Coyote (Canis latrans)
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 | |
Longevity | review | Not Reported | Adult | Not Reported | Exposure Factor Datasets | |
Clutch or Litter Size | review | Female | Adult | 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 |
Body Weight - Mean | range of means for two adult age groups | kg | Male | Adult | 69 - 76 | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | Exposure Factor Datasets | >2.5 - >3.0 yrs |
Body Weight - Mean | range of means for two adult age groups; excluding those in latter half of gestation | kg | Female | Adult | 43-66 | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | Exposure Factor Datasets | >2.5 - >3.0 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 | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Home Range | 68 | km2 | Male | Adult | 25 | Aitkin and Itasca counties | Exposure Factor Datasets | |
Home Range | 16 | km2 | Female | Adult | 25 | Aitkin and Itasca counties | Exposure Factor Datasets | |
Home Range | prior to dispersal | km2 | Both Male and Female | Juvenile | 50 | Aitkin and Itasca counties | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Population Density | 0.77 | #/km2 | Not Reported | Pup | Not Reported | National Elk Refuge, Jackson Hole | Exposure Factor Datasets | 0.33 SD | |
Population Density | 1.37 | post-whelping population density | #/km2 | Not Reported | Both Adults and Juveniles | Not Reported | National Elk Refuge, Jackson Hole | Exposure Factor Datasets | |
Population Density | peak density | #/km2 | Not Reported | Adult | Not Reported | National Elk Refuge, Jackson Hole | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Age at Fledging, Metamorphosis, Weaning | 30 | d | Both Male and Female | Juvenile | 6 | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | rabbits (70.6%); livestock (14.0%); mice (10.5%); birds (4.2%) | % volume of principal foods in stomachs, body weight range 14.5 - 37.0 lbs | % | Both Male and Female | Not Reported | 151 | Exposure Factor Datasets | |
Dietary Composition | plant foods (29.2%); rabbits (27.6%); mice and rats (24.6%); livestock (7.4%) | % volume of principal foods in scats | % | Both Male and Female | Not Reported | 147 | Exposure Factor Datasets | |
Longevity | 6 | maximum age in field | yrs | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets | |
Population Density | 1 | greatest density | #/1.4 mi2 | Both Male and Female | Not Reported | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | blueberries (68%); white-tailed deer (43%); snowshoe hare (30%); small mammals (21%); birds (2%) | % occurrence of food items in scats | % | Both Male and Female | Both Adults and Juveniles | 452 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | mammals (28.9%; cottontail rabbit, 12.1%, Botta's pocket gopher, 6.8%); birds (15.9%); vegetation (21.7%); misc. (16.7%) | % frequency of occurrence of items in scats | % | Not Reported | Not Reported | 97 scats | El Cajon, near San Diego | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | mule deer (7%); small mammals (67%); reptiles (11%); insects (8%); fruits (5%); other (21%) | % frequency of food items in scats | % | Not Reported | Not Reported | 60 | Sierra National Forest (elev. 300 -3900 m) | Exposure Factor Datasets | Fresno |
Dietary Composition | mule deer (3%); small mammals (30%); birds (6%); reptiles (6%); insects (8%); fruits (64%); other (4%) | % frequency of food items in scats | % | Not Reported | Not Reported | 216 | Sierra National Forest (elev. 300 -3900 m) | Exposure Factor Datasets | Fresno |
Dietary Composition | mule deer (3%); small mammals (18%); birds (2%); reptiles (2%); insects (2%); fruits (82%); other (1%) | % frequency of food items in scats | % | Not Reported | Not Reported | 199 | Sierra National Forest (elev. 300 -3900 m) | Exposure Factor Datasets | Fresno |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Population Density | range over 6 counting periods | #/km2 | Both Male and Female | Not Reported | 28-40/period | Saguaro National Monument | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|
Home Range | 18.7 | km2 | Male | Adult | 7 | Champlain Valley | Exposure Factor Datasets | 4.6 SE |
Home Range | 17.1 | km2 | Female | Adult | 4 | Champlain Valley | Exposure Factor Datasets | 3.2 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 28.2 | composite home range estimated by minimum area method | km2 | Male | Adult | 5 | Lancaster and Cass Counties | Exposure Factor Datasets | 16.6 SD |
Home Range | 24.2 | composite home range estimated by minimum area method | km2 | Female | Adult | 4 | Lancaster and Cass Counties | Exposure Factor Datasets | 20.7 SD |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Body Weight - Mean | 24.25 | lbs | Male | Adult | 28 | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | Exposure Factor Datasets |
Body Weight - Mean | 21.5 | lbs | Female | Adult | 26 | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | Exposure Factor Datasets |
Body Weight - Mean | lbs | Both Male and Female | Juvenile | 47 | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: Sylvilagus sp. (50.6 - 73.1%); Lepus sp. (0 - 5.0%); Neotoma (0 - 5.5%); Microtus (0-11.1%); Cricetid mice (1.2-8.9%); Bos taurus (1.9 - 7.9%); Odocoileus hemionus (3.6 - 15.5%) | range of % relative dry weight of major food items (>5%) measured at 3 sites, based on scat analysis | % | Not Reported | Not Reported | 42 - 48/ site | Montezuma, La Plata and Saguache Counties | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 7.9 (0.5yr); 9.8 (1.5 yr); 11.0 (2.5 yr); 11.5(3.5 yr); 10.8 (4.5 yr); 11.6 (5.5 yr); 10.4 (6.5 yr); 10.9 (>7.5 yr) | average body weights at various ages | kg | Female | Both Adults and Juveniles | 3 - 121/age | King and Knox counties | Exposure Factor Datasets | 0.5 - >7.5 yr |
Body Weight - Mean | 8.2 (0.5yr); 10.4 (1.5 yr); 12.8 (2.5 yr); 13.2 (3.5 yr); 13.7 (4.5 yr); 12.5 (5.5 yr); 12.1 (6.5 yr); 12.6 (>7.5 yr) | average body weights at various ages | kg | Male | Both Adults and Juveniles | 8 - 76/age | King and Knox counties | Exposure Factor Datasets | 0.5 - >7.5 yr |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | grasses (81.6%); persimmon (3.7%); unidentified seeds (5.2%); other plant material (44.9%); grasshoppers (11.8%); beetles (12.5%); chicken (2.2%); other birds (3.7%); cottontail (13.9%); pocket gopher (5.9%); cotton rat (14.7%); wood rat (2.2%); pine vole (2.2%); coyote (28.7%); cattle (33.8%) | % frequency of occurrence in stomach contents | % | Not Reported | Not Reported | 136 | Cleveland, Grady and McClain Counties | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
Longevity | 15 | maximum lifespan | yrs | Male | Adult | 1 | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | lagomorphs (27 - 54%); woodrat (5-21%); cotton rat (0-40%); small rodents (4-12%); deer (4-19%); other prey (8 - 22%) | range of percent distribution of prey items over 8 yrs | % | Not Reported | Not Reported | 2335 scats | Webb County | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 10.4 | kg | Male | Pup | 28 | Naval Petroleum Reserves (elev., 88 - 473 m) | Exposure Factor Datasets | <1yr | Kern | 0.2 SE |
Body Weight - Mean | 11.4 | kg | Male | Juvenile | 10 | Naval Petroleum Reserves (elev., 88 - 473 m) | Exposure Factor Datasets | 1yr | Kern | 0.2 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | voles (79.4%); deer mice (4.7%); other rodents (7.9%); deer (9.8%); pronghorn (1.6%); other ungulates (5.4%); lagomorphs (1.6%); other mammals (1.9%); birds and eggs (6.6%); seeds and fruit (1.0%); insects (2.2%); unknown (3.8%) | % frequency of occurrence of items in scats | % | Not Reported | Not Reported | 315 | National Bison Range (elev., 696-1361 m) | Exposure Factor Datasets |
Dietary Composition | voles (88.8%); deer mice (2.8%); other rodents (10.0%); deer (6.2%); other ungulates (11.0%); other mammals (0.8%); birds and eggs (7.6%); seeds and fruit (0.4%); insects (0.8%); unknown (4.8%) | % frequency of occurrence of items in scats | % | Not Reported | Not Reported | 250 | National Bison Range (elev., 696-1361 m) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | poultry (34%); persimmons (23%); insects (11%); rodents (9%); songbirds (8%); cattle (7%); rabbits (7%); deer (5%); woodchucks (4%); goats (4%); watermelons (4%) | % occurrence of 11 most common items in stomach contents | % | Not Reported | Both Adults and Juveniles | 168 | Ozarks, Ouachitas, Coastal Plain and Delta | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | mammals (64%); birds (1%); insects (10%); fruits (20%); misc. (5%) | annual diet determined by averaging monthly food type percent occurrence, obtained from scats | % | Not Reported | Not Reported | 570-3610 scats/sample | Welder Wildlife Refuge, Corpus Christi | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 15.7 | overall annual home range estimated using the minimum convex polygon method | km2 | Both Male and Female | Adult | 9 | Saguaro National Park, Pima County (elev., 800-1300m) | Exposure Factor Datasets | 4.2 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | mesquite pods (29%); prickly pear fruit (16%); other plants(24%); rodent (28%); lagomorph (22%); mule deer (3%); other mammals (3%); dog food or human-related (35%); misc. (14%) | annual % occurrence of prey items identified in scats | % | Not Reported | Not Reported | 667 scats | suburban area near Saguaro National Monument | Exposure Factor Datasets |
Dietary Composition | mesquite pods (39%); prickly pear fruit (21%); other plants(35%); rodent (27%); lagomorph (20%); mule deer (9%); other mammals (4%); dog food or human-related (trace); misc. (16%) | annual % occurrence of prey items identified in scats | % | Not Reported | Not Reported | 449 scats | rural area near Saguaro National Monument | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | pronghorn antelope (55%); mule deer (5%), other native ungulate (3%); sciurids (21%); microtines (13%); cricetines (3%); unidentified cricetines (7%); western jumping mouse (1%); plant material (42%); coyote (22%); arthropods (18%) | % frequency in scats | % | Not Reported | Not Reported | 404 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Error |
---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.70 | overall annual survival rate (autumn-autumn), estimated over 4 yr periods | Both Male and Female | Adult | 88 | Webb County | Exposure Factor Datasets | > 1.5 yr | 0.58 - 0.82 (95% CL) |
Survival/ Mortality | 0.42 | overall annual survival rate (autumn-autumn), estimated over 3 yr periods | Both Male and Female | Juvenile | 38 | Webb County | Exposure Factor Datasets | 0.5 - 1.5 yr | 0.24 - 0.60 (95% CL) |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Body Fat (total or %) | 9.5 | % | Both Male and Female | Both Adults and Juveniles | 36 | Quebec | Exposure Factor Datasets | CANADA | 1.3 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Sylvilagus spp. (39.7); Microtus montanus (15.9); Perognathus spp. (8.0); Spermophilus townsendii (6.5); Peromyscus maniculatus (5.7); Dipodomys ordii (6.6); Antilocapra americana (5.1); Eutamias minimus (3.6); Lepus californicus (3.4); Thomomys talpoides (3.0); reptiles (1.6); Centrocercus urophasianus (1.5); small birds (2.4) | relative dry weight ingested, estimated from scats | % | Not Reported | Not Reported | 979 scats | Idaho National Engineering Lab | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | white-tailed deer (56.1%); mouse/vole (14.8%): cottontail rabbit (9.4%); woodchuck (10.6%); squirrel (5.2%); raccoon (5.2%); porcupine (2.9%); unidentified mammal hair (18.4%); feathers (10.3%); insects (18.1%); grass/sedge (35.5%); leaf fragments (15.2%); twigs/bark (6.4%); seeds/fruit (15.8%); other plants (2.9%); manmade materials (2.3%) | % frequence of occurrence of major (>2%) food items in scats | % | Not Reported | Not Reported | 310 scats | northcentral, southcentral and northeast regions | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 5.4 | estimated by placental scars, number of foeti and 2 litters | young/litter | Female | Adult | 20 | Lower Fraser Valley, British Columbia | Exposure Factor Datasets | CANADA | 1.8 SD |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | leporids (66.5%); rodents (21.5%); livestock (17.8%); coyote (2.1%); birds (17.8%); reptiles (5.4%); insects (18.6%); fruit (4.5%); other (2.1%); refuse (5.8%) | % frequency of occurrence in stomach contents estimated over 6 yrs | % | Not Reported | Not Reported | 242 | Naval Petroleum Reserves, Bakersfield (elev., 88-473m) | Exposure Factor Datasets | Kern |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | mule deer (35.2%); cattle (11.5%); sheep (3.7%); coyote (2.9%); Microtus sp. (47.7%); Thomomys sp. (6.8%); Lepus americanus (4.4%); Marmota flaviventris (3.9%); Citellus lateralis (3.9%); Erethizon dorsatum (3.7%); song birds (3.7%); other insects (4.7%); pine and fir needles (19%); grass (17.6%); other vegetable matter (8.7%) | % of scats containing food item | % | Both Male and Female | Adult | 384 scats | Sagehen Creek Field Station, Truckee | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | rodents (36%); ungulates (26%); lagomorphs (23%); insectivores (2%); other mammals (1%); unidentified mammals (13%); birds (8%); reptiles (2%); insects (3%); fruit (38%); grass (13%); human refuse (1%) | annual % frequency of occurrence in scats | % | Not Reported | Not Reported | 844 | Willamette National Forest, Lane County (elev., 500-1500 m) | Exposure Factor Datasets |