Idaho
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
TOXAPHENE (POLYCHLORINATED CAMPHENES) | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
PCB | 0.19 ppm ww | Egg concentration | Embryo | 3 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
HEXACHLOROBENZENE | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
DDE (2,4'-) | <5 ppm: 4, >5 ppm: 5 eggs/nest | Clutch size relative to DDE concentration | Embryo | 10 | Toxicity Factor Datasets | USA | |
MIREX | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
<5 ppm: 81%, >5 ppm: 48% | Hatching success | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | ||
PCB | 0.08 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
<5 ppm: 95%, >5 ppm: 86% | Young survived 7-10 days | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | ||
DDE (2,4'-) | 4.2 ppm ww | Egg concentration | Embryo | 10 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
<5 ppm: 0.232, >5 ppm: 0.201 mm | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | |||
DDD (2,4'-) | 0.12 ppm ww | Egg concentration | Embryo | 4 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
DDT (2,4'-) | 0.46 ppm ww | Egg concentration | Embryo | 6 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
DDE (2,4'-) | 4.8 ppm ww | Egg concentration | Embryo | 9 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
DIELDRIN | 0.02 ppm ww | Egg concentration | Embryo | 2 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
DDD (2,4'-) | 0.16 ppm ww | Egg concentration | Embryo | 6 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
HEPTACHLOR EPOXIDE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
DDT (2,4'-) | 0.47 ppm ww | Egg concentration | Embryo | 6 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
OXYCHLORDANE | 0.02 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
DIELDRIN | 0.11 ppm ww | Egg concentration | Embryo | 2 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
CIS-CHLORDANE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
HEPTACHLOR EPOXIDE | 0.04 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
CIS-NONACHLOR | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
OXYCHLORDANE | 0.04 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
ENDRIN | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
CIS-CHLORDANE | 0.01 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | 0.04 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
CIS-NONACHLOR | 0.01 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
HEXACHLOROBENZENE | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
ENDRIN | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
MIREX | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | 10.4% decrease | change in mean eggshell thickness (relative to control) 0-0.8 miles from sprayed area | Female | Adult | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
DDT (Technical Grade Mixture) | no effect | mean productivity (young produced) | Both Male and Female | Adult | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
DDT (Technical Grade Mixture) | 0.78 ppm | mean DDT concentration in plasma of birds sampled 0-1.5 mi from sprayed area | Both Male and Female | Adult | 23 birds | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
DDT (Technical Grade Mixture) | 6.42 ppm | mean DDT concentration in eggs 0-0.8 mi from sprayed area | Both Male and Female | Embryo | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | 0.24 ug/g at study area, 0.087 ug/g at reference area |
mean lead concentration in blood (wet wt) | Both Male and Female | Nestling | 30 (study area) 22 (reference) |
Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | 0.46 ug/g at study area 0.25 ug/g at reference area |
mean lead concentration in blood (wet wt) | Both Male and Female | Adult | 3 (study area) 6 (reference) |
Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | decreased | red blood cell delta aminolevulinic acid dehydratase activity (relative to control) | Both Male and Female | Both Adults and Juveniles | 33 | Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | decreased | hematocrit | Both Male and Female | Juvenile | 30 | Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | decreased | hemoglobin (relative to control) | Both Male and Female | Both Adults and Juveniles | 33 | Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | 0.23 ug/g (wet wt) | mean lead concentration in liver | Both Male and Female | Juvenile | 30 | Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | no effect | number of young produced | Both Male and Female | Adult | 20 nests | Coeur D'Alene River | Toxicity Factor Datasets |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
RADIONUCLIDES | 160 +/- 162SE mrem/d; range = 7-982 mrem/d | whole animal dose estimated with implanted dosimeters | Not Reported | Not Reported | 70 animals | test reactor area, Idaho National Engineering Lab | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Lepidoptera (71% in June); Graminae seeds (66% in July); crested wheat grass (76% in Aug.) | % of fragments identified in stomach contents; dominant food items for 3 months | % | Not Reported | Not Reported | 72 | 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 | ARTHROPODS (78-95%); SEEDS, Halogeton (0-58%), Shadscale (0-27%); grass (0-19%); prickly pear (0-34%), Tansy mustard (0-8%); LEAVES, Halogeton (2-39%), Shadscale (3-14%); grass (17-34%), Tansy mustard (0-11%), peppergrass (0-5%); Russian thistle (0-12%); MISC., mammalian hair (3-13%), prickly pear stems (0-9%) | range of % frequency of food items in stomachs over 3 mo. | % | Not Reported | Not Reported | 405 | Raft River Valley; Cassia County | Exposure Factor Datasets |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
RADIONUCLIDES | see citation | table of mean concentrations of 6 radionuclides (238Pu, 239Pu, 241Am, 242Cm, 244Cm, 90Sr) in 6 mallard tissue types | Not Reported | Adult | 7-15 | leaching ponds, Test Reactor Area, Idaho National Engineering Laboratory | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
RADIONUCLIDES | 131I 10d; 140Ba 22d; 51Cr 86d; 58Co 32d; 75Se 26d; 65Zn 67d; 134Cs 10d; 60Co 67d; 137Cs 11 d | mean biological half-lives for whole-body retention of 9 radionuclides; ducks exposed in field for varying time periods then depurated in laboratory to determine half-life | Both Male and Female | Not Reported | 4-6/sample | Idaho National Engineering Lab | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | Equation: fecal Pb conc./fecal acid insoluble ash content = 61 + (1.06 x sediment Pb conc.) | relation between waterfowl fecal lead concentration (dry wt) and sediment lead concentration (dry wt) | Not Reported | Not Reported | 521 fecal analyses at 11 wetlands (at least 20 per wetland) | Coeur d'Alene and St. Joe River Basins | Toxicity Factor Datasets |
Pacific Treefrog (Pseudacris regilla formerly Hyla regilla)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Time of Fledging or Metamorphosis | July - Sept. | Not Reported | Juvenile | Not Reported | Moscow, Latah County (elev., 850m) | Exposure Factor Datasets | |
Time of Hatching or Parturition | May | Not Reported | Hatchling | Not Reported | Moscow, Latah County (elev., 850m) | Exposure Factor Datasets | |
Time of Mating/ Laying | Apr. - May | time of laying | Female | Adult | Not Reported | Moscow, Latah County (elev., 850m) | Exposure Factor Datasets |
Gopher Snake (Pituophis catenifer formerly Pituophis melanoleucus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 45.0 | g | Male | Juvenile | 44 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 38.9 SD | |
Body Weight - Mean | 59.8 | g | Female | Juvenile | 59 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 43.0 SD | |
Body Weight - Mean | 238.4 | g | Male | Adult | 231 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 101.5 SD | |
Body Weight - Mean | 267.9 | g | Female | Adult | 90 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 123.0 SD | |
Clutch or Litter Size | 6.9 | eggs/clutch | Female | Adult | 20 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 2.10 SD | |
Time of Hatching or Parturition | Oct. | Not Reported | Hatchling | Not Reported | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | |||
Time of Mating/ Laying | June - July | time of laying | Female | Adult | Not Reported | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | ||
Duration of Incubation or Gestation | 125 | d | Female | Adult | Not Reported | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | ||
Age at Sexual Maturity | 3 | yr | Male | Adult | Not Reported | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | ||
Dietary Composition | Townsend ground squirrel (10.6%); Mountain conttontail (11.6%); Deer mouse (43.3%); Ord kangaroo rat (5.8%); Great Basin pocket mouse (5.8%); Montane vole (9.6%); House mouse (6.7%); Other species (6.7%) | % frequency of prey based on stomach contents and scats | % | Not Reported | Not Reported | 104 prey items/455 snakes | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | |
Dietary Composition | Townsend ground squirrel (30.3%); Mountain conttontail (34.4%); Deer mouse (15.8%); Ord kangaroo rat (5.9%); Great Basin pocket mouse (1.7%); Montane vole (5.6%); House mouse (2.2%); Other species (4.1%) | % biomass of prey based on stomach contents and scat analysis | % | Not Reported | Not Reported | 104 prey items/455 snakes | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | |
Time of Torpor or Hibernation | Oct. - Apr. | Not Reported | Not Reported | 455 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | |||
Body Weight - Mean | 11.5 | g | Both Male and Female | Neonate | 9 | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 0.3 SD |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Townsend ground squirrel (8.7%); Mountain conttontail (7.8%); Deer mouse (47.5%); Ord kangaroo rat (4.9%); Great Basin pocket mouse (5.8%); Montane vole (9.7%); House mouse (7.8%); Other species (7.8%) | % frequency of prey ingested based on stomach content and scat analysis | % | Not Reported | Not Reported | 103 items/405 captures | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | |
Dietary Composition | Townsend ground squirrel (27.7%); Mountain conttontail (31.6%); Deer mouse (19.0%); Ord kangaroo rat (5.4%); Great Basin pocket mouse (1.8%); Montane vole (6.1%); House mouse (2.8%); Other species (5.5%) | % biomass of prey ingested based on stomach content and scat analysis | % | Not Reported | Not Reported | 103 items/405 captures | Snake River Birds of Prey Area, southwestern ID | Exposure Factor Datasets | |
Population Density | 1.2 | mean density in 9 habitat types | #/ha | Both Male and Female | Not Reported | Not Reported | Snake Rive Birds of Prey Area, southwestern ID | Exposure Factor Datasets | 0.6 SD |
Loggerhead Shrike (Lanius ludovicianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Apr-mid Aug | period from clutch initiations to chicks fledging | Both Male and Female | Adult | 98 pairs | Ada, Elmoor, Owyhee Counties | Exposure Factor Datasets | ||
Clutch or Litter Size | 6.1 | average number of eggs per clutch, 2 years | eggs/clutch | Female | Adult | 84 clutches | Ada, Elmoor, Owyhee Counties | Exposure Factor Datasets | 0.8 SD |
Fledging or Weaning Rate | 5.1 | average number of fledglings per sucessful pair | fledglings/pair | Not Reported | Fledgling | 65 pairs | Ada, Elmoor, Owyhee Counties | Exposure Factor Datasets | 1.5 SD |
Age at Fledging, Metamorphosis, Weaning | age at which young left nests | d | Not Reported | Fledgling | 65 pairs | Ada, Elmoor, Owyhee Counties | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Population Density | range of nesting density, 2 study areas | Both Male and Female | Adult | 10-19 pairs/study area | Ada, Elmore, Owyhee Counties | Exposure Factor Datasets | ||
Age at Sexual Maturity | 1 | yr | Not Reported | Adult | 4 birds | Ada, Elmore, Owyhee Counties | Exposure Factor Datasets |
Pacific Giant Salamander (Dicamptodon tenebrosus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Ascaphus truei larvae (14.0%); Gastropoda (2.0%); Nematomorpha (2.0%); Arachnoidea (8.0%); Plecoptera (46.0%); Tricoptera larvae (52.0%); Tricoptera adults (6.0%); Coleoptera larvae (30.0%); Coleoptera adults (28.0%); Ephemeroptera nymphs (28.0%); Emphemeroptera adults (2.0%); Diptera larvae (20.0%); Diptera adults (10.0%); Lepidoptera larvae (4.0%); Orthoptera (2.0%); Misc. (46.0%) | % of stomach contents containing item | % | Not Reported | Juvenile | 50 | Palouse River, Latah County | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Ascaphus truei larvae (7%); Gastropoda (1%); Nematomorpha (1%); Arachnoidea (4%); Plecoptera nymphs (23%); Tricoptera larvae (26%); Tricoptera adults (3%); Coleoptera larvae (15%); Coleoptera adults (14%); Ephemeroptera nymphs (14%); Diptera larvae (10%) Diptera adults (5%); Lepidoptera (2%); Orthoptera (1%); Misc. (23%) | % of stomachs containing the item | % | Not Reported | Juvenile | 50 | Palouse River, Latah County | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Growth Rate | increase in total length | mm/mo | Not Reported | Juvenile | Not Reported | Mary's Peak and Palouse | Exposure Factor Datasets |
Sideblotched Lizard (Uta stansburiana)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Age at Sexual Maturity | 1 | based on presence of mature spermazoa or yolked ovarian follicles, oviducal eggs or corpora lutea; snout-vent length = 40-43 mm | yr | Both Male and Female | Adult | 275 | Snake River Valley (elev., 530-750m) | Exposure Factor Datasets |
Time of Mating/ Laying | Apr.-May and June-July | time of laying | Female | Adult | 124 | Snake River Valley (elev., 530-750m) | Exposure Factor Datasets | |
Clutches or Litters per year | clutches/yr | Female | Adult | 124 | Snake River Valley (elev., 530-750m) | Exposure Factor Datasets | ||
Clutch or Litter Size | 3.75 | mean clutch size | eggs/clutch | Female | Adult | 124 | Snake River Valley (elev., 530-750m) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Spiders (4.70); Solpugids (0.56); Ants (7.87); Other Hymenoptera (0.54); Grasshoppers and Crickets (21.68); Roaches (0.20); Mantids (0.66); Beetles (12.35); Termites (0.10); Homoptera-Hemiptera (2.19); Diptera (2.54); Lepidoptera (1.24); Insect larvae (6.13); Unidentified Insects (6.52); Plant Materials (0.89); Unidentified (2.89) | volume (cc) of prey items in stomach contents | cc | Not Reported | Not Reported | 556 | Mountain Home, ID; Granstville, UT; Lovelock, Gabbs and Beatty, NV [lat., 37-42] | Exposure Factor Datasets |
Eastern Long-toed Salamander (Ambystoma macrodactylum ssp. columbianum)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 4.63 | g | Male | Adult | 134 | Moscow, Latah County | Exposure Factor Datasets | 0.07 SE |
Body Weight - Mean | 6.02 | g | Female | Adult | 134 | Moscow, Latah County | Exposure Factor Datasets | 0.04 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Feb. - Apr. | time of breeding | Both Male and Female | Adult | Not Reported | Lindsey Creek, Perce County (elev., 420m) | Exposure Factor Datasets | ||
Clutch or Litter Size | 166.5 | eggs/cluster averaged 16.7 | eggs/female | Female | Adult | 25 | Lindsey Creek, Perce County (elev., 420m) | Exposure Factor Datasets | 59.7 SD |
Growth Rate | increase in snout-vent length | mm/d | Both Male and Female | Juvenile | 223 | Lindsey Creek, Perce County (elev., 420m) | Exposure Factor Datasets |
Coyote (Canis latrans)
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 | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 29.3 | estimated by modified minimum area method | km2 | Female | Adult | 4 | Idaho National Engineering Laboratory | Exposure Factor Datasets | 2.4 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | 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 | 51 scats | Big Creek Ranger District | Exposure Factor Datasets |
Mourning Dove (Zenaida macroura)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | halogeton (22.0% +/- 33.9), pigweed (3.9% +/- 13.5), common vetch (4.1% +/-17.9), Indian ricegrass (26.1% +/- 37.6), collomia(6.7% +/- 21.6), barnyard grass (0.3% +/- 5.0), gromwell (0.4% +/- 3.7), wheat (13.2% +/- 29.9), oats (0.6% +/- 4.2), cottonwood (1.6% +/- 11.6), other species (1.7% +/- 7.9), grit (13.9% +/- 23.9) | percent occurrence by mass in crop contents (mean +/- SD) | % | Not Reported | Not Reported | 223 birds | Idaho National Engineering Laboratory | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Population Density | 0.02 | density of nests | nests/ha | Both Male and Female | Adult | 15 plots | Idaho National Engineering Laboratory | Exposure Factor Datasets |
Fledging or Weaning Rate | 75% | proportion of active nests that fledged young | Both Male and Female | Adult | 24 nests | Idaho National Engineering Laboratory | Exposure Factor Datasets | |
Fledging or Weaning Rate | mean number of fledglings per successful nest (over three years) | Both Male and Female | Adult | 5-7 nests/yr | Idaho National Engineering Laboratory | Exposure Factor Datasets | ||
Survival/ Mortality | 0.50 | survival rate from incubation to fledging (26 days) | Both Male and Female | Nestling | 24 nests | Idaho National Engineering Laboratory | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Population Density | 208 | number of nests found in 13.4 acres of orchards | Both Male and Female | Adult | Not Reported | near American Falls | Exposure Factor Datasets |
Time of Nesting | latter two-thirds of July | time of peak nesting activity | Both Male and Female | Adult | Not Reported | near American Falls | Exposure Factor Datasets |
Fledging or Weaning Rate | 1.62 | number of doves fledged per breeding adult | Both Male and Female | Fledgling | Not Reported | near American Falls | Exposure Factor Datasets |
Long-tailed Weasel (Mustela frenata)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 199.2 | g | Male | Adult | 46 | northern/central ID and Whitman County, WA | Exposure Factor Datasets | 35.0 SD |
Body Weight - Mean | 98.9 | g | Female | Adult | 17 | northern/central ID and Whitman County, WA | Exposure Factor Datasets | 14.4 SD |
Great Horned Owl (Bubo virginianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Dietary Composition | unident. snake (0.3%), Sylvilagus nuttallii (19.2%), Lepus californicus (14.3%), unident. leporid (16.1%), Spermophilus townsendii (0.6%), Thomomys townsendii (14.6%), Perognathus parvus (0.4%), Dipodomys ordii (11.1%), Reithrodontomys megalotis (0.2%), Peromyscus spp (2.3%), Neotoma cinerea (4.6%), Neotoma lepida (2.0%), unident. woodrat (0.3%), Microtus montanus (4.7%), Mus musculus (0.7%), Mustela frenata (0.1%), Falco sparverius (0.1%), Phasianus colchicus (1.9%), Callipepla californicus (0.1%), unident. galliform (0.4%), Fulica americana (0.4%), Columba livia (0.9%), Tyto alba (0.3%), Sturnus vulgaris (0.2%), unident. passerine (0.6%), unident. bid (3.4%) | occurence in diet as percent of total prey biomass, based on pellet analysis | Not Reported | Not Reported | 14 nesting areas, 1472 prey items | Snake River Birds of Prey National Conservation Area (42 deg, 50'N, 115 deg, 50'W) | Exposure Factor Datasets |