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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 | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
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 | Sierra National Forest (elev. 300 -3900 m) | 60 | Exposure Factor Datasets |
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 | Sierra National Forest (elev. 300 -3900 m) | 216 | Exposure Factor Datasets |
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 | Sierra National Forest (elev. 300 -3900 m) | 199 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | 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 | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | Willamette National Forest, Lane County (elev., 500-1500 m) | 844 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Scapanus latimanus (3%); Spermophilus beechyi (24%); Thomomys bottae (64%); Reithrodontomys megalotis (4%); Peromyscus sp. (19%); Neotoma spp. (4%); Microtus californicus (32%); Odocoileus hemionus (41%); birds (6%); reptiles (12%); arthropods (47%); vegetation (33%) | % occurrence of major food items (>1%) in scats | % | Not Reported | Not Reported | East Mesa, Cuyamaca Rancho State Park (elev., 1525 m) | 223 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Home Range | 12.6 | 85% harmonic mean estimate of home range for "territorial" class | 1.8 SE | km2 | Both Male and Female | Both Adults and Juveniles | Jornada Experimental Range, Dona Ana County (elev., 1320-1390 m) | 13 | Exposure Factor Datasets |
Home Range | 25.9 | 85% harmonic mean estimate of home range for "transient" class | 6.5 SE | km2 | Both Male and Female | Both Adults and Juveniles | Jornada Experimental Range, Dona Ana County (elev., 1320-1390 m) | 12 | Exposure Factor Datasets |
Body Weight - Mean | 11.6 | 1.4 SE | kg | Male | Adult | Jornada Experimental Range, Dona Ana County (elev., 1320-1390 m) | 21 | Exposure Factor Datasets | |
Body Weight - Mean | 9.5 | 1.0 SE | kg | Female | Adult | Jornada Experimental Range, Dona Ana County (elev., 1320-1390 m) | 13 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 7.6 | 0.2 SE | kg | Male | Juvenile | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 38 | Exposure Factor Datasets | ||
Body Weight - Mean | 6.5 | 0.2 SE | kg | Female | Juvenile | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 40 | Exposure Factor Datasets | ||
Body Weight - Mean | 9.1 | 0.2 SE | kg | Male | Juvenile | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 32 | Exposure Factor Datasets | ||
Body Weight - Mean | 8.0 | 0.1 SE | kg | Female | Juvenile | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 50 | Exposure Factor Datasets | ||
Body Weight - Mean | range of means for two yearling age groups | 10.0 - 10.8 | kg | Male | Juvenile | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 19-35 | Exposure Factor Datasets | ||
Body Weight - Mean | range of means for two yearling age groups | 8.6 - 8.9 | kg | Female | Juvenile | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 22 - 32 | Exposure Factor Datasets | ||
Body Weight - Mean | range of means for two adult age groups | 10.6 - 11.4 | kg | Male | Adult | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 69 - 76 | Exposure Factor Datasets | ||
Body Weight - Mean | range of means for two adult age groups; excluding those in latter half of gestation | 9.1 - 9.6 | kg | Female | Adult | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | 43-66 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | 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 | Webb County | 2335 scats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.70 | overall annual survival rate (autumn-autumn), estimated over 4 yr periods | 0.58 - 0.82 (95% CL) | Both Male and Female | Adult | Webb County | 88 | Exposure Factor Datasets |
Survival/ Mortality | 0.42 | overall annual survival rate (autumn-autumn), estimated over 3 yr periods | 0.24 - 0.60 (95% CL) | Both Male and Female | Juvenile | Webb County | 38 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Home Range | 29.3 | estimated by modified minimum area method | 2.4 SE | km2 | Female | Adult | Idaho National Engineering Laboratory | 4 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | leporid (76.4%); rodent (18.0%); livestock (13.5%); bird (13.5%); insect (4.5%); other (14.6%) | % frequency of occurrence in stomach contents | % | Both Male and Female | Adult | Naval Petroleum Reserves (elev., 88-473m) [lat., 35^oN; long., 119^oN] | 89 | Exposure Factor Datasets |
Dietary Composition | leporid (57.6%); rodent (27.1%); livestock (27.1%); bird (20.3%); insect (11.9%); other (25.4%) | % frequency of occurrence in stomach contents | % | Both Male and Female | Juvenile | Naval Petroleum Reserves (elev., 88-473m) [lat., 35^oN; long., 119^oN] | 59 | Exposure Factor Datasets |
Dietary Composition | leporid (62.7%); rodent (19.4%); livestock (17.9%); bird (14.9%); insect (41.8%); other (26.9%) | % frequency of occurrence in stomach contents | % | Both Male and Female | Juvenile | Naval Petroleum Reserves (elev., 88-473m) [lat., 35^oN; long., 119^oN] | 59 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Columbian ground squirrel (56.85); mule deer (27.4%); deer mouse (15.6%); moose (13.7%); northern pocket gopher (11.7%); montane vole (11.7%); golden-mantled ground squirrel (5.8%); Audubon's cottontail (3.9%); horse (3.9%); unknown mammals (5.8%); reptiles (3.9%); arthropods (39.2%); birds (27.4%); plants (21.5%) | % occurrence of major (>1.9%) food items in scats | % | Not Reported | Not Reported | Big Creek Ranger District | 51 scats | Exposure Factor Datasets |