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Mallard duck (Anas platyrhynchos)

Citation:

Embryotoxicity of polycyclic aromatic hydrocarbons (PAHs) in three domestic avian species, and of PAHs and coplanar polychlorinated biphenyls (PCBs) in the common eider

Author(s)
Brunstrom, Bjorn, Dag Broman and Carina Naf
Pages
133-143
Year
Volume
67
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
POLYCYCLIC AROMATIC HYDROCARBONS (PAHs) increase @ 0.2, 2.0 mg/kg egg embryonic mortality, compared to controls Not Reported Embryo 22/dose Toxicity Factor Datasets 5 d of incubation Laboratory
BENZO[k]FLUORANTHENE increase @ 0.2, 2.0 mg/kg egg embryo mortality, compared to controls Not Reported Embryo 20/dose Toxicity Factor Datasets 5 d of incubation Laboratory
Citation:

Effect of dietary acid or aluminum on growth and growth-related hormones in mallard ducklings (Anas platyrhynchos)

Author(s)
Capdevielle, M.C. and C.G. Scanes
Pages
462-468
Year
Volume
29
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
ALUMINUM SULFATE decrease @ 0.5% body weight, average daily weight gain and tibiotarsus length, compared to controls Not Reported Juvenile 8/dose Toxicity Factor Datasets Laboratory
ALUMINUM SULFATE 3.59 ppm dry wt @ control, 5.16 ppm @ 0.1%, 15.52 ppm @ 0.05% liver aluminum concentrations (ppm, dry wt) in ducklings Not Reported Juvenile 8/dose Toxicity Factor Datasets Laboratory
ALUMINUM SULFATE no effect plasma growth hormone and insulin-like growth factor-I concentrations Not Reported Juvenile 8/dose Toxicity Factor Datasets Laboratory
Citation:

Effects of sewage sludge on the immune defenses of mallards

Author(s)
Goldberg, D.R. and T.M. Yuill
Pages
209-217
Year
Volume
51
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
SEWAGE SLUDGE no effect immune defenses; resistance to Pasturella multocida estimated by % mortality 14 d after challenge, compared to controls Male Adult 10/dose Toxicity Factor Datasets Laboratory
SEWAGE SLUDGE increase @ 20% Milorganite or Metrogro liver cadmium concentrations; compared to controls Male Adult 10/dose Toxicity Factor Datasets Laboratory
Citation:

Toxicity of trimethyltin and triethyltin to mallard ducklings

Author(s)
Fleming, W. James, Elwood F. Hill and Jeffrey J. Momot
Pages
255-260
Year
Volume
10
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
TRIMETHYLTIN CHLORIDE increase @ 5, 50 ppm % mortality (100% mortality within 5 d for 50 ppm dose), compared to controls Not Reported Juvenile 5/dose Toxicity Factor Datasets 3-4 d Laboratory
TRIMETHYLTIN CHLORIDE increase @ 50 ppm incidence of mild to marked degeneration of neurons of the pons, medulla oblongata, gray matter of the spinal cord and pyrimidal cells of the cerebral cortex; mild to moderate lympoid depletion of spleen and thymus; atrophy of myofibers in skeletal and ca Not Reported Juvenile 5/dose Toxicity Factor Datasets 3-4 d Laboratory
TRIMETHYLTIN CHLORIDE 17% decrease @ 5 ppm body weight Not Reported 5/dose Toxicity Factor Datasets 3-4 d Laboratory
TRIMETHYLTIN CHLORIDE increase @ 5 ppm cephalic tumor incidence Not Reported Juvenile 5/dose Toxicity Factor Datasets 3-4 d Laboratory
TRIETHYLTIN CHLORIDE no effect % mortality, compared to controls Not Reported Juvenile 5/dose Toxicity Factor Datasets 3-4 d 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) 6.96 mg/kg bw (2.66-8.96 95% CI) 24 hour median lethal dose Female Adult 6 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) 6.46 mg/kg bw (5.19-7.69 95% CI) 24 hour median lethal dose Male Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) 3.90 mg/kg bw (3.24-4.69 95% CI) 24 hour median lethal dose Female Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) reduced above 6.2 mg/kg bw body weight versus controls Not Reported Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) increased above 4.3 mg/kg bw liver to body weight ratio versus controls Not Reported Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) positive relationship relation between liver to body weight ratio and dose Male Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) positive correlation relation between dose and frequency and severity of hepatic and kidney lesions Not Reported Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) positive correlation P4 concentration in fat versus dose Male Adult 4-5 birds/dose Toxicity Factor Datasets Laboratory
Citation:

Subchronic dietary toxicity of strychnine: bobwhite quail are less sensitive than mallard ducks.

Author(s)
Sterner, R.T., C.A. Pederson, B.R. Helsten, and M.J. Goodall
Pages
498-505
Year
Volume
35
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
PHOSPHORUS (YELLOW OR WHITE) increased @ 484.2, 972.0 ug/g diet (nominal concentrations) incidence of mortality versus controls Both Male and Female Adult 5 males, 5 females/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) increased @ 235.0, 484.2, 972.0 ug/g (nominal concentrations) incidence of clinical signs versus controls Both Male and Female Adult 5 males, 5 females/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) decreased @ 484.2, 972.0 ug/g (nominal concentrations) food consumption during first week of treatment versus controls Both Male and Female Adult 5 males, 5 females/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) decreased @ 235.0, 484.2, 972.0 ug/g (nominal concentrations) body weight versus controls Both Male and Female Adult 5 males, 5 females/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) 91.1 ug/g No Observable Effect Level, based on mortality, pathology, clinical signs Both Male and Female Adult 5 males, 5 females/dose Toxicity Factor Datasets Laboratory
PHOSPHORUS (YELLOW OR WHITE) 679.8 ug/g (194.3-442.6 95% CI ) LC50 Both Male and Female Adult 5 males, 5 females/dose Toxicity Factor Datasets Laboratory
Citation:

Organochlorine accumulation by sentinel mallards at the Winston-Thomas sewage treatment plant, Bloomington, Indiana

Author(s)
Custer, T.W., D.W. Sparks, S.A. Sobiech, R.K. Hines, and M.J. Melancon
Pages
163-169
Year
Volume
30
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS positive correlation relationships between EROD activity and dieldrin concentrations Female Adult 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) Bloomington Toxicity Factor Datasets
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS positive correlation relationship between BROD, PROD, and EROD activities and total PCB, oxychlordane, and TEQs concentrations Female Adult 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) Bloomington Toxicity Factor Datasets
Citation:

Effects of Aroclor 1254 on the thyroid gland, immune function and hepatic cytochrome P450 activity in mallards

Author(s)
Fowles, Jefferson R., Anne Fairbrother, Kimberly A. Trust and Nancy I. Kerkvliet
Pages
119-129
Year
Volume
75
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
AROCLOR 1254 increased @ 100, 250, 500 mg/kg bw thyroid wt/body wt and liver wt/body wt ratios versus controls Male Adult 6-12/dose Toxicity Factor Datasets 1-2 yr Laboratory
AROCLOR 1254 increased @ 20,100, 250, 500 mg/kg bw hepatic microsomal EROD and PROD activities versus controls Male Adult 6-12/dose Toxicity Factor Datasets 1-2 yr Laboratory
AROCLOR 1254 decreased @ 20, 100, 250, 500 mg/kg bw plasma triiodothyronine concentrations versus controls Male Adult 6-12/dose Toxicity Factor Datasets 1-2 yr Laboratory
AROCLOR 1254 no effect leukocyte counts, plasma biochemistry, corticosterone concentration versus controls Male Adult 6-12/dose Toxicity Factor Datasets 1-2 yr Laboratory
AROCLOR 1254 increased @ 250, 500 mg/kg bw lymphocyte proliferation to PHA versus controls Male Adult 6-12/dose Toxicity Factor Datasets 1-2 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 no effect reproductive success or nest attentiveness versus controls Both Male and Female Adult 22 pairs Toxicity Factor Datasets Laboratory
AROCLOR 1254 no effect body and liver weights of parents and offspring versus controls Both Male and Female Both Adults and Juveniles 22 pairs Toxicity Factor Datasets Laboratory
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
AROCLOR 1254 29.5(1.4) ppm mean(SE) wet wt concentrations of Aroclor 1254 in carcasses of 3 week old ducklings Not Reported Juvenile 10 Toxicity Factor Datasets Laboratory
AROCLOR 1254 23.3(1.0) ppm mean(SE) wet wt concentrations of Aroclor 1254 in eggs Not Reported Embryo 19 eggs Toxicity Factor Datasets Laboratory
Citation:

Response of ducks to glyphosphate-induced habitat alterations in wetlands

Author(s)
Linz, George M., Dage C. Blixt, David L. Bergman and William J. Bleier
Pages
38-44
Year
Volume
16
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type
GLYPHOSATE increased @ 50, 90 percent population density 2 years post-spray versus controls Not Reported Not Reported 3-6 sample wetlands/treatment near Lakota (48deg03'N, 98deg21'W) Toxicity Factor Datasets
Citation:

Kinetics of selenium incorporation into tissues of female mallard ducks

Author(s)
Wilson, David S., Peng Zhang, Rong He, Ron Ota, Stanley T. Omaye
Pages
51-60
Year
Volume
122
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Lab
SELENITE, SODIUM figure/table figures and tables of selenium concentration over time (% of administered dose) Female Adult Not Reported Toxicity Factor Datasets Laboratory
Citation:

Subchronic and reproductive toxicity of emamectin benzoate to mallard ducks and northern bobwhite quail

Author(s)
O'Grodnick, Joseph S., Peter G. Wislocki, Kevin P. Keenan, Joann B. Beavers, Larry T. Frey, and Mark Jaber
Pages
2318-2324
Year
Issue
11
Volume
17
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
EMAMECTIN BENZOATE no effect numbers of eggs laid and hatched, eggshell thickness, and 14-day hatchling survival versus controls Both Male and Female Both Adults and Juveniles 16 pairs/group Toxicity Factor Datasets 22 weeks Laboratory
EMAMECTIN BENZOATE no effect mortality versus controls Both Male and Female Adult 16 pairs/group Toxicity Factor Datasets 22 weeks Laboratory
EMAMECTIN BENZOATE no effect incidence of signs of toxicity and body weight versus controls Both Male and Female Adult 16 pairs/group Toxicity Factor Datasets 22 weeks Laboratory
EMAMECTIN BENZOATE no effect feed consumption versus controls Both Male and Female Adult 16 pairs/group Toxicity Factor Datasets 22 weeks Laboratory
EMAMECTIN BENZOATE no effect microscopic changes to brain, spinal cord, or peripheral nerves versus controls Both Male and Female Adult 16 pairs/group Toxicity Factor Datasets 22 weeks Laboratory
Citation:

Toxicity of emamectin benzoate to mallard duck and northern bobwhite quail

Author(s)
Chukwudebe, Amechi C., Joann B. Beavers, Mark Jaber, and Peter G. Wislocki
Pages
1118-1123
Year
Issue
6
Volume
17
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
EMAMECTIN BENZOATE 76 mg/kg bw, 56-102 (95% CI) acute oral LD50 Both Male and Female Adult 10/dose Toxicity Factor Datasets 19 weeks Laboratory
EMAMECTIN BENZOATE < 25 mg/kg bw no-observed-effect level, based on body weight loss Both Male and Female Adult 10/dose Toxicity Factor Datasets 19 weeks Laboratory
EMAMECTIN BENZOATE 570 ppm diet, 391-915 (95% CI) dietary LC50 Both Male and Female Juvenile 10/dose Toxicity Factor Datasets 10 days Laboratory
EMAMECTIN BENZOATE 20 ppm diet no-observed-effect concentration (NOEC), based on reduced feed consumption and weight gain Both Male and Female Juvenile 10/dose Toxicity Factor Datasets 10 days Laboratory
Citation:

Diagnostic criteria for selenium toxicosis in aquatic birds: Histologic lesions

Author(s)
Green, D. Earl and Peter H. Albers
Pages
385-404
Year
Volume
33
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
SELENOMETHIONINE no effect histological changes to nervous system, bones, feathers, feather follicles, claws and scaled skin versus controls Male Adult 21/dose Toxicity Factor Datasets 14 mo Laboratory
SELENOMETHIONINE increased in birds that died, and in some 40 ppm survivors histological changes to skin (loss of fat), muscle, liver, pancreas, kidney, lymph nodes, spleen, seminiferous tubules Male Adult 21/dose Toxicity Factor Datasets 14 mo Laboratory
Citation:

Diagnostic criteria for selenium toxicosis in aquatic birds: Dietary exposure, tissue concentrations and macroscopic effects

Author(s)
Albers, Peter H., D. Earl Green and Caroline J. Sanderson
Pages
468-485
Year
Volume
32
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
SELENOMETHIONINE increased @ 80 ppm mortality versus controls Male Adult 21/dose Toxicity Factor Datasets 1 yr Laboratory
SELENOMETHIONINE decreased @ 80 ppm feed consumption over time versus controls Male Adult 21/dose Toxicity Factor Datasets 1 yr Laboratory
SELENOMETHIONINE decreased @ 40 and 80 ppm body weight over exposure period versus controls Male Adult 21/dose Toxicity Factor Datasets 1 yr Laboratory
SELENOMETHIONINE increased in birds that died incidence of macroscopic abnormalities versus controls Male Adult 21/dose Toxicity Factor Datasets 1 yr Laboratory
SELENOMETHIONINE increased @ 40 ppm incidence of macroscopic abnormalities of muscles, claws and feathers versus controls Male Adult 21/dose Toxicity Factor Datasets 1 yr Laboratory
SELENOMETHIONINE decreased in birds that died mean weights of heart, spleen, pancreas, testis versus controls Male Adult 21/dose Toxicity Factor Datasets 1 yr Laboratory
SELENOMETHIONINE 33(7) ppm @ 10 ppm Se, 49(9) ppm @ 20 ppm Se, 87(11) ppm @ 40 ppm Se, 99(9) ppm in birds that died mean (SE) dry wt concentrations of selenium in liver Male Adult 10-25 Toxicity Factor Datasets 1 yr Laboratory
Citation:

Aluminum and acid effects on calcium and phosphorus metabolism in young growing chickens (Gallus gallus domesticus) and mallard ducks (Anas platyrynchos).

Author(s)
Capdevielle, M.C., and L.E. Hart, J. Goff and C.G. Scanes
Pages
82-88
Year
Volume
35
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
ALUMINUM SULFATE, SULFURIC ACID reduced @ 0.5% Al or 0.277 mol sulfate/kg growth of tibia versus ad libidum controls Both Male and Female Juvenile 8 birds/treatment Toxicity Factor Datasets 3 d Laboratory
ALUMINUM SULFATE, SULFURIC ACID reduced @ 0.5% Al tibial dry weight, and ash and calcium content versus ad libidum controls Both Male and Female Juvenile 8 birds/treatment Toxicity Factor Datasets 3 d Laboratory
Citation:

Effects of boron and selenium on mallard reproduction and duckling growth and survival

Author(s)
Stanley, Thomas R., Jr., Gregory J. Smith, David J. Hoffman, Gary H. Heinz, and Roger Rosscoe
Pages
1124-1132
Year
Issue
7
Volume
15
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
BORIC ACID, SELENOMETHIONINE reduced @ 900 ppm B body weight versus controls Both Male and Female Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE decreased @ 900 ppm B liver weight versus 450 ppm B group Male Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 900 ppm B hemoglobin concentrations versus controls Male Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE no effect onset of egg laying, eggshell thickness, frequency of embryo deformities versus controls Both Male and Female Both Adults and Juveniles 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 900 ppm B egg weight, hatching success, egg fertility versus controls Both Male and Female Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 7 ppm Se body weight versus controls Female Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE no effect due to added Se liver weight, hemoglobin concentrations, hematocrit versus controls Both Male and Female Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE no effect due to added Se onset of egg laying, eggshell thickness, egg weight, egg fertility, embryo deformities versus controls Both Male and Female Both Adults and Juveniles 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 7 ppm Se hatching success versus controls Female Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE decreased @ 900 ppm B total SH, liver protein, sorbitol dehyrogenase versus controls Both Male and Female Juvenile 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 900 ppm B body weight and growth at 0, 7,and 14 days post-hatch versus controls Both Male and Female Juvenile 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 7 ppm Se body weight and weight gain at 7 and 14 days post-hatch versus 3.5 ppm Se group Both Male and Female Juvenile 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE increased @ 3.5 ppm Se survival between 7 and 14 days post-hatch versus controls Both Male and Female Juvenile 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE reduced @ 7 ppm duckling production versus 3.5 ppm Se group Both Male and Female Both Adults and Juveniles 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE 4.6 (0.18) ppm B @ 450 ppm B; 8.5 (0.34) ppm B @ 900 ppm B; 3.7 (0.16) ppm Se @ 3.5 ppm Se; 6.2 (0.27) ppm Se @ 7 ppm mean (SE) wet wt concentrations of B and Se in liver Both Male and Female Adult 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
BORIC ACID, SELENOMETHIONINE 6.5 (0.25) ppm B @ 450 ppm B; 11 (0.4) ppm B @ 900 ppm B; 3.5 (0.10) ppm Se @ 3.5 ppm Se; 7.1 (0.28) ppm Se @ 7 ppm mean (SE) wet wt concentrations of B and Se in egg Both Male and Female Both Adults and Juveniles 14 pairs/treatment Toxicity Factor Datasets 1 yr Laboratory
Citation:

Toxicity of lead-contaminated sediment to mallards

Author(s)
Heinz, G.H., D.J. Hoffman, L. Sileo, D.J. Audet, and L.J. LeCaptain
Pages
323-333
Year
Volume
36
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type Age-Specific Lab
LEAD COMPOUNDS no effect body weight versus controls Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS reduced @ 828 ug/g hemoglobin concentrations versus controls Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS reduced @ all doses delta aminolevulinic acid dehydratase activity versus controls Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS increased @ 414, 828 ug/g occurrence of intranuclear inclusion bodies in kidneys versus controls Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS increased @ 828 ug/g occurrence of lead poisoning signs versus controls Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS increased @ all doses protoporphyrin levels in blood versus controls Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS 4.6(0.66) ppm @ 103 ug/g Pb; 9.3(0.82) ppm @ 207 ug/g Pb; 12(1.3) ppm @ 414 ug/g Pb; 28(4.6) ppm @ 828 ug/g Pb mean(SE) wet wt concentrations of lead in liver Male Adult 10/ Pb treatment; 20/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS no effect body weight versus controls Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS reduced @ 624 and 1284 ug/g delta aminolevulinic acid dehydratase activity and hemoglobin concentrations Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS increased @ 642 and 1284 ug/g protoporphyrin versus controls Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS reduced @ 1284 ug/g hematocrit versus controls Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS increased @ 642 and 1284 ug/g occurrence of renal tubular nuclear inclusion bodies versus controls Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS 3.0(0.30) ppm @ 642 ug/g Pb; 6.8(0.84) ppm @ 1284 ug/g Pb mean (SE) wet wt Pb concentrations in blood Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS 9.1(0.61) ppm @ 642 ug/g Pb; 16(1.5) ppm @ 1284 ug/g Pb mean (SE) wet wt Pb concentrations in liver Male Adult 10/ Pb treatment; 5/control treatment Toxicity Factor Datasets approx. 5 mo Laboratory
LEAD COMPOUNDS reduced @ 869 ug/g, corn diet body weight compared to corn diet controls Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
LEAD COMPOUNDS reduced @ 869 ug/g, corn diet hemoglobin concentration versus corn diet controls Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
LEAD COMPOUNDS increased @ 869 and 954 ug/g protoporphyrin versus corn or complete diet controls Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
LEAD COMPOUNDS reduced @ 869 and 954 ug/g delta aminolevulinic acid dehydratase activity versus corn or complete diet controls Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
LEAD COMPOUNDS increased @ 869 ug/g, corn diet mortality versus corn diet controls Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
LEAD COMPOUNDS increased @ 869 and 954 ug/g incidence of renal tubular intranuclear inclusion bodies versus corn or complete diet controls Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
LEAD COMPOUNDS 4.1(1.03) ppm in blood, 13(1.2) ppm in liver @ 954 ug/g, complete diet; 4.0(0.58) ppm in blood, 38(6.5) ppm in liver @ 869 ug/g, corn diet mean (SE) wet wt Pb concentrations in blood and liver Male Adult 5/ Pb treatment;3/control treatments Toxicity Factor Datasets approx. 7 mo Laboratory
Citation:

Site-specific lead exposure from lead pellet ingestion in sentinel mallards

Author(s)
Rocke, Tonie E., Christopher J. Brand, John G. Mensik
Pages
228-234
Year
Volume
61
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Location Type California Counties
LEAD (elemental) higher in P8 than in T19 and TF, and in T19 than in TF maximum likelihood estimate of 2-week Pb exposure rate Both Male and Female Both Adults and Juveniles 50 birds/treatment Sacramento National Wildlife Refuge; Willows, CA (39deg29'N, 122deg20'W) Toxicity Factor Datasets Sacramento
LEAD (elemental) higher in P8 than in T19 and TF, and in T19 than in TF mortality rate (over 4 years) Both Male and Female Both Adults and Juveniles 50 birds/treatment Sacramento National Wildlife Refuge; Willows, CA (39deg29'N, 122deg20'W) Toxicity Factor Datasets Sacramento
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
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