USA
Least Tern (Sterna antillarum)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Hatching Success | 0.67 | Fledglings/pair | NR | Fledgling | Arkansas River at Tulsa | Exposure Factor Datasets | USA |
Population Density | 212 | Adult pairs along 94 km | B | Adult | Arkansas River at Tulsa | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|
Survival/ Mortality | Review | Percent survival | Embryo | Salt Plains National Wildlife Refuge | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 1995: 2.7, 1996: 2.3, 1997: 2.0 | Clutch size | Mean number of eggs/nest | Embryo | 1995: 550, 1996: 265, 1997: 172 | Cow Island, lower Mississippi River | Exposure Factor Datasets | USA |
Clutch or Litter Size | 1995: 2.6, 1996: 2.3, 1997: 1.9 | Clutch size | Mean number of eggs/nest | Embryo | 1995: 201, 1996: 392, 1997:361 | Porter Lake, lower Mississippi River | Exposure Factor Datasets | USA |
Clutch or Litter Size | 1995: 2.4, 1996: 2.6, 1997: 1.9 | Clutch size | Mean number of eggs/nest | Embryo | 1995: 245, 1996: 183, 1997: 374 | St. Francis, lower Mississippi River | Exposure Factor Datasets | USA |
Great Horned Owl (Bubo virginianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Mammalia: 95.74, aves: 0.85 | Percent biomass in undisturbed site | % | B | Not Reported | 2448 | US Army Dugway Proving Ground | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Class aves: 13.8, class mammalia: 86.2, class crustacae: 0.0 | Percent biomass | % | NR | Not Reported | 285 | Fort Cluster | Exposure Factor Datasets | USA |
Dietary Composition | Class aves: 24.8, class mammalia: 75.2, class crustacae: 0.0 | Percent biomass | % | NR | Not Reported | 285 | Trowbridge | Exposure Factor Datasets | USA |
Killdeer (Charadrius vociferus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Territory Size | December: 14.52 km, January: 16.00, February: 15.86 km | Distance traveled | sq km | NR | Adult | December: 11, January: 13, February: 14 | Willamette Valley | Exposure Factor Datasets | USA | December: 2.73, January: 3.50, February: 2.28 km |
Home Range | Winter residents: 7.73 sq km, year-round residents: 2.28 sq km | sq km | NR | Adult | Winter residents: 249, year-round residents: 86 | Willamette Valley | Exposure Factor Datasets | USA | Winter residents: 3.19 sq km, year-round residents: 2.05 sq km |
Burrowing Owl (Athene cunicularia)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Invertebrates: 97, Vertebrates: 66 | Percent frequency of occurrence | % | NR | Not Reported | 426 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 95, Vertebrates: 67 | Percent frequency of occurrence | % | NR | Not Reported | 1631 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 100, Vertebrates: 34 | Percent frequency of occurrence | % | NR | Not Reported | 213 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 83, Vertebrates: 67 | Percent frequency of occurrence | % | NR | Not Reported | 186 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 99, Vertebrates: 79 | Percent frequency of occurrence | % | NR | Not Reported | 806 | Nevada Test Site | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Aranedia: 31.5, Coloptera: 51.9, Dermaptera: 64.8, Isopoda: 3.7, Lepidoptera: 14.8, Orthoptera: 98.2, Rodentia: 3.7, Solipugida: 40.7 | Percent frequency of occurrence in stomach contents | % | NR | Not Reported | 53 | Calipatria State Prison | Exposure Factor Datasets | Imperial | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Vertebrates: 362, Arthropods: 233.2 | Percent of total prey biomass | % | NR | Not Reported | 2 | Tall Grass Prairie National Preserve | Exposure Factor Datasets | USA |
Dietary Composition | See citation Figure 2 | Percent of total prey biomass at different breeding stages | % | NR | Not Reported | 2 | Tall Grass Prairie National Preserve | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Arachnida: 7, Crustacea: <1, Insecta: see citation, Reptilia: <1, Aves: <1, Mammalia: see citation, Other vertebrates: <1 | Percent count of prey items | % | NR | Not Reported | 182 | Southern coastal Texas | Exposure Factor Datasets | USA |
Dietary Composition | Arachnida: 1, Crustacea: <1, Insecta: see citation, Reptilia: 2, Aves: 9, Mammalia: see citation, Other vertebrates: 8 | Percent biomass of prey items | % | NR | Not Reported | 182 | Southern coastal Texas | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Mice: 57.0, Insects: 31.6, Petrels 32.9, Auklet: 2.5, Unknown bird: 10.1 | Percent frequency of occurrence | % | NR | Not Reported | 79 | Southeast Farallon Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | 6.9 | Breeding pairs/sq km | B | Adult | 264 | Cape Coral, Lee County | Exposure Factor Datasets | Breeding | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | >60% developed: 0.81, 40-60% developed: 0.62, 20-39% developed: 0.62, <20% developed: 0.81 | Estimated percent survival by percent urban housing development | % | M | Adult | Cape Coral, Lee County | Exposure Factor Datasets | USA | >60% developed: 0.04, 40-60% developed: 0.05, 20-39% developed: 0.05, <20% developed: 0.04 |
Survival/ Mortality | >60% developed: 0.69, 40-60% developed: 0.52, 20-39% developed: 0.69, <20% developed: 0.69 | Estimated percent survival by percent urban housing development | % | F | Adult | Cape Coral, Lee County | Exposure Factor Datasets | USA | >60% developed: 0.04, 40-60% developed: 0.06, 20-39% developed: 0.04, <20% developed: 0.04 |
Survival/ Mortality | >60% developed: 0.11, 40-60% developed: 0.28, 20-39% developed: 0.43, <20% developed: 0.18 | Estimated percent survival by percent urban housing development | % | B | Juvenile | Cape Coral, Lee County | Exposure Factor Datasets | USA | >60% developed: 0.02, 40-60% developed: 0.04, 20-39% developed: 0.08, <20% developed: 0.08 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Insecta: see citation, Arachnida: 8.3, Gastropoda: 1.7, Reptilia: 0, Aves: 0.7, Mammalia: 0.2 | Percent frequency of occurrence | % | NR | Not Reported | 29 | Rutland Ranch, rural habitat | Exposure Factor Datasets | USA |
Dietary Composition | Insecta: see citation, Arachnida: 9.1, Gastropoda: 0.8, Reptilia: 1.0, Aves: 2.9, Mammalia: 0.3 | Percent frequency of occurrence | % | NR | Not Reported | 55 | Marco Island, urban habitat | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Population Density | See citation Figure 2 | Individuals/100ha | 60 | Eastern Colorado | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 1 | Percent biomass/burrow | Exposure Factor Datasets | Santa Clara | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Table1 | Breeding pairs/sq km | B | Adult | Northern Mojave Desert-eastern Sierra Nevada | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Baiomys taylori: 16, Reithrodontomys fulvescens: 11, Peromyscus: 7, Cryptotis parva: 6, Mus musculus: 6, Perognathus merriami: 3, Sigmodon hispidus: 1 |
Percent frequency of occurrence of mammalian species in pellets | % | NR | Not Reported | 182 | Southern Texas | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Table 1 | Number of individuals/706.5 ha | B | Adult | 946 territories in FL | Exposure Factor Datasets | USA |
Population Density | See citation Table 1 | Number of individuals/706.5 ha | B | Juvenile | 946 territories in FL | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Foraging Distance | 1762 | Distance moved from nest post-fledging | m | F | Juvenile | 21 | El Centro | Exposure Factor Datasets | Imperial | USA | 630 |
Foraging Distance | 397 | Distance moved from nest post-fledging | m | M | Juvenile | 8 | El Centro | Exposure Factor Datasets | Imperial | USA | 124 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Rodentia: 27.8, Procellariiformes: 5.3, Charadriiformes: 0.1, Passeriformes: 0.2, Unknown bird: 0.7, Arachnida: 0.4, Orthoptera: 28.1, Dermaptera: 0.2, Coleoptera: 32.3, Lepidoptera: 3.8, Lithobiomorpha: 0.6, Peracarida/amphipoda: 0.3, Isopoda: 0.2, Unknown arthropod: 0.1 | Percent of total in pellets | % | NR | Not Reported | 679 | Southeast Farallon Island | Exposure Factor Datasets | San Francisco | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 7.4 | Number of eggs | eggs | Embryo | 92 | Southern portion of the Sonny Bono Salton Sea National Wildlife Refuge | Exposure Factor Datasets | Imperial | Breeding | USA | 1.9 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.57 [0.41-0.73 (95% CI)] | Juvenile survival | NR | Juvenile | 38 | Little Missouri National Grassland | Exposure Factor Datasets | Post-fledgling | USA | |
Time of Migration or Dispersal | 2003: September 2, 2004: August 24 | Mean date of mirgration from nest | NR | Juvenile | 38 | Little Missouri National Grassland | Exposure Factor Datasets | Post-fledgling | USA | 2003: ±3 d, 2004: ±2 d |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 139 [1-277 (95%CI)] | Mean by 95% fixed-kernel | ha | M | Adult | 9 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Home Range | 177 [52-302 (95% CI)] | Mean by 100% MCP | ha | M | Adult | 11 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Home Range | 98 [64-132 (95% CI)] | Mean by 95% fixed-kernel | ha | M | Adult | 19 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Home Range | 189 [122-256 (95% CI)] | Mean by 100% MCP | ha | M | Adult | 22 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Population Density | See citation Figure 2 | Number of pairs (temporal) | Managed vegetated areas on Norman Y. Mineta San Jose International Airport (SJC) in San Jose< CA |
Exposure Factor Datasets | Santa Clara | USA |
Double-crested Cormorant (Phalacrocorax auritus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent composition and biomass | B | Chick | Exposure Factor Datasets | Leech Lake | USA | |
Dietary Composition | See citation | Percent composition and biomass | B | Adult | Exposure Factor Datasets | Leech Lake | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 17490 sq km | sq km | B | Adult | 37 | Mississipi Alluvial Valley (AR, MS, LA) & Upper Coastal Plain (AL, MS) | Exposure Factor Datasets | Over-wintering populations | USA | 1986 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | See citation | Breeding pairs/location | 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 | 2008: 1.79 ± 0.03, 2009: 1.96 ± 0.02 | Brood size | Number of hatchlings | NR | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA |
Time of Hatching or Parturition | 2008: June 4, 2009: May 29 | Earliest hatch date | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA | ||
Hatching Success | 2008: 49.5% [45.9-52.9 (95% CI)], 2009: 59.4% [55.8-63.1 (95% CI)] | Fledge success | Hatchling | 2008: 28, 2009: 25 | Northeast SD | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Figure 2 | Active nests/11,000 ha | Adult | Estero Bay Aquatic Preserve | Exposure Factor Datasets | Breeding | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Herring, shad: 0.6, Peamouth/Pikeminnow: 24.0, Sucker: 5.8, Smelt: 0.3, Salmonid: 45.5, Stickleback: 5.0, Sculpin: 8.0, Surfperch: 0.3, Flounder: 8.5, Other: 1.8 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 206 | Rice Island/Channel Markers | Exposure Factor Datasets | USA |
Dietary Composition | Herring, shad: 27.8, Peamouth/Pikeminnow: 0.7, Sucker: 4.7, Smelt: 7.6, Salmonid: 15.9, Stickleback: 2.1, Sculpin: 9.2, Surfperch: 7.3, Flounder: Pacific sand lance: 1.8, Flounder: 9.8 Other: 1.3 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 128 | East Sand Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number before alewife eastablishment | % | Exposure Factor Datasets | USA | |
Dietary Composition | Alewife ,cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number after alewife eastablishment | % | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets | USA |
Clapper Rail (Rallus longirostris)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.5 | Mean annual survivial rate | NR | Adult | 11329 | Exposure Factor Datasets | USA | 0.025 | |
Survival/ Mortality | 0.368 | Mean annual survivial rate | NR | Adult | 11329 | Exposure Factor Datasets | USA | 0.07 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | 90 [58-163 (95% CI)] | Breeding males/sq km | M | Adult | Sapelo Island salt marsh | Exposure Factor Datasets | Breeding | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 0.28 | ha | B | Adult | 16 | LCP Superfund Site, Tutle River | Exposure Factor Datasets | USA | 0.8 |
Brown Pelican (Pelecanus occidentalis)
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Hatching Success | 0 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.677 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.635 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.576 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.695 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.588 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.646 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.5 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.537 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|
Population Density | See citation Table 2 | Nests/ha/year | Adult | Coastal LA | Exposure Factor Datasets | USA |
Population Density | See citation Table 2 | Colonies/ha/year | Both Adults and Juveniles | Coastal LA | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Population Density | 0-910 | Number of individuals/90 sq km (temporal) | San Nicolas Island | Exposure Factor Datasets | Ventura | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Population Density | 1722 | Number of individuals (area size NR) | Both Adults and Juveniles | 1722 | Three sites in Jacksonville, FL | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | Review | Number of individuals/sq km | Exposure Factor Datasets | USA |
Pine Snake (Pituophis melanoleucus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | See citation | ha | B | 12 | Baker County |
Exposure Factor Datasets | USA | ||
Body Weight - Mean | 1004.6 | Mean weight | g | M | 12 | Baker County |
Exposure Factor Datasets | USA | 151.4 |
Body Weight - Mean | 836 | Mean weight | g | F | 12 | Baker County |
Exposure Factor Datasets | USA | 371.5 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Foraging Distance | See citation | Mean distance per day | m | B | 17 | Pine Barrens | Exposure Factor Datasets | USA | |
Home Range | 37.5 | Mean by min convex polygon | ha | B | 7 | Pine Barrens | Exposure Factor Datasets | USA | 5 |
Home Range | 100 | Mean by 95% isopleth | ha | B | 7 | Pine Barrens | Exposure Factor Datasets | USA | 16.6 |
Home Range | 18.5 | Mean core activity | ha | B | 7 | Pine Barrens | Exposure Factor Datasets | USA | 2.9 |
Home Range | 70 | Mean by min convex polygon | ha | B | 17 | Pine Barrens | Exposure Factor Datasets | USA | 6.9 |
Home Range | 71.7 | Mean by 95% isopleth | ha | B | 17 | Pine Barrens | Exposure Factor Datasets | USA | 10.9 |
Home Range | 8.7 | Mean core activity | ha | B | 17 | Pine Barrens | Exposure Factor Datasets | USA | 1.3 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Home Range | See citation Table 4 | Min convex polygon & kernel | Sq km | B | 14 | Pine Barrens | Exposure Factor Datasets | USA |
Foraging Distance | B | 14 | Pine Barrens | Exposure Factor Datasets | USA | |||
See citation Table 4 | Max distance from den | km | B | 11 | Pine Barrens | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 79.1 | Mean by min convex polygon (50%) | ha | B | 9 | Arnold Air Force Base | Exposure Factor Datasets | USA | 16.2 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 1300 | Mean weight | g | B | 9 | Arnold Air Force Base | Exposure Factor Datasets | USA |
Western Pond Turtle (Actinemys marmorata)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | 49 | Model calculation | Individuals in 10 acre waterway | Both Adults and Juveniles | Exposure Factor Datasets | Yolo | USA | |
Population Density | 53 [48-66 (95% CI)] | Model calculation | Individuals in 10 acre waterway | Both Adults and Juveniles | Exposure Factor Datasets | Yolo | USA |
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Time of Nesting | June 4-July 18 | Adult | 17 | Fern Ridge Resevoir | Exposure Factor Datasets | Gravid | USA |
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries |
---|---|---|---|---|---|---|---|---|
Time of Nesting | May 28-June 30 | Adult | 15 | Cambria | Exposure Factor Datasets | San Luis Obispo | Gravid | USA |
Sideblotched Lizard (Uta stansburiana)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | See citation Table 1, Figures 4-5 | Overwinter mortality rate | deaths/100 lizards/day | B | Adult | CA, NV, OR, WA | Exposure Factor Datasets | Adults ≥40 mm | USA |
Survival/ Mortality | See citation Figure 2 | Overwinter mortality rate by latitude | deaths/100 lizards/day | B | Adult | CA, NV, OR, WA | Exposure Factor Datasets | Adults ≥40 mm | USA |
Northern Red-legged Frog (Rana aurora)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|
Time of Migration or Dispersal | January 29-May 1 | Post-breeding migration | Adult | 26-Aug | Scott Creek watershed | Exposure Factor Datasets | Santa Cruz | Post-breeding | USA |
Desert Tortoise (Gopherus agassizi)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | 42941 | Oviposition date | Date | Adult | 7 | Sugarloaf Mountain, AZ | Exposure Factor Datasets | USA | 21 d |
Giant Garter Snake (Thamnophis gigas)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | 177 [124-280 (95% CI)] | Abundance estimates | NR | Not Reported | 88 | Gilsizer Slough: 1,400 ha | Exposure Factor Datasets | Sutter | USA |