TOX-EXP IND - accumulation

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Mallard duck (Anas platyrhynchos)

Citation:

Influence of laying on lead accumulation in bone of mallard ducks

Author(s)
Finley, M.T.; Dieter, M.P.
Pages
123-129
Year
Volume
4
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) one shot: 180.4 (18.1), female; 5.0 (0.6), male
two shot: 183.4 (21.2), female; 15.9 (4.1), male 		mean (SE) lead residues in femur Both Male and Female Adult 20 females, 10 males/group Toxicity Factor Datasets Laboratory
Citation:

Acute effects of lead, steel, tungsten-iron and tungsten-polymer shot administered to game-farm mallards

Author(s)
Kelly, M.E., S.D. Fitzgerald, R.J. Aulerich, R.J. Balander, D.C. Powell, R.L. Stickle, W. Stevens, C. Cray, R.J. Tempelman and S.J. Bursian
Pages
673-687
Year
Volume
34
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS 10.3(0.7) ppm in femur, 14.1(0.6) ppm in liver, 6.8(0.2) in kidneys mean(SE) dry wt tungsten concentrations in tissues of tungsten-iron-dosed birds Both Male and Female Adult 16/treatment Toxicity Factor Datasets 6 mo Laboratory
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS 4.3(0.7) ppm in femur, non-detect. in liver, 2.4(0.2) in kidneys mean(SE) dry wt tungsten concentrations in tissues of tungsten-polymer-dosed birds Both Male and Female Adult 16/treatment Toxicity Factor Datasets 6 mo Laboratory
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS 250.6(39.0) ppm in femur, 78.3(9.7) ppm in liver, 256.3(22.2) in kidneys mean(SE) dry wt lead concentrations in tissues of lead-dosed birds Both Male and Female Adult 16/treatment Toxicity Factor Datasets 6 mo Laboratory
Citation:

Dieldrin and DDT effects on reproduction and some hepatic mixed-function oxidases in the mallard duck

Author(s)
Davison, K.L. and J.L. Sell
Pages
302-314
Year
Volume
2
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
DIELDRIN 0.3 ug/g dry wt. @ 0 ppm; 0.9 - 5.0 @ 1 ppm; 4.1 - 40.1 @ 5ppm; 6.1 - 78.5 @ 10 ppm dieldrin concentrations in egg dry matter ranging from 0-14 d to 330 - 343 d sampling periods at 4 dietary doses Female Adult 18/dose Toxicity Factor Datasets Laboratory
Citation:

Effects of lead shot ingestion on selected cells of the mallard immune system

Author(s)
Rocke, Tonie E. and Michael D. Samuel
Pages
1-9
Year
Issue
1
Volume
27
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
LEAD (elemental) ppm wet wt: 4.15 (3.56), blood; 13.85 (7.96), liver; 577.07 (156.4), femur@ 2 #four shot mean (2SE) lead concentrations in liver, femur and blood Female Adult 5 birds Toxicity Factor Datasets 1 yr Laboratory
Citation:

Sublethal effects of chronic lead ingestion in mallard ducks

Author(s)
Finley, Mack T., Michael P. Dieter and Louis N. Locke
Pages
929-937
Year
Volume
1
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
LEAD NITRATE increased @ 25 ppm/3wks accumulation in livers and kidneys versus controls Male Adult 20/dose; 5/dose x time group Toxicity Factor Datasets 1 yr Laboratory
LEAD NITRATE increased @ 5 ppm diet (66 +/-13 ppm blood) and @ 25 ppm diet (154 +/-28 ppm blood) lead concentration in blood after 12 weeks exposure (mean +/- SE) versus controls Male Adult 20/dose; 5/dose x time group Toxicity Factor Datasets 1 yr Laboratory
Citation:

Acid precipitation and food quality: effects of dietary Al, Ca, and P on bone and liver characteristics in American black ducks and mallards

Author(s)
Sparling, Donald W.
Pages
281-288
Year
Volume
21
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
ALUMINUM SULFATE see table Ca, Al, P concentrations in femur for different treatments after 2 and 10 wks of treatment Not Reported Juvenile 12-14/group Toxicity Factor Datasets Laboratory
Citation:

Hepatic glutathione metabolism and lipid peroxidation in response to excess dietary selenomethionine and selenite in mallard ducklings

Author(s)
Hoffman, David J., Gary H. Heinz and Alexander J. Krynitsky
Pages
263-271
Year
Volume
27
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
SELENITE, SODIUM increased to 0.4 (@ 0 ppm), 5.0 (@ 10 ppm), 3.2 (@ 20 ppm), 2.8 (@ 40 ppm) ppm, wet wt Se concentrations in livers after 6 wks of treatment versus controls Not Reported Juvenile 40 birds/group Toxicity Factor Datasets day old Laboratory
Citation:

Effects of dieldrin in food on growth and bioaccumulation in mallard ducklings

Author(s)
Nebeker, A.V., K.D. Dunn, W.L. Griffis and G.S. Schuytema
Pages
29-32
Year
Volume
26
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
DIELDRIN 80.7 ug/g lipid, 30.1 ug/g skin, 1.6 ug/g brain, 4.1 ug/g liver, 1.8 ug/g muscle at 49.3 ug/g food mean of day 5, 7, 8 (approx. steady state) tissue concentrations Not Reported Juvenile 6 Toxicity Factor Datasets 1 d Laboratory
Citation:

Lead exposure of waterfowl ingesting Coeur d'Alene River basin sediments

Author(s)
Beyer, W. Nelson, Daniel J. Audet, Anna Morton, Julie K. Campbell and Leonard LeCaptain
Pages
1533-1538
Year
Volume
27
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
LEAD COMPOUNDS Equation: fecal Pb conc./fecal acid insoluble ash content = 61 + (1.06 x sediment Pb conc.) relation between waterfowl fecal lead concentration (dry wt) and sediment lead concentration (dry wt) Not Reported Not Reported 521 fecal analyses at 11 wetlands (at least 20 per wetland) Coeur d'Alene and St. Joe River Basins Toxicity Factor Datasets
Citation:

Subchronic effects of sodium selenite and selenomethionine on several immune functions in mallards.

Author(s)
Fairbrother, A. and J. Fowles
Pages
836-844
Year
Volume
19
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
SELENOMETHIONINE increased (12-fold) selenium concentrations in pectoral muscle Male Adult Controls = 24
Treated = 8 		Laboratory Toxicity Factor Datasets Laboratory
Citation:

Effects of cadmium ingestion and food restriction on energy metabolism and tissue metal concentrations in mallard ducks (Anas platyrhynchos)

Author(s)
Di Giulio, R.T. and P.F. Scanlon
Pages
433-444
Year
Volume
37
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
CADMIUM CHLORIDE increased @ 10, 50 ug/g diet liver cadmium concentration versus controls Male Adult 8 Toxicity Factor Datasets 32 weeks Laboratory
CADMIUM CHLORIDE no effect liver Cu concentration versus controls Male Adult 8 Toxicity Factor Datasets 32 weeks Laboratory
CADMIUM CHLORIDE no effect liver Zn concentration versus controls Male Adult 8 Toxicity Factor Datasets 32 weeks Laboratory
CADMIUM CHLORIDE increased @ 10, 50 ug/g diet kidney Cd concentration versus controls Male Adult 8 Toxicity Factor Datasets 32 weeks Laboratory
Citation:

Accumulation and excretion of Cl36 DDT in mallard and lesser scaup duck

Author(s)
Dindal, Daniel L.
Pages
74-92
Year
Volume
34
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
DDT (Technical Grade Mixture) see citation table of DDE, DDD and DDT residues in 21 tissues following varying times after application Not Reported Not Reported 1-6/sample Sandusky Bay, Port Clinton Toxicity Factor Datasets
Citation:

Effects of ingested lead on antibody production in mallards (Anas platyrynchos)

Author(s)
Trust, Kimberly A., Michael W. Miller, James K. Ringelman and Ian M. Orme
Pages
316-322
Year
Issue
3
Volume
26
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) increased @ 7, 14, 21 d post-dose concentration of lead in blood versus controls Male Adult 4/group Toxicity Factor Datasets Laboratory
Citation:

Effects of dietary nickel on mallards

Author(s)
Eastin, William C., Jr. and Thomas J. O'Shea
Pages
883-892
Year
Volume
7
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
NICKEL SULFATE increased @ 12.5, 50, 200, 800 ppm diet kidney, blood, liver, and feather concentrations of Ni compared to controls Both Male and Female Adult 6 pairs/group Toxicity Factor Datasets Laboratory
NICKEL SULFATE 1.94 (kidney), 0.52 (liver), 0.139 (blood), 68.06 (feathers) ppm, wet wt mean tissue concentrations @ 800 ppm Ni in diet Both Male and Female Adult 6 pairs/group Toxicity Factor Datasets Laboratory
Citation:

Effects of dietary cadmium on mallard ducklings

Author(s)
Cain, Brian W., Lou Sileo, J. Christian Franson and John Moore
Pages
286-297
Year
Volume
32
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
CADMIUM CHLORIDE 0.10 (@ 0 ppm), 10.13 (@ 5 ppm), 16.25 (@ 10 ppm), 42.21 (@ 20 ppm) ppm, wet wt mean Cd concentrations in liver by 12 wks of treatment Not Reported Juvenile 12 birds per timexdose treatment day old Toxicity Factor Datasets Laboratory
Citation:

Comparison of game-farm and wild-strain mallard ducks in accumulation of methylmercury

Author(s)
Heinz, Gary H.
Pages
379-386
Year
Volume
3
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
METHYLMERCURY DICYANDIAMIDE 0.51-0.54 ppm blood, 2.07-2.41 ppm kidney, 2.35-2.26 ppm liver, 0.74-0.97 ppm breast muscle, 0.47-0.51 ppm brain, 0.88 ppm eggs @ 0.5 ppm in diet range of mean Hg (ppm wet-weight) concentrations in wild-strain males and females Both Male and Female Adult 6-9 (9 breeding pairs/dose) Toxicity Factor Datasets Laboratory
Citation:

Toxicity of lead shot to wild black ducks and mallards fed natural foods.

Author(s)
Chasko, G.G., T.R. Hoehn and P. Howell-Heller
Pages
417-428
Year
Volume
32
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) increased @ all doses Pb concentrations in wing bone and liver Both Male and Female Not Reported 5-6/group Toxicity Factor Datasets Laboratory
Citation:

Effects of lead, iron, and bismuth allow shot embedded in the breast muscles of game-farm mallards

Author(s)
Sanderson, Glen C., William L. Anderson, George L. Foley, Stephen P. Havera, Loretta M. Skowron, Jeffrey W. Brawn, Gale D. Taylor and James W. Seets
Pages
688-697
Year
Volume
34
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) 130(10.1) ppm in kidneys, 0.19(0.06) ppm in liver mean(SE) wet wt concentration of bismuth in organs Both Male and Female Adult 5 males, 5 females per group Toxicity Factor Datasets 6-8 mo Laboratory
Citation:

Biological elimination rates of radioisotopes by mallards contaminated at a liquid radioactive waste disposal area

Author(s)
Halford, Douglas K., O. Doyle Markham and Gary C. White
Pages
745-756
Year
Volume
45
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
RADIONUCLIDES 131I 10d; 140Ba 22d; 51Cr 86d; 58Co 32d; 75Se 26d; 65Zn 67d; 134Cs 10d; 60Co 67d; 137Cs 11 d mean biological half-lives for whole-body retention of 9 radionuclides; ducks exposed in field for varying time periods then depurated in laboratory to determine half-life Both Male and Female Not Reported 4-6/sample Idaho National Engineering Lab Toxicity Factor Datasets
Citation:

Effects on wildlife from use of endrin in Washington state orchards

Author(s)
Blus, Lawrence J., Charles J. Henny, T. Earl Kaiser and Robert A. Grove
Pages
159-174
Year
Volume
48
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
ENDRIN breast muscle=non-detect.; liver=non-detect.-0.05; fat=non-detect.-0.50 ppm, wet wt tissue endrin residues Not Reported Not Reported 7-10 animals Wenatchee Toxicity Factor Datasets
Citation:

Effects of dietary mercury and lead on eggshell thickness in mallards

Author(s)
Haegele, Max A., Richard K. Tucker and R.H. Hudson
Pages
5-11
Year
Issue
1
Volume
11
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
DDE (4,4'-) 78.2 (carcass); 61.6 (egg); 4.1 (brain) ppm, wet wt DDE residues in whole carcass, egg contents, and brain Female Adult 10/group Toxicity Factor Datasets Laboratory
MERCURY COMPOUNDS 2.5 (carcass); 1.25 (egg); 23.7 (kidney) ppm, wet wt mercury residues in whole carcass, egg contents, and kidneys Female Adult 10/group Toxicity Factor Datasets Laboratory
LEAD COMPOUNDS 3.7 (carcass); 2.5 (egg); 2.5 (eggshells); 9.6 (bone) ppm, wet wt @ 100 ppm lead;
3.4 (carcass); 0.88 (egg); 2.8 (eggshells); 35.0 (bone) ppm, wet wt @ 100 ppm lead + DDE 		lead residues in whole carcass, egg contents, eggshells, and bone Female Adult 10/group Toxicity Factor Datasets Laboratory
Citation:

Subchronic hepatotoxicity of selenomethionine ingestion in mallard ducks

Author(s)
Hoffman, David J., Gary H. Heinz, Leonard J. LeCaptain, Christine M. Bunck and David E. Greene
Pages
449-464
Year
Volume
32
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
SELENOMETHIONINE increased @ 2 ppm or greater Se concentrations in liver versus controls Male Adult 10 birds/group Toxicity Factor Datasets 2 yr Laboratory
Citation:

DDE feeding and plasma osmoregulation in ducks, guillemots and puffins

Author(s)
Miller, David S., William B. Kinter, David B. Peakall and Robert W. Risebrough
Pages
370-376
Year
Volume
231
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
DDE (4,4'-) 10.6 +/- 2.2 ppm nasal gland, 16.1 +/- 5.1 ppm liver, 5.8 +/- 1.1 ppm kidney, 1.9 +/- 0.1 ppm brain @ 100 ppm diet mean (+/- SE) DDE levels (ppm wet weight) Both Male and Female Juvenile 4 Toxicity Factor Datasets 3-5 mo Laboratory
Citation:

Comparison of the effects of seleno-L-methionine, seleno-D,L-methionine, and selenized yeast on reproduction in mallards

Author(s)
Heinz, Gary H. and David J. Hoffman
Pages
169-175
Year
Volume
91
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
SELENIUM COMPOUNDS, SELENOMETHIONINE 9.2(0.52) ppm with seleno-D,L-methionine; 8.9(0.35) ppm with seleno-L-methionine; 6.6(0.37) ppm with selenized yeast mean(SE) wet wt concentrations of selenium in 8th egg laid Female Adult 15 pairs/treatment group, 10 pairs/control group Toxicity Factor Datasets Laboratory
Citation:

Selenium accumulation and elimination in mallards

Author(s)
Heinz, G.H., G.W. Pendleton, A.J. Krynitsky and L.G. Gold
Pages
374-379
Year
Volume
19
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
SELENOMETHIONINE liver: C = 7.4(1-e^-0.382t)
muscle: C = 8.0(1-e^-0.037t) 		selenium accumulation equations Both Male and Female Adult 3 Toxicity Factor Datasets Laboratory
SELENOMETHIONINE liver: C = 7.4e^-0.037t
muscle: C = 5.6e^-0.023t
liver at peak body burden: C = 22.6e^-0.246t + 2.5 e^-0.008t
muscle at peak body burden: C = 6.4e^-0.029t
Loss phase for blood at peak body burden: C = 12.0e^-0.071t 		selenium depuration equations Both Male and Female Adult 3 Toxicity Factor Datasets Laboratory
SELENOMETHIONINE liver: 18.7 d
muscle: 30.1 d 		half life of selenium in tissues Both Male and Female Adult 3 Toxicity Factor Datasets Laboratory
Citation:

Elimination of endrin by mallard ducks

Author(s)
Heinz, Gary H. and Richard W. Johnson
Pages
189-196
Year
Volume
12
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
ENDRIN see citation figures of carcass and blood endrin concentrations during elimination period (0-64d) Male Adult 2-5/sample Toxicity Factor Datasets 1 yr Laboratory
Citation:

Effects of dietary nickel on survival and growth of mallard ducklings

Author(s)
Cain, Brian W. and Ellen A. Pafford
Pages
737-745
Year
Volume
10
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
NICKEL SULFATE 1.0-22.7 (liver), 2.7-74.4 (kidney) ppm, wet wt Ni concentrations (ranges) in liver and kidney in ducklings that died @ 1200 ppm Both Male and Female Juvenile 36 birds/dose Toxicity Factor Datasets 14 d Laboratory
Citation:

Interactive effects of boron, selenium, and dietary protein on survival, growth, and physiology in mallard ducklings

Author(s)
Hoffman, David J., Caroline J. Sanderson, Leonard J. LeCaptain, Eugene Cromartie and Grey W. Pendleton
Pages
288-294
Year
Volume
20
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
BORIC ACID, SELENOMETHIONINE 10.8 (@ 15 ppm Se), 56.0 (@ 60 ppm) ppm Se, wet wt
11.0 (@ 1000 ppm B) ppm B, wet wt 		geometric mean Se and B concentrations in liver Not Reported Juvenile 15 birds/group Toxicity Factor Datasets day old Laboratory
BORIC ACID, SELENOMETHIONINE 22.5 (@ 15 ppm Se w/out B), 41.9 (@ 15 ppm Se w/B) ppm Se, wet wt
13.0 (@ 1000 ppm B) ppm B, wet wt 		geometric mean Se and B concentrations in liver Not Reported Juvenile 15 birds/group Toxicity Factor Datasets day old Laboratory
Citation:

Effect of DDE on the Ca metabolism of the duck eggshell gland and its subcellular fractions; Relations to the functional stage

Author(s)
Lundholm, C.E.
Pages
5-12
Year
Volume
78
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
DDE (4,4'-) 1.23 +/- 0.12 ug/g wet weight mean +/- SE p,p'-DDE concentration in shell gland mucosa Female Adult Not Reported Toxicity Factor Datasets 1 yr Laboratory
Citation:

Toxicity of white phosphorus to waterfowl: Acute exposure to mallards

Author(s)
Sparling, Donald W., Mary Gustafson, Patrice Klein and Natalie Karouna-Renier
Pages
187-197
Year
Volume
33
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
PHOSPHORUS (YELLOW OR WHITE) positive correlation P4 concentration in fat versus dose Male Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
Citation:

Methylmercury chloride and selenomethionine interactions on health and reproduction in mallards

Author(s)
Heinz, Gary H., and David J. Hoffman
Pages
139-145
Year
Issue
2
Volume
17
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
METHYLMERCURY CHLORIDE, SELENOMETHIONINE 7.6(0.26) ppm, egg, 6.0(0.31) ppm, fem. liver, 9.6(0.95) ppm, male liver @ 10 ppm Se; 9.3(0.85) ppm, egg, 9.2(1.61) ppm, female liver, 114(25.3) ppm, male liver @ 10 ppm Se + 10 ppm Hg mean(SE) wet wt concentration of Se in egg and liver of treated birds Both Male and Female Adult 12/group Toxicity Factor Datasets 18 mo Laboratory
METHYLMERCURY CHLORIDE, SELENOMETHIONINE 16(0.8) ppm, egg, 22(1.5) ppm, fem. liver, 71(8.9) ppm, male liver @ 10 ppm Hg; 17(0.6) ppm, egg, 21(4.3) ppm, female liver, 65(4.1) ppm, male liver @ 10 ppm Se + 10 ppm Hg mean(SE) wet wt concentration of Hg in egg and liver of treated birds Both Male and Female Adult 12/group Toxicity Factor Datasets 18 mo Laboratory
Citation:

Aroclor 1242 and reproductive success of adult mallards (Anas platyrhynchos)

Author(s)
Haseltine, Susan D. and Richard M. Prouty
Pages
29-34
Year
Volume
23
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
AROCLOR 1242 105.0 (7.7 SE) mg Aroclor 1260/kg egg @ 150 ppm PCB concentration in eggs (PCB resembled Aroclor 1260 profile most closely) Female Adult 12 pairs/dose Toxicity Factor Datasets Laboratory
Citation:

Behavior of mallard ducklings from parents fed 3 ppm DDE

Author(s)
Heinz, Gary H.
Pages
640-645
Year
Volume
16
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
DDE (4,4'-) 0.021 - 0.028 ppm wet wt @ 0 ppm; 5.8 (0.32 SE; range 4.28-7.23) ppm wet wt @ 3 ppm mean and range of DDE egg concentrations Female Adult 8 eggs/dose Toxicity Factor Datasets 10 mo Laboratory
Citation:

Uptake and retention of dietary cadmium in mallard ducks

Author(s)
White, Donald H. and Mack T. Finley
Pages
53-59
Year
Volume
17
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
CADMIUM CHLORIDE 2.116 (@ 2 ppm), 19.510 (@ 20 ppm), 96.600 9@ 200 ppm) ppm, wet wt mean Cd concentrations in liver after 90 d of treatment Both Male and Female Adult 20 pairs/group Toxicity Factor Datasets 1 yr Laboratory
CADMIUM CHLORIDE 4.627 (@ 2 ppm), 54.333 (@ 20 ppm), 77.222 (@ 200 ppm) ppm, wet wt mean Cd concentrations in kidneys after 90 d of treatment Both Male and Female Adult 20 pairs/group Toxicity Factor Datasets 1 yr Laboratory
Citation:

Effect of p-p'-DDE administered in vivo and in vitro on Ca2+ binding and Ca2+-Mg2+-ATPase activity in egg shell gland mucosa of ducks

Author(s)
Lundholm, C.E.
Pages
121-129
Year
Volume
50
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
DDE (4,4'-) 38 ug/g wet weight egg (yolk + white), 1.20 ug/g wet weight egg shell gland mucosa @ 40 mg/kg mean DDE concentrations Female Adult 7-9 Toxicity Factor Datasets 1 yr Laboratory
Citation:

Reproductive success and nest attentiveness of mallard ducks fed Aroclor 1254

Author(s)
Custer, Thomas W. and Gary H. Heinz
Pages
313-318
Year
Volume
21
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
AROCLOR 1254 55-65 ppm range of wet wt concentrations of Aroclor 1254 in adult carcasses Both Male and Female Adult 22 pairs Toxicity Factor Datasets Laboratory
Citation:

Tissue residues of lindane in domestic duck (Anas platyrhynchos domesticus) following its repeated oral administration

Author(s)
Mandal, Aditya, Jagadbandhu Chakrabarti and Pulak Lahiri
Pages
56-57
Year
Volume
26
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Condition Lab
LINDANE serum (0.13); fat (0.20); muscle (0.70); kidney (0.02); liver (0.02); brain (0.01) ppm @ 20 mg/kg 2x/wk mean lindane residue levels Female Adult 5/dose Toxicity Factor Datasets laying Laboratory
Citation:

Lead poisoning in waterfowl from the Ebro Delta, Spain: Calculation of lead exposure thresholds for mallards

Author(s)
Guitart, R., J. To-Figueras, R. Mateo, A. Bertolero, S. Cerradelo and A. Martinez-Vilalta
Pages
289-293
Year
Volume
27
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Countries
LEAD COMPOUNDS 0.822 (0.059-21.60) ppm wet wt geometric mean liver concentration (range) Not Reported Not Reported 39 birds Ebro Delta Natural Park Toxicity Factor Datasets ITALY
Citation:

Effects of arsenate on growth and physiology in mallard ducklings

Author(s)
Camardese, Michael B., David J. Hoffman, Leonard J. LeCaptain and Grey W. Pendleton
Pages
785-795
Year
Volume
9
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
ARSENATE, SODIUM increased @ 100 ppm ( 0.4 ppm, dry wt), 300 ppm (0.8 ppm, dry wt) accumulation of arsenic in brain tissue (geometric means in parentheses) Both Male and Female Juvenile 30 birds/group Toxicity Factor Datasets Laboratory
Citation:

Effects of boron on growth and physiology in mallard ducklings

Author(s)
Hoffman, David J., Michael B. Camardese, Leonard J. Lecaptain
Pages
335-346
Year
Volume
9
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
BORIC ACID 2 ug/g @ control; 4 ug/g @ 100 ppm; 5 ug/g @ 400 ppm; 51 ug/g @ 1600 ppm boron accumulation in brain (geometric mean; ug/g dry weight) Both Male and Female Juvenile 10 animals/pen; 3 pens/dose Toxicity Factor Datasets 1 d Laboratory

Double-crested Cormorant (Phalacrocorax auritus)

Citation:

Insecticides, polychlorinated biphenyls, and mercury in wild cormorants, pelicans, their eggs, food and environment

Author(s)
Greichus, Yvonne A. Greichus and R.J. Emerick
Pages
321-328
Year
Issue
6
Volume
9
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific
MERCURY (elemental), POLYCHLORINATED BIPHENYLS 14 Ratio of concentration in carcass (0.64 ppm wet wt mercury) to dietary concentration (fish) Not Reported Adult 10 carcasses Lake Pointsett, Dry Lake Toxicity Factor Datasets
MERCURY (elemental), POLYCHLORINATED BIPHENYLS 0.29 ppm wet wt mercury mean concentration in eggs Female Adult 5 eggs Lake Pointsett, Dry Lake Toxicity Factor Datasets
MERCURY (elemental), POLYCHLORINATED BIPHENYLS 0.28 ppm wet wt mercury concentration in liver Not Reported Nestling 5 birds Lake Pointsett, Dry Lake Toxicity Factor Datasets 2-4 wks old
MERCURY (elemental), POLYCHLORINATED BIPHENYLS 7.98 ppm wet wt mercury concentration in liver Both Male and Female Adult 5 birds Lake Pointsett, Dry Lake Toxicity Factor Datasets

Mourning Dove (Zenaida macroura)

Citation:

Effects of diet and cold exposure on captive female mourning doves dosed with lead shot

Author(s)
Marn, Carolyn M., Ralph E. Mirarchi and Michael E. Lisano
Pages
589-594
Year
Volume
17
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) 2.80-4.98 ug/g, dry wt mean lead concentrations in liver (greater accumulation with mixed seed vs. pelleted diet) Female Adult 12/group Toxicity Factor Datasets Laboratory
LEAD (elemental) 47.2-190.7 ug/g, dry wt mean lead concentrations in kidney (greater accumulation with mixed seed vs. pelleted diet) Female Adult 12/group Toxicity Factor Datasets Laboratory
Citation:

Effects of lead shot ingestion on captive mourning dove survivability and reproduction

Author(s)
Buerger, Theodore T., Ralph E. Mirarchi and Michael E. Lisano
Pages
1-8
Year
Issue
1
Volume
50
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Error Lab
LEAD (elemental) 169.2 ug/g, dry wt. lead concentration in bone Not Reported Adult 10 birds Toxicity Factor Datasets 33.9 SE Laboratory
LEAD (elemental) 198.2 ug/g, dry wt lead concentration in bone Not Reported Adult 10 birds Toxicity Factor Datasets 39.9 SE Laboratory
Citation:

Histologic and ultrastructural lesions of mourning doves (Zenaida macroura) poisoned by lead shot

Author(s)
Kendall, Ronald J., Patrick F. Scanlon and Hugo P. Veit
Pages
952-956
Year
Issue
6
Volume
62
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) 639.43 and 345.95 ug/g, dry wt lead concentration in kidneys of treated birds Not Reported Not Reported 2 Toxicity Factor Datasets Laboratory
LEAD (elemental) 58.35 and 214.71 ug/g, dry wt lead concentrations in livers of dosed birds Not Reported Not Reported 2 Toxicity Factor Datasets Laboratory
Citation:

Some effects of aldrin-treated rice on gulf coast wildlife

Author(s)
Flickinger, Edward L. and Kirke A. King
Pages
706-727
Year
Issue
3
Volume
36
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
ALDRIN, DIELDRIN <0.1 ppm aldrin, 3.8 ppm dieldrin, 0.3 ppm DDT and metabolites, wet wt post-mortem whole body concentrations Not Reported Not Reported 1 bird Toxicity Factor Datasets

American Kestrel (Falco sparverius)

Citation:

Polychlorinated biphenyl (PCB) effects on hepatic mixed function oxidases and porphyria in birds - II. American kestrel

Author(s)
Elliot, J.E., S.W. Kennedy, D. Jeffrey and L. Shutt
Pages
141-145
Year
Issue
1/2
Volume
99
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) 2.4 (control), 119.0 (PCB 153), 182.0 (PCB 105), 3.3 (PCB 126) mg/kg, wet weight PCB concentrations in pooled adipose tissue Female Adult 5-6/group Toxicity Factor Datasets 1 yr Laboratory
Citation:

Developmental Toxicity of PCB 126 (3,3',4,4',5-Pentachlorobiphenyl) in nestling American kestrels (Falco sparverius)

Author(s)
Hoffman, David J., Mark J. Melancon, Patrice N. Klein, Clifford P. Rice, John D. Eisemann, Randy K. Hines, James W. Spann, and Grey W. Pendleton
Pages
188-200
Year
Volume
34
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) in ng/g, wet wt: 156 (@ 50 ng/g), 380 (@ 250 ng/g), 1098 (@1000 ng/g) concentration in liver Not Reported Nestling 9-11/group Toxicity Factor Datasets Day 1-Day 10 Laboratory
Citation:

DDE at Low Dietary Levels Kills Captive American Kestrels

Author(s)
Porter, Richard D. and Stanley N. Wiemeyer
Pages
193-199
Year
Issue
4
Volume
8
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
DDE (4,4'-) 984.1-1438.6 ppm (dry wt) brain residues in birds that died Male Adult 2 Toxicity Factor Datasets Laboratory
DDE (4,4'-) 232.9 ppm (dry wt) mean brain residues in birds that survived Male Adult 11 Toxicity Factor Datasets Laboratory
DDE (4,4'-) 507-877.1 ppm (dry wt) liver residues in birds that died Male Adult 2 Toxicity Factor Datasets Laboratory
DDE (4,4'-) 88.1 ppm (dry wt) mean liver residues in birds that survived Male Adult 11 Toxicity Factor Datasets Laboratory
Citation:

Accumulation and effects in birds

Author(s)
Peakall, D.B.
Pages
31-47
Publisher
CRC Press, Inc.
Year
Chemical Endpoint Value Location Type
POLYCHLORINATED BIPHENYLS review Toxicity Factor Datasets
Citation:

Survival, growth, and accumulation of ingested lead in nestling American kestrels (Falco sparverius)

Author(s)
Hoffman, David J., Christian J. Franson, Oliver H. Pattee, Christine M. Bunck and Allen Anderson
Pages
89-94
Year
Volume
14
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) increase at all doses
1.4, 3.5, 5.5 ppm at 25, 125, 625 mg/kg bw, respectively 		liver lead concentration Both Male and Female Nestling 10/group Toxicity Factor Datasets Laboratory
LEAD (elemental) increase at 125, 625 mg/kg bw
7.2, 15.5 ppm at 125, 625 mg/kg bw, respectively 		kidney lead concentrations Both Male and Female Nestling 10/group Toxicity Factor Datasets Laboratory
Citation:

Eggshell modifications in captive American kestrels resulting from Aroclor 1248 in the diet

Author(s)
Lowe, Peter T. and Rey C. Stendell
Pages
519-522
Year
Volume
20
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
AROCLOR 1248 18.5 ug/g (5.1SD), PCBs; 0.10 ug/g (0.03 SD), dieldrin;1.02 ug/g (0.39 SD), DDE @ 3.0 ug/g mean carcass concentrations, wet wt Both Male and Female Adult 8 pairs/group Toxicity Factor Datasets Laboratory
AROCLOR 1248 5.60 ug/g (1.15 SD), PCBs; 0.15 ug/g (0.05 SD), dieldrin; 0.15 ug/g (0.07 SD), DDE @ 3.0 ug/g mean egg concentrations, wet wt Female Adult 8 pairs/group Toxicity Factor Datasets Laboratory
Citation:

Eggshell thickness and reproduction in American kestrels exposed to chronic dietary lead

Author(s)
Pattee, Oliver H.
Pages
29-34
Year
Volume
13
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) no effect lead concentration in eggshell Female Adult 16 pairs/group Toxicity Factor Datasets Laboratory
LEAD (elemental) 62.0 ppm tibia, 13.5 ppm humeri at 50 ppm lead concentrations in bones Female Adult 16 pairs/group Toxicity Factor Datasets Laboratory
Citation:

Effects of chronic dietary lead in American kestrels (Falco sparverius)

Author(s)
Franson, J. Christian, Louis Sileo, Oliver H. Pattee and John F. Moore
Pages
110-113
Year
Issue
2
Volume
19
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
LEAD (elemental) increase at 50 ppm
1.3 ppm (1.00 SD) males; 2.4 ppm (1.40 SD) females 		mean lead concentration in liver Both Male and Female Adult 16 pairs/group Toxicity Factor Datasets Laboratory
Citation:

Metabolism and storage of p,p' dicofol

Author(s)
Schwarzbach, S.E., D. Michael Fry, B.E. Rosson and David M. Bird
Pages
206-210
Year
Volume
20
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
DICOFOL 8.11 (fat), 0.28 (liver) ug/g @ 0.3 mg/kg bw/d sum of geometric mean tissue concentrations (wet wt) of dicofol and metabolites (dichlorobenzophenone, mono-dechlorinated dicofol, dichlorobenzhydrol, DDE) Female Adult 2-4/group Toxicity Factor Datasets Laboratory
DICOFOL 82.36 (fat), 4.93 (liver), 1.15 (brain), 0.84 (oviduct) ug/g @ 3.0 mg/kg bw/d sum of geometric mean tissue concentrations (wet wt) of dicofol and metabolites (dichlorobenzophenone, mono-dechlorinated dicofol, dichlorobenzhydrol, DDE) Female Adult 2-4/group Toxicity Factor Datasets Laboratory
Citation:

Tissue lead distribution and hematologic effects in American kestrels (Falco sparverius L.) fed biologically incorporated lead

Author(s)
Custer, Thomas W., J.Christian Franson, and Oliver H. Pattee
Pages
39-43
Year
Issue
1
Volume
20
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
LEAD COMPOUNDS 1.13 ppm blood at 212 ppm; 1.69 ppm blood at 448 ppm mean lead concentration in blood Both Male and Female Adult 8-14/group Toxicity Factor Datasets 1-2 yr Laboratory
Citation:

Accumulation of lead and organochlorine residues in captive American kestrels fed pine voles from apple orchards

Author(s)
Stendell, Rey C., W. Nelson Beyer and Robert A. Stehn
Pages
388-391
Year
Issue
3
Volume
25
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS 1.05 (0.05 SE) ppm (wet wt) lead concentration in liver Female Juvenile 2 Toxicity Factor Datasets Laboratory
Citation:

Lead in hawks, falcons and owls downstream from a mining site on the Coeur D'Alene River, Idaho

Author(s)
Henny, Charles J., Lawrence J. Blus, David J. Hoffman and Robert A. Grove
Pages
267-288
Year
Volume
29
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
LEAD COMPOUNDS 0.24 ug/g at study area,
0.087 ug/g at reference area 		mean lead concentration in blood (wet wt) Both Male and Female Nestling 30 (study area)
22 (reference) 		Coeur D'Alene River Toxicity Factor Datasets

Peregrine Falcon (Falco peregrinus)

Citation:

A toxicological assessment of peregrine falcons, Falco peregrinus tundrius, breeding in the Keewatin District of the Northwest Territories, Canada

Author(s)
Court, G.S., C.C. Gates, D.A. Boag, J.D. MacNeil, D.M. Bradley, A.C. Fesser, J.R. Patterson, G.B. Stenhouse, and L.W. Oliphant
Pages
255-272
Year
Issue
2
Volume
104
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS log DDE in eggs = 0.9723 + 0.8506(log DDE in plasma); r = 0.66 log-log relationship between DDE in plasma of female birds and DDE in eggs Female Adult 10 females Rankin Inlet Toxicity Factor Datasets
Citation:

DDE in a resident Aleutian Island peregrine population

Author(s)
White, Clayton M., William B. Emison, and Francis S.L. Williamson
Pages
306-311
Year
Volume
75
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
DDE (4,4'-) 1.89 (1.27-2.43) -6.96 (3.28-13.37) ppm, wet wt annual mean (range) concentrations in eggs Female Adult 3-6 eggs/year Amchitka Island Toxicity Factor Datasets
Citation:

Chlorinated hydrocarbons in peregrines and their prey species from northern Canada

Author(s)
Enderson, James H. and Daniel D. Berger
Pages
149-153
Year
Issue
2
Volume
70
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Condition Countries
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE 0.9-7.2 (DDT); 10.4-41.8 (DDE); 0.9-3.4 (DDD); 0.3-2.0 (dieldrin); 0.2-1.2 (heptachlor epoxide) range of concentrations in eggs (ppm, wet wt) Female Adult 7 eggs Peace, Slave, and Mackenzie Rivers Toxicity Factor Datasets CANADA
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE 37.3 (DDT), 284 (DDE), 39.5 (DDD), 3.3 (dieldrin), 4.4 (heptachlor epoxide) mean residue concentrations in fat (ppm, wet wt) Female Adult 9 birds Peace, Slave, and Mackenzie Rivers Toxicity Factor Datasets nesting CANADA
Citation:

Peregrines and pesticides in Alaska

Author(s)
Cade, Tom J., Clayton M. White, and John R. Haugh
Pages
170-178
Year
Issue
2
Volume
70
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN 48.0 (DDE), 3.35 (DDD), 1.02 (DDT), 1.45 (dieldrin) mean concentrations of pesticides in eggs (ppm, dry weight) Female Adult 2 eggs Yukon River Toxicity Factor Datasets

Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)

Citation:

Teratogenesis, toxicity and bioaccumulation in frogs exposed to dieldrin

Author(s)
Schuytema, Gerald S., Alan V. Nebeker, William L. Griffis and Karsten N. Wilson
Pages
332-350
Year
Volume
21
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
DIELDRIN 360 - 900 range of bioconcentration factors; calculated by dividing the whole body tissue dieldrin concentration by water dieldrin concentration Not Reported Tadpole 20 animals/replicate; 4 replicates/dose Toxicity Factor Datasets 29 d Laboratory
DIELDRIN 36,000 - 90,000 range of lipid bioconcentration factors; calculated by dividing the whole body bioconcentration values x 100 by percent lipid Not Reported Tadpole 20 animals/replicate; 4 replicates/dose Toxicity Factor Datasets 29 d Laboratory

Great Horned Owl (Bubo virginianus)

Citation:

Productivity and survival of great horned owls exposed to dieldrin

Author(s)
Frank, Rosemary A. and R. Scott Lutz
Pages
331-339
Year
Volume
101
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
DIELDRIN 0.07 +/- 0.03 ppm (uncontaminated site); 0.34 +/- 0.21 ppm (contaminated site) mean (+/- SE) concentrations in plasma Not Reported Adult 2 birds on contaminated sites; 5 birds on uncontaminated sites Rocky Mountain Arsenal National Wildlife Refuge Toxicity Factor Datasets
DIELDRIN 0.01 +/- 0.003 ppm (uncontaminated site); 0.22 +/- 0.03 ppm (contaminated site) mean (+/- SE) concentrations in plasma Not Reported Juvenile 6 birds on contaminated sites; 10 birds on uncontaminated sites Rocky Mountain Arsenal National Wildlife Refuge Toxicity Factor Datasets
Citation:

Effects on wildlife from use of endrin in Washington state orchards

Author(s)
Blus, Lawrence J., Charles J. Henny, T. Earl Kaiser and Robert A. Grove
Pages
159-174
Year
Volume
48
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
ENDRIN breast muscle=0.02 ppm, wet wt tissue endrin residues Not Reported Not Reported 1 animal Wenatchee Toxicity Factor Datasets

California Ground Squirrel (Spermophilus beecheyi)

Citation:

Fluoroacetate residues in ground squirrel and coyote tissues due to primary or secondary 1080 poisoning

Author(s)
Casper, Howard H., Michael E. Mount, Rex E. Marsh and Robert H. Schmidt
Pages
441-442
Year
Volume
69
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
SODIUM MONOFLUOROACETATE 182-1309 ppb wet wt. @ 0.8 mg/kg; 535-9754 ppb wet wt. @ 4.8 mg/kg range of fluoroacetate residues in brain, caecum, kidney, liver, spleen, muscle and lung tissue of dead squirrels Not Reported Adult 2/dose Toxicity Factor Datasets Laboratory

California Newt (Taricha torosa)

Citation:

Residues of cutthroat trout (Salmo clarkii) and California newts (Tarichia torosa) from a lake treated with technical chlordane

Author(s)
Albright, L.J., P.C. Oloffs and S.Y Szeto
Pages
333-349
Year
Issue
4
Volume
815
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Countries
CHLORDANE 8,906 ppb, range; 4,954 - 15, 609 ppb mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 14 days after application Both Male and Female Both Adults and Juveniles 4 Toxicity Factor Datasets CANADA
CHLORDANE 2,116 ppb, range; 1,354 - 3,783 ppb mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 451 days after application Both Male and Female Both Adults and Juveniles 6 Toxicity Factor Datasets CANADA

Great Horned Owl (Bubo virginianus), Northern Flicker (Colaptes auratus), Mourning Dove (Zenaida macroura)

Citation:

Effects on wildlife from use of endrin in Washington state orchards

Author(s)
Blus, Lawrence J., Charles J. Henny, T. Earl Kaiser and Robert A. Grove
Pages
159-174
Year
Volume
48
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
ENDRIN brain=greater than or equal to 0.8 ppm, wet wt tissue endrin residues Not Reported Not Reported 1-3 animals Wenatchee Toxicity Factor Datasets
ENDRIN brain=greater than or equal to 0.8 ppm, wet wt tissue endrin residues Not Reported Not Reported 1-3 animals Wenatchee Toxicity Factor Datasets

Pallid Bat (Antrozous pallidus)

Citation:
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Countries
DDE (4,4'-) 5.8 ppm; range, 3.6-8.2 ppm (wet wt) mean and range of concentration in carcass, wet wt Both Male and Female Adult 4 bats near cities Toxicity Factor Datasets MEXICO
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