Species

Filter by Species
Filter by Toxicity Endpoint Type
Filter by Exposure Endpoint Type
Filter by Chemical
Filter by Location
Displaying 1881 - 1920 of 4244 datapoints
Export to CSV

Anas platyrhynchos

Citation:

Sublethal effects of cadmium ingestion on mallard ducks

Author(s)
Di Giulio, Richard T. and Patrick F. Scanlon
Pages
765-771
Year
Volume
13
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
CADMIUM CHLORIDE decreased @ 450 ppm body and liver weights compared to controls Not Reported Adult 12 birds/group 0,50,150,450 ppm diet TOX-Non-Repro-Sublethal - whole animal 42 (+/-1) d diet Toxicity Factor Datasets
CADMIUM CHLORIDE increased @ 150, 450 ppm kidney and adrenal weights compared to controls Not Reported Adult 12 birds/group 0,50,150,450 ppm diet TOX-Non-Repro-Sublethal - organ/system effects 42 (+/-1) d diet Toxicity Factor Datasets
CADMIUM CHLORIDE increased @ 450 ppm plasma uric acid, adrenal corticosterone levels Not Reported Adult 12 birds/group 0,50,150,450 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 42 (+/-1) d diet Toxicity Factor Datasets
CADMIUM CHLORIDE no effect food consumption compared to controls Not Reported Adult 12 birds/group 0,50,150,450 ppm diet TOX-Non-Repro-Sublethal - behavioral effects 42 (+/-1) d diet Toxicity Factor Datasets
CADMIUM CHLORIDE decreased @ 450 ppm liver aldolase activity, plasma triiodothyronine levels Not Reported Adult 12 birds/group 0,50,150,450 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 42 (+/-1) d diet Toxicity Factor Datasets
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 Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
CADMIUM CHLORIDE decreased @ 20 ppm packed cell volume and hemoglobin concentration by 8 wks of treatment compared to controls Not Reported Juvenile day old 12 birds per timexdose treatment 0,5,10,20 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 4,8,12 wks diet Toxicity Factor Datasets
CADMIUM CHLORIDE increased @ 20 ppm incidence of kidney lesions by 12 wks of treatment compared to controls Not Reported Juvenile day old 12 birds per timexdose treatment 0,5,10,20 ppm diet TOX-Non-Repro-Sublethal - organ/system effects 4,8,12 wks diet Toxicity Factor Datasets
CADMIUM CHLORIDE increased @ 20 ppm serum glutamic pyruvic transaminase activity by 8 wks of treatment compared to controls Not Reported Juvenile day old 12 birds per timexdose treatment 0,5,10,20 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 4,8,12 wks diet Toxicity Factor Datasets
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 day old 12 birds per timexdose treatment 0,5,10,20 ppm diet TOX-EXP IND - accumulation 4,8,12 wks diet Toxicity Factor Datasets
CADMIUM CHLORIDE no effect body weight, liver weight, and femur density compared to controls Not Reported Juvenile day old 12 birds per timexdose treatment 0,5,10,20 ppm diet TOX-Non-Repro-Sublethal - whole animal 4,8,12 wks diet Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
SELENOMETHIONINE increased @ 32 ppm incidence of liver histopathological lesions, liver:body wt ratios versus controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-Non-Repro-Sublethal - organ/system effects 14 wks diet Toxicity Factor Datasets
SELENOMETHIONINE increased @ 32 ppm plasma alkaline phosphatase activity and total protein levels versus controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 14 wks diet Toxicity Factor Datasets
SELENOMETHIONINE decreased @ 32 ppm body weight, liver DNA:RNA ratio, hematocrit compared to controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-Non-Repro-Sublethal - whole animal 14 wks diet Toxicity Factor Datasets
SELENOMETHIONINE decreased @ 16, 32 ppm hemoglobin concentration compared to controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 14 wks diet Toxicity Factor Datasets
SELENOMETHIONINE increased @ 2 ppm or greater plasma glutathione peroxidase activity versus controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-Non-Repro-Sublethal - cellular/biochemical effects 14 wks diet Toxicity Factor Datasets
SELENOMETHIONINE increased @ 16, 32 ppm liver reduced gluthathione, oxidized glutathione, malondialdehyde concentrations versus controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-Non-Repro-Sublethal - organ/system effects 14 wks diet Toxicity Factor Datasets
SELENOMETHIONINE increased @ 2 ppm or greater Se concentrations in liver versus controls Male Adult 10 birds/group 0.2,1,2,4,8,16,32 ppm diet TOX-EXP IND - accumulation 14 wks diet Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
BORIC ACID, SELENOMETHIONINE decreased @ 60 ppm Se (47% mort.) survival versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 22% protein in the diet) TOX-MORT - dose-response data 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE decreased @ 60 ppm Se body, liver, and spleen weight; tarsus length versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 22% protein in the diet) TOX-Non-Repro-Sublethal - whole animal 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE decreased @ 60 ppm Se (100% mort.) survival versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 7% protein in the diet) TOX-MORT - dose-response data 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE decreased @ 15 ppm Se body, liver, and spleen weight; tarsus length versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 7% protein in the diet) TOX-Non-Repro-Sublethal - whole animal 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE increased @ 15, 60 ppm Se (with and w/out B), 1000 ppm B incidence of plasma chemistry changes versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 22% protein in the diet) TOX-Non-Repro-Sublethal - cellular/biochemical effects 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE increased @ 15 ppm Se (with and w/out B), 1000 ppm B incidence of plasma chemistry changes versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 7% protein in the diet) TOX-Non-Repro-Sublethal - cellular/biochemical effects 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE decreased @ 1000 ppm B hematocrits and hemoglobin concentrations versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm Bo, 15 ppm Se + 1000 ppm Bo, 60 ppm Se + 1000 ppm Bo (all treatments were conducted with 22% protein in the diet) TOX-Non-Repro-Sublethal - cellular/biochemical effects 4 wks diet Toxicity Factor Datasets
BORIC ACID, SELENOMETHIONINE decreased @ 15 ppm Se (with or w/out B), and 1000 ppm B hematocrits and hemoglobin concentrations versus controls Not Reported Juvenile 15 birds/group 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 7% protein in the diet) TOX-Non-Repro-Sublethal - cellular/biochemical effects 4 wks diet Toxicity Factor Datasets
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 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 22% protein in the diet) TOX-EXP IND - accumulation 4 wks diet Toxicity Factor Datasets
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 0, 15 ppm Se, 60 ppm Se, 1000 ppm B, 15 ppm Se + 1000 ppm B, 60 ppm Se + 1000 ppm B (all treatments were conducted with 7% protein in the diet) TOX-EXP IND - accumulation 4 wks 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 Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
MONOCROTOPHOS 5.86 (4.70-7.29), 7.21 (5.79-8.98), 5.10 (4.44-5.86), 3.36 (2.77-4.09) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
PROPOXUR 7.38 (5.97-9.14), 12.7 (10.2-15.9), 14.6 (12.4-17.4), 9.58 (7.61-12.1) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
DICROTOPHOS 6.17 (3.33-11.4), 7.03 (5.30-9.31), 6.73 (5.53-8.19), 4.14 (3.33-5.16) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
FENSULFOTHION 0.528, 0.747, 1.06 (0.868-1.29), 0.747 (0.588-0.949) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
ENDRIN 22.3 (9.88-50.3), 3.37 (2.36-4.80), 2.90 (2.17-3.88), 5.33 (3.67-7.73) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
CARBOFURAN 0.370 (0.283-0.484), 0.628 (0.530-0.744), 0.510 (0.410-0.635), 0.415 (0.333-0.516) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
DEMETON 13.3 (11.0-16.2), 15.3 (12.9-18.1), 15.1 (12.0-19.0), 8.19 (6.58-10.2) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
TOXAPHENE (POLYCHLORINATED CAMPHENES) 130 (80.4-210), 30.8 (23.3-40.6), 70.7 (37.6-133) LD50's determined at ages 36 hr, 7 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
MEXACARBATE 3.16 (2.17-4.61), 4.11 (2.70-6.26), 3.61 (2.37-5.49), 3.23 (2.72-3.85), 2.72(2.28-3.23) LD50's determined at ages 48 hr, 7 d, 14 d, 30 d and 60 d, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
SODIUM MONOFLUOROACETATE 9.78 (6.31-15.2), 3.71 (2.50-5.48), 3.71, 4.81 (2.57-8.99) LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) Both Male and Female Juvenile 5 NR TOX-MORT - toxicity benchmarks Single exposure Gavage Toxicity Factor Datasets
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 Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
ARSENATE, SODIUM no effect hematocrit and hemoglobin Both Male and Female Juvenile 30 birds/group 0, 30, 100, 300 ppm TOX-Non-Repro-Sublethal - cellular/biochemical effects 10 wks diet Toxicity Factor Datasets
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 0, 30, 100, 300 ppm TOX-EXP IND - accumulation 10 wks diet Toxicity Factor Datasets
Citation:

Neurotoxic and teratogenic effects of an organophosphorus insecticide (phenyl phosphorothioic acid-o-ethyl-o-[4-nitrophenyl] ester) on mallard development

Author(s)
Hoffman, David J. and Louis Sileo
Pages
284-294
Year
Volume
73
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
EPN decreased @ 12, 36 ug/g brain weight, protein content, acetylcholinesterase and neurotoxic esterase versus controls Not Reported Hatchling 12/group 0,12,36,108 ug/g egg TOX-Non-Repro-Sublethal - cellular/biochemical effects single application to egg surface 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