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Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | see citation | figure of seasonal changes in diet based on scat analysis; mean % volume of food items | % | Not Reported | Not Reported | Pinon Canyon Maneuver Site, Las Animas County (elev., 1310 - 1740 m) | 3270 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 11.3 | mean annual home range of resident coyotes | 5.8 SD | 2.8 - 32.0 | km2 | Both Male and Female | Both Adults and Juveniles | Pinon Canyon Maneuver Site, Las Animas County (elev., 1310-1740 m) | 56 | Exposure Factor Datasets |
Home Range | 106.5 | mean annual home range of transient coyotes | 27.7 SD | 60.9 - 185.3 | km2 | Both Male and Female | Both Adults and Juveniles | Pinon Canyon Maneuver Site, Las Animas County (elev., 1310-1740 m) | 16 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 10 | 0.04 SE | kg | Both Male and Female | Not Reported | captured in Maricopa County, AZ | 18 | Exposure Factor Datasets | |
Metabolic Rate | 0.0015 | basal metabolic rate at 22-26C estimated via oxygen consumption | watts/g | Both Male and Female | Not Reported | captured in Maricopa County, AZ | 3 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | 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 | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 24.25 | 18.0 - 27.5 | lbs | Male | Adult | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | 28 | Exposure Factor Datasets |
Body Weight - Mean | 21.5 | 17.0 - 26.5 | lbs | Female | Adult | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | 26 | Exposure Factor Datasets |
Body Weight - Mean | 7 - 22 | lbs | Both Male and Female | Juvenile | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | 47 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | Sagehen Creek Field Station, Truckee | 384 scats | Exposure Factor Datasets |
Dietary Composition | mule deer (8.7%); cattle (4.4%); sheep (17.4%); coyote (8.7%); Microtus sp. (56.5%); Eutamias (13%); Thomomys sp. (8.7%); Marmota flaviventris (4.4%); Citellus beldingi (4.4%); Erethizon dorsatum (8.7%); song birds (21.7%); grasshoppers (13.0%); other insects (34.8%); pine and fir needles (30.4%); grass (56.5%); other vegetable matter (13.2%) | % of scats containing food item | % | Both Male and Female | Juvenile | Sagehen Creek Field Station, Truckee | 23 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Home Range | 10.1 | overall home range estimated by minimum convex method (95% probability) | 6.9 (95% CI) | km2 | Both Male and Female | Both Adults and Juveniles | McRae and Irwin Counties | 12 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | % body weight/d based on a deer and snowshoe hare diet | 5.2 - 13.1 | %/d | Both Male and Female | Both Adults and Juveniles | Chequamegon National Forest | 3 animals/ 1-2 time periods | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 5.0 | estimated by placental scars | 1 - 12 | young/litter | Female | Adult | 59 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|
Home Range | review | Both Male and Female | Both Adults and Juveniles | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | mammals (80%; deer 45.4%, rabbits 23.7%); birds (2.0%); reptiles (0.7%); insects (10.5%); vegetation (46.7%) | % of scats containing food item | % | Not Reported | Not Reported | Billings County | 152 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 68.7 | minimum area home range | 89.1 SD | 4.9 - 233.0 | km2 | Female | Adult | Wichita Mountains National Wildlife Refuge | 6 | Exposure Factor Datasets |
Home Range | 31.3 | minimum area home range | 42.5 SD | 4.0 - 106.2 | km2 | Male | Adult | Wichita Mountains National Wildlife Refuge | 5 | Exposure Factor Datasets |
Home Range | 39.9 | minimum area home range | 27.6 SD | 12.3 - 76.2 | km2 | Female | Juvenile | Wichita Mountains National Wildlife Refuge | 4 | Exposure Factor Datasets |
Home Range | 1.0 | minimum area home range | 0.7 SD | 0.5 - 2.0 | km2 | Both Male and Female | Juvenile | Wichita Mountains National Wildlife Refuge | 4 | Exposure Factor Datasets |
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 | Wichita Mountains National Wildlife Refuge | 361 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | El Cajon, near San Diego | 97 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | Montezuma, La Plata and Saguache Counties | 42 - 48/ site | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|
Longevity | 15 | maximum lifespan | yrs | Male | Adult | 1 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | suburban area near Saguaro National Monument | 667 scats | 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 | rural area near Saguaro National Monument | 449 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | snowshoe hare (31.7%); white-tailed deer (24.5%); plants (20.4%); small mammals (14.3%); non-edibles (13.2%); large birds (6.0%); porcupine (4.9%); Canis spp. (2.6%); carrion (1.9%); small birds (1.9%); apple (1.9%); human garbage (1.5%); moose (1.5%); feces (1.1); sheep (1.1%); cattle (0.8%) | % frequency of occurrence of items identified from stomach contents | % | Both Male and Female | Both Adults and Juveniles | New Brunswick and Nova Scotia | 265 | Exposure Factor Datasets |
Body Weight - Mean | 13.32 | unskinned weight estimated from skinned weight | kg | Male | Juvenile | New Brunswick and Nova Scotia | 89 | Exposure Factor Datasets |
Body Weight - Mean | 16.64 | unskinned weight estimated from skinned weight | kg | Male | Adult | New Brunswick and Nova Scotia | 50 | Exposure Factor Datasets |
Body Weight - Mean | 11.42 | unskinned weight estimated from skinned weight | kg | Female | Juvenile | New Brunswick and Nova Scotia | 80 | Exposure Factor Datasets |
Body Weight - Mean | 15.24 | unskinned weight estimated from skinned weight | kg | Female | Adult | New Brunswick and Nova Scotia | 23 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | leporids (68.5%); Sigmodon spp. (31.8%); aves (5.9%); grass (16.3%); Juniperus deppeana (7.2%); other vegetation (20.0%); other materials (9.6%) | overall % occurrence of major food items (>5%) in scats | % | Not Reported | Not Reported | Appleton-Whittel Research Ranch, Santa Cruz County (elev., 1500 m) | 759 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | 10.6 | yearly mean basal metabolic rate; range of seasonal means | 9.8 - 11.6 | L O2/kg/d | Both Male and Female | Adult | 4 | Exposure Factor Datasets |
Metabolic Rate | 163.5 | field metabolic rate estimated as 3 times basal metabolic rate | kcal/kg | Both Male and Female | Adult | 4 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Home Range | 7.8 | mean den area; land area around a den or rendezvous used by group | 7.0 - 9.3 | km2 | Female | Adult | Missouri River Breaks | 3 | Exposure Factor Datasets |
Home Range | 9.7 | mean den area; land area around a den or rendezvous used by group | 0.3 - 15.5 | km2 | Male | Adult | Missouri River Breaks | 12 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | Rocky Flats Nuclear Weapons Plant, Denver | 54 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | see figure | bar graph showing use of leporids, rodents, insects and other food items over 6 years | Not Reported | Not Reported | Naval Petroleum Reserves in California | 449 scat samples | Exposure Factor Datasets | |||
Survival/ Mortality | 61.0 | mean annual mortality rate over 13 years | 5.2 SE | 30.0-84.0 | % | Not Reported | Adult | Naval Petroleum Reserves in California | 306 foxes | Exposure Factor Datasets |
Survival/ Mortality | 79.8 | mean annual mortality rate over 13 years | 4.5 SE | 50.0-100 | % | Not Reported | Juvenile | Naval Petroleum Reserves in California | 177 foxes | Exposure Factor Datasets |