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Peromyscus maniculatus

Citation:

Lead poisoning in roadside populations of deer mice

Author(s)
Mierau, Gary W. and Blaise E. Favara
Pages
55-64
Year
Volume
8
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
LEAD COMPOUNDS no effect number of litters per 100 breeding females, measured by observing litters in nesting boxes at a control and roadside site Female Adult Interstate 25, Denver (elev. 1884-2018 m) 50 nesting boxes, 66 observation periods nimals mean surface soil; 73.0 +/- 19.9SD ppm, dry weight TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets
LEAD COMPOUNDS significant increase mortality during winter, estimated by number of mice recaptured the following breeding season at a control and roadside site Both Male and Female Adult Interstate 25, Denver (elev. 1884-2018 m) 98 - 180 tagged animals mean surface soil; 73.0 +/- 19.9SD ppm, dry weight TOX-MORT - mortality in the field NR multiple Toxicity Factor Datasets
LEAD ACETATE increase at 0.5 and 1% diet incidence of acid-fast staining intranuclear inclusion bodies within kidney proximal convoluted tubule cells Both Male and Female Adult 5 breeding pairs/dose 0, 0.1, 0.5, 1.0% TOX-Non-Repro-Sublethal - cellular/biochemical effects 26 wk diet Toxicity Factor Datasets
LEAD ACETATE no effect litter mortality Both Male and Female Adult 5 breeding pairs 0, 0.1, 0.5, 1.0% TOX-REPRO - reproductive success 26 wk diet Toxicity Factor Datasets
LEAD ACETATE no effect incidence of congenital malformations Both Male and Female Juvenile 5 breeding pairs/dose 0, 0.1, 0.5, 1.0% TOX-REPRO - development 26 wk diet Toxicity Factor Datasets
Citation:

Comparative toxicity of azinophos-methyl to house mice, laboratory mice, deer mice and gray-tailed voles

Author(s)
Meyers, S.M. and J.O. Wolff
Pages
478-482
Year
Volume
26
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
AZINPHOS-METHYL (GUTHION) 48 mg/kg bw (95% CL: 39-74 mg/kg, slope = 2.57 +/- 0.73SE) LD50 Male Adult 5-7 animals/dose 0, 20, 25, 32, 40, 50, 63, 79 mg/kg body weight TOX-MORT - toxicity benchmarks single gavage Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) 1180 ppm diet (95% CL: 709-1485, slope = 1.88 +/- 0.57SE) LD50 Both Male and Female Adult 10 animals/dose 6 doses TOX-MORT - toxicity benchmarks 10 d diet Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) 2425 ppm diet (95% CL: 1856-3245, slope = 1.45 +/- 0.25SE) LD50 Both Male and Female Adult 10 animals/dose 6 doses TOX-MORT - toxicity benchmarks 5 d diet Toxicity Factor Datasets
Citation:

Mercury and behavior in wild mouse populations

Author(s)
Burton, Gary V., Robert J. Alley, G. Lynn Rasmussen, Paul Orton, Vance Cox, Paul Jones and Darrell Graff
Pages
30-34
Year
Volume
14
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
MERCURY COMPOUNDS increase and decrease decreased swimming ability, increased time for mouse to leave circle in center of field, decreased number of lines crossed and increased number of backward movements compared to a reference site Male Adult Bird Island, Great Salt Lake 7 - 14 animals Mean hair concentration; 10.8 +/- 2.0 ppm TOX-Non-Repro-Sublethal - behavioral effects NR site contamination Toxicity Factor Datasets
Citation:

Copper, zinc, and cadmium concentrations in Peromyscus maniculatus sampled near an abandoned copper mine

Author(s)
Laurinolli, M. and L.I. Bendell-Young
Pages
481-486
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
CADMIUM COMPOUNDS, COPPER COMPOUNDS, ZINC COMPOUNDS Diet:Soil; 128.0 (Cd), 1.31 (Cu), 1.87 (Zn). Liver:Soil; 35.3 (Cd), 0.17 (Cu), 1.25 (Zn). Liver:Diet; 0.27 (Cd), 0.12 (Cu), 0.66 (Zn). Ratio of metal concentrations (ug/g dry weight) in diet:soil, liver:soil and liver:diet at an abandoned mine site. Diet concentrations measured from stomach contents. Soil based on acid extractable concentrations. Soil copper; liver cadmium, copper an Both Male and Female Adult Blue Grouse Mountain Copper Mine, Honeymoon Bay, Vancouver Island, British Columbia 6-9 soil or tissue samples/site Soil: 0.21 +/- 0.006 SD (Cd), 315.0 +/- 3.15SD (Cu), 80.6 +/- 10.4SD (Zn) mg/kg dry weight TOX-EXP IND - accumulation NR site contamination Toxicity Factor Datasets
Citation:

Demographic responses of small mammal populations to a herbicide application in coastal coniferous forest: population density and resiliency

Author(s)
Sullivan, Thomas P.
Pages
874-883
Year
Volume
68
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 no effect population density, compared to control site Both Male and Female Both Adults and Juveniles Maple Ridge, British Columbia 13 trapping periods 0, 3.0 kg/ha TOX-POP - size effects up to 4 yr field application Toxicity Factor Datasets
GLYPHOSATE increase % of trapped males and females in breeding condition, compared to control site Both Male and Female Adult Maple Ridge, British Columbia 24 - 62 animals 0, 3.0 kg/ha TOX-REPRO - physiology up to 4 yr field application Toxicity Factor Datasets
GLYPHOSATE no effect average duration of life during summer and winter periods Both Male and Female Adult Maple Ridge, British Columbia 2 - 40 animals 0, 3.0 kg/ha TOX-MORT - mortality in the field up to 4 yr field application Toxicity Factor Datasets
Citation:

Toxicological foundations of ecological risk assessment: biomarker development and interpretration based on laboratory and wildlife species

Author(s)
Dickerson, Richard L., Michael J. Hooper, Nicholas W. Gard, George P. Cobb and Ronald J. Kendall
Pages
65-69
Year
Issue
Supp.
Volume
102
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
METHYLCHLORANTHRENE (3-) 0.14 mg/kg/d ED50 for immunosuppression, measured as suppression of plaque forming cell response Male Juvenile Not Reported NR TOX-Non-Repro-Sublethal - organ/system effects 1, 3, 5, 7, 9 d intraperitoneal Toxicity Factor Datasets
METHYLCHLORANTHRENE (3-) 1.24 mg/kg/d ED50 for ethoxyresorufin-O-dealkylase (EROD) activity Male Juvenile Not Reported NR TOX-Non-Repro-Sublethal - cellular/biochemical effects 1, 3, 5, 7, 9 d intraperitoneal Toxicity Factor Datasets
DIBENZ[A]ANTHRACENE (1,2,5,6-) 0.048 mg/kg/d ED50 for immunosuppression, measured as suppression of plaque forming cell response Male Juvenile Not Reported NR TOX-Non-Repro-Sublethal - organ/system effects 1, 3, 5, 7, 9 d intraperitoneal Toxicity Factor Datasets
DIBENZ[A]ANTHRACENE (1,2,5,6-) 0.85 mg/kg/d ED50 for ethoxyresorufin-O-dealkylase (EROD) activity Male Juvenile Not Reported NR TOX-Non-Repro-Sublethal - cellular/biochemical effects 1, 3, 5, 7, 9 d intraperitoneal Toxicity Factor Datasets
DIMETHYLBENZ[A]ANTHRACENE (7,12-) 0.026 mg/kg/d ED50 for immunosuppression, measured as suppression of plaque forming cell response Male Juvenile Not Reported NR TOX-Non-Repro-Sublethal - organ/system effects 1, 3, 5, 7, 9 d intraperitoneal Toxicity Factor Datasets
Citation:

Uptake of environmental contaminants by small mammals in pickleweed habitats of San Francisco Bay, California

Author(s)
Clark, Jr., Donald R., Kevin S. Foerster, Carolyn M. Marn and Roger L. Hothem
Pages
389-396
Year
Volume
22
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 COMPOUNDS, LEAD COMPOUNDS, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS, SELENIUM COMPOUNDS no effect incidence of liver and kidney histopathologies was not related to contaminant concentrations Not Reported Not Reported salt marsh, San Pablo and San Francisco Bays 26 animals Range of tissue means (ppm, dry wt.): Liver; 0.05-1.08 (mercury), 2.32-3.53 (selenium). Kidney; 0.4-2.11 (cadmium), 0.6-1.92 (lead). Carcass; 0.02-0.22 (PCBs). TOX-Non-Repro-Sublethal - cellular/biochemical effects NR site contamination Toxicity Factor Datasets

Lithobates catesbeianus

Citation:

3-Trifluoromethyl-4-nitrophenol (TFM) toxicity and heptic microsomal UDP-glucuronyltransferase activity in larval and adult bullfrogs

Author(s)
Kane, Andrew S., Wesley W. Day, Renate Reimschuessel and Michael M. Lipsky
Pages
51-60
Year
Volume
27
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) 11.62 mg/kg bw (95% CL: 10.71-13.14) LD50 Not Reported Tadpole 5 NR TOX-MORT - toxicity benchmarks single intraperitoneal Toxicity Factor Datasets
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) 15.35 mg/kg bw (95% CL: 8.72-21.98) LD50 Not Reported Adult 7 NR TOX-MORT - toxicity benchmarks single intraperitoneal Toxicity Factor Datasets
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) 0.95 mg/l (95% CL: 0.72 - 1.14) LC50 Not Reported Tadpole 5 NR TOX-MORT - toxicity benchmarks 24 hr waterborne Toxicity Factor Datasets
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) 12.99 mg/l (95% CL: 6.75 - 19.22) LC50 Not Reported Adult 7 NR TOX-MORT - toxicity benchmarks 24 hr waterborne Toxicity Factor Datasets
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) effect observed at 1.0 - 3.0 mg/l growth development arrested Not Reported Embryo Not Reported 0.1, 0.25, 0.5, 1.0, 2.0, 3.0 mg/l TOX-REPRO - development 96 hr waterborne Toxicity Factor Datasets

Citation:

Effects of some insecticides on productivity of burrowing owls

Author(s)
James, Paul C. and Glen A. Fox
Pages
65-71
Year
Issue
2
Volume
45
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
CARBOFURAN decrease proportion of pairs that raised at least one young (vs. untreated controls) Both Male and Female Adult Saskatchewan 13 pairs standard application within 50 m of burrow TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets
CARBARYL no effect proportion of pairs that raised at least one young (vs. untreated controls) Both Male and Female Adult Saskatchewan 30 pairs standard application within 50 m of burrow TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets
CARBOFURAN decrease maximum number of young observed per nest (vs. untreated controls) Both Male and Female Juvenile Saskatchewan 13 pairs standard application within 50 m of burrow TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets
CARBOFURAN no effect maximum number of young observed per nest (vs. untreated controls) Both Male and Female Juvenile Saskatchewan 30 pairs standard application within 50 m of burrow TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets
CARBARYL, CARBOFURAN no effect maximum number of young observed per nest (vs. untreated controls) Both Male and Female Juvenile Saskatchewan 18 pairs standard application within 400 m of burrow TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets
CARBARYL, CARBOFURAN no effect proportion of pairs that raised at least 1 young (vs. untreated controls) Both Male and Female Adult Saskatchewan 18 pairs standard applications within 400 m of burrow TOX-REPRO - reproductive success NR multiple Toxicity Factor Datasets

Athene cunicularia

Citation:

Is the operational use of strychnine to control ground squirrels detrimental to burrowing owls?

Author(s)
James, Paul C., Glen A. Fox and Thomas J. Ethier
Pages
120-123
Year
Issue
4
Volume
24
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
STRYCHNINE no effect proportion of pairs that raised at least 1 young Both Male and Female Adult Saskatchewan 27 pr 2.5 mg/g dry bait application for ground squirrels TOX-REPRO - reproductive success NR diet (secondary exposure) Toxicity Factor Datasets
STRYCHNINE no effect number of young produced per nest attempt Both Male and Female Juvenile Saskatchewan 27 pr 2.5 mg/g dry bait application for ground squirrels TOX-REPRO - reproductive success NR diet (secondary exposure) Toxicity Factor Datasets
STRYCHNINE no effect number of chicks produced per successful pair Both Male and Female Juvenile Saskatchewan 27 pr 2.5 mg/g dry bait application for ground squirrels TOX-REPRO - reproductive success NR diet (secondary exposure) Toxicity Factor Datasets
STRYCHNINE no effect chick mass index Both Male and Female Juvenile Saskatchewan 27 pr 2.5 mg/g dry bait application for ground squirrels TOX-REPRO - development NR diet (secondary exposure) Toxicity Factor Datasets
STRYCHNINE decrease adult body weight Both Male and Female Adult Saskatchewan 27 pr 2.5 mg/g dry bait application for ground squirrels TOX-Non-Repro-Sublethal - whole animal NR diet (secondary exposure) Toxicity Factor Datasets
Citation:

Heptachlor seed treatment contaminates hawks, owls, and eagles of Columbia Basin, Oregon

Author(s)
Henny, Charles J., Lawrence J. Blus and T. Earl Kaiser
Pages
41-48
Year
Issue
2
Volume
18
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
HEPTACHLOR no effect mean clutch size Female Adult Columbia Basin 6 nests 0.16-0.19 ppm (wet wt) TOX-REPRO - reproductive success NR in ovo Toxicity Factor Datasets
HEPTACHLOR no effect eggshell thickness Female Adult Columbia Basin 6 nests 0.16-0.19 ppm (wet wt) TOX-REPRO - physiology NR in ovo Toxicity Factor Datasets

Anas platyrhynchos

Citation:

DDE, PTH, and Eggshell Thinning in Mallard, Pheasant and Ring Dove

Author(s)
Haseltine, S., K. Uelbelhart, T. Peterle and S. Lustick
Pages
139-145
Year
Issue
2
Volume
11
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'-) 20.4% decrease eggshell thickness versus controls Female Adult 6 hens; 45 total eggs 0, 10 ppm TOX-REPRO - physiology 3 weeks Diet Toxicity Factor Datasets
DDE (4,4'-) 17% decrease serum calcium versus controls Female Adult 6 hens; 45 total eggs 0, 10 ppm TOX-Non-Repro-Sublethal - cellular/biochemical effects 3 weeks Diet Toxicity Factor Datasets
DDE (4,4'-) no effect serum calcium after PTH injection versus controls Female Adult 6 hens; 45 total eggs 0, 10 ppm TOX-Non-Repro-Sublethal - cellular/biochemical effects 3 weeks Diet Toxicity Factor Datasets
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