Deer Mouse (Peromyscus maniculatus)
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CHLOROCHOLINE CHLORIDE | increase @ 80 mg/kg bw/d | white blood cell counts | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROCHOLINE CHLORIDE | increase @ 80 mg/kg bw/d | plaque forming cells/g spleen | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROCHOLINE CHLORIDE | decrease @ 80 mg/kg bw/d | reciprocal of hemolysin titers (against sheep rbc) | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | increase @ 20, 80 mg/kg bw/d | liver weight to body weight ratio | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | increased @ 1-80 mg/kg | thymus weight to bw ratio | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | increase@ 80 mg/kg bw/d | white blood cell count | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | increase @ 80 mg/kg bw/d | plaque forming cell count/g spleen | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
GLYPHOSATE | no effect | reciprocal of hemolysin titer (against sheep rbc) | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROCHOLINE CHLORIDE | increase @ 1, 20, 80 mg/kg bw/d | liver weight to bw ratio | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROCHOLINE CHLORIDE | increase @ 1-80 mg/kg | thymus weight to bw ratios | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DIELDRIN | decrease at 5 mg/kg | homing orientation test, measured as time in maze pointing to capture site | Both Male and Female | Both Adults and Juveniles | 15 animals/dose | NR | Toxicity Factor Datasets |
DIELDRIN | decrease at 5 mg/kg | homing, measured as number recaptured at pre-exposure site | Both Male and Female | Both Adults and Juveniles | 15 animals/dose | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | Bone; 52.10 +/- 33.81SD, Kidney; 8.46 +/- 3.03SE, Liver; 3.29 +/- 1.77SD, Brain; 0.84 +/- 0.25SE, Feces; 153.6+/- 103.5SD ppm (dry weight) | Mean concentrations in deer mice from roadside site (ppm, dry weight). Feces collected from nest box after 1 yr accumulation. Roadside tissue concentrations significantly different from control site. | Both Male and Female | Adult | 9 - 10 animals | Interstate 25, Denver (elev. 1884-2018 m) | Toxicity Factor Datasets | ||
LEAD COMPOUNDS | no effect | number of litters per 100 breeding females, measured by observing litters in nesting boxes at a control and roadside site | Female | Adult | 50 nesting boxes, 66 observation periods nimals | Interstate 25, Denver (elev. 1884-2018 m) | Toxicity Factor Datasets | ||
LEAD COMPOUNDS | significant increase | mortality during winter, estimated by number of mice recaptured the following breeding season at a control and roadside site | Both Male and Female | Adult | 98 - 180 tagged animals | Interstate 25, Denver (elev. 1884-2018 m) | Toxicity Factor Datasets | ||
LEAD ACETATE | increase at 0.5 and 1% diet | incidence of acid-fast staining intranuclear inclusion bodies within kidney proximal convoluted tubule cells | Both Male and Female | Adult | 5 breeding pairs/dose | Toxicity Factor Datasets | 2-3 mo | Laboratory | |
LEAD ACETATE | no effect | litter mortality | Both Male and Female | Adult | 5 breeding pairs | Toxicity Factor Datasets | 2-3 mo | Laboratory | |
LEAD ACETATE | no effect | incidence of congenital malformations | Both Male and Female | Juvenile | 5 breeding pairs/dose | Toxicity Factor Datasets | 2-3 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 0.048 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 0.85 mg/kg/d | ED50 for ethoxyresorufin-O-dealkylase (EROD) activity | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
DIMETHYLBENZ[A]ANTHRACENE (7,12-) | 0.026 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
METHYLCHLORANTHRENE (3-) | 0.14 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
METHYLCHLORANTHRENE (3-) | 1.24 mg/kg/d | ED50 for ethoxyresorufin-O-dealkylase (EROD) activity | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | no effect | population density (decreases) | Both Male and Female | Both Adults and Juveniles | Not Reported | University of British Columbia Research Forest, Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TERBUFOS | increase @ 1.69 and 2.48 mg/kg | Both Male and Female | Not Reported | 70 animals/dose | Toxicity Factor Datasets | Laboratory | ||
TERBUFOS | decrease at 1.69 and 2.48 mg/kg | brain cholinesterase activity | Both Male and Female | Not Reported | 70 animals/dose | Toxicity Factor Datasets | Laboratory | |
TERBUFOS | increase @ 1.69 and 2.48 mg/kg | incidence of tremors and rapid breathing | Both Male and Female | Not Reported | 70 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, LEAD COMPOUNDS, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS, SELENIUM COMPOUNDS | no effect | incidence of liver and kidney histopathologies was not related to contaminant concentrations | Not Reported | Not Reported | 26 animals | salt marsh, San Pablo and San Francisco Bays | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
MALATHION | no effect | population size in sprayed areas, compared to control areas | Not Reported | Not Reported | Not Reported | Lexington, Dawson County | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | decrease | number of hardwood trees in study area | Both Male and Female | Both Adults and Juveniles | 1 study area | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | proportion of trapped animals in breeding condition | Both Male and Female | Both Adults and Juveniles | 151 | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | increase | survival over summer and winter | Both Male and Female | Both Adults and Juveniles | 545 | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | juvenile growth rate (summer and fall) | Both Male and Female | Both Adults and Juveniles | 283 | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DIELDRIN | increase | population size at contaminated vs reference sites | Both Male and Female | Both Adults and Juveniles | Not Reported | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
DIELDRIN | increase | % of female deer mice exhibiting signs of reproduction increased as dieldrin levels increased at contaminated vs control sites | Female | Adult | Not Reported | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|
ALDICARB | no effect | food intake | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory | |
ALDICARB | no effect | growth rate estimated by changes in body weight | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory | |
ALDICARB | no effect | daily activity measured as time spend in burrow or moving in/out of burrow | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AZINPHOS-METHYL (GUTHION) | 48 mg/kg bw (95% CL: 39-74 mg/kg, slope = 2.57 +/- 0.73SE) | LD50 | Male | Adult | 5-7 animals/dose | Toxicity Factor Datasets | Laboratory | |
AZINPHOS-METHYL (GUTHION) | 1180 ppm diet (95% CL: 709-1485, slope = 1.88 +/- 0.57SE) | LD50 | Both Male and Female | Adult | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
AZINPHOS-METHYL (GUTHION) | 2425 ppm diet (95% CL: 1856-3245, slope = 1.45 +/- 0.25SE) | LD50 | Both Male and Female | Adult | 10 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DICHLOROPHENOXY-ACETIC ACID (2,4-) | no effect | changes in population density; treated versus control site | Not Reported | Both Adults and Juveniles | 6 study areas/dose | Gunnison County and Saquache County, (elev., 8500 - 9300 ft.) | Toxicity Factor Datasets |
DICHLOROPHENOXY-ACETIC ACID (2,4-) | no effect | mean litter size, based upon number of viable embryos or placental scars | Female | Adult | 66-77 animals | Gunnison County and Saquache County, (elev., 8500 - 9300 ft.) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | 0.29 | relative density (vs. control) in sprayed area | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | decrease | percent vegetation cover (vs control) in study area | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | adult sex ratios | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | age structure as indicated by number of juveniles trapped | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | increase | mean number of foeti in trapped females | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHIOCARB | effect @ 0.03-0.5% | suppression of feeding on treated corn | Both Male and Female | Not Reported | 10 - 12 animals/dose | Toxicity Factor Datasets | Laboratory | |
THIRAM | effect at 0.03-0.5% | suppression of feeding on treated corn | Both Male and Female | Not Reported | 10 - 12 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
MERCURY COMPOUNDS | increase and decrease | decreased swimming ability, increased time for mouse to leave circle in center of field, decreased number of lines crossed and increased number of backward movements compared to a reference site | Male | Adult | 7 - 14 animals | Bird Island, Great Salt Lake | Toxicity Factor Datasets |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
DIPHACINONE | increase at 0.0025% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROPHACINONE | increase at 0.00125% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
DIPHACINONE | increase @ 0.00125- 0.02% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROPHACINONE | increase @ 0.00125-0.02% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, COPPER COMPOUNDS, ZINC COMPOUNDS | Diet:Soil; 128.0 (Cd), 1.31 (Cu), 1.87 (Zn). Liver:Soil; 35.3 (Cd), 0.17 (Cu), 1.25 (Zn). Liver:Diet; 0.27 (Cd), 0.12 (Cu), 0.66 (Zn). | Ratio of metal concentrations (ug/g dry weight) in diet:soil, liver:soil and liver:diet at an abandoned mine site. Diet concentrations measured from stomach contents. Soil based on acid extractable concentrations. Soil copper; liver cadmium, copper an | Both Male and Female | Adult | 6-9 soil or tissue samples/site | Blue Grouse Mountain Copper Mine, Honeymoon Bay, Vancouver Island, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | no effect | recruitment measured as number of new animals that entered the population through reproduction or immigration in treated and control areas | Both Male and Female | Both Adults and Juveniles | Not Reported | University of British Columbia Research Forest, Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | body weight | Both Male and Female | Both Adults and Juveniles | 67 - 138 animals | University of British Columbia Research Forest, Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | growth rate, estimated by changes in body weight | Both Male and Female | Juvenile | 23 - 55 | University of British Columbia Research Forest, Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | no effect | population density, compared to control site | Both Male and Female | Both Adults and Juveniles | 13 trapping periods | Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | increase | % of trapped males and females in breeding condition, compared to control site | Both Male and Female | Adult | 24 - 62 animals | Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | average duration of life during summer and winter periods | Both Male and Female | Adult | 2 - 40 animals | Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
ARSENIC COMPOUNDS, CADMIUM COMPOUNDS, COPPER COMPOUNDS, LEAD COMPOUNDS, ZINC COMPOUNDS | Arsenic, <0.02; Cadmium, 0.08; Copper, 3.4; Lead, <0.003; Zinc, 29.5 ug/g | mean carcass concentration (ug/g wet wt.); mean deer mice body weight = 36.0 +/- 8.3SD, n=8 | Not Reported | Not Reported | 8 animals | Milltown Reservoir, Missoula | Toxicity Factor Datasets |
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
AZINPHOS-METHYL (GUTHION) | decrease @ 3.61 kg/ha | population density in enclosures with mowed alfalfa | Both Male and Female | Both Adults and Juveniles | 0-30 animals/enclosure; 4 enclosures/dose | Hyslop Crop Science Field Laboratory, Corvallis | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
AMINOCARB | no effect | mean activity level estimated by frequency of crossing sand transects | Not Reported | Not Reported | Not Reported | southwestern Quebec [lat., 46^oN; long., 74^o10'W] | Toxicity Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | ANIMAL MATTER: Coleoptera adults (4.8); Coleoptera larvae (0.1); Grasshoppers (2.5); Leaf hoppers (7.0); Lepidoptera adults (0.5); Lepidoptera larvae (1.3); Spiders (0.3); PLANT MATTER: Seeds (65.4); Total forbs (4.3) - Kochia scoparia (0.6); Total grasses and sedges (4.8); Total shrubs (2.6). | estimated percent volume, by ranking method, of total matter in stomach contents | % | Both Male and Female | Both Adults and Juveniles | 97 | Pawnee National Grassland | Exposure Factor Datasets |
Dietary Composition | ANIMAL MATTER: Coleoptera adults (11.0); Coleoptera larvae (3.6); Grasshoppers (6.4); Leaf hoppers (13.3); Lepidoptera adults (2.3); Lepidoptera larvae (19.4); Spiders (2.6); PLANT MATTER: Seeds (22.5); Total forbs (4.7) - Kochia scoparia (1.9); Total grasses and sedges (4.0); Total shrubs (3.8). | estimated percent volume, by ranking method, of total matter in stomach contents | % | Both Male and Female | Both Adults and Juveniles | 108 | Pawnee National Grassland | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition |
---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | Range of weighted means of dry weights of stomach contents; | mg | Female | Adult | 33-116 | Ward and McLean Counties | Exposure Factor Datasets | Gravid or lactating |
Food Ingestion Rate | range of weighted means of dry weights of stomach contents; | mg | Male | Adult | 59-359 | Ward and McClean Counties | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 4.70 | #/litter | Female | Adult | 10 | Pinawa, Manitoba | Exposure Factor Datasets | primiparous | CANADA | 0.54 SE |
Clutch or Litter Size | 5.24 | #/litter | Female | Adult | 46 | Pinawa, Manitoba | Exposure Factor Datasets | multiparous | CANADA | 0.22 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Metabolic Rate | 3.21 | average resting metabolic rate estimated as oxygen consumption at 14.45C | ml O2/g/hr | Male | Adult | 4 | animals placed in cages in forest near Lethbridge, Alberta | Exposure Factor Datasets | CANADA | 0.10 SE |
Metabolic Rate | 2.66 | average resting metabolic rate estimated as oxygen consumption at 20.6C | ml O2/g/hr | Male | Adult | 4 | animals placed in cages in forest near Lethbridge, Alberta | Exposure Factor Datasets | CANADA | 0.08 SE |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Apr. - Dec. | Both Male and Female | Adult | Not Reported | Bass Lake (elev., 4500 ft.) | Exposure Factor Datasets | |
Home Range | 0.24 | acres | Male | Adult | 29 | Bass Lake (elev., 4500 ft.) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | seeds (6-49%); fruit (0-24%); arthropods (27-80%); leaves (0-20%); fungi (0-5%); misc. (0-18%) | volumetric % of stomach contents, range of monthly means for 2 yrs. and 2 habitat types | % | Not Reported | Not Reported | 48-59 | western slope of Sierra Nevada (elev., 3500 - 5000 ft.) | Exposure Factor Datasets |
Dietary Composition | seeds (0-68%); fruit (0-24%); arthropods (0-47%); leaves (0-19%); fungi (0-43%); misc. (0-27%) | volumetric % of stomach contents, range of monthly means for 2 yrs. and 2 habitat types | % | Not Reported | Not Reported | 78-105 | western slope of Sierra Nevada (elev., 3500 - 5000 ft.) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Longevity | 7 | yrs | Male | Adult | 1 | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 0.01 | area of subniven runway systems | ha | Female | Adult | 5 | eastern slope, Colorado Rocky Mountains (elev., 3120 m) | Exposure Factor Datasets | 0.36 SE |
Home Range | 0.03 | ha | Male | Adult | 18 | eastern slope, Colorado Rocky Mountains (elev., 3120 m) | Exposure Factor Datasets | 0.54 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 4.3 | pups/litter | Female | Adult | 10 | Exposure Factor Datasets | 0.36 SE | Laboratory | ||
Metabolic Rate | 4.46 | rate of energy expenditure for lactation per gram maternal weight | kJ/g/d | Female | Adult | 10 | Exposure Factor Datasets | 0.29 SE | Laboratory |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|
Home Range | 392.0 | m2 | Female | Not Reported | 8 | sagebrush habitat, Malheur National Wildlife Refuge | Exposure Factor Datasets | 173.2 - 573.3 (2-sigma) |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 4.6 | #/litter | Female | Adult | 6 | Cascade Mountains, Fish Lake [lat., 47^o, 49'N; long., 120^o, 40'W] | Exposure Factor Datasets | 1.37 SD |
Clutches or Litters per year | litters/yr | Female | Adult | Not Reported | Cascade Mountains, Fish Lake [lat., 47^o, 49'N; long., 120^o, 40'W] | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Population Density | 0.28 | mean density | #/ha | Both Male and Female | Both Adults and Juveniles | 74 | Portal, Cochise County (elev. 1330 m) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | range of means from 3 sites | pups/litter | Female | Adult | 19-29 | adults captured at Milk River, Alberta [lat., 49^o07'N; long., 111^o45'W] and Sydney, British Columbia, Canada [lat., 48^o43'N; long., 123^o20'W] | Exposure Factor Datasets | Laboratory |
Deer Mouse (Peromyscus maniculatus ssp. bairdii)
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | range of mean daily consumption (g food/animal/d) during 3 sampling periods; fed Agway Lab chow | g/d | Both Male and Female | Adult | 4/group | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | Range of mean body weights for neonates from varying litter sizes (2-9) | g | Both Male and Female | Neonate | 3 - 112 | Exposure Factor Datasets | 1 d | Laboratory |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
Water Ingestion Rate | 0.126 | total daily water intake (water drunk + water in food) at 21C | cc/g/d | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets | Laboratory |
Deer Mouse (Peromyscus maniculatus ssp. borealis)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 33.6 | g | Female | Adult | 45 | Original pairs trapped at Heart Lake, Northwest Territories | Exposure Factor Datasets | 1-2 d postpartum | 0.7 SE | Laboratory |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 1.70 | g | Both Male and Female | Neonate | 165 | adults captured at Kananaskis Valley, Alberta [lat., 51 N] | Exposure Factor Datasets | 0.02 SE | Laboratory |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 23.9 | g | Female | Adult | 8 | captured in Lethbridge, Alberta | Exposure Factor Datasets | lactating (end) | 0.47 SE | Laboratory |
Deer Mouse (Peromyscus maniculatus ssp. gambelii)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | 0.22 | mean dry stomach content mass | g | Female | Adult | 90 | Tule Lake National Wildlife Refuge (1230 m) | Exposure Factor Datasets | Siskiyou | 0.02 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|
Metabolic Rate | 3.26 | resting oxygen consumption rate at 25C | cc O2/g/hr | Both Male and Female | Not Reported | 8 | Exposure Factor Datasets | 0.09 SE | Laboratory |
Deer Mouse (Peromyscus maniculatus ssp. nebrascensis)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 3.7 | pups/litter | Female | Adult | 25 litters | captured in Nebraska | Exposure Factor Datasets | 0.3 SE | Laboratory |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 18.93 | g | Not Reported | Not Reported | 5 | Exposure Factor Datasets | Laboratory |
Deer Mouse (Peromyscus maniculatus ssp. nubiterrae)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Mar. - Nov. (peaks; Apr.-June and Sept.-Oct.) | time of breeding | Both Male and Female | Adult | Not Reported | Mountain Lake Biological Station, Giles County [lat., 37^010'N; long., 80^o30' W] | Exposure Factor Datasets |
Deer Mouse (Peromyscus maniculatus ssp. sonoriensis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | California Counties |
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Survival/ Mortality | 88 | annual mortality rate of post-weaned individuals calculated from age structure data | % | Both Male and Female | Juvenile | White Mountain (elev., 4500-7100 ft) | Exposure Factor Datasets | Mono |