Carnivores (Carnivora)
Coyote (Canis latrans)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 11.3 | kg | B | Juvenile | 12 | Eastern New Brunswick | Exposure Factor Datasets | 0.5-2.0 y | CANADA | 0.3 |
Body Weight - Mean | 12.5 | kg | B | Adult | 15 | Eastern New Brunswick | Exposure Factor Datasets | 2.5-4.0 y | CANADA | 0.5 |
Body Weight - Mean | 13.8 | kg | B | Adult | 18 | Eastern New Brunswick | Exposure Factor Datasets | 4.5-6.0 y | CANADA | 0.5 |
Body Weight - Mean | 14.9 | kg | B | Adult | 19 | Eastern New Brunswick | Exposure Factor Datasets | 6.5-8.0 y | CANADA | 0.6 |
Body Weight - Mean | 15.2 | kg | B | Adult | 13 | Eastern New Brunswick | Exposure Factor Datasets | >8.0 y | CANADA | 0.8 |
Body Fat (total or %) | 12 | % | F | Both Adults and Juveniles | 39 | Eastern New Brunswick | Exposure Factor Datasets | CANADA | 0.6 | |
Body Fat (total or %) | 10.6 | % | M | Both Adults and Juveniles | 38 | Eastern New Brunswick | Exposure Factor Datasets | CANADA | 0.6 | |
Body Fat (total or %) | 10 | % | B | Juvenile | 12 | Eastern New Brunswick | Exposure Factor Datasets | 0.5-2.0 y | CANADA | 0.9 |
Body Fat (total or %) | 10.8 | % | B | Adult | 15 | Eastern New Brunswick | Exposure Factor Datasets | 2.5-4.0 y | CANADA | 1.1 |
Body Fat (total or %) | 11.6 | % | B | Adult | 18 | Eastern New Brunswick | Exposure Factor Datasets | 4.5-6.0 y | CANADA | 0.7 |
Body Fat (total or %) | 11.4 | % | B | Adult | 19 | Eastern New Brunswick | Exposure Factor Datasets | 6.5-8.0 y | CANADA | 1.1 |
Body Fat (total or %) | 12.6 | % | B | Adult | 13 | Eastern New Brunswick | Exposure Factor Datasets | >8.0 y | CANADA | 1.1 |
Body Weight - Mean | 13.1 | kg | F | Both Adults and Juveniles | 39 | Eastern New Brunswick | Exposure Factor Datasets | CANADA | 0.3 | |
Body Weight - Mean | 14.6 | kg | M | Both Adults and Juveniles | 38 | Eastern New Brunswick | Exposure Factor Datasets | CANADA | 0.5 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Rodents: 64, lagomorphs: 61, deer: 35, carnivores: 56, pets: 41, soricomorphs: 10, unknown: 14, native seeds: 27, non-native seeds: 35, unknown seeds: 19, trash: 27 | Frequency by group | NR | Both Adults and Juveniles | 64 | Denver metro area | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 6.6 | pups | B | Pup | 55 | Central Western, Northwestern, Great Valley, and Sierra Nevada bioregion | Exposure Factor Datasets | USA | 2.2 | |
Body Weight - Mean | See citation Figure 4 | Body mass by reproductive period | kg | F | Adult | Not reported | Central Western, Northwestern, Great Valley, and Sierra Nevada bioregion | Exposure Factor Datasets | USA | |
Body Fat (total or %) | See citation Figure 4 | Visceral fat index | F | Adult | Not reported | Central Western, Northwestern, Great Valley, and Sierra Nevada bioregion | Exposure Factor Datasets | USA | ||
Body Weight - Mean | 10.1 | First year non-reproductive | kg | M | Juvenile | Not reported | Central Western, Northwestern, Great Valley, and Sierra Nevada bioregion | Exposure Factor Datasets | USA | 0.4 |
Body Weight - Mean | 11.5 | First year reproductive | kg | M | Juvenile | Not reported | Central Western, Northwestern, Great Valley, and Sierra Nevada bioregion | Exposure Factor Datasets | USA | 0.2 |
Body Weight - Mean | 12.5 | Adult reproductive | kg | M | Juvenile | Not reported | Central Western, Northwestern, Great Valley, and Sierra Nevada bioregion | Exposure Factor Datasets | USA | 0.3 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type |
---|---|---|---|---|
Body Weight - Mean | Review | Reported weights across North America | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | High diet: 6.0, low diet: 4.8 | Pups | F | Adult | 11 | National Wildlife Research Center | Exposure Factor Datasets | Breeding | USA | High diet: 0.5, low diet: 0.26 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: 72.7, birds: 7.3, reptiles: 16.4, insects: 12.7, crustaceans: 1, vegetable matter: 60 | Frequency of occurrence | B | Both Adults and Juveniles | 59 | Chamela-Cuixmala Biosphere Reserve | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Insect: 25.6, reptile: 1.5, bird: 3.0, small rodent: 27.0, large rodent: 27.9, leporidae: 12.2, cattle: 24.1, pronghorn: 1.4, unknown mammal: 0.2, crops: 12.3, other seeds: 5.0, other vegetation: 22.9 | Frequency of occurrence, seasonal mean | % | NR | Both Adults and Juveniles | 280 | Dallam County: continuous short-grass prairie | Exposure Factor Datasets | USA |
Dietary Composition | Insect: 17.0, reptile: 0, bird: 6.7, small rodent: 37.3, large rodent: 30.3, leporidae: 18.2, cattle: 9.7, pronghorn: 1.7, crops: 16.6, other seeds: 2.2, other vegetation: 15.8 | Frequency of occurrence, seasonal mean | % | NR | Both Adults and Juveniles | 186 | Stratford: fragmented short-grass prairie | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation for values: Lepus californicus, Peromyscus maniculatus, Reinthrodontomys megalotis, Lemmiscus curtatus, Menniscus curtatus, Perognathus parvus, Dipodomys spp., other rodents | Prey identified by teeth in coyote scat | NR | Not Reported | 39-58 | Curlew Valley | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.84 | Breeding season survival | % | B | Adult | Tallahala Wildlife Management Area | Exposure Factor Datasets | USA | 0.05 |
Survival/ Mortality | 0.89 | Winter season survival | % | B | Adult | Tallahala Wildlife Management Area | Exposure Factor Datasets | USA | 0.04 |
Survival/ Mortality | 0.98 | Pup-rearing season survival | % | B | Adult | Tallahala Wildlife Management Area | Exposure Factor Datasets | USA | 0.01 |
Exposure Endpoint Type | Endpoint Value | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|
Dietary Composition | See citation Figure 3 for values: Deer, rodent, lagmorph, avian, herptofauna, unknown mammal, plant | 128 | MeadWestvaco Wildlife and Ecosystem Research Forest |
Exposure Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIPHACINONE | 0.6 [0.3 - 1.2 (95% CL)] mg/kg | LD50 | Both Male and Female | Adult | 2/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LITHIUM CHLORIDE | decrease @ 18g/1500 g/d | body weight gain in nursing pups of mothers fed LiCl contaminated diet | Both Male and Female | Both Adults and Juveniles | 4 pups/2 adults | Toxicity Factor Datasets | 10-19d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | increase @ 535-9754 ppb | all coyotes died after ingesting 1-2 ground squirrels poisoned with sodium monofluoroacetate | Not Reported | Pup | 2 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | increase @ 0.240 - 0.625 mg 1080/kg coyote | 5/6 coyotes died after eating squirrels contaminated with 1080 bait (sodium monofluroacetate) | Not Reported | Adult | 4-6/dose | Toxicity Factor Datasets | Laboratory | |
STRYCHNINE | increase @ 1.321 - 2.860 mg strychnine/kg coyote | 1/4 coyotes died after ingesting contaminated ground squirrels | Not Reported | Adult | 4/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | increase @ 6.7 kg/ha | 5/6 radio-equipped coyotes were found dead during post-treatment period | Not Reported | Not Reported | 6 | Exeter, Tulare | Toxicity Factor Datasets | Tulare |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PENTACHLOROBENZENE | no effect | mean body mass and appearance of eyes, gums, teeth and fur, compared to controls | Both Male and Female | Adult | 3/dose | Toxicity Factor Datasets | 2 - 12 yrs | Laboratory | |
PENTACHLOROBENZENE | no effect | serum chemistry and hematological profile, compared to control | Both Male and Female | Adult | 3/dose | Toxicity Factor Datasets | 2 - 12 yrs | Laboratory | |
PENTACHLOROBENZENE | see citation | figures of feces and serum concentrations over time at the tested doses | Both Male and Female | Adult | 3/dose | Toxicity Factor Datasets | 2 - 12 yrs | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PARA-AMINOPROPIOPHENONE | 5.6 [3.0-10.4 (95% CI)] mg/kg | LD50 | Not Reported | Not Reported | 4/dose | Toxicity Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
Population Density | review | Not Reported | Not Reported | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
Metabolic Rate | 0.0015 | basal metabolic rate at 22-26C estimated via oxygen consumption | watts/g | Both Male and Female | Not Reported | 3 | captured in Maricopa County, AZ | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | rodents (53%); fruits and seeds (32%); deer (20%); insects (19%); avian (19%); lagomorphs (11%); armadillo (9%); cattle (6%); reptile (4%) | overall % occurrence in scats | % | Both Male and Female | Both Adults and Juveniles | 361 scats | Wichita Mountains National Wildlife Refuge | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | grass species (78%); meadow vole (73%); northern pocket gopher (43%); insects (40%); passerines (30%); lagomorphs (24%); cricetid mice (19%); mule deer (13%) | % occurrence of food items in scats | % | Not Reported | Not Reported | 54 | Rocky Flats Nuclear Weapons Plant, Denver | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | range of means for two yearling age groups | kg | Female | Juvenile | 22 - 32 | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | Exposure Factor Datasets | 1.5 - 2.0 yrs |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Body Fat (total or %) | 12.08 | body fat content | % | Both Male and Female | Both Adults and Juveniles | 22 | Quebec | Exposure Factor Datasets | CANADA | 7.36 SD |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Home Range | 68 | km2 | Male | Adult | 25 | Aitkin and Itasca counties | Exposure Factor Datasets |
Long-tailed Weasel (Mustela frenata)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | Rainy season: 0.10, dry: 0.18 | Estimated average density by season | individuals/km2 | NR | Not Reported | See citation | Sierra de Oaxaca | Exposure Factor Datasets | MEXICO |
Population Density | Cloud forest: 0.26, semi-evergreen forest: 0.01 | Estimated average density by vegetation type | individuals/km2 | NR | Not Reported | See citation | Sierra de Oaxaca | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type |
---|---|---|---|---|
Survival/ Mortality | Review | Daily survival | Exposure Factor Datasets | |
Survival/ Mortality | Review | Annual survival index | Exposure Factor Datasets |
Kit Fox (Vulpes macrotis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Population Density | See citation Table 1 | Number/km2 | B | Both Adults and Juveniles | See citation | Naval Petroleum Reserve | Exposure Factor Datasets | Kern | USA | |
Survival/ Mortality | See citation | Survival | B | Both Adults and Juveniles | See citation | Naval Petroleum Reserve | Exposure Factor Datasets | Kern | USA | |
Clutch or Litter Size | See citation Table 6 | Pups/litter | B | Pup | See citation | Naval Petroleum Reserve | Exposure Factor Datasets | Kern | USA | |
Dietary Composition | Leporids: 44.1, kangaroo rats: 31.0, pocket mice: 1.2, antelope squirrels: 2.3, other rodents: 4.1, sheep: 0.8, birds: 2.5, snakes: 1.4, lizards: 0.1, orthopterans: 6.4, colopterans: 1.3, other arthropods: 0.1, other items: 6.9 | Frequency of occurrence | % | Both Adults and Juveniles | 4393 | Naval Petroleum Reserve | Exposure Factor Datasets | Kern | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 2.69 | Pups/litter | B | Pup | 32 | Upper Chuckwalla Valley | Exposure Factor Datasets | Riverside | USA | 0.3 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 80 | Mortality | % | B | 56 | Upper Chuckwalla Valley | Exposure Factor Datasets | Riverside | USA | ||
Survival/ Mortality | 2012-2013: pair formation: 0.868, pup-rearing: 0.944, dispersal: 1.000, annual: 0.752; 2013-2014: pair formation: 0.891, pup-rearing: 1.000, annual: 0.892 | Survival | M | Adult | 56 | Upper Chuckwalla Valley | Exposure Factor Datasets | Riverside | USA | 2012-2013: pair formation: 0.014, pup-rearing: 0.0.14, dispersal: 0.000, annual: 0.010; 2013-2014: pair formation: 0.023, pup-rearing: 0.000, annual: 0.017 | |
Survival/ Mortality | 2012-2013: pair formation: 0.885, pup-rearing: 0.1.000, dispersal: 1.000, annual: 0.885; 2013-2014: pair formation: 0.836, pup-rearing: 0.923, annual: 0.772 | Survival | F | Adult | 56 | Upper Chuckwalla Valley | Exposure Factor Datasets | Riverside | USA | 2012-2013: pair formation: 0.0.033, pup-rearing: 0.000, dispersal: 0.0000, annual: 0.012; 2013-2014: pair formation: 0.0.028, pup-rearing: 0.019, annual: 0.022 | |
Survival/ Mortality | 2012-2013: pair formation: 0.876, pup-rearing: 0..969, dispersal: 1.000, annual: 0.809; 2013-2014: pair formation: 0.864, pup-rearing: 0.9640, annual: 0.833 | Survival | B | Adult | 56 | Upper Chuckwalla Valley | Exposure Factor Datasets | Riverside | USA | 2012-2013: pair formation: 0.019, pup-rearing: 0.001, dispersal: 0.000, annual: 0.012; 2013-2014: pair formation: 0.019, pup-rearing: 0.011, annual: 0.014 |
Striped Skunk (Mephitis mephitis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | Claytonville: 0.27, Halfway: 0.71, Olton: 0.63, Plainview: 0.10 | Individuals/12.8 sq km | Individuals/12.8 sq km | B | Both Adults and Juveniles | 104 | Lamb/Hale/Swisher counties | Exposure Factor Datasets | USA |
Population Density | Claytonville: 0.36, Halfway: 0.59, Olton: 0.38, Plainview: 0.20 | Individuals/12.8 sq km | Individuals/12.8 sq km | B | Both Adults and Juveniles | 104 | Lamb/Hale/Swisher counties | Exposure Factor Datasets | USA |
Survival/ Mortality | 1994: 0.40, 1995: 0.48 | Annual survival | % | B | Both Adults and Juveniles | 104 | Lamb/Hale/Swisher counties | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 7 | Offspring/litter | B | Neonate | 3 | Delta Waterfowl and Wetlands Research Station |
Exposure Factor Datasets | CANADA | |
Clutch or Litter Size | 5.5 | Offspring/litter | B | Neonate | 11 | Delta Waterfowl and Wetlands Research Station |
Exposure Factor Datasets | CANADA | |
Survival/ Mortality | 97.9 | Survival >60 d post weaning | % | B | 93 | Delta Waterfowl and Wetlands Research Station |
Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 1800 | g | F | Adult | 1 | Baja California | Exposure Factor Datasets | MEXICO |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | 0.347 mg/kg (95% CI; 0.212 - 0.541 mg/kg) | median lethal dose | Not Reported | Not Reported | 5-6 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | 165 mg administered to coyote (95%CI; 107 - 392 mg) | LD50; based on dose given to coyote; skunks were fed contaminated coyote tissue | Not Reported | Not Reported | 1-8 per dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PARA-AMINOPROPIOPHENONE | > 400 mg/kg | LD50 | Not Reported | Not Reported | 2/dose | Toxicity Factor Datasets | Laboratory |
California Sea Lion (Zalophus californianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | See citation Table 3 | Abundance | M | Adult | See citation | San Benito Archipelao | Exposure Factor Datasets | MEXICO |
Population Density | See citation Table 3 | Abundance | M | Juvenile | See citation | San Benito Archipelao | Exposure Factor Datasets | MEXICO |
Population Density | See citation Table 3 | Abundance | F | Adult | See citation | San Benito Archipelao | Exposure Factor Datasets | MEXICO |
Population Density | See citation Table 3 | Abundance | B | Juvenile | See citation | San Benito Archipelao | Exposure Factor Datasets | MEXICO |
Population Density | See citation Table 3 | Abundance | B | Pup | See citation | San Benito Archipelao | Exposure Factor Datasets | MEXICO |
Population Density | Review; See citation Table 4 | Abundance | B | Pup | See citation | San Benito Archipelao | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 86 | Maternal | kg | F | Adult | 20 | Coastal sites | Exposure Factor Datasets | USA | 15 | |
Body Weight - Mean | 5 | Premature fetuses | kg | B | Embryo | 7 | Coastal sites | Exposure Factor Datasets | Premature fetuses | USA | 2 |
Body Weight - Mean | 7 | Late-term fetuses | kg | B | Embryo | 9 | Coastal sites | Exposure Factor Datasets | Late-term fetuses | USA | 1 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Survival/ Mortality | See citation Table 5 | Model estimates of age-specific survival probability | B | Pup | See citation | Los Islotes colony in southern Gulf of California | Exposure Factor Datasets | MEXICO |
Survival/ Mortality | 0.9 | Model estimates of age-specific survival probability | B | Juvenile | See citation | Los Islotes colony in southern Gulf of California | Exposure Factor Datasets | MEXICO |
Survival/ Mortality | 0.904 | Model estimates of age-specific survival probability for young adults | B | Adult | See citation | Los Islotes colony in southern Gulf of California | Exposure Factor Datasets | MEXICO |
Survival/ Mortality | 0.746 | Model estimates of age-specific survival probability for old adults | B | Adult | See citation | Los Islotes colony in southern Gulf of California | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | See citation Figure 1 | Annual food consumption | B | Both Adults and Juveniles | 26 | Harderwijk Marine Mammal Park | Exposure Factor Datasets | NETHERLANDS |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 9.4 | Newborn weight | kg | M | Pup | 9 | Gulf of Mexico | Exposure Factor Datasets | MEXICO | 0.35 |
Body Weight - Mean | 7.7 | Newborn weight | kg | F | Pup | 7 | Gulf of Mexico | Exposure Factor Datasets | MEXICO | 0.45 |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Cephalopods: 25%, fishes: 65%, crustacean: 7% | % occurrence | NR | Not Reported | 289 scat samples | San Benito Islands | Exposure Factor Datasets | MEXICO |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, LEAD COMPOUNDS, SELENIUM COMPOUNDS, ZINC COMPOUNDS | increase | incidence of epileptiform seizures and subsequent death associated with "unusual" Se levels | Female | Adult | 1 | Toxicity Factor Datasets | 18 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturtion associated with elevated DDT and PCB residues, compared to full term parturient group | Female | Adult | 4-6/group | San Miguel Island | Toxicity Factor Datasets | 6 - 15 yrs |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENIUM COMPOUNDS | 36.11 - 88.4 ug/g wet wt (liver); 7.12 - 32.8 ug/g wet wt (kidney) | selenium concentration range in liver and kidney of dead animals | Not Reported | Not Reported | 3 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturition associated with elevated DDT and PCB levels, compared to full term parturient group | Female | Adult | 10/group | San Miguel Island | Toxicity Factor Datasets | 6 - 14 yrs |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, DDT (Technical Grade Mixture), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | increase | incidence of kidney histopathological lesions in "sick" or dead animals compared to "healthy" animals, consistent with diagnosis of leptospirosis | Male | Adult | 2-8/group | Toxicity Factor Datasets | 5 - 9 yr |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
BROMINE COMPOUNDS, CADMIUM COMPOUNDS, COPPER COMPOUNDS, IRON COMPOUNDS, MANGANESE COMPOUNDS, MERCURY COMPOUNDS, SELENIUM COMPOUNDS, SILVER COMPOUNDS, ZINC COMPOUNDS | increase | incidence of premature parturition correlated with different metal concentrations and ratios | Both Male and Female | Both Adults and Juveniles | 10/group | Toxicity Factor Datasets |
Sea Otter (Enhydra lutris)
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
CRUDE OILS | review | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets |
Southern Sea Otter (Enhydra lutris ssp. nereis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
TIN, BUTYL | increase | otters that died of infectious disease contained butyltin liver concentrations greater than those that died of trauma | Both Male and Female | Adult | 8-14 animals | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | increase | otters that died from infectious diseases contained higher liver DDTs concentrations that those that died of trauma | Both Male and Female | Adult | 4-8 | Toxicity Factor Datasets |
Desert Kit Fox (Vulpes macrotis ssp. arsipus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | 0.22 mg/kg bw (95% CI; 0.15 - 0.34 mg/kg) | LD50 | Not Reported | Adult | 2 animals/dose | Toxicity Factor Datasets | Laboratory | |
STRYCHNINE | 0.75 mg/kg bw (95% CI; 0.33-1.69 mg/kg) | LD50 | Not Reported | Adult | 2 animals/dose | Toxicity Factor Datasets | Laboratory | |
ZINC PHOSPHIDE | 93 mg/kg bw (95% CI; 62-140 mg/kg) | LD50 | Not Reported | Adult | 2 animals/dose | Toxicity Factor Datasets | Laboratory |