Species

Filter by Species
Filter by Toxicity Endpoint Type
Filter by Exposure Endpoint Type
Filter by Chemical
Filter by Location
Displaying 1481 - 1520 of 1626 datapoints
Export to CSV

Anas platyrhynchos

Citation:

Marked DDE impairment of mallard reproduction in controlled studies

Author(s)
Heath, R.G., J.W. Spann and J.F. Kreitzer
Pages
47-48
Year
Volume
224
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DDE (4,4'-) decreased number of 14-day old ducklings per hen versus controls Both Male and Female Hatchling 274-327, 69-167, and 26-113 for the 0, 10, and 40 ppm DDE groups 0, 10, or 40 ppm TOX-REPRO - reproductive success 2 years Diet Toxicity Factor Datasets
DDE (4,4'-) increased % cracked eggs versus controls Female Hatchling 666-696, 620-664, and 317-602 for the 0, 10, and 40 ppm DDE groups 0, 10, or 40 ppm TOX-REPRO - physiology 2 years Diet Toxicity Factor Datasets
DDE (4,4'-) decreased eggshell thickness versus controls Female Adult 20-28, 21-25, and 10-23 for the 0, 10, and 40 ppm DDE groups 0, 10, or 40 ppm TOX-REPRO - physiology 2 years Diet Toxicity Factor Datasets
Citation:

Effect of age on sensitivity: Acute oral toxicity of 14 pesticides to mallard ducks of several ages

Author(s)
Hudson, R.H., R.K. Tucker and M.A. Haegele
Pages
556-561
Year
Volume
22
Chemical Endpoint Value Endpoint Description Range Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
CHLORPYRIFOS 145 mg/kg LD50 55.8 - 377 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
CHLORPYRIFOS 29.4 mg/kg LD50 18.6 - 46.7 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
CHLORPYRIFOS 50.4 mg/kg LD50 32.5 - 78.1 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
CHLORPYRIFOS 83.3 mg/kg LD50 44.0 - 158 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ENDOSULFAN 27.8 mg/kg LD50 22.8 - 33.8 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ENDOSULFAN 6.47 mg/kg LD50 5.19 - 8.05 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ENDOSULFAN 7.89 mg/kg LD50 5.77 - 10.8 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ENDOSULFAN 34.4 mg/kg LD50 26.1 - 45.3 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ALDICARB 1.92 mg/kg LD50 1.55 - 2.37 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ALDICARB 3.60 mg/kg LD50 2.90 - 4.49 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ALDICARB 6.73 mg/kg LD50 5.29 - 8.55 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ALDICARB 4.44 mg/kg LD50 3.49 - 5.65 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
PARATHION 1.65 mg/kg LD50 1.40 - 1.96 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
PARATHION 1.44 mg/kg LD50 1.13 - 1.83 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
PARATHION 1.65 mg/kg LD50 1.40 - 1.96 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
PARATHION 2.34 mg/kg LD50 1.98 - 2.78 (95% CI) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
Citation:

p,p' - DDE - induced changes in the organic and inorganic structure of eggshells of the mallard, Anas platyrhynchos

Author(s)
Greenburg, R.R., Risebrough, R.W. and D.W. Anderson
Pages
279-286
Year
Volume
48
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
AROCLOR 1254, DDE (4,4'-) decreased with all treatments numbers of mammillary cores and basal caps on eggshell membranes versus controls Female Adult 6-8 eggs/group from 10 hens 0, 40 ppm DDE, 40 ppm Aroclor, 40 ppm DDE + 40 ppm Aroclor TOX-REPRO - physiology NR Diet Toxicity Factor Datasets
Citation:

Toxic, neurochemical and behavioral effects of dieldrin exposure in mallard ducks

Author(s)
Sharma, R.P., D.S. Winn and J.B. Low
Pages
43-53
Year
Issue
1
Volume
5
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DIELDRIN decreased @ 10 ppm (serotonin only) and 30 ppm Serotonin, norepinephrine, and dopamine levels versus controls Both Male and Female Juvenile 3-6 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - cellular/biochemical effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN increased with all doses brain, liver, and adipose dieldrin concentrations Both Male and Female Juvenile 4-6 per group 0, 4, 10, and 30 ppm Dieldrin TOX-EXP IND - accumulation Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN no effect bw versus controls Both Male and Female Juvenile 9-25 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - organ/system effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN increased @ 10 ppm (liver only), 30 ppm (brain only) brain and liver weight to body weight ratios versus controls Both Male and Female Juvenile 9-25 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - organ/system effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN increased@ 4, 10, 30 ppm hepatic microsomal enzyme activity versus controls Both Male and Female Juvenile 5-15 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - cellular/biochemical effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN increased @ 30 ppm liver protein concentration versus controls Both Male and Female Juvenile 5-15 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - cellular/biochemical effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN increased @ 10, 30 ppm liver DNA content versus controls Male Both Adults and Juveniles 5-15 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - cellular/biochemical effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
DIELDRIN decreased @ all doses % drake encounter scores Male Both Adults and Juveniles 30 per group 0, 4, 10, and 30 ppm Dieldrin TOX-Non-Repro-Sublethal - behavioral effects Second - generation. Exposed 75 days after hatch. Diet Toxicity Factor Datasets
Citation:

Effects of DDT on eggshell quality and calcium adenosine triphosphatase

Author(s)
Kolaja, Gerald J. and David E. Hinton
Pages
699-704
Year
Volume
3
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DDT (4,4'-) decreased eggshell thickness versus controls Female Adult 5 hens; 19 eggs 0, 50 ppm TOX-REPRO - physiology 6 months Diet Toxicity Factor Datasets
DDT (4,4'-) decreased eggshell weight versus controls Female Adult 5 hens; 19 eggs 0, 50 ppm TOX-REPRO - physiology 6 months Diet Toxicity Factor Datasets
DDT (4,4'-) decreased eggshell quality (R-value) versus controls Female Adult 5 hens; 19 eggs 0, 50 ppm TOX-REPRO - physiology 6 months Diet Toxicity Factor Datasets
DDT (4,4'-) no effect calcium concentration in eggshell versus controls Female Adult 5 hens; 19 eggs 0, or 50 ppm DDT TOX-REPRO - physiology 6 months Diet Toxicity Factor Datasets
DDT (4,4'-) no effect total Ca/eggshell Female Adult 5 hens; 19 eggs 0, or 50 ppm TOX-REPRO - physiology 6 months Diet Toxicity Factor Datasets
DDT (4,4'-) no effect Ca - ATPase activity in eggshell glands versus controls Female Adult 5 hens; 19 eggs 0, or 50 ppm TOX-REPRO - physiology 6 months Diet Toxicity Factor Datasets

Laterallus jamaicensis

Citation:
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
METHYLMERCURY See citation Figures 3 & 4 Blood concentration Both Male and Female Not Reported Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough 64 NR TOX-EXP IND - accumulation Environmental contamination Toxicity Factor Datasets
METHYLMERCURY See citation Figures 3 & 4 Feather concentration Not Reported Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough 127 NR TOX-EXP IND - accumulation Environmental contamination Toxicity Factor Datasets

Egretta thula

Citation:
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
MERCURY (elemental) 0.81 ± 0.50 µg/g dw Feather concentration Both Male and Female Nestling Georgia & South Carolina 10 NR TOX-EXP IND - accumulation Environmental Contamination Toxicity Factor Datasets
METHYLMERCURY Review, see citation Figure 2 Egg concentration Embryo Not reported NR TOX-EXP IND - accumulation Toxicity Factor Datasets
METHYLMERCURY Review, see ciation Figure 3 Feather concentration Not Reported Not reported NR TOX-EXP IND - accumulation Toxicity Factor Datasets
DDE (2,4'-) 4.8 ppm ww Egg concentration Embryo Blackfoot Reservoir 9 NR TOX-EXP IND - accumulation Environmental contamination Toxicity Factor Datasets
Download CSV

Comment

Please let us know if the information on this page is helpful for you. Enter your comment and leave your email address if you would like to receive a response. Thank you!
OEHHA is subject to the California Public Records Act and other laws that require the release of certain information upon request. If you provide comments, please be aware that your name, address and e-mail may be available to third parties. In addition, all public comments will be posted on our web site upon the close of the comment period.
OEHHA California Office of Environmental Health Hazard Assessment