v/i
(PG9E)
*-0 IPGBE)
Zt*-0 (PGBE)
Zi*-0 fPGBE)
IPGBE)
Z,*-D IPGBEI
Crassostrea 1
vlrglnlca
I larvae)
Rasbora BCFA
heteromorpha and
BSA
0.7li
1,160 ITU
sane as abovo
Ganmarus BSA
fasclatus
2.6 (T2), Z.5
ITd)
Paleonontes BSA
hadlaHensls
AseMus BSA
brevlcaudus
Orconectes BSA
nals
Daphnla mains BSA —
Cyprldopsls BSA
vldua
Lepoals BSA
•acrochlrus
?.T CTZ)
2.Z «TZ)
greater than
100.0 (TZ)
0.1 (TZ)
0.3Z (T?)
0.90 (T2>
a*,e,e,f. One hundred sixty-four
hard pesticides, wetting agents, and
(HH)or miscellaneous Hater pollutants showed a
soft (SH) Hide range of toxlclty scanning 1Z orders
synthetic of magnitude. Knowing the toxlcity 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 i»ost toxic in hard water
and sometimes the ooooslte was true.
Testing the actual material as sold was
found to be essential.
a* Of the aauatlc need herbicides
evaluated, Olclone Has the most toxic,
Oaohnla Has generally the »ost sensitive
organism. All of the Crustacea Here
affected by much lower concentration
levels of herbicides than Indicated by
the TL sub 50 values. All of the animals
represent Important food chain links.
a* sane as above
Davis, et al
(1969),AHIC-
5990
Alabaster
(1969),
AMIC-5W5
same as above
same as above
same as above
sane as above
sane as above
Sanders
C1970),AHIC-
H53
Sanders
(1970),
AHIC-1.53
Sanders
(1970),
AMIC-453
Sanders
(1970),
AMIC-«tS3
Sanders
(1970),
AMtC-li53
Sanders
(1970),
Sanders
(1970),
-------
Toxlclty, Exoerlmental
Active Variables,
Field Field Ingredient, Controlled
Compound Organism Study Location Pon or Noted Comments
2,*-D (resin based) Rasbors BCFA — ?,i(80 (T2) a*,c,e,f,
heteromorpha and hard(HH)
BSA or soft
(SW)
syn thet Ic
dilution
Mater, or
seanater
for sane
species
2,*-0 tresln based! Salwo BCFA — 1,920 (T2) a*,c,e,f.
qalrdneri and hard
BSA (HH)or
soft (SH)
synthetic
dilution
nater, or
seanater
for some
species
2,%-0 Fish (not — — greater than
specified) 0.1-1.0 (K)
2 h_D Wolff la L « 1000 (K) Hunter's-
papullfera "?edl UT-I
diluted
1:5
Z,k dlnllrophenol Negaorion BSA ~ 10 (NTE 3 hr) a,c,e
brevlrostpjs
(1-3 Kg)
One hundred sixty-four
pesticides, netting agents, and
m 1 see 1 1 aneous nater pollutants shoHed a
nMe range of toxlclty spanning 1Z orders
of magnitude. Knonlng 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 opposite Has true.
Testing the actual material as sold Has
found to be essential.
sane as above
Approximate toxlcltles of
numerous pesticides commonly used In
Britain were 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,^-D) caused teratogenlc
effects at concentrations as low as 1 ppm
Data from study of drug effects
on young lemon' sharks Here treated
mathematically to demonstrate
Reference
AHIC-<>53
Alabaster
(1969), AHIC-
5*25
Alabaster
(1969) ,
AHIC-5*i25
Handesley-
Thomas
(1971), AHIC-
1056
Worthley, et
al (1971),
AMIC-3233
•
Saldrldqe
(1969).
AHIC-383Z
Ibutoxyettiylester)
Rasbora BCFA
hetero«orpha and
BSA
1.0 (T2)
a*,c,e,».
hard (HH)
or soft
aoollcrab 111 ty of classical rate theory to
the study of chenrical shark deterrents.
Incaoacltatlon (narcosis) Has the primary
parameter timed for effectiveness. This
Has usually quite rapid lor the nor*
effective drugs.
On* hundred sixty-four Alabaster
pesticides, netting agents, and (1969).
• Iscel laneous nater pollutants shoved • ANIC-5<>35
-------
Fish (not
Specified)
2"-bro»o-3-nltPosall Sal mo
eylanlllde galrdnerl
2"-bromo-3-nltposal1 Capasslus
eylanlllde auratus
2~-bPomo-3-nltPosall Cvorlnus
cylanllide earolo
2"-bromo-3-nltrosal1
cylanllide
?"-bromo-3-nltposa11
cylanllide
Z"-bPomo-3-nl tposal 1
cylanltide
2"-chloPO-
1.0 (Kl)
1.0 (K 3 hPl
(SH) -Hide range of toxlclty snannlng 1? orders
synthetic of magnitude. Knowing the toxlclty and
dilution percentage of all components of a
Hater, or formulation did not result In easy
seawater 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 nas
found to be essential.
Approximate toxicltles of Mawdesley-~
numerous pesticides commonly used In Thomas
Britain Here summarized. An excellent (19711,AMIC-
brief, general discussion of toxlclty 1056
testing is also present.
a* Tnenty-nlne nltrosalIcvlanlI Ides Marking,ef
and related compounds Here evaluated for al (1970),
their relative toxic effect to selected AMIC-6391
fish. Potency varied with type and
position of substitutions. Several
compounds Here selectively toxic to
yellow perch. Goldfish Here the »ost
resistant to the sallcylanlI ides.
a* same as above Marking,
etal (1970),
ANIC-6391
Marking,et
al (1970),
AMIC-63gi
Marking,et
al (1970),
AMIC-6391
Marking,
etal (1970),
AMIC-6391
Marklnq,et
al (1970),
AMIC-6391
Marking,et
al (1970),
AMIC-6391
Marking,
etal (1970),
ANIC-6391
Marking, et
•I (1970),
AMIC-6391
sa*e as above
same as above
same as above
same as above
sane as above
same as above
sane as above
-------
o>
Conpound
?"-chl or o- *•""-*« thy 1 -
3-nitro3allcyl-
anlllde
?"-chloro-'t"-'«ethyl-
3-nltrosallcyl-
anllide
2"-ch loro-*"-" ethyl -
3-nltrosallcyl-
anilide
2 — c hlopo*'* ~inctf>Yi*
3-nltrogallcyl-
anillde
Z"-chloro-*"-"ethyl-
3-nltroaallcyl-
anlllde
2~-ch 1 or o- *•*-«<• thy 1-
3-nltrosalioyl-
anlllde
?"-chloro- ••"-methyl-
S-iil tr-osallcyl-
anillde
2~-chl oro-»"-nltro-3
-n I trosal Icylanl 1 Ide
Z"-ehloro-ii~-nltro-3
-nl trosal Icy Ian 11 Ide
2"-chloro-fc"-nltro-3
-n I trosal ley I an II Ide
?"-ehl oro-*"-nl tro-3
-nitrosallcylanll Ide
Z"-«hlore-»"-nltro-3
Field Field
Organism Study Location
Carasslus BSA —
auratus
Cyprlnus BSA
car pi o
Plmephales BSA
prone las
Ic t a 1 urus BSA — —
npl as
Lepomls BSA
cyanel lus
Leponls BSA ~
nacroehlrus
Perca BSA
tlavescens
Sal mo BSA
qalrdnerl
Carasslus BSA — -
auratus
Cyprlnus BSA —
carplo
Plnephales BSA —
crone las
Ictalurus BSA
Toxlclty, Experlnental
Active Variables,
Ingredient, Controlled
Ppa or Noted
1.0 (K 3 hr) a'
1.0 (Kl) a*
1.0 (Kl) a*
l.O(Kl) a*
1.0 (Kt) a»
1.0 (Kl) ••
1.0 (Kl) a*
1.0 (K 3 hr) a'
1.0 (Kl) a*
1.0 (Kl) a*
1.0 (Kl) a*
1.0
-------
-nltposatleylanll Ide net as
Z"-cMopo-*"-nltPo-3 Leoonls
-nltrosalleylanlllde cyanallus
Z"-chlopo-*"-nltPo-3 Leoomls
-nltrosalIcylanll Ide mscrochlrus
2"-ehloro-fc"-nltPo-3 Pepca
-nltrosal Icytanll Ida ftavescens
2"-chloro-5-nltpo
salicylanilide
2"-chIopo-5-nItro
salicylanilide
2"-chlOPo-5-nltPO
salicylanilide
Z"-chlOPO-5-n1tpo
Mlicylanllide
Z"*-ehIOPO-5-n1tpo
salicylanilide
Z"-chloPO-5-nltpo
salicylanilide
2"-cM oro-5-nl tpo
•alicylanilide
Z"-chIOPO-5-nItpo
salicylanilide
Z"-lodo-3-nItPo
salicylanilide
Sal no
galrdnepl
Carasslus
aupatus
Cyorlnus
carolo
Plmeohales
pponelas
Ictatupus
•elas
Leooitls
cyahelIus
Leponis
•acpochlrus
Pepca
f lavescens
Sal no
galPdnep!
BS» —
BS»
BS» —
BS» —
8S»
BSA
BS» —
BSA
BSA
BSA —
BSA —
BSA
1.0 (K2I
1.0 (Kl)
1.0 (Kl)
1.0 IK 3 hp)
10 (Kl)
10 (K 3 hp)
10 (K 3 hp)
1.0 (KZ)
10 (K 3 hp)
10 (K 3 hp)
10 (K 3 hp)
l.OtK 3 hp)
sane as abova
sana as abova
same as above
sane as abova
same as above
same as above
same as above
same as above
same as above
same as above
same as above
sane as above
al (1970).
ANIC-6391
MarKlng, et
al (1970),
AHIC-6391
HaPhlnq, et
al (1970),
AHIC-6391
, et
al (1970),
AHIC-6391
Marking, et
al (1970),
AHIC-H391
MarKlng, et
al (1970),
AHIC-6391
Mar-King, et
al (1970),
ANIC-6391
MapKIng, et
at (1970),
AHIC-6391
MapKIng, et
al (1970),
AHIC-6391
MarKlng, et
al (1970),
AMIC-6391
MarKlng, et
al (1970),
AMIC-6391
MarKlnq, et
al (1970),
AHIC-6391
MarKlng, et
al (1970),
AHIC-6391
Z*-iodO-3-nltPO
Capass1us
BSA —
10 (Kl)
same as above
MarKlng,
-------
Conoound
WLllcylanillde
?"-lodo-3-nI trosal Ic
ylanll Ide
Z"-lodo-3-nl trosal Ic
ylanll Ide
Z"-lo4o~3-nI trosal Ic
ylanll Ide
Jr- 2~-lodo-3-nl trosal Ic
—J ylanlllde
0
2"-lodo-3-nl trosal Ic
ylanlllde
Z"-lodo-3-nl trosal Ic
ylanlllde
Z"-«ethoxy-i."-nltro-
3-nl tro sail cyl-
anllida
2**-«ethoxy-ii"-nl tro-
3-nitrosalicyl-
anillde
?"-»ethoxy-i,"-nI tro-
3-nltrosalicyl-
anlllde
?~-«ethoxy-«i"-nltro-
3-nltrosallcyl-
•Jillida
2"-»«thoxy-«i"-nltro-
3-ni tro sail cyl-
anlllde
Field Field
Organls* Study Location
auratus
Cyorlnus BSA --
carplo
Plmephales BSA
Ictalurus BSA --
me las
Lepomls BSA — >
cyanel lus
Lepomls BSA -—
macrochlrus
Perca BSA
Havescens
Sal no BSA
galrdnerl
Car ass lus BSA — -
auratus
Cvorlnus BSA —
carplo
Plmeohales BSA —
pronelas
Ictalurus BSA —
•el as
Toxlclty. Experimental
Active Variables,
Ingredient, Controlled
Pom or Noted
1.0 (Kll a*
1.0 (Kl) a*
10 (Kl) »•
10 (K 3 hrl a»
10 (K 3 hr) a»
1.0 (Kl) a»
10 (K 3 hr) a*
10 (Kl) a*
10 (Kl) a*
10 (Kl) a*
10 (Kl) a*
Comments
same as above
sane as above
same as above
same as above
same as above
same as above
same as above
same as above
same as above
sane as above
sane as above
Reference
eta 1 1 1970) ,
AMIC-f.391
Marking, et
al (1970) ,
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Mark Inq,
etal (1970),
AMIC-6391
Marklna.et
al (1970),
flMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
at (1970),
AMIC-6391
Harking, et
al (1<*70) ,
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-5391
Marking, et
at (1970),
AMIC-6391
Harking, et
al (1970),
ANIC-6391
-------
Z"-nethoxy-*"-nltro- Leoonls
3-nltro3ollcyl- cyanellus
anllide
Z"-nethoxy-i»"-nltro- LCD on Is
3-nltrosallcyl- nacroehlrus
anllide
?">-nethoxy-l>"-nltro- Perca
3-nltrosallcyl- Maveseens
anllide
Z",*"-dlnethv»-3- Sal mo
nltrosallcylanllide galrdnerl
2",*"-dlnethyl-3- Carasslus
nitrosalicylanillde auratus
Z",«i--dli»ethyl-3- Cyorinus
nitrosalicylanillde carpi o
- PlneDhal«s
nltrosalloylanilide oronelas
2",it~-dliiethvl-3- tctalurus
nltroaalicylanllide velas
2"t*"-dli««thyl-3- Lepomls
nitrosalicylanillde crane 1 1 us
J",<.--dI»«!thy1-3- Leponls
nitrosalicylanillde nacrochlrus
Z"t%"-dlmethyl-3- Perca
nltroaalicylanillde flavesccns
Z"t5"-dlbPOi«o-3- Sal mo
nitrosallcylanilid"e galrdnerl
Z"i5"-dlbroi»o-3- Carasslus
nitrosalicylanillde auratus
BSA
BSA —
9S» —
BSA —
BSA
BSA —
8SA
BSA
BSA
BSA
BSA
BSA
BSA
10 IK1I
10 (Kl)
a»
10 (K 3 hr) a*
1.0 (K 3 hr) a* *
10 IK 3 hr)
1.0 (KZ>
1.0 «<•)
1.0 (Kl)
10 IK 3 hr)
10 IK 3 hr)
1.0 IK1)
1.0 IK 3 hr)
10 1K1)
a»
sana 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
sane as above
sane as above
Harklngt et
al (1970).
AMIC-6391
HarKIng, et
al (1970).
AMIC-6391
Marklnq. et
81 (1970),
AMIC-6391
Hsrklnq, et
al (1970).
OHIC-6391
Harking, et
al (1970),
AHIC-6391
MarKlng, et
al (197H),
AMIC-6391
Harking, et
al (1970),
AMIC-6391
Harking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AHIC-6391
Harking, et
al (1970),
AHIC-6391
Marking, et
81 (1970),
AHIC-6391
Marking,et
al (1970).
AMIC-6391
Marking,et
a I (1970),
AHIC-6391
-------
ro
Conoound
nitroeallcylanlllde
Z", 5~-dlbr ooo-3-
nltroaalloylanlllda
Z",5~-dlbrooo-3-
aitronalicylanllldo
Z-,5"-dlbrono-3-
nltroaallcylanllide
nl troaal icylanlllde
Z", 5"-dlbr ooo-3-
nl troaall cylanilide
Z",5"-dlnethoxy-i>"-
chloro-3-ni tro sa-
lieylanllida
Z",5"-dlnethoxy-i>"-
ohloro-3-nltrosa-
lloylanllido
Z",S~-dlnethoxy-%--
oliloro-3-nl trosa-
llcylanlllda
Z",5"-dlnethoxy-i»"-
ohloro-3-nltrosa-
chloro-3-nl-tros*-
llcylmniaida
Z-,5"-dl««thoKX-*"-
Fleld Field
Organise Study Location
Crprlnos BSA —
carplo
Plneohales BSA —
oronelas
let slur us BSA —
net as
Leponls BSA
cyanel I us
Leponls BSA —
nacrochlrus
Perca BSA —
f lavescens
Sal no BSA
qalrdner I
Carasslus BSA
auratus
Cyprlnus BSA —
carplo
Plneohales BSA
prone las
Ictalurus BSA
eel as
Leoonls BSA
Toxiclty, Cxperlnental
Active Variables,
Ingredient, Controlled
PD» or Noted
1.0 (K3I a*
1.0 (Kl) a*
1.0 (Kl) a*
1.0 (Kit a*
10(K 3 hr) a»
1.0 (K 3 hr) a*
1.0 (K 3 hr) a*
1.0 (KM a*
1.0 IK?) a*
1.0 (Kl) a>
1.0 (Kl) a"
1.0 IK?) a*
Conoents
sane as above
sane as above
sane as above
saoe as above
sane as above
sane as above
sane as above
same as above
sane as above
sane as above
sane as above
sane as above
Reference
Harklnq, et
al (1970),
AHIC-6391
Harklnq, et
al (1970),
AHIC-6391
Harklnq, et
al (1970),
AHIC-6391
Harklnq, et
al (1970),
AHIC-fi391
Harklnq, et
al (1970),
AMTC-6391
Harklnq, et
al (1070),
AMIC-6391
Harking, et
al (1970),
AHIC-6391
Harking, et
al (19701,
AMIC-6391
Harking, et
al (1970),
AHIC-6391
Harklnq, et
al (1970),
AHIC-6391
Harking, et
al (1970),
AHIC-6391
Harking, et
-------
ehloro-3-altrosa-
aicylanmde
cyan*11us
y-fc"- Leponls BSA
• c6lOPO-3-nltroa»- aacroehlrus
lloylanlllde
2-,5"-dlaethoxy-»"-
chloro-3-nltroa«-
licylanllldo
PerC8
flavescens
u>
Z~,6"-dIethyl-3,5-dl Sal no
nltrobenzanlllde galrdnerl
Z-,6"-dlethyl-3,5-dl Carasslus
nltrobenzanlllde auratus
3",6"-dlethyl-3,5-dl Cyprlnus
nltrobenzanlllde earplo
Z",6--«ll«thyl-3,5-dl Plmephalcs
nltrobenzanlllde prone I as
BSA —
BSA ~
BSA —•
BSA
8S» —
1.0 (Kll
1.0 IKll
10 INTEI
10 INTEI
10 (NTE)
10 (NTE)
saae as above
save as above
saae as above
saae as above
sane as above
saae as above
al (1970),
»NIC-<>391
MarKInq, at
al (1970),
*MIC-6391
Harklngt et
al (1970),
•HIC-6391
Harklna, et
al (1970),
4HIC-6391
Narhlnq, et
al (1970),
AHTC-6391
MarKing, et
al < 117(1),
AMIC-6391
Harking, et
al (1970).
!~,6"-dlethyl-3t5-dl letalurus BS» —
nltrebenzanlllde meI as
Z-,6--dle»hy«-3t5-dl Leponls BSA
nltrobenzanlllde eyanellus
Z",6"-diethy1-3,5-dl Leoonls BS» —
nltrebenzanlllde «acrochlrus
Z",6"-dlethyl-3,5-dl Perca BS« —
nltrobenzanlllde flavesc.ens
3-chloropropane-lt2 Rasbora BCFA
dlol heteroaorpha and
as*
10 INTEI
10 INTE)
10 (NTE)
10 (NTEI
P,10fl(T2)
sane as above
saae as above
sane as above
sane as above
a*,c,e,l. One hundred sixty-four
hard(HW) pesticides, netting aqents, and
or soft Miscellaneous Hater ool lutants showed a
ISM) Hide range of toxlclty scanning 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 toxlclty of a
for soae nlxture of materials. Sometimes
pesticides Here most toxic In hard water
and soaetlmes the opposite Has true.
Harklnq, et
al (1970).
AM.IC-6391
Harking, et
al (1970),
AHIC-6391
Marking, et
al (1970),
AHIC-6391
Harklnq, et
al (1970),
AHIC-6391
Alabaster
(1969),ANIC-
-------
Co'oound
D-chloropheny 1)
l-dl»ethylurea
Organic*
Phormldlun
amblguum
Field Field
Study Location
I
Toxlcl ty,
Active
Ingredient,
Ppn
0.5-10.0 (NTE)
Experimental
Variables,
Control 1 *d
ar Noted Comments
species
-- Ot 7it chemicals evaluated as
alglcldest only 9 Here more toxic than
Reference
Otto (1970),
AHIC-892
-p-
S.V-dlchlorobenzyl
•ethyl carbonate
Phormldlun
amb1guum
3,*-dIhydroxybenzotc Phorinldlui
acid (Dfotocafechulc anhlguun
acid)
3,*,5-trlhydroxy
benzole acid
(gallic acid)
Phornldlun
anblguu*
J,5-dlbro»o-*-hir
drcoqrbansonitrlle
Phor«ldlu»
aBblguui
0.5-10.0(16
oercent growth
Inhibited !<•)
0.5-10.0(50
percent growth
Inhibited !<•)
0.5-10.0 (NTE) —
0.5-10.0 (NTE) —
CuS9 chemicals evaluated as
alglcides, only 9 were »ore toxic than
Otto (1970),
AHIC-89?
Otto (1970),
AMIC-892
Otto (1970),
AMIC-89Z
Otto (1970),
AHIO892
-------
VJ1
3,5-dI Iodo-i»-hydPOxy Phopmldlun
droxybenionitrile amb1guun
3,5-dlnethyltetPahyd Phopmldlun
hydro 1,3,5,2- amblguun
thlodlzlne
3,5,7-tPlaza-l-azonl Phopnldlun
azonla adamantane amblguum
3"-bPono-3-nltPosall Salmo
cylanlllde galpdn*pl
3"-bPono-3-nltPosall Capasslus
cylanlllde aupatus
3"-bPomo-3-nltPosa11
cylanlllde
3"-bro»o-3-nltPosa11
cylanlllde
3"-bPo*o-3-nltPosatl
cylanlllde
3"-bPO«o-3-nltPosal1
cylanlllde
3"-brono-3-nltrosal1
cylanlllde
Cypplnus
carplo
Plmephales
ppomelas
IctalUPus
me I as
Leponls
cyan*11 us
I —
BSA
BSA
BS» ~
BS» —
as*
BSA —
0.5-10.0 (NTE) --
0.5-10.0
(16oepcent
gponth
inhibited I",I
0.5-10.0
-------
1
0\
Conoound
3"-bro»o-3-nl trosal 1
cylanl llde
3"-chl oro-3-nl troben
zanl llde
3~-chloro-3-nl troben
zanl 1 Ide
3~-chloro-3-nI troben
zanl 1 Ide
3~-chl oro-3-nl troben
zanllide
3~-chl oro-3-nl troben
zanl llde
3"-chloro-3-nl troben
zanillde
3"-c hi oro-3-nl troben
zanl llde
3~-chl oro-5-nl tro
lallcylanllida
3"-chl oro-5-nl tro
sallcylanllida
J"-chloro-5-nItro
sallcylanillde
Field Field
Organism Study Location
Perca BSA
tl avescens
Carasslus BSA
auratus
Cyprlnus BSA --
carolo
Plmeohales BSA
Drome las
Ictalurus BSA —
net as
Leoomls BSA ~
cyanel lus
Leoomls BSA —
macrochlrus
Perea BSA —
f lavescens
Sal mo BSA —
galrdner 1
Carasslus BS» —
auratus
Cyprlnus BSA —
carplo
Toxlclty, Exoerlnentat
Active Variables,
Ingredient, Controlled
Po« or Noted
1.0 IK 3 hr) »•
10 (K 3 hr) e»
10 8»
10 (K 3 hr) a»
10 (Kl) a»
10 IK 3 hr) 8»
1.0 «K«i) a»
10 IK1) 8»
10 IK 3 hr) a»
Comments
same as above
same as above
same as above
same as above
same as above
sane as above
sane as above
sane as above
same as above
same as above
sane as above
Reference
AMIC-6391
Markl ng.et
al (1970),
AMIC-6391
Mark 1 no, e t
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Mark I ng , et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6J9t
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
-------
3*"-chl oro-5-nltro
sallcylanillde
3"-chloPO-5-nItro
salieylanllida
3"-chlopo-5-nltPO
sallcylanlUde
3"-chIoro-5-nltro
salioylanlllde
Ictalupus
nelas
Leponls
cyanelI us
Leoomls
nacpoehlpus
Pepca
flavescens
3"-lodo-3-nl tposal Ic
ylanlllde
3"-lodo-3-nItposal le
ylanlllde
3"-lodo-3-nltposaIIc
ylanlllde
3~-lodo-3-nltposal Ic
ylanllIde
3"-lodo-3-nltposatIc
ylanlIIde
3"-lodo-3-nItPosal Ic
ylanllIde
3"-lodo-3-nltPosallc
ylanllIde
3"-lodo-3-nltposa I Ic
ylanllIde
3"«»~-dlchlopo-3-
nitrosalloylanillde
Capasslus
auratus
Cyprlnus
carplo
Plmeohales
ppomelas
Ictalupus
net as
Leoomls
cyanellus
Leoomls
macpochlpus
Pepca
I lavescens
Salmo
galPdnePl
Salmo
BS»
BSA
BSA
BS»
BS» —
BSA
BSA
BSA
BSA
BSA
BSA
BSA
BSA
10 «K 3 hP)
ID (K 3 np) a*
10 (K 3 hPt
1.0 (KZ>
10 (Kll
10 (K 3 hPl
1.0 (Kl) a*
10 (K 3 np)
1.0 (Kl)
1.0 (Kll
1.0 (K 3 hP)
10 (K 3 hp) a>
1.0 (K 3 hP)
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
same as above
Twenty-nine nltposalIcylanlI Ides
and related compounds were evaluated fop
their relative toxic effect to selected
fish. Potency varied with type and
MaPhlno, et
al (1970)t
AMIC-6391
Marking, et
al (1970).
AMIC-6391
MaPKlng. et
al (1970),
AMIC-6391
Marking, et
al (1970).
AMIC-6391
MapKlng,
etal (1970),
AMIC-6391
Marking, et
al(1970),
AMIC-6391
Marking,et
al (1970),
AMIC-6391
MaPklno,
etal (1970),
AMIC-6391
Marklng.et
at (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
MaPklng.et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Mapklng, et
al (1970),
AMIC-6391
-------
>
I
-p-
CoBDound
3",)
0.1 «<•)
0.5-10.0 (NTE)
Experimental
Variables.
Control led
or Noted Comments
position of substitutions. Several
compounds Here selectively toxic to
ye 11 OB perch. Goldfish were the nost
resistant to the sal Icylanl 1 Ides.
a* sane as above
a* sane as above
a> same as above
a* same as above
a* sane as above
a* sane as above
»• sane as above
~ Of 7i( chemicals evaluated as
alqlcldes, only 9 n
-------
V-8Zopnenyl-3-nltro Sal no
sallcytanlIIde galrdnerl
V-azophenyl-3-nltro Carasslus
sal Icytanltide auratus
*"-azophenyl-3-nltro Cyprlnus
satlcylanlllde carplo
l»"-azophenyl-3-nl tro Plmephales
sal IcylanlIide Drome I as
*"-azophenyl-3-nltro Ictalurus
salIcytanlIIde melas
*"-azophenyl-3-nltro Leoomls
sallcytanl1Ide cyanellus
V-azophenyl-3-nltro Lepomls
salIcylanltIde nacrochlrus
BS»
BSA —
BSA
BSA
BSA
BSA
BSA
0.1 tKl)
1.0 IK 3 hr)
0.1 (Kit)
0.1 (Kl)
0.1 (KZ>
0.1 (Kit)
0.1 (KH
a»
a»
controlling algae by environmental
management. No practical environmental
meins Here found.
Twenty-nine nltrosalIcylanlI Ides
and related compounds Here evaluated for
their relative toxic effect to selected
fish. Potency varied with type and
position of substitutions. Several
compounds Here selectively toxic to
yetlOH perch. Goldfish Here the HOST
resistant to the salIcylanlI Ides.
same as above
same as above
same as above
same as above
same as above
sane as above
Marking, »t
at (1970).
AMIC-6391
Marking, et
al (1970),
AHIC-6391
Marking, et
al (1970),
4MIC-6391
Marking, et
al (1970),
AMTC-6391
Marking, et
al (1970),
AMIC-6791
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
*"-azophenyl-3-nltro Perca BSA
sallcylanlIIde flavescens
•(••-bromo-Z-iiiethyl-3- Salmo BSA
nltrosalIcytanlllde galrdnerl
»"-bro»o-Z-methyl-3- Carasslus BSA
nltrosalIcylanlllde auratus
V-brono-?-«iethyl-3- Cyprlnus BSA —
nltrosalIcylanlIIde carplo
0.1 (Kl)
1.0 (K 3 hr)
1.0 (Kl)
0.1 («.)
a»
same as above
same as above
same as above
same as above
Marking, et
al (1970),
AMIC-6391
Marking,et
al (1970),
AMIC-6391
Marking,et
at (1970),
AMIC-6391
Marking,
etat (1970).
AMIC-6391
-------
Conoound
»"-brofo-?-methyl-3-
nl trosal Icylanl llde
*"-brono-?-»e thy 1-3-
nl trosal Icylanl llde
*"-bro«o-2-nethyl-3-
nl trosal Icy lanl 1 Ide
nl trosat Icylanl llde
*"-bro«o-2-«ethyl-3-
nl trosal Icylanl llde
V"-broi«o-3-nl trosal 1
cylanl llde
*"-brono-3-nl trosa 1 1
cylanlllde
»"-bro»o-3-nl trosal 1
cvlanl llde
•"-broiio-3-nl trosal I
eylanlllde
%"-bro»o-3-n! trosal 1
cylanllld*
»"-bro«o-3-nl trosa 11
cylanllld*
*>"-bro«o-3-nI trosal 1
Field Field
Organise Study Location
Plneohales BSA —
pro** las
Ictalurus BS* —
nel as
Leoomls BS* —
cyanel lus
leponls BS*
nacrochlrus
Perca BSA
tlavescens
Sal no BS*
galrdnerl
Carasslus BS* —
auratus
Cyprlnus BSA
carplo
prone las
Ictalurus BSA —
•elas
Leponls BSA
cyanel I us
Leponls BS* —
Toxlclty, Exoerlmental
Active Variables,
Ingredient, Controlled
Ppn or Noted
1.0 (Kl> a»
1.0 (K 3 hr) a»
1.0 (K 3 hr) a*
1.0 (Kl) a*
O.UKZ) a'
1.0 (K 3 hr) a"
1.0 (Kl) a*
0.1 (K 3 hr) a*
1.0 (K 3 hr) a»
1.0 (Kl) a*
1.0 (K 3 hrl a»
1.0 (Kl) a*
Comments
same as above
sane as above
same as above
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
Reference
Mar king, et
al (1970) ,
AMIC-6391
Marking, ef
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-f.391
Markl ng,e t
at (1970),
AMIC-6391
Marking, et
at (1970),
AMIC-6391
Marking, et
al (1970) ,
AMIC-H391
Marking,
etal (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
-------
cylanltlde
nacroehlrus
%"-bropo-3-nltrosalI Perca BS»
cytanltide flavescens
V*-bro»o-5-brono-3- Sal no BSA
nltrosal leylanl Ude galrdnerl
%~-brono-5-bromo-3- Carass Ius BSA —
nltrosal leyl anl Ude auratus
%~-brono-5-brono-3- Cyorinus BSA
nltrosalIcyIanlIIde carplo
0.1 l
sane as abova
same as above
same as above
sane as above
at (1970),
AMIC-6391
Marking,et
at (1970),
AMIC-6391
Marking,et
at (1970),
AMIC-6391
Harking,«t
at (1970),
AMIC-6391
Harking,
eta I (1970).
AMIC-6391
§
H
V-brono-5-brono-3-
nltrosal(cvlanlllde
V-brono-5-bromo-3-
nltrosalieylanlllde
Plmeohales
orone I as
Ictalurus
net as
BSA
BSA
0.1 (KZ)
0.1 (KM
sane as above
sane as above
Marklnq.et
al (1970),
AHIC-F.391
Marhlnq,et
al (1970),
AMIC-63<>t
*™-brono-5-bro"io-3-
nltrosalIcyIanlIIde
Leoomls
cvanellus
BSA
same as above
Marklnq.et
al (1970),
AMIC-6391
*"-brono-5-bromo-3-
nltrosalIcylanlIIde
Leoomls
rtiacrochlrus
BSA
0.1 (KZ)
sane as above
Marking,et
al (1970),
AMIC-6391
*"-brono-5-broi»o-3-
nltrosaIIcylanlIIde
Perca
ftavescens
BSA
0.1 (Kl)
sane as above
Harking, et
al (1970),
AMIC-6391
nltrosal Icylanl IItic
Plmechales
prone I as
BSA
1.0 (Kl)
same as above
Marking, et
al (1970),
AMIC-6391
»"-chloro-Z"-nethyI-
nltrosal Icylanl Ude
Ictalurus
net as
BSA
1.0 (K 3 hr)
sane as above
Harking, et
al (1970),
AMIC-6391
*~-cMoro-Z"-nethyl-
nltrosalicyIanlIIde
Leponls
cyanellus
BSA
1.0 (Kl)
sane as above
Marking, et
al (1970),
AHIC-6391
V-ehloro-Z"-»ethyl- Leoonls
BSA —
1.0 (Kl)
sane as above
Harking, et
-------
CoBDOund
nl trosal leyl an 1 1 Ide
»~-chloro-?"-nefhyl-
nltrosatlcylanlllde
*™-ehl oro-2"-methyl-
nltrosallcylanlllde
*"-chl oro-?"-nethy 1-
nl trosal ley lanl tide
> *--chloro-3"-nethyl-
> nltrosal Icylanl tide
§
ro
*"-chl oro-3-nl trosal
Icylanlllde
*"-c hi oro-3-nl trosal
icylanll Ide
V~-chl oro-3-nl trosal
Icylanll Ide
*"-c hi oro-3-nl trosal
Icylanlllde
»"-chl oro-3-nl trosal
leytenlllde
*"-chl oro-3-nl trosal
Icylanlllde
*"-chl oro-3-nl trosal
leylanltlde
Field Field
Organise! Study Location
•acrocMrus
Perca BSA —
I lavescens
Salno BSA —
galrdnerl
Carasslus BSA
auratus
Cyorlnus BSA ™
carolo
Salmo BSA
galrdnerl
Carasslus BSA
auratus
Cyorlnus BSA
carplo
Plneohales BSA
prone las
Ictalurus BSA --
•el as
Leoonls BSA --
cyanel lus
LcDoals BS»
•acrochlru*
Toxlclty, Cxoerlnental
Active Variables,
Ingredient, Controlled
Ppn or Noted
1.0 (K 3 hr) »•
1.0 (K 3 hr) a»
1.0 (Kl) a*
1.0 (Kl) a>
1.0 (Kl) a*
1.0 (Kl) a*
1.0 (Kl) a*
1.0 (K3 hr) a*
1.0 (K 3 hrl a"
1.0 (Kl) a'
1.0 (Kl) ••
Comments
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
Refer ence
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Mark 1 no, e t
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Mark Inq.e t
al (1970),
AMIC-6391
Marklng,et
al (1970),
AMIC-6391
Mark 1 ng ,<» t
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
at (1970),
AMIC-6391
Marking, nt
al (1970),
AMIC-6391
Marking, et
at (1970),
AMIC-6391
-------
£
U)
<"-ehloro-3-nltPOsal Pepca BSA
Icylanlltde flavescens
*"-chloPo-S-bPono-nl Salmo BSA
tposallcylanlllde galPdnerl
%~-chloPo-5-bPono-nl Capasslus BSA —•
trosalleylanillde aupatus
V-chloPo-5-bPomo-nl Cvorlnus BSA —•
trosalIcy I anil Id* carplo
V-cMoPo-5-bPomo-nl Plneohales BSA —•
trosalleylanillde pponetas
V-ehlOPo-5-brono-nl Ictafurus BSA ~
trosalIcylanllIda nelas
*~—chloro-5-broxo-nI Leoonls BSA
trosalIcylanll Ida cyancllus
*"-chloro-5-bPo*o-nl Leoomls BSA ~
tposalleylanlI Ida nacrochlPus
*"-ehlOPo-S-bPO»o-nl Pepca BSA —•
tposalleylanillde flavescens
*"-ch!oPo-5-nltPosal Sal no BSA —
IcylanllId* galPdnePl
»"-ehloPo-5-nltposal Capas-slus BSA
leylanillde aupatus
*"-chloPO-5-nltPO»al CypPlnus BSA —
leylanillde capplo
*"-chlOPo-5-nltPOS8l Plncphales BSA —
leylanillde pponelas
1.0 (Kt)
0.1 (Kl)
1.0 (Kl)
0.1 IKZ)
0.1 (K2)
1.0 (K 3 hPt
0.1 «K«t)
0.1
0.1 (Kl)
1.0 (Kl)
10 (K2)
10 (K<«)
l.O(Kl)
a»
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
sane as above
sane as above
HarKlng,et
al (1970),
AMIC-6391
Marking, et
al (1970).
AHTC-6391
MarKlnq, et
al (1970),
4MTC-&391
HarKlnq, et
al (1970),
AMIC-6391
Harking, et
al (1970),
»HIC-f>391
HarKlnq, et
al (1970).
Marking, et
al (1970),
AHIC-S391
Harking, et
al (1970),
AMIC-1J391
MarKlnq, et
al (1970),
AMIC-6391
HarKlnq, et
al (1970),
AMIC-6391
Harking, et
al (1970),
AMIC-6391
Harking, et
al (1970),
AMIC-6391
MarKlnq, *t
al (1970).
AHTC-6391
-------
Compound
*"-ehloro-5-nl tro
sal IcylanI tide
»°*-chl oro-5-nl tro
sallcylanl I id*
*"-chl oro-5-nl tro
sallcylanll Ide
*"-chl oro-5-n I tro
sallcylanlllde
*™-lodo-3-nl tro
sallcylanll Ide
Field Field
t)rganlsn Study Location
Ictalurus BS* ™
melas
Leoomls BS* —
cyanel lus
Lepomls BS* --
macrochlrus
Peres BS*
tl avescens
Ictalurus I
nebulosus
Toxlcltyt
Active
Pp.
1.0 (Kl)
1.0 (Kl)
1.0 (Kl)
1.0 (Kl)
9.0 (K)
Experimental
Variables,
Control led
or Noted Comments
a* same as above
a* same as above
a* same as above
a* same as above
a,c«9 Rrown bullheads were sub)ected to
solutions of V- lodo-nl trosal Icy 1 anl 1 Id*
Reference
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al M9ro),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Loeb, et at
(1966),
%"-lodo-3-nItro
sallcylanlllde
*"-lodo-3-nltro
sallcylanlllde
Ictalurus
nebulosus
(7.S-6.0
IN.)
Salmo
qalrdnerl
»"-lodo-3-nltro
sallcylanlllde
»"-lodp-3-nltro
salicylanllld*
BS*
?.5 (partial
K)
0.1 (K2)
Carasslus
auratus
Cyorlnus
carplo
BS* —
BS*
1.0 (K 3 hr)
0.1 (Kl)
In laboratory Jars some of which
contained bottom sediments of different
deoths up to 2 Inches. Upon exposure to
the toxicant, some of the bullheads
burled themselves In the sediments
thereby surviving the chemical treatment
8 to 16 days. The phenomenon of burying
appeared to be temperature dependent.
a.c.g same as above
Twenty-nine nltrosalIcylanl11des
and related comoounds were evaluated for
their relative toxic effect to selected
fish. Potency varied with type and
position of substitutions. Several
compounds were selectively toxic to
yellow perch. Goldfish were the «ost
resistant to the sal IcylanlI Ides.
same as above
see* as above
AMIC-6199
Loeb, et al
(19*6),
AMIC-5199
Marklnq, et
al (1970),
AMIC-6391
Marking,et
al (1970).
AMIC-6391
Marking,
etal (1970),
AMIC-6391
»"-Ied*-3-nltre
Pldephales
8SA —
0.1 (Kl)
sane as above
Marking,et
-------
tallertanlIIde
proneI as
at (19701
k
vn.
V-lodo-3-nltrosal Ic
Vlanllide
»"-lodo-3-nltrosalIc
rlanlllde
*"-! odo-3-nl trosa l.i e
Vlanllide
»"-lodo-3-nltrosalIe
rlanlllde
*"-lodo-5-nltrosalle
rlanlllde
*"-lodo-5-nlfrosalle
rlanlllde
*"-Iodo-5-nltros8lIc
Vlanllide
*"-lodo-5-nltrosalle
yI an 111de
*"-lodo-5-nItrosalIc
ylanlllde
*"-lodo-5-nltros8lIc
Vlanllide
V-lodo-5-nltPosslIc
Vlanllide
Ictalurus
•el as
LeoonIs
cyanellus
leoomls
macroeMrus
Perca
f lavescens
Sal no
galrdnerl
carasslus
auratus
Crnrlnus
carplo
PInephales
orone I as
Ictalurus
•el as
Lepoiils
crane11us
leponls
•acrochlrus
8S»
BS*
BS»
BS*
BS» —
BSA —
BSA
as*
BSA
BSA
BSA
0.1 IK1I
1.0 (K 3 hP)
0.1 (K2>
O.l(Kl)
1.0 IK1)
1.0 (KZ)
1.0 (KZ)
1.0 IK1)
1.0 (Kl>
1.0 IKZ)
1.0 IK1)
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
same as above
sane as above
Marking,
etal (1970),
AMIC-6391
Harking, et
at (19701,
AMIC-6391
Marking, et
at (1970),
AMIC-6391
Mark Ing, et
at (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking,
etal (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970,
AMIC-6391
Marking, et
al (1970),
AMIC-5391
Marking, et
81(1970),
AMIC-6391
-------
Compound
*™-lodo-5-nl frosal Ic
ylanll Ide
ii~-methoxy-Z"-nl tro-
3-nltrosallcyl-
anlllde
%~-»ethoxy-?"-n| f ro—
3-nltro3alicyl-
anillde
l,--(nethoxy-2"-nltro-
3-nl tro aal 1 cyl -
anllide
ii~-methoxy-2"-nl tro-
3-nitr03allcyl-
anilide
i,"-«ethoxy-Z"-nl tro-
3-nitro3allcyl-
anilide
V"-methoxy-?"-nltro-
3-nltro3Blloyl-
anllide
ii<*-»ethoxy-2''-nl tro-
3-nltro3alicyl-
anllide
*"-methoxy-Z"-nltro-
3-nl trosal icyl-
anilide
5-bro«o-3-nl trosal Ic
yllc acid
Field Field
Organism Study Location
Perca BSA
f 1 sveseens
Salmo BSA
galrdnerl
Carasslus BSA
auratus
Cyprlnus BSA
carplo
Plmephales BSA —
promelas
Ictalurus BSA
me 1 as
Leoomls BSA --
cyanel lus
teoonls BSA
macrochlrus
Perca BSA
f lavescens
Salno BSA
galrdnerl
Toxlclty, Experimental
Active Variables,
Ingredient, Controlled
Ppm or Noted Comments
1.0
-------
5-bro«o-3-nltrosal 1C
yllc acid
5-bromo-3-nltrosalIc
yllc acid
S-bro*o-3-nltrosalIc
yllc acid
S-brono-3-nltrosalIc
yllc acid
5-brono-3-nltrosalIc
rile acid
5-bro«io-3-nl trosal Ic
yl Ic acid
5-bro«o-3-nltrosatIc
yl Ic acid
5-bromo-3-sec-butyI-
6-nethyluraclI
Carasslus
auratus
Cyprlnus
carplo
Ictal urus
me I as
(.epomls
cyaneltus
Perca
f lavescens
Phornldluii
amblquun
BSA
BSA
PImeohales BSA
promelas
BSA
BSA
Leoomls BSA
nacrochlrus
BSA
1 .^^
1.0 (Kl) a*
1.0 IK1)
1.0 (Kl)
1.0 (Kl)
1.0 (Kl)
1.0 (Kl)
0.1 (Kl)
0.5-10.0 (NTE) —
compounds Mere selectively toxic to
yellow perch. Goldfish Mere the nost
resistant to the sal IcytanlI Ides.
sane as above
same as above
sane as above
sane as above
sane as above
sane as above
sane as above
Harking, et
al (19701,
AMIC-6391
Marking, et
al (1970),
AHIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Harking, et
al (1970),
AMIC-6391
Marking, et
81 (1970),
AMIC-6391
Marking, et
at (1970),
AMIC-6391
Otto (1970),
AMIC-892
5-mathyl 2- Rasbora BCFA
(1-iaethyl-n-heptyl) heteronorpha and
-U.,6-dlnltropb,enyl- BSA
1.52 (T2>
Of 7ii chemicals evaluated as
alglcldes, only 9 were more toxic than
CuSOU. None inhibited growth of
mat-forming alqae for more than 2 weeks.
CuSOU formulated with certain wetting
agents was more toxic than CuSO<» alone.
Cooper chloramlne was also found to be
more toxic than CuSOit. No wetting agents
were found to be Inhibitory at the
concentrations Investigated (0.05 and
O.OO1; pom). 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.
a*,c,e,f. One hundred sixty-four Alabaster
hard (HM) pesticides, Netting agents, and (1969),
or soft miscellaneous water pollutants showed a AMIC-?i»25
-------
Co»oound
thlol carbon»»e
Toxlclty,
Active
Field Field Ingredient,
Organise Study Location Pon
Experiments!
Variables,
Control l«d
or Noted Comments Reference
(SW) wide range ot toxlclty scanning 12 orders
?,8-dlhydroxyl-l.Z,3 pnoraldlui
,* »9»9-hexachloro-l, aeblguu*
*-«efhano-l,it-rtiriy
dronaphthaiana
I —
0.9-10.0 (33
percent growth
inhibited lit)
5"-chloro-2"-methoxy Sal»o
-3-nltrosallcyl galrdnerl
anilIde
BSA —
1.0 (K 3 hr)
synthetic of magnitude. KnOMlnq the toxlclty and
dilution percentage of all conoonents of a
cater* or formulation did not result In easy
seaxater predictability of the toxlclty of a
for some mixture of materials. Sometimes
species pesticides were nost toxic In hard Mater
and sometimes the opposite was true.
Testing the actual material as sold Has
found to be essential.
Of 71, chemicals evaluated as Otto (1970),
alqlcldes, only 9 Here more toxic than AMIC-R9?
CuSO"t. None Inhibited growth of
mat-forming a Iqae for more than ? weeks.
CuSOt, formulated with certain wetting
agents was more toxic than CuSOit alone.
CoDDer chlorafflne was also found to be
more toxic than CuSOfc. No wetting agents
were found to be Inhibitory at the
concentrations Investigated (0.05 and
0.005 DPm). 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.
• * Twenty-nine nltrosaI Icy Ianl11des Marking, et
and related compounds were evaluated for al (1970),
the'lr relative toxic effect to selected AMIC-6391
fish. Potency varied with type and
position of substitutions. Several
compounds were selectively toxic to
yellow perch. Goldfish were the most
resistant to the salIcylanlI Ides.
5"-chloro-2~-methoxy Carasslus 8SA —
-3-nltrosalIcyl auratus
anilIde
5"-ehloro-?"-methoxy Cyorlnus BSA ~
-J-nlfrosallcyl carplo
•nilIde
5"-chloro-?"-methoxy Plmeohales 8S»
-3-nltrosalIcyl pronelas
anlIIde
10 (Kl)
1.0 (Kl)
1.0 (Kl)
a»
saee as above
same as above
same as above
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-%391
-------
5"-chloro-2"-«ethoxy letslurus 8S» —
-3-nltrosallcyl • > •• «elas
anllldc
5"-cMoro-2"-»iethoxy leoonls BS»
-3-nltrossllcyl cyanetlus
anlllde
5"-chloro-Z"-nethoxy Leponls BS» —
—3-nltPosalley I nacrochlrus
anlllde
5"-ehloro-2"-nethoxy Perea BS» —
-3-nltrosa!leyl flavescens
Villlde
1.0 (Kl)
1.0 IK1)
1.0 (Kit
1.0 (Kl)
san* as above
sane as above
sane as above
save as above
Harklnq, et
al (1970),
AMIC-6391
Marking, et
al (1970),
AMIC-6391
Marking, et
al (1970),
tHIC-6391
Marking, et
al (1970),
4MIC-6391
6,7-DJhydrodlpyrldo Thormidlua
PTTtzldiiniun salt
IDlquat)
0.5-10.0 (66
percent growth
Inhibited 11».)
Of 71). chemicals evaluated as
alglcldes, only 9 were nore toxic than
CuSOL).. None Inhibited growth of mat-
forming alpae for more than 2 weeks.
CuSOL). formulated with certain wetting
agents was more toxic than CuSOl).. Copper
chloramine was also found to be nore
toxic than CuSOfj.. Ko wetting agents were
found to be Inhibitory at the concentra-
tions investigated (0.05 and O.C05 ppm).
Also reported are factors affecting
growth of algae in canals to determine
whether there ware leads to controlling
algae by environmental management. Ho
partial environmental means were found.
Otto (1970),
AKIC-892
-------
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 occidentalis - A-115, 130, 157
Agmenellum quadruplicatum - A-7, 199, 23^, 278, 376, 377
Agonus cataphractus - A-23, 2U, 26, 28, kg, 50, 53, 75, 80, 8l, 103,
206, 221, 232, 301, 311, 33^, 393, ^Qk, k06, UlU
Alewife - A-17U, 206
Algae - A-1U9
Alosa pseudoharengus - A-29, 55, 76, 82, 96, 117, 131, 166, U27,
Ambassis safgha - A-308, 369
Ambloplites rupestris - A-117, 119, 131, 133, 166, 176
Ameirus nebulosus - A-118, 132, 176
American smelt - A-17^, 206
Amia calva - A-18
Amphidinium carter! - A-105, 335
Amphipnous cuchla - A-180, 263, 373
Anabaena - A-9
Anabas testudineus - A-178, 26J, 373
Anacystis nidulans - A-7, 199, 233, 278, 376, 377
Anas cyanoptera - A-158, 360
Anguilla rostrata - A-113, 121, lUl, 266, 355
Anisoptera - A-178, 26U, 373
Anisotremis davidsoni - A-1U9, 35^
Aplodinotus grunniens - A-19
Aquatic plants - A-1^9
Aquila chrysaetos - A-159, 202, 360
Archoplites interruptus - A-115, 116
Arctic grayling - AJ»6, 12U, 1U6, 197, 35^, ^22
Artemia salina - A-307
Artemia spp. - A-1U8
Asellus brevicaudus - A-lU, l8U, 190, 191, 217, 2U6, 320, 397, 398,
lK)l, U38, M*6, U62, k6k, ^65
Asplanchnopus - A-112, 121, 136, 313
Asterias forbesi - A-68
Asterias rvfoens - A-10, 65, 75, 302, 33^, kk6
Backswimmers - A-Uo
Belostoma indica - A-180, 26^, 373
Benthic insects - A-177
Betta splendens - A-U8, 2bk
Bigmouth buffalo - A-^5, 123, 1^, 196, 352, U20
Birds - A-150
Black bullhead - A-^5, 123, 1^5, 197, 353,
Black crappie - A-U5, 12^, 1^5, 197, 353, 2
Bloater - A-UU, 123, l1^, 17^, 195, 207, 352,
B-l
-------
Blue catfish - A-44, 71, 122, 144, 261, 352, 420
Bluegills - A-44, 122, 146, 195, 3^6, 351, 419
Blue-green sunfish - A-435, 436
BOD - A-22, 66, 100, 276, 292, 409
Bottom invertebrates - A-168
Boyeria vinosa - A.269
Brachionus - A-179, 265, 37^
Brachycentrus americanus - A-269
Brachydanio rerio - A-2, 7, 62, 211, 250, 370, 382, 449
Bridgelip sucker - A-46, 124, Ik6, 197, 35 ^, U21
Brevoortia patronus - A-27
Brook trout - A-269
Brown bullhead - A-43, 71, 125, 1^7, 175, 195, 207, 260, 351, 419
Bucephala clangula - A-115
Bugula neritina - A-89, 306, 452
Callibaetis sp. - A-185, 186, 218
Callinectes sapidus - A-27, 28
Cambarus bartoni - A-150
Campeloraa decisum - A-94, 95
Campeloma sp. - A-119, 133, 176
Cancer magister - A-127, ^22
Carassius auratus - A-18, 30, 4l, 52, 55, 64, 97, H1*, 128, 15^, 155,
164, 235, 247, 248, 258, 277, 279, 280, 284, 298, 308, 309, 317,
365, 391, 403, ^28, 431, UUi, 449, ^54, 458, 467, ^68, 469, ^70,
471, 472, 473, ^75, ^76, 477, ^78, U79, ^80, 481, 482, 483, ^84,
485, 486, 487, ^88
Carcinus maenas - A-3, 33, 34, 47, 48, 68, 79, 86, 87, 90, 103, 170,
205, 213, 224, 227,, 242, 252, 254, 270, 279, 307, 329, 33^, 337,
3^0, 368, 378, 379, 38l, 399, ^00, 4oi, 402, 405, 4o8, 4l4, 434,
Cardium edule - A-10, 22, 24, 26, 28, 29, 32, 33, 3^, ^7', ^9, 50, 5^,
65, 67, 75, 79, 80, 81, 85, 86, 91, 101, 104, 110, 170, 181, 206,
213, 221, 224, 225, 227, 232, 242, 245, 250, 253, 251*, 278, 279,
291, 301, 302, 207, 3H, 323, 329, 33^, 337, 3^1, 3^6, 3^9, 369,
378, 379, 399, ^00, 401, 4o2, 4o5, ^06, 409, UlU, 425, ^3^
Carp - A-43, 71, 122, 147, 175, 195, 260, 351, 419
Carpiodes cyprinus - A-20
Carpiodes sp. - A-198
Catostomus commersoni - A-20, 82, 105, 108, 117, 118, 131, 133, 165,
176, 277, 297, 337, ^58
Ceriodaphnia - A-179, 265» 376
Cerorhinca monocerata - A-161, 362
Chaetoceros sp. - A-105, 335
Chain pickerel - A-43, 125, l1^, 19^, 350, 419
Channa punctatus - A-7, 177, 180, l8l, 263, 372
Channel catfish - A-4o, 43, 71, 122, 147, 175, 195, 207, 260, 345,
351, 419
Chara sp. - A-345
Chironomus sp. - A-7, 129, 130, 134, 135
Chironomus tentans - A-313
ChiseLnouth - A-46, 124, 145, 197, 353,
Chlanydotheca arcuata - A-8, 203
B-2
-------
Chrosomus eos - A-18
Closterium - A-179, 265, 376
Clupea harengus - A-113, 121, l4l, 266, 355, 447, 448
Coho salmon - A-6, 69, 101, 175, 207, 246, 253, 268, 276, 365, 379,
393, ^09
Coleps - A-112, 120, 136, 313
Copepods - A-72, 73, 203, 204, 238, 239, 267, 285, 286, 299, 300,
371, Ull, 412, 432
Coregonus artedii - A-29, 55, 82, 96, 427, 44l, 454
Coregonus clupeaformis - A-17, 29, 30, 31, 51, 55, 56, 77, 82, 96,
97, 280, 281, 302, 310, 331, 393, 391*, ^27, 429, 44l, 454, 455'
Coregonus hoyi - A-29, 51, 55, 83, 96, 428, 44l, 454
Coscinodiscus - A-112, 120, 137, §13
Cottus bairdi - A-114, 126, 138, 151, 200
Crangon crangon - A-2, 3, 5, 10, 22, 23, 24, 26, 28, 29, 32, 33, 34,
36, 38, 47, 49, 50, 54, 66, 67, 79, 80, 81, 86, 87, 91, 101,
102, 103, 104, 107, 110, 182, 206, 213, 214, 221, 224, 225, 227,
231, 232, 242, 243, 245, 248, 250, 251, 254, 255, 256, 257, 268,
270, 277, 286, 287, 289, 301, 302, 307, 311, 319, 323, 328, 329,
337, 338, 341, 346, 349, 363, 364, 369, 370, 371, 376, 378, 379,
381, 386, 388, 389, 391, 39^, 399, 4oi, 402, 403, 405, 4o6, 409,
U15, U25, ^26, U3U, UU6, hkj, ^59
Crangon septeraspinosa - A-67
Crassostrea commercialis - A-307
Crassostrea virglnica - A-U, 13, lU, 26, 103, 169, l8l, 20^, 205,
217, 220, 223, 230, 231, 233, 2to, 260, 28^, 300, 301, 305, 326,
3^0, 3^3, 36^, 367, 377, 389, 39^, 398, Ul6, Ul8, U2U, U25, ^38,
1*63, U6U, 465
Crepidostxomum farionis - A-222
Culex pipiens - A-112, 120, 133, 13^, 136, 312
Cybister sp. - A-178, 26U, 373
Cyclops - A-179, 265, 37^
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, 412, 432, 433
Cyclops vernalis - A-72, 73, 168, 203, 204, 238, 239, 285, 286, 299,
300, 371, 4ll, 412, 432, 433
Cyclotella nana - A-105, 335
Cynoscion nebulosus - A-27
Cypridopsis vldua - A-l4, 185, 191, 217, 246, 320, 397, 298, 400,
439, 1*6, 463, ^6^, ^65
Cyprinodon variegatus - A-68, 176, 24l
Cyprinus carplo - A-9, 19, 4l, 64, 117, 118, 131, 132, 164, 166,
176, 198, 258, 277, 284, 296, 298, 299, 317, 431, 449, 467, ^68,
469, ^70, 471, 472, 475, 476, 477, Vf8, 479, ^80, 481, 482, 483,
484, 485, 486, 487, W8
Cyprls - A-279, 265, 37^
Daphnla - A-179, 264, 267, 374
Daphnia magna - A-6, 7, 14, 69, 112. 114, 115, 120, 128, 129>
133, 131*, 136, 184, 191, 217, 246, 312, 320, 397, 398, 400, 439,
446, 462, 463, 464, 465, 466
B-3
-------
Diaptomus - A-180, 26k
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-l?8, 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, 2U8, 2&0, 306, 330, 452
Ephemerella sutrmria - 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, 39^, 429, 442, 455
Esox nlger - A-113, 117, 121, 131, I1*!, 166, 266, 297, 355
Estigmene acrea - A-111, 119, 135, 312
Eucalia inconstans - A-20
Euclanls - 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, 433
Falco columbarius - A-159, 361
Falco peregrinus - A-162, 201, 202, 261, 356
Falco sparverius - A-159, 160, 361
Fathead minnow - A-74
Fish (not specified) - A-7, 13, 34, 62, 88, 109, 143, 150, 181, 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, 145, 196, 353, 421
Flathead catfish - A-45, 123, 144, 196, 352, 420
Fregata magnificens - A-158, 359
Freshwater drum - A-44, 122, l44, 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, 341, 342, 363, 4l4, 430
Fundulus majalis - A-68
Gadus macrocephalus - A-127. 153, 423
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, 134, 184, 190, 191, 215,
217, 222, 242, 246, 271, 273, 319, 338, 363, 384, 397, 4oo, 416,
430, 439, 445, 462, 464, 465
B-4
-------
Gammarus oceanlcus - A-2U, 25, 101, 102, UU8
Gammarus pseudolironaeus - A-69, 95, 271
Gamraarus sp. - A-llU, 126, 138, 151, 200, 235
Gastrotricha - A-179, 26U, 376
Gerris - A-267
Gizzard shad - A-UU, 71, 122, lU3, nkt 195, 208, 26l, 351,
Golden shiner - A-1K35, 1*36
Goldeye - A-U5, 1^5, 196, 351, 352, 1+20
Goldfish - AJ+3, 123, 125, 1^6, 170, 19U, 1*19
Green sunfish - A-3U6
Haliotus corrugata - A-1^9, 355
Haliotis rufescens - A-1^9, 35^
Halocyptena microsoma - A-163, 357
Heteropneustes fossilis - A-178, 263, 33^, 373
Hexagenia bilineata - A-7, 129, 133, 135
• Hinnites multirugosis - A-1^9, 35U
Hippoglossoides platessoides - A-121, 356
Homarus araericanus - A-.lj.l4-7
Hyallela azteca - A-189, 219
Hydrophilus sp. - A-179, 265, Jjh
Hydroprogne caspia - A-160, §62
Hydropsyche - A-5^, 76, 82, 92, 2U8, 280, 306, 330,
Hydropsyche betteni - A-26§
Ictalurus catus - A-20, 116, 165
Ictalvtrus melas - A-20, kl, 63, 16U, 199, 258, 277, 28^, 298, 317,
U31, UU9, U67, ^68, 1*69, ^70, U?!, ^72, ^73, ^75, ^76, U77,
U79, U8o, U8i, U82, U83, U8U, U85, U86, 1*87, U89
Ictalurus nebulosus - A-21, 117, 131, 166, 350, k&k
Ictalurus punctatus - A-7, 20. Uo, 59, 63, 163, 198, 2U9, 258, 277,
283, 298, 315, 316, 390,- U31, UU8
Ictiobus cyprinellus - A-20, 198
Invertebrates - A-150
Ischnura vertical!s - A-129, 131*-, 135
Isochrysis galbana - A-105, 335
Isogenus frontalis - A-270
Kelletia kelletii - A-1^9, 355
Kiyi - A-171, 208
Klamath sucker - A-12U, lUj, 353, ^21
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-UU, 123, 1^, 171, 196, 208, 352, 1^20
Lake whitefish - A.UU, 123, 1^, 171, 196, 209, 352, U20
Largemouth bass - A-U3, 71, 125, 1^7, 195, 351, Ul9
Largescale sucker - A-U6, 12k, lkjt 197, 353, ^21
Larus delawarensis - A-115, 130
B-5
-------
Larus heermanl - A-156, 357
Larus occidentails - A-160, 36l
Larus spp. - A-115, 130
Lavinia exilicauda - A-ll6
Leblstes retlculatus - A-169, 205, 26?, 28?, 368, 381, 450
Leiostomus xanthurus - A-25
Lepdotius floridanus - A-199
Lepisosteus platostomus - A-17
Lepomls auritus - A-118, 132, 16?
Lepomis cyanellus - A-20, 72, 116, 201, 238, 262, 277, 283, 316, 347,
3U8, 394, 410, 4ii, 467, 468, 469, 470, 471, 472, 473, 475, 476,
477, 4?8, 4?9, 480, 481, 482, 483, 484, 485, 486, 487, 489
Lepomis gibbosus - A-l§, 116, 131, 165
Lepomis macrochirus - A-2, 3, 4, 14, 16, 19, 21, 4l, 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, 3&0, 382, 388, 390, 394, 397,
398, 4oo, 403, 4o4, 4o8, 431, 439, 446, 449, 450, 452, 457, 462,
U63, 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, 24o, 258, 271, 284, 298, 431,
453
Llbellula sp. - A-129, 130, 134, 135, 187, 219, 228
Limanda limanda - A-34, 49, 101, 382
Lepomis megalotis - A-19
Limnephilus rhombicus - A-113, 125, 137, 150, 199, 235
Limnephilus sp. - A-187, 188, 219
Limnodrilus sp. - A-410
Longnose sucker - A-46, 124, 146, 197, 354, 422
Loomelania melania - A-163, 357
Lophodytes cucullatus - A-150
Lymnaea stagnalis - A-17
Macrocyclops albidus - A-72, 73, 168, 203, 204, 238, 239, 285, 286,
299, 300, 371, 411, 412, 432, 433
Macrognathus aculeatum - A-180, 372
Mastocembelus pancalus - A-180, 372
Megaceryle alcyon - A-150
Mercenaria mercenaria - A-4, 8, 9, 10, 69, 70, 102, 103, Ibl, 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,
4i6, 417, 4l8, 433, 434, 438
Mergus merganser - A-115, 150
Merluccius productus - A-123, 128, 152, 153, 422, 423
Microcystis - A-9
Micropogon undulatus - A-27
Micropterus dolomieul - A-19, 117, 131, 166
Micropterus salmoides - A-19, 4l, 64, 116, 130, 164, 188, 259, 284
299, 316, 317, 431, 449
Minytreraa melanops - A-20
Monochrysis lutheri - A-106, 335
B-6
-------
Morone saxatilis - A-5, 22, 39, 67, 102, 285, 295, 299, 1*25
Mosquitofish - A -4 36
bfods - A -150, 3^5
%a arenaria - A -68, 220
%riophylluni spicatum - A -221
Ifystus vitatus - A-180, 265, 373
%tilus edulis - A-68, 121, 307, 355
edulis planulatus - A -89
Nandus nandus - A-180, 265, 372
Nannochloris occulata - A-106, 335
Nassarius obsoletus - A-69
Nauplius - A -179, 264, 374
Navicula - A-112, 120, 137, 313
Negaprion brevirostris - A-69, l8l, 242, 267, 323, 333, 365, 384,
386, 405, 414, 466
Nepa sp. - A -179, 265, 375
Nereis virens - A-23, 51, 69, 79, 108, 228, 319, 327, 342, 363, 430
Nine-spined stickleback - A -172, 209
Nitzschia closterium - A-106, 335
Nitzschia linearis - A-2, 3, 4, 16, 59, 60, 87, 327, 367, 380, 382,
4o4, 408, 450
Northern squawfish - A -46, 124, 145, 197, 353, 423
Notemigonus crysoleucas - A-72, 117, 131, 166, 262, 283, 297, 316,
3^7, 3W, 3^9, 39^, Uli, ^58
Notomatta - A-112, 121, 136, 313
Notonecta sp. - A -178, 265
Notropis analostanus - A -132, 167
Notropis hudsonius - A-30, 51*, 76, 82, 97, ^28, kkl
Notropis cornutus - A -117, 132, 166
Nuclearia - A-112, 120, 136, 313
Nycticorax nycticorax - A-160, 36l
Oceanodroma homochroa - A -15 7, 359
Oedogonium cardiacum - A-112, 120, 136, 312
Ollsthodiscus luteus - A-106, 335
Oncorhynchus kisutch - A-35, Ul, 63, 64, lU8, 152, l6k, 235, 252,
259, 284, 296, 299, 317, 336, 383, 385, U32, M*9, ^59
Oncorhynchus nerka - A -337
Oncorhynchus tshawytscha - A-9^, 336, 387, ^59
Ophiogomphus rubinsulensis - A -269
Orconectes nais - A-lU, Uo, 133, 13^. 18U, 190, 191, 217, 2«+6, 320,
397, 398, ^00, MK), UU8, 463, 464, 465
Orconectes rusticus - A-94
Orthocyclops modestus - A-72, 73, 168, 169, 203, 204, 238, 239, 285,
286, 299, 300, 371, 4li, 412, 432, 433
Orthodon microlepidotus - A -115
Oscillator ia - A -9
Osmerus mordax - A-17, 30. 31, 55, 57, 77, 83, 96, 98, 28l, 303, 310,
331, 394, 428, 430, 441, 442, 448, 455
Ostrea edulis - A-49, 91, 243, 255, 307, 329, 403
B-7
-------
Pacific oyster - A-6, 101
Pagurus longicarpus - A -68
Palaemonetes kadiakensis - A-13, 72, 110, 111, 115, 129, 133,
165, 184, 170, 191, 217, 228, 237, 246, 259, 262, 263, 285,
317, 318, 320, 3^8, 393, 397, 4oo, 4ll, 432, 439, kk6t ^62, 464,
465
Palaemonetes vulgaris - A-68, 3^-2
Pandalus montagui - A-379, 381, 39^, kQl, 402, 403, 409, 4l5, 434
Pandion haliaetus - A -159, 236, 361
Pandorina - A-179, 264, 37^
Pandulus montagui - A-32, 35, ^9, 80, 91, 182, 213, 224, 225, 227,
243, 247, 253, 254, 256, 279, 280, 307, 329, 337, 3^1, 369
Panopenus herbstii - A -199
Panulirua interruptus - A -149, 355
Paralabrax clathratus - A-ll, 12, 13, 37, 38, 57, 58, 60, 6l, 77, 78,
79, 83, 84, 85, 98, 99, loo, 274, 275, 281, 282, 283, 289, 290,
292, 293, 303, 304, 305, 320, 321, 322, 331, 332, 333, 375, 376,
395, 396, 397, 412, 413, 4l4, 443, ^44, 455, ^56, 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 -2 5, 27, 28
Penaeus setiferus - A-27
Perca flavescens - A-17, 19, 30, 31, Ul, 56, 57, 6k, 77, 83, 97, 98,
116, 118, 130, 132, 16U, 165, 176, 259, 281, 285, 297, 299, 303,
310, 317, 331, 39^, ^28, ^30, 1+32, k^Q, kkz, kkg, ^55, ^67, U68,
, U70, U71, <472, U73, ^76, U77, ^78, kl9, hQo, U8l,
Percopsis omiscomaycus - A-30, 56, 77, 83, 97, U28,
Petromyzon marinus - A-U25
Phalacrocorax pelagicus - A -158, 360
Phalacrocorax peniciliatus - A -158, 359
Phalaropus fulicarus - A-160, 362
Phormidium ambiguum - A-U, 9, 10, 15, kf, U8, 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, ^07, 4o8, Uio, U26,
^37, U51, ^59, ^60, 46l, 462, 473, 474, 475, ^78, 487, ^88, 489
Physa gyrina - A-204, 239, ^33
Physa heterostropha - A-2, 17, 109, 327, 367, 380, 382, 450
Physa Integra - A-95
Physa spp. - A -111, 119, 136, 312
Pilodictus olivaris - A-20
Pimelometopon pulchrum - A-149, 354
Pimephales promelas - A-20, 22, 4l, 47, 64, 66, 69, 73, 8l, 93, 100,
105, 108, I4o, 153, 164, 211, 214, 215, 235, 237, 245, 258, 272,
276, 278, 284, 287, 291, 292, 297, 298, 301, 317, 337, 3^6, 3^7,
409, ^26, 431, 449, 452, 453, 458, 461, 467, ^68, 469, ^70, 471,
472, 473, 475, 476, 477, ^78, 479, U8o, 481, 482, 483, ^84, 485,
486, 487, 488
B-8
-------
Pisidium sp. - A-119, 133
Pizonyx viversi - A-163, 357
Plankton - A-115
Plants - A-ll*9
Platessa vulgaris - A-250
Platichthys flexus - A .91, 110, 225, 251, 308, 3!*!, 369, Ul5,
Platichthys stellatus - A-127, 153, ^23
Platymonas subcordiformis - A-105, 335
Pleuronectes platessa - A-lQl*, 170, 31*9
Podiceps caspicus - A-163
Poecilia latipinna - A-193, 19!*
Poecilia reticulata - A-1*23, ^2l*
Pomoxis annularis - A-156, 198, 358
Pomoxis nlgromaculatus - A-19, 115, 118, 132, 156, 167, 198, 358
Porphyridium cruentum - A-105, 335
Procambarus siraulans - A-1*0
Prosopium cylindraceum - A-29, 51, 55, 83, 96, 1*28, 1*1*1,
Protozoa - A-112, 120, 136, 313
Pseudopleuronectes americanus - A-92, 93
Pteronarcys dorsata - A-270
Ptychocheilus oregonensis - A-1*58
Ptychocheilus umpquae - A-1*59
Ptychoramphus aleuticua - A-l6l, 362
Puffinus creatopus - A-157, 358
Puffinus griseus - A-157, 359
Puffinus tenuirostris - A-157, 359
Pumpkinseed - AJ*3, 125, iVf, 19^, 351, 1*19
Puntius sophore - A-8, 177, 180, 265, 33^-, 313
Puntius ticto - A-1*6, 212, 252, 278, 297, 39^,
Pygoscelis adeliae - A-156, 358
Rainbow trout - A-l*6, 12U, lU5, 197, 3^5, 353, ^21, ^35, ^53
Rana tenrporaria - A-128, 15 U
Ranatra filifonnls - A-178, 265, 33^, 373
Rasbora heteromorpha - A-3, 5, 6, 11, 15, 16, 21, 23, 31, 32, 33, 3^,
35, 36, 38, 39, M, ^2, 51, 52, 53, 6l, 65, 66, 67, 73, 7^, 75,
87, 102, 10U, 106, 109, 110, 137, 139, 1M, 1^2, 1^3, 182, 183,
I8i*, 185, 192, 193, 211, 212, 216, 226, 229, 230, 232, 2Ul, 2^,
2U5, 2U6, 2U8, 2U9, 252, 255, 256, 257, 26l, 267, 273, 275, 276,
288, 391, 293, 291*, 297, 305, 306, 310, 318, 319, 32U, 325, 326,
327, 338, 339, 3^, 3^5, 366, 367, 370, 371, 377, 3&*, 385, 386,
387, 393, ^2, UoU, U07, Ul6, Ul7, ^25, U26, 1*27, ^30, U31, ^36,
1+39, ^2, 1*UU, Ul*5, ^7, ^8, 1*51, U63, ^65, 1*66, 1*73, ^87
Redbreast sunfish - A-122, lU6, 295, 351, 1*21
Redhorse sucker - A-l*3, 71, 122, ll*3, 195, 351, 1*19
Red shiner - A .1*36
Rhinichthys atratulus - A-lll*, 118, 126, 132, 138, 139, 151, 16?, 200,
201
Rita rita - A-180
Roccus americanus - A-ll8, 132, 166
Roccus chrysops - A-30, 52, 56, 83, 97, 199, ^28, 1*1*0, 1*5^
Roccus saxatilis - A-l*0, 9!*, 220, 229, 252, 256, 277, 380, 383, 399
Rock bass - A-l*l*, 122, Ikk, 171, 195, 209, 352, 1*20
B-9
-------
Rotifers - A-112, 120, 136, 313
Round whitefish - AJ»6, 124, 146, 171, 197, 209, 354,
Salmo aquabonita - A-223
Salmo clarki - A-21, 62, 63, 148, 234, 296
Salmo gairdneri - A-14, 15, 18, 21, 35, 4l, 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, ^05, 4o6, 407, 429, 432, 437, ^39, W*2, 445,
449, 452, 453, 454, 457, 459, ^66, 467, ^68, 469, ^70, U?l, ^72,
^73, ^75, ^76, U77, ^79, ^80, 481, 482, 483, 484, 485, W6, ^88
Salmo salar - A-23, 24, 101, 113, 121, l4l, 155, 266, 355, ^7
Salmo trutta - A-18, 4l, 64, 142, 143, 164, 251, 259, 284, 299, 315,
317, 432, 449
Salvelinus fontinalis - A-18, 62, 98, 107, II1*, 126, 137, 138, 147,
150, 151, 152, 155, 167, 200, 234, 295, 296, 315, 407, 437, ^38,
44l, 448, 459
Salvelinus namaycush - A-18, 30, 51, 55, 83, 96, 309, 310, 3lh, 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 corporalis - A-117, 131, 166
Sialis sp. - A-114, 126, 138, 151, 200, 235
Simulium venustum - A-168
Siphlonurus sp. - A-134, 135
Skeletonema costatum - A-105
Slimy sculpin - A-172, 209
Smallmouth bass - A-46, 124, 145, 197, 353, 421
Smallmouth buffalo - A-45, 123, 144, 196, 261, 352, 420
Sorghum halpense - A-111, 119, 3H
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, 36l
Stlzostedion 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, 14*, 195, 351, 420
Strongylocentrotus franciscanus - A -1*9, 35^
Sturnella neglecta - A-l6l, 363
Sula leucogaster - A -158, 202, 236, 359
Synthliboraraphus antiquum - A-l6l, 362
Taeniopteryx nivalis - A -313
Taeniopteryx maura - A -269
Tendipedldae - A -220
Thalasseus elegans - A -156, 357
Tilapia mossambica - A -169, 205, 287, 368
Trachinotus carolinus - A-5, 93, 252, 383
Trichogaster fascia tus - A -177, 265, 372
Triturus cristatus - A -128, 154
Trout perch - A -173
Tub if ex sp. - A -412
Tubifex tubifex - A-8, 73, 169, 204, 215, 228, 239, 2*4, 259, 277,
286, 300, 318, 3*9, 364, 372, 393, *12, 424, 433
Tubificids - A-267
Tyto alba - A-l6l, 363
Ulothrix sp. - A-8, 203
Uria aalge - A-l6l, 362
Urophycis tenuis - A-121, 355
Urosalpinx cineria - A-68
Volvox - A-179, 26U, 37^
Vorticella - A -112, 120, 136, 313
Walleye - A-U5, 71, 123, 1^5, 173, 196, 210, 353,
Watersipora cucxillata - A-306, U51
Whirligig beetles - A-UO
White bass - A-U5 , 123, 1^5, 173, 197, 210, 353,
White catfish - A-U3, 125, l1^, 19^, 350, lH9
White crappie - A-U5, 123, l1^, 196, 352, U20
White perch - A-U3, 71, 125, lU6, 173, 19^, 210, 350, U18,
White sucker - A-U2, 71, 125, 1U3, 173, 19*, 210, 350, klQ
Wolffia papulifera - A -105, 1*7, 1&* 211, 272, 301, 39*,
Xiphophorus macula tus - A -45 3
Yellow perch - A-U2, 125, 1*6, 173, 19*, 211, 350
Zenaidura macroura - A-l6l, 363
B-ll
-------
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
Acriflavine
Acrolein
Actusol
Aflatoxin Bl
Agridip
Amitrole
Amitrol-T
Amphenone B
Antimycin A
Aphitox
AQ
Aquaclene
Aquaclene 100
Aqualin
Aquathol
Aroclor 1221
Aroclor 12U2
Aroclor 12U8
Aroclor 125^
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,U-diaminoacridine
see Aqualin
No information available
C1TH1206
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
C28HlK)N209
Fluoroacetamide and Lissapol
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 k2 percent
chlorine
Commercial PCB with H8 percent
chlorine
Commercial PCB with 5^ 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,U-D, 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 39007
•Bayluscide
Baytex
Baywood k"$
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
Casol
Casoron
Casoron G
Casoron 133
Chem-Hoe
Chevron NI-0
2-Chloro-U-ethylamine-6-isopropyl-
amino-s-tria z ine
S-2,3 J)ichloroallyl 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
U-Chloro-2-butyny1-m-chlorocarbanilate
No information available
No information available
N-methyl 2 isopropoxyphenyl carbamate
2',5 -Dichloro-V-nitrosalicylanilide
ethanolamine
see Fenthion
Maleic hydrazide, 2,^-D as triethanol,
amine salt, wetting agent, water
No information available
see Betasan
S-(0,0-Diisopropyl phosphorodithioate)
ester of N-(2-mercaptoethyl)
benzene sulfonamide
Benzene hexachloride
No information available
No information available
No information available
No information available
No information available
U-CPA
see QMS-658
3,5 J3ibromo-U-hydroxybenzonitrile
No information available
Organosulfur formulation
No information available
cis-N-((trichloromethyl)thio)-
U-cyclohexene-1,2-dicarboximide
1-Naphthyl methylcarbamate
see Trithion
see Barban
No information available
see Dichlobenil
see Dichlobenil
see Dichlobenil
Isopropyl N-phenylcarbamate
No information available
C-2
-------
Chemical Name
Chloramphenicol
Chloral hydrate
Chloramlne
Chlorax
Chlordane
Chlorea
Chlorfenvinfos
Chloroflurazole
Chloropropylate
Chlorthiamld
CI
Cleanosol
Clophen A30
Clophen Al»0
Clophen A50
Clophen A60
Compass
Cooper's Fly Dip
Co-Ral
Corexit J66k
Corexit 8666
Coumaphos
Craine OSR
Crossguard
Crotothane
Crow Solvent M
Cunilate RQ 2k
Cuprinol
CX
Dalacide
Dalapon
D.B. Granular
DBF
DDD
DDE
DDT
DDVP
Decamethdnium dibromide
De De Tane
Delrad
Composition
(Chloromycetin) D-( -)-threo-2-
dichloroacetamido-1-p-nitrophenyl-
!j 3-propanediol
2,2,2-Trichloro-l,1-ethanediol
(N-Chloro-p-toluenesulf onamido)sodium
No information available
Mixture of 60 percent octachloro-^,7-
methanotetrahydroindane and kO
percent related compounds
see Monuron
2,UJDichlorophenyl-l-chloroethylene
diethy1 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 PCB
No information available
No information available
see Chlorfenvinfos
0,0-Diethyl 0-3-chloro-U-methyl-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
Dalapon-Na, Sodium 2,2,3>trichloro-
propionate
2,2 Dichloropropionic acid
No information available
k,h'-Dichlorobenzophenone
see TDE
1,l-Dichloro-2,2-bis (p-chlorophenyl)
ethylene
1,1,l-Trichloro-2,2-bis(p-chlorophenyl)
ethane
0,0-dimethyl-0-(2,2-dichlorovinyl)
phosphate
No information available
see DDT
Dehydroabiethylamine acetate
c-3
-------
Chemical Name
Delrad 70
Demeton methyl
Dermol
Diazinon
Dicamba
Dicapthon
Dichlobenil
Dichlone
D ichlorofenthion
Dichlorophen
Dichlorvos
Dicofol
Dieldrin
Difolatan
Dlmanln
Dlmecron
Dimethoate
Dimite
Dinocap
Dinoseb
Diphenamld
Dipterex
Diquat
Dlspersol 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
Composition
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-l4~nitrophenyl)0,0-
dimethyl phosphorothioate
2,6-Dichlorobenzonitrile
2,3 J)ichloro-l,U-naphthoquinone
see VC-13
2,2'-Methylenebis [U-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]-
h- cyclohexene-1,2-dicarboximide
Alkyldimethylbenzyl ammonium chloride
plus urea
see Phosphamidon
0,0-Dimethyl S-(N-methylcarbamyl-
methyl) phosphorodithioate
1,l-bis(p-Chlorophenyl)ethanol
see Karathane
2-(sec-Butyl)-U,6-dinitrophenol
N,N-Dimethyl-2,2-diphenylacetamid
see Dylox
6,7-Dehydrodipyrido [l,2a:2',l'c]
pyrazinedium salts
No information available
0,0-Diethyl-S-[2-(ethylthio)-ethyl]
phosphorodithioate
see Disulfoton
3_(3,UJ)ichlorophenyl)-1.1-dimethylurea
2-Methyl-U,6-dinitrophenol sodium salt
No information available
No information available
0-phenylphenol, sodium salt
Sodium pentachlorophenate
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-li*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
EVUC
Fenac
Fenoprop
Fenthion
Fentin acetate
Fenuron
Finasol ESK
Finasol OSR2
Finasol SC
Flock O.P. Fly Dip
Florescein sodium
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,k,3-
benzodioxathiepin-3-oxide
see Endothall
7-Oxabicylo(2.2.1)heptane-2,3-
dicarboxylic acid
1,2,3,k,10,10-Hexachloro-6,7-epoxy-
1,k,Ua,5,6,7,8,8a-octahydro-l,U-endo-
endo - 5 , 8-dime thanonaphthalene
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,Sf-methylene
biophosphorodithioate
No information available
see Parathion
2-(Ethylamino)-U-(isopropylamino)=
6-(methylthio)-s-triazine
2,3,6-Trichlorophenylacetic acid or
sodium salt
No information available
0,0 J)imethyl-0-[ k] (methylthio) -m-
tolyl]-phosphorothioate
No information available
3 Pheny 1-1,1-dimethylurea
No information available
No information available
No information available
see Dichlorofenthion
9-(0-carboxyphenyl)-6-hydroxy-3-
i s oxanthenone
Fluoroacetamide
No information available
No information available
N-(Trichloromethylthio)-phthalimide
Phosphorodithioic acid 0,0-dimethyl
ester S-ester with N-formyl-2-
mercapto-W -methylacetamide
2-Furaldehyde
No information available
No information available
No information available
C-5
-------
Chemical Name
Composition
Gamlen PBX
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
Boughtosolve
Hydrothol 191
IAA
laline Brushweed Killer
laline grass growth regulator
(Regulox)
laline Vergicide Weedkiller D
laline Vergicide Weedkiller
I.C.I. Summer Sheep Dip
loxynil
loxynil Na
IPC
Jansolv-6o
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
T-Chloro-21,U,6-trimethoxy-6'p-
spiro-Oenzofuran^CSH),!1 [2]
cyclohexene]-3* ^'-dione
No information available
0,0-Diethyl-s-[U-oxo-l,2,3-benzotriazin-
3( UH)-ylmethyl]-phosphorodithioate
Jb percent l,U,5,6,7,8.8a-Heptachloro-
3a,U,7a-tetrahydro-4,7-methanoindene
Photoisomer of Heptachlor
3-(Hexahydro-4,7-methanoinden-5-yl)-l,
a-dimethylurea
Di chlorofenthi on
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-^-hydroxybenzonitrile
No information available
see Chem Hoe
No information available
5-Hydroxy-1,h-naphthoquir one
2-(1-Methylheptyl)-b,6-dinitrophenyl
crotonate
see Diuron
see Dicofol
No information available
No information available
Linear alkylate sulfonate
3-Cyclohexyl-6,7-dihydro-lH-
cyclopentapyrimidine-2,(3H,5H)-
dione
1,2,3}b,5,6-Hexachlorocyclohexane
containing at least 99 percent
gamma isomer
C-6
-------
Chemical Name
Linuron
Lirostanol
Lissapol IPA
Lissapol NM
Lissapol NX
Lubrol APNS
Lubrol L
Magic Power
Malathlon
Maleic hydrazide
Manazon
Mancozeb
Maneb
Manoxol
MCPA
Mecarbam
Mecoprop
Menazon
Meta-Systox
Methoxychlor
Methyl parathion
Methylpentynol
Mevinfos (Mevlnphos)
Milbex
MM
Moaspill
Mobilsol
Molinate
Monoxone
Monuron
Morphothion
MS-222
Mystox LSC-P
Mystox LSE-L
Mystox LSE-P
Mystox LSI
Mystox LSL-L
Mystox LSL-P
Composition
3_( 3, lj.-Dichlorophenyl) -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
diethyl mercaptosuccinate
1,2-Dihydro-3,6-pyridazinedione
No information available
No information available
Manganous ethylene bisdithiocarbamate
No information available
2-Methyl-i)-chlorophenoxyacetic acid
No information available
No information available
S-(k, 6 -Diamino-s-triazin-2-yImethy1)
0,0-dimethyl phosphorodithioate
Isomeric mixture of 0-[2-(ethylthio)
ethyl]0,0-dimethyl phosphorothioate
2,2-bis(p-Methoxyphenyl)-1,1,1-
trichloroethane
0,0-Dimethyl 0-p-nitrophenyl
phosphorothioate
No information available ~
2-Carbomethoxy-1-methylvinyl
dimethyl phosphate, aisomer
No information available
No information available
No information available
No information available
see Ordram
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 2^0
Nalco 2U3
Neburon
Nemagon
New BP 1100
Nitrofurazone
Nitrofen
Norea
Norseman
NPH 1253
NPH 1313
Nucidol Diazinon Sheep Dip
Nystatin
OD
Oil Herder
Ordram
Omazene (Omazine)
QMS-658
Paraquat
Parathion
PC
PCB
Pebulate
Penetone X
Perolin No.
Perthane
Petrolite W-
Phenkapton (Phencapton)
Phenobarbital
Phenoxylene
Phenoxytol (Phenoxetol)
Phorate
Phordene
Phosalone
Phosdrin
2-Chloro-l-nit ropropane
No information available
Disodium ethylenebisdithiocarbamate
Chlorinated phenol formulation
Organobromine formulation
Organosulfur formulation
l-n-Butyl-3-(3* 4-dichlorophenyl)-
1-methylurea
1,2-Dibromo-3-chloropropane
No information available
5-Nitro-2-furaldehyde semicarbazone
2,k-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-(U-Bromo-2,5-dichlorophenyl)
0,0-dimethyl phosphorothioate
1,1' -JDimethyl-U,U'-bipyridinium
dichloride or l,l'-Dimethyl-U,V-
bipyridiniumbis [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-
thiomethyl) 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-11
Polyotic
Polyram
Praparat Alfol WV 1019
Princep
Procaine hydrochloride
Pro-Noxfish
Propanil
Propham
Protim
PVP-Iodine
Pyramin
Pyrazon
Pyrimithate
Quinaldine
R-1910
Raynap Sol B
RD 11+639
Reglone
Rhodamine 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
lj-Amino-3,5,6-trichloropicolinic acid
Pyridylmercuric 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 bisfdithiocarbamatic acid],
bimolecular and trimolecular cyclic
anhydrosulfides and disulfides
Hexadecanol
2-Chloro-U,6-bis( ethylamino)-s-triazine
p^Aminobenzoyldiethylaminoethanol
hydrochloride
Rotenone
3,^-Dichloropropionanilide
see Chem Hoe
Copper pentachlorophenate plus
chloronaphthalene and dieldrin
l-Vinyl-2-pyrrolidinone polymers,
iodine complex
5-AminoJuchloro-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
Di quat-dibromide
[ 9-( O^arbaxyphenyl) -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.
Seasweep
Sefoil
Sesamex
Sevin
Shamash R1885
Shell D-50
Silvex
Simazine
Slickgone 1
Slickgone 2
Slix
S.N. 5215
Snowdrift SC98
Spill Remover
Spill-X
Streptomycin Sulfate
Strobane
Sulfieoxazole
Sulmet
Sumithion
Sutan
TCC
TCP
TDE
TEPA '
TEPP
Tetradifon
TFN (Lamprecid)
Thimet
Thiolutin
Thiumet
Thyroxine
Tillam
Timsan
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,k,5-trichlorophenyl)vinyl
dimethyl phosphate
No information available
No information available
No information available
see Carbaryl
No information available
2,h,D amine (triethanolamine salt)
2-(2,U,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 H^N^g.SHpSO^
Terpene poiychlorinates
Nl-(3,4-Dimethyl-5-isoxazolyl)
sulfanilamide
(Sodium sulfamethazine) sodium (U,6-
dimethyl-2-sulfanilamidopyramidine)
0,0-Dimethyl O-(U-nitro-m-tolyl)-
phosphorothioate
S^Ethyl diisobutylthiocarbamate
3,U,U'-Trichlorocarbanilide
Tritolyl phosphate (C21H2iO^P)
l,l-Dichloro-2,2-bis(p-chlorophenyl)
ethane
tris-(l-Aziridinyl)phosphine oxide
Tetraethyl pyrophosphate
k-' -Chlorophenyl 2, k, 5 -trichlorophenyl
sulfone
3-Triflu©romethyl-U-nitrophenol,
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
TDK
Tordon C
Tordon M
Toxaphene
Toxion
Treflan E.G.
Trifluralin
Trioxone
Trithion
Trixabon
Tubotox
Ureabor
Vamidothion
Vapam
VC-13
Velsicol AR 50G
Venzar
Vergemaster
Vernam
Vernolate
Weedazol
Weedazol T-L
WL U205
Young's Defly
Zectran
Zolone
see Nitrofen
Picloram (potassium salt) plus mecoprop
Piclorara (potassium salt) plus MCPA
Chlorinated camphene with 67-69 percent
chlorine
No information available
see Triflurolin
at, at, 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, eraulsifier, methyl alcohol,
propionic acid, and solvent
naphtha
see Dinoseb
No information available
No information available
Sodium N-methyl-dithiocarbamate
0-2,U-Dichlorophenyl 0,0-diethyl
phosphorothi oate
No information available
see Lenacil
No information available
S-Propyl dipropylthiocarbamate
see Vernam
see Amitrole
No information available
A triazine
see Trithion
U-Dimethylamino 3,5-Xylyl methyl-
carbamate
0,OJ)iethyl S[(6-chloro-2-
oxobenzoxazolin-3-yl)methyl]
phosphorodithioate
2,U-Dlchlorophenoxyacetic acid
2,k,5-Trichlorophenoxyacetic acid
C-ll
-------
SELECTED WATER
RESOURCES ABSTRACTS
INPUT TRANSACTION FORM
1. Report No.
w
4 rule WATER QUALITY CRITERIA DATA BOOK - VOL. 5 -
EFFECTS OF CHEMICALS ON AQUATIC LIFE
". VulbonU
Kemp, H. T.| Little, R. L.; Holoman, V, L.| Darby, R. L.
S. K«po.-t Tial'i
6.
8. ferfurmiii;; Orgaouatioii
Report No,
Battalia Mamorlal Institute, Columbus, Ohio
Columbus Laboratories
12. Sponsoring Organization
15. Supp'enu'auu y V.>t-~s
Environmental Protection Agency report number, 18050HLA09/73
R-8009U2
18050 HLA
13, Type ot Report and
Pecioi' CovereJ
16. Abstract
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, 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. (Little-Battelle)
!,.:. Descriptor Toxlcity, 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. Thlocarbamate pesticides, Triazine pesticides, Organophosphorus pesticides,
Polychlorlnated biphenyls, Surfactants, Nutrients. Urea pesticides. Organic compounds,
Organic pesticides, Zooplankton. Phytoplankton. Aquatic algae, Marine algae, Water birds,
Chlorophyta, Pyrrophyta, Cyanophyta. Chrysophyta, Crustaceans, Mollusks, Annelids,
Aquatic insects, Benthlc fauna, Protozoa, Invertebrates, Diatoms, Euglenophyta, Frogs,
Marine animals, Newts, Toxins, Phenolic pesticides, Dyes, Chemicals,
17b. Identifiers
Anesthetics, Oil dlspersants, Echlnoderms, Macroinvertebrates
u'id.i Otcup 05C, 05B, 05A
"19. Seeurify- Class-
•' "
29. Security Class.
- (Page)
31. No. of
; Pagss
22, Price
Send To:
WATER RESOURCES SCIENTIFIC INFORMATION CENTER
U.S. DEPARTMENT OF THE INTERIOR
WASHINGTON. O.C. 2024O
Absuacloi
Robert L. Little
Battelle's Columbus Laboratories, Columbus, Ohio
U. S. GOVERJ1MENT PRINTDJG OFFICE : 1974 72C-125/5U
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