Species

Filter by Species

Filter by Toxicity Endpoint Type

Filter by Exposure Endpoint Type

Filter by Chemical

Filter by Location

Displaying 7401 - 7440 of 9478 datapoints
Export to CSV

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 Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DIELDRIN no effect daily survival rates on uncontaminated versus contaminated sites Not Reported Adult Rocky Mountain Arsenal National Wildlife Refuge 9 birds on contaminated sites; 11 birds on uncontaminated sites 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges TOX-MORT - mortality in the field NR habitat contamination Toxicity Factor Datasets
DIELDRIN 0.07 +/- 0.03 ppm (uncontaminated site); 0.34 +/- 0.21 ppm (contaminated site) mean (+/- SE) concentrations in plasma Not Reported Adult Rocky Mountain Arsenal National Wildlife Refuge 2 birds on contaminated sites; 5 birds on uncontaminated sites 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges TOX-EXP IND - accumulation NR habitat contamination 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 Rocky Mountain Arsenal National Wildlife Refuge 6 birds on contaminated sites; 10 birds on uncontaminated sites 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges TOX-EXP IND - accumulation NR habitat contamination Toxicity Factor Datasets

Anas platyrhynchos

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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
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 0, 6.0, 7.9, 10.2, 13.5, 18.0 mg/kg bw (dissolved in corn oil) TOX-MORT - toxicity benchmarks single oral gavage Toxicity Factor Datasets
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 0, 2, 4, 5.2, 6.1, 7.1, 8.0, 9.1 mg/kg bw (dissolved in corn oil) TOX-MORT - toxicity benchmarks single oral gavage Toxicity Factor Datasets
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 0, 1.0, 2.0, 3.4, 4.0, 6.5 mg/kg bw (pelletized) TOX-MORT - toxicity benchmarks single oral gavage Toxicity Factor Datasets
PHOSPHORUS (YELLOW OR WHITE) reduced above 6.2 mg/kg bw body weight versus controls Not Reported Adult 4-5 birds/dose 0, 6.0, 7.9, 10.2, 13.5, 18.0 mg/kg bw (dissolved in corn oil) TOX-Non-Repro-Sublethal - whole animal single oral gavage Toxicity Factor Datasets
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 0, 6.0, 7.9, 10.2, 13.5, 18.0 mg/kg bw (dissolved in corn oil) TOX-Non-Repro-Sublethal - organ/system effects single oral gavage Toxicity Factor Datasets
PHOSPHORUS (YELLOW OR WHITE) positive relationship relation between liver to body weight ratio and dose Male Adult 4-5 birds/dose 0, 6.0, 7.9, 10.2, 13.5, 18.0 mg/kg bw (dissolved in corn oil) TOX-Non-Repro-Sublethal - organ/system effects single oral gavage Toxicity Factor Datasets
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 0, 6.0, 7.9, 10.2, 13.5, 18.0 mg/kg bw (dissolved in corn oil) TOX-Non-Repro-Sublethal - organ/system effects single oral gavage Toxicity Factor Datasets
PHOSPHORUS (YELLOW OR WHITE) positive correlation P4 concentration in fat versus dose Male Adult 4-5 birds/dose 0, 1.0, 2.0, 3.4, 4.0, 6.5 mg/kg bw (pelletized) TOX-EXP IND - accumulation single oral gavage Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
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 0, 17.3-19.7, 72.0-79.1, 243.3-260, 461-498.3, 900.7-1023.3 ug/g diet (range in measured concentrations over 4 wks) TOX-MORT - dose-response data 4 wks diet Toxicity Factor Datasets
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 0, 17.3-19.7, 72.0-79.1, 243.3-260, 461-498.3, 900.7-1023.3 ug/g diet (range in measured concentrations over 4 wks) TOX-Non-Repro-Sublethal - whole animal 4 wks diet Toxicity Factor Datasets
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 0, 17.3-19.7, 72.0-79.1, 243.3-260, 461-498.3, 900.7-1023.3 ug/g diet (range in measured concentrations over 4 wks) TOX-Non-Repro-Sublethal - behavioral effects 4 wks diet Toxicity Factor Datasets
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 0, 17.3-19.7, 72.0-79.1, 243.3-260, 461-498.3, 900.7-1023.3 ug/g diet (range in measured concentrations over 4 wks) TOX-Non-Repro-Sublethal - whole animal 4 wks diet Toxicity Factor Datasets
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 0, 17.3-19.7, 72.0-79.1, 243.3-260, 461-498.3, 900.7-1023.3 ug/g diet (range in measured concentrations over 4 wks) TOX-MORT - toxicity benchmarks 4 wks diet Toxicity Factor Datasets
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 0, 17.3-19.7, 72.0-79.1, 243.3-260, 461-498.3, 900.7-1023.3 ug/g diet (range in measured concentrations over 4 wks) TOX-MORT - toxicity benchmarks 4 wks diet Toxicity Factor Datasets
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 Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS positive correlation relationships between EROD activity and dieldrin concentrations Female Adult Bloomington 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) in ppm wet wt, carcass, after 100 d exposure: 0.08 (dieldrin); 0.18 (oxychlordane); 0.09 (DDE), 16.56 (total PCBs) TOX-EXP IND - biomarkers up to 100 d habitat contamination 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 Bloomington 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) in ppm wet wt, carcass, after 100 d exposure: 0.08 (dieldrin); 0.18 (oxychlordane); 0.09 (DDE), 16.56 (total PCBs) TOX-EXP IND - biomarkers up to 100 d habitat contamination 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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
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 0,4,20,100,250,500 mg/kg bw TOX-Non-Repro-Sublethal - organ/system effects twice/wk for 5 wks oral gavage Toxicity Factor Datasets
AROCLOR 1254 increased @ 20,100, 250, 500 mg/kg bw hepatic microsomal EROD and PROD activities versus controls Male Adult 6-12/dose 0,4,20,100,250,500 mg/kg bw TOX-EXP IND - biomarkers twice/wk for 5 wks oral gavage Toxicity Factor Datasets
AROCLOR 1254 decreased @ 20, 100, 250, 500 mg/kg bw plasma triiodothyronine concentrations versus controls Male Adult 6-12/dose 0,4,20,100,250,500 mg/kg bw TOX-Non-Repro-Sublethal - organ/system effects twice/wk for 5 wks oral gavage Toxicity Factor Datasets
AROCLOR 1254 no effect leukocyte counts, plasma biochemistry, corticosterone concentration versus controls Male Adult 6-12/dose 0,4,20,100,250,500 mg/kg bw TOX-Non-Repro-Sublethal - organ/system effects twice/wk for 5 wks oral gavage Toxicity Factor Datasets
AROCLOR 1254 increased @ 250, 500 mg/kg bw lymphocyte proliferation to PHA versus controls Male Adult 6-12/dose 0,4,20,100,250,500 mg/kg bw TOX-Non-Repro-Sublethal - organ/system effects twice/wk for 5 wks oral gavage Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
AROCLOR 1254 no effect reproductive success or nest attentiveness versus controls Both Male and Female Adult 22 pairs mean(SE) of 4 samples: 26.3(0.2) ppm, wet wt, in diet TOX-REPRO - reproductive success at least one month diet Toxicity Factor Datasets
AROCLOR 1254 no effect body and liver weights of parents and offspring versus controls Both Male and Female Both Adults and Juveniles 22 pairs mean(SE) of 4 samples: 26.3(0.2) ppm, wet wt, in diet TOX-Non-Repro-Sublethal - organ/system effects at least one month diet Toxicity Factor Datasets
AROCLOR 1254 55-65 ppm range of wet wt concentrations of Aroclor 1254 in adult carcasses Both Male and Female Adult 22 pairs mean(SE) of 4 samples: 26.3(0.2) ppm, wet wt, in diet TOX-EXP IND - accumulation at least one month diet Toxicity Factor Datasets
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 mean(SE) of 4 samples: 26.3(0.2) ppm, wet wt, in diet TOX-EXP IND - accumulation at least one month diet Toxicity Factor Datasets
AROCLOR 1254 23.3(1.0) ppm mean(SE) wet wt concentrations of Aroclor 1254 in eggs Not Reported Embryo 19 eggs mean(SE) of 4 samples: 26.3(0.2) ppm, wet wt, in diet TOX-EXP IND - accumulation at least one month diet Toxicity Factor Datasets
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 Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
GLYPHOSATE increased @ 50, 90 percent population density 2 years post-spray versus controls Not Reported Not Reported near Lakota (48deg03'N, 98deg21'W) 3-6 sample wetlands/treatment 0, 50, 70, or 90 percent of wetland sprayed TOX-Non-Repro-Sublethal - indirect effects 2 yrs spray application to habitat 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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
SELENITE, SODIUM figure/table figures and tables of selenium concentration over time (% of administered dose) Female Adult Not Reported 0.21-0.24 ug/kg bw TOX-EXP IND - accumulation single intravenous Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
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 0, 4, 8, 20, 40 ppm in diet TOX-REPRO - reproductive success 20 weeks diet Toxicity Factor Datasets
EMAMECTIN BENZOATE no effect mortality versus controls Both Male and Female Adult 16 pairs/group 0, 4, 8, 20, 40 ppm in diet TOX-MORT - dose-response data 20 weeks diet Toxicity Factor Datasets
EMAMECTIN BENZOATE no effect incidence of signs of toxicity and body weight versus controls Both Male and Female Adult 16 pairs/group 0, 4, 8, 20, 40 ppm in diet TOX-Non-Repro-Sublethal - whole animal 20 weeks diet Toxicity Factor Datasets
EMAMECTIN BENZOATE no effect feed consumption versus controls Both Male and Female Adult 16 pairs/group 0, 4, 8, 20, 40 ppm in diet TOX-Non-Repro-Sublethal - behavioral effects 20 weeks diet Toxicity Factor Datasets
EMAMECTIN BENZOATE no effect microscopic changes to brain, spinal cord, or peripheral nerves versus controls Both Male and Female Adult 16 pairs/group 0, 4, 8, 20, 40 ppm in diet TOX-Non-Repro-Sublethal - organ/system effects 20 weeks diet Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
EMAMECTIN BENZOATE 76 mg/kg bw, 56-102 (95% CI) acute oral LD50 Both Male and Female Adult 10/dose 0, 25, 50, 100, 200, 400, 800 mg/kg bw; avg measured concentration was 107% of nominal TOX-MORT - toxicity benchmarks single oral gavage Toxicity Factor Datasets
EMAMECTIN BENZOATE < 25 mg/kg bw no-observed-effect level, based on body weight loss Both Male and Female Adult 10/dose 0, 25, 50, 100, 200, 400, 800 mg/kg bw; avg measured concentration was 107% of nominal TOX-Non-Repro-Sublethal - whole animal single oral gavage Toxicity Factor Datasets
EMAMECTIN BENZOATE 570 ppm diet, 391-915 (95% CI) dietary LC50 Both Male and Female Juvenile 10/dose 0, 10, 20, 40, 80, 163, 327, 654, 1308 mg/kg bw; avg measured concentration was 108% of nominal TOX-MORT - toxicity benchmarks 5 d diet Toxicity Factor Datasets
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 0, 10, 20, 40, 80, 163, 327, 654, 1308 mg/kg bw; avg measured concentration was 108% of nominal TOX-Non-Repro-Sublethal - whole animal 5 d diet 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