\
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**> &<*,Ł., 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, aeŁ' 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
vŁ>
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)
Ł
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
.Ł-
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
Łndomychura
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
Ł 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 Ł3T-
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)
**' ?'?Ł,*?
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»)
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