Mammals
Kit Fox (Vulpes macrotis)
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 |
---|---|---|---|---|---|---|---|---|---|
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 | 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 |
Coyote (Canis latrans)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
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 | 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 | 13.1 | 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 | 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 | 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 | 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 |
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 |
---|---|---|---|---|---|---|---|---|
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 |
Pallid Bat (Antrozous pallidus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Acrididae: 16.1, Ceuthophilus californianus: 4.7, Gryllidae: 8.3, Stenopelmatus fuscus: 27.3, Microcentrum rhombifolium: 0.6, Diptera: 0.2, Lepidoptera: 5.8, Carabidae: 8.4, Prionus californicus: 1.0, Chilopoda: 11.8, Solpugidae: 7.8, Lycosidae: 7.8 | Percentage of total volume | % | M | Adult | 116 | Exposure Factor Datasets | Marin | USA | |
Dietary Composition | Tytthotyle maculata: 9.9, Grylliacrididae: 1.0, Gryllus: 4.0, Diptera: 0.3, Lepidoptera: 5.7, Coleoptera: 2.3, Cyclocephla longula: 24.4, Tenebrionidae: 3.6, Edrotes ventricosus: 0.6, Hippomelas: 21.0, Tiphiidae: 1.5, Pentatomidae: 4.3, Geocoris: 0.1, Myrmeleontidae: 4.9, Solpugidae: 14.1 | Percentage of total volume | % | M | Adult | 29 | Exposure Factor Datasets | Kern | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Insecta: 81.3, arachnida: 17.2, reptilia: 0.9 | % | B | Both Adults and Juveniles | Not reported | University of Texas at El Paso Indio Mountains Research Station | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Arachnida: 0.8, insecta: 97.8, other: 1.6 | Perent frequency | B | Both Adults and Juveniles | 93 | Nk'Mip Indian Band Reserve | Exposure Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 5.8 ppm; range, 3.6-8.2 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | 4 bats | near cities | Toxicity Factor Datasets | MEXICO |
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 |
Little Pocket Mouse (Perognathus longimembris)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 8.6 | g | NR | Not Reported | 2 | East Mojavae National Preserve | Exposure Factor Datasets | San Bernardino | USA | 0.035 |
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 | 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 |
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 |
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 |
California Ground Squirrel (Spermophilus beecheyi)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|---|
Inhalation Rate | 0.4 | Air intake | m3/d | M | Yearling | 7 | Altamont Hills | Exposure Factor Datasets | 9 m | San Joaquin | USA |
Exposure Endpoint Type | Endpoint Value | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|
Body Weight - Mean | Historical: 551.97, modern: 527.09 | Historical: 117, modern: 55 | Exposure Factor Datasets | USA | Historical: 124.77, modern: 126.93 |
Brush Rabbit (Sylvilagus bachmani)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 87 | % mortality | NR | Not Reported | 325 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Reintroduced, captive-bred | USA | NR |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | See citation Table 3 | Overlap index | B | Not Reported | 325 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Reintroduced, captive-bred | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 272.2 | g | B | Juvenile | 340 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Born in propagation facillity | USA | 141.72 | |
Survival/ Mortality | 0.79 | In captivity | Survival rate | B | Not Reported | 62 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Born/raised in propagation facillity | USA | |
Survival/ Mortality | 0.86 | In captivity | Survival rate | B | Not Reported | 278 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Born/raised in propagation facillity | USA | |
Survival/ Mortality | 0.23 | In captivity | Survival rate | B | Not Reported | 49 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Born/raised in propagation facillity then released | USA | |
Survival/ Mortality | 0.22 | In captivity | Survival rate | B | Not Reported | 196 | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets | San Joaquin | Born/raised in propagation facillity then released | USA |
Broad-footed Mole (Scapanus latimanus)
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Body Weight - Mean | Review | B | Not Reported | See citation | Exposure Factor Datasets | USA | |
Clutch or Litter Size | Review | B | Adult | Exposure Factor Datasets |
California Vole (Microtus californicus)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | 1 | Animal number | M | Adult | 1 | Sierra San Pedro M´artir, Baja California, Mexico |
Exposure Factor Datasets | Subadult | MEXICO |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 39.1 | g | F | Not Reported | 21 | Davis, California | Exposure Factor Datasets | Yolo | USA | 2.5 | |
Body Weight - Mean | 39.4 | g | F | Not Reported | 25 | Davis, California | Exposure Factor Datasets | Yolo | USA | 3.6 | |
Body Weight - Mean | 46.1 | g | M | Not Reported | 14 | Castroville, California | Exposure Factor Datasets | Monterey | Previously exposed to anticoagulant rodenticides | USA | 3 |
Body Weight - Mean | 35.2 | g | F | Not Reported | 11 | Castroville, California | Exposure Factor Datasets | Monterey | Previously exposed to anticoagulant rodenticides | USA | 4.6 |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | decrease | number of hardwood trees in study area | Both Male and Female | Both Adults and Juveniles | 1 study area | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | proportion of trapped animals in breeding condition | Both Male and Female | Both Adults and Juveniles | 151 | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | increase | survival over summer and winter | Both Male and Female | Both Adults and Juveniles | 545 | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | juvenile growth rate (summer and fall) | Both Male and Female | Both Adults and Juveniles | 283 | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | increase@ 80 mg/kg bw/d | white blood cell count | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | increase @ 80 mg/kg bw/d | plaque forming cell count/g spleen | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | no effect | reciprocal of hemolysin titer (against sheep rbc) | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TERBUFOS | increase @ 1.69 and 2.48 mg/kg | incidence of tremors and rapid breathing | Both Male and Female | Not Reported | 70 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD ACETATE | no effect | incidence of congenital malformations | Both Male and Female | Juvenile | 5 breeding pairs/dose | Toxicity Factor Datasets | 2-3 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DIELDRIN | increase | population size at contaminated vs reference sites | Both Male and Female | Both Adults and Juveniles | Not Reported | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
DIELDRIN | increase | % of female deer mice exhibiting signs of reproduction increased as dieldrin levels increased at contaminated vs control sites | Female | Adult | Not Reported | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|
ALDICARB | no effect | food intake | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory | |
ALDICARB | no effect | growth rate estimated by changes in body weight | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory | |
ALDICARB | no effect | daily activity measured as time spend in burrow or moving in/out of burrow | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 | Toxicity Factor Datasets | Laboratory | |
AZINPHOS-METHYL (GUTHION) | 1180 ppm diet (95% CL: 709-1485, slope = 1.88 +/- 0.57SE) | LD50 | Both Male and Female | Adult | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
AZINPHOS-METHYL (GUTHION) | 2425 ppm diet (95% CL: 1856-3245, slope = 1.45 +/- 0.25SE) | LD50 | Both Male and Female | Adult | 10 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DICHLOROPHENOXY-ACETIC ACID (2,4-) | no effect | changes in population density; treated versus control site | Not Reported | Both Adults and Juveniles | 6 study areas/dose | Gunnison County and Saquache County, (elev., 8500 - 9300 ft.) | Toxicity Factor Datasets |
DICHLOROPHENOXY-ACETIC ACID (2,4-) | no effect | mean litter size, based upon number of viable embryos or placental scars | Female | Adult | 66-77 animals | Gunnison County and Saquache County, (elev., 8500 - 9300 ft.) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | 0.29 | relative density (vs. control) in sprayed area | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHIOCARB | effect @ 0.03-0.5% | suppression of feeding on treated corn | Both Male and Female | Not Reported | 10 - 12 animals/dose | Toxicity Factor Datasets | Laboratory |
Merriam's Kangaroo Rat (Dipodomys merriami)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
HEXACHLOROETHANE | decrease | mean chromosomal abberrations per cell, compared to controls (not exposed to obscurant smoke) | Not Reported | Not Reported | 3-4/group | Goldstone, Fort Irwin | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLPARATHION | no effect | discrimination between seeds and beads | Both Male and Female | Adult | 22 animals | Toxicity Factor Datasets | Laboratory | |
METHYLPARATHION | 18-19 % decrease | brain cholinesterase activity, compared to control | Both Male and Female | Adult | 2 animals | Toxicity Factor Datasets | Laboratory |