Mammals
Deer Mouse (Peromyscus maniculatus)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| LEAD ACETATE | no effect | incidence of congenital malformations | Both Male and Female | Juvenile | 5 breeding pairs/dose | Toxicity Factor Datasets | 2-3 mo | Laboratory | |
| 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 |
| 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 | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| 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 | Lab |
|---|---|---|---|---|---|---|---|---|
| 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 | |
| CHLOROCHOLINE CHLORIDE | increase @ 80 mg/kg bw/d | white blood cell counts | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory |
| 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 | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| 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 | |
| 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 |
| 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 |
| 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 |
Desert Kit Fox (Vulpes macrotis ssp. arsipus)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| ZINC PHOSPHIDE | 93 mg/kg bw (95% CI; 62-140 mg/kg) | LD50 | Not Reported | Adult | 2 animals/dose | Toxicity Factor Datasets | Laboratory |
Pallid Bat (Antrozous pallidus)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| DDD (4,4'-) | 0.1 ppm; range, <0.1-0.3 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | 4 bats | near cities | Toxicity Factor Datasets | MEXICO |
| DDT (4,4'-) | 1.8 ppm; range, 0.6-3.8 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | 4 bats | near cities | Toxicity Factor Datasets | MEXICO |
| Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| Survival/ Mortality | Review | Both Male and Female | Not Reported | Not Reported | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Longevity | 57 | captive longevity record | mo | Not Reported | Adult | Not Reported | Exposure Factor Datasets | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition |
|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 34.7 | g | Female | Adult | 10 | Exposure Factor Datasets | Kern, San Luis Obispo | late pregnancy |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| Inhalation Rate | see citation | figure of breaths/minute over time | Not Reported | Adult | Not Reported | Exposure Factor Datasets | Laboratory |
Coyote (Canis latrans)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| PENTACHLOROBENZENE | no effect | serum chemistry and hematological profile, compared to control | Both Male and Female | Adult | 3/dose | Toxicity Factor Datasets | 2 - 12 yrs | Laboratory | |
| PENTACHLOROBENZENE | see citation | figures of feces and serum concentrations over time at the tested doses | Both Male and Female | Adult | 3/dose | Toxicity Factor Datasets | 2 - 12 yrs | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| PARA-AMINOPROPIOPHENONE | 5.6 [3.0-10.4 (95% CI)] mg/kg | LD50 | Not Reported | Not Reported | 4/dose | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DIPHACINONE | 0.6 [0.3 - 1.2 (95% CL)] mg/kg | LD50 | Both Male and Female | Adult | 2/dose | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| LITHIUM CHLORIDE | decrease @ 18g/1500 g/d | body weight gain in nursing pups of mothers fed LiCl contaminated diet | Both Male and Female | Both Adults and Juveniles | 4 pups/2 adults | Toxicity Factor Datasets | 10-19d | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
|---|---|---|---|---|---|---|---|---|---|
| Home Range | 28.2 | composite home range estimated by minimum area method | km2 | Male | Adult | 5 | Lancaster and Cass Counties | Exposure Factor Datasets | 16.6 SD |
| Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| Clutch or Litter Size | review | Female | Adult | Not Reported | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 24.25 | lbs | Male | Adult | 28 | Sagehen Creek Field Station, Truckee (elev., 5000-6300 ft) | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Mammals: Sylvilagus sp. (50.6 - 73.1%); Lepus sp. (0 - 5.0%); Neotoma (0 - 5.5%); Microtus (0-11.1%); Cricetid mice (1.2-8.9%); Bos taurus (1.9 - 7.9%); Odocoileus hemionus (3.6 - 15.5%) | range of % relative dry weight of major food items (>5%) measured at 3 sites, based on scat analysis | % | Not Reported | Not Reported | 42 - 48/ site | Montezuma, La Plata and Saguache Counties | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
|---|---|---|---|---|---|---|---|---|---|
| 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 | 216 | Sierra National Forest (elev. 300 -3900 m) | Exposure Factor Datasets | Fresno |
| Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | range of means for two adult age groups; excluding those in latter half of gestation | kg | Female | Adult | 43-66 | Webb County [lat., 27^o20'-28^o00N; long., 99^o00'-99^o40'W] | Exposure Factor Datasets | >2.5 - >3.0 yrs |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 7.9 (0.5yr); 9.8 (1.5 yr); 11.0 (2.5 yr); 11.5(3.5 yr); 10.8 (4.5 yr); 11.6 (5.5 yr); 10.4 (6.5 yr); 10.9 (>7.5 yr) | average body weights at various ages | kg | Female | Both Adults and Juveniles | 3 - 121/age | King and Knox counties | Exposure Factor Datasets | 0.5 - >7.5 yr |
| Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Home Range | prior to dispersal | km2 | Both Male and Female | Juvenile | 50 | Aitkin and Itasca counties | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Population Density | peak density | #/km2 | Not Reported | Adult | Not Reported | National Elk Refuge, Jackson Hole | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
|---|---|---|---|---|---|---|---|---|
| Home Range | 17.1 | km2 | Female | Adult | 4 | Champlain Valley | Exposure Factor Datasets | 3.2 SE |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Longevity | 6 | maximum age in field | yrs | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets |
Merriam's Kangaroo Rat (Dipodomys merriami)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| METHYLPARATHION | 18-19 % decrease | brain cholinesterase activity, compared to control | Both Male and Female | Adult | 2 animals | Toxicity Factor Datasets | Laboratory | |
| METHYLPARATHION | 97.1 mg/kg (95% CI, 42.6-178.6 mg/kg) | LD50 | Both Male and Female | Adult | 3-4 animals/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| HEXACHLOROETHANE | no effect | sister chromatid exchange counts, compared to controls | Not Reported | Not Reported | 3-4/group | Goldstone, Fort Irwin | Toxicity Factor Datasets |
California Sea Lion (Zalophus californianus)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, LEAD COMPOUNDS, SELENIUM COMPOUNDS, ZINC COMPOUNDS | increase | incidence of epileptiform seizures and subsequent death associated with "unusual" Se levels | Female | Adult | 1 | Toxicity Factor Datasets | 18 yr | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
|---|---|---|---|---|---|---|---|---|
| DDT (Technical Grade Mixture), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturtion associated with elevated DDT and PCB residues, compared to full term parturient group | Female | Adult | 4-6/group | San Miguel Island | Toxicity Factor Datasets | 6 - 15 yrs |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| SELENIUM COMPOUNDS | 36.11 - 88.4 ug/g wet wt (liver); 7.12 - 32.8 ug/g wet wt (kidney) | selenium concentration range in liver and kidney of dead animals | Not Reported | Not Reported | 3 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturition associated with elevated DDT and PCB levels, compared to full term parturient group | Female | Adult | 10/group | San Miguel Island | Toxicity Factor Datasets | 6 - 14 yrs |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
|---|---|---|---|---|---|---|---|---|
| CADMIUM COMPOUNDS, DDT (Technical Grade Mixture), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | increase | incidence of kidney histopathological lesions in "sick" or dead animals compared to "healthy" animals, consistent with diagnosis of leptospirosis | Male | Adult | 2-8/group | Toxicity Factor Datasets | 5 - 9 yr |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| BROMINE COMPOUNDS, CADMIUM COMPOUNDS, COPPER COMPOUNDS, IRON COMPOUNDS, MANGANESE COMPOUNDS, MERCURY COMPOUNDS, SELENIUM COMPOUNDS, SILVER COMPOUNDS, ZINC COMPOUNDS | increase | incidence of premature parturition correlated with different metal concentrations and ratios | Both Male and Female | Both Adults and Juveniles | 10/group | Toxicity Factor Datasets |
California Ground Squirrel (Spermophilus beecheyi)
| Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|
| STRYCHNINE | increase at 6.7-44.5 mg/kg bw | Both Male and Female | Not Reported | 3-5/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| SODIUM MONOFLUOROACETATE | 182-1309 ppb wet wt. @ 0.8 mg/kg; 535-9754 ppb wet wt. @ 4.8 mg/kg | range of fluoroacetate residues in brain, caecum, kidney, liver, spleen, muscle and lung tissue of dead squirrels | Not Reported | Adult | 2/dose | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
|---|---|---|---|---|---|---|---|---|
| SODIUM MONOFLUOROACETATE | decrease @ 6.7 kg/ha | population size | Not Reported | Not Reported | 38.7-54.2 mean squirrel population size range | Exeter, Tulare | Toxicity Factor Datasets | Tulare |
Sea Otter (Enhydra lutris)
| Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| CRUDE OILS | review | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets |
Striped Skunk (Mephitis mephitis)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| SODIUM MONOFLUOROACETATE | 0.347 mg/kg (95% CI; 0.212 - 0.541 mg/kg) | median lethal dose | Not Reported | Not Reported | 5-6 animals/dose | Toxicity Factor Datasets | Laboratory |
Southern Sea Otter (Enhydra lutris ssp. nereis)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| TIN, BUTYL | increase | otters that died of infectious disease contained butyltin liver concentrations greater than those that died of trauma | Both Male and Female | Adult | 8-14 animals | Toxicity Factor Datasets |
Deer Mouse (Peromyscus maniculatus ssp. bairdii)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Water Ingestion Rate | 1.74 | daily water ingestion at ambient temperature of 21C | cc/animal/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 | Age-Specific | Error | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 1.87 | g | Both Male and Female | Neonate | 281 | original pairs trapped at Heart Lake, Northwest Territories | Exposure Factor Datasets | 0 d | 0.01 SE | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 13.7 | g | Both Male and Female | Juvenile | 110 | Kananaskis Valley, Alberta [lat., 51 N] | Exposure Factor Datasets | "young of the yr" | CANADA | 0.3 SE | |
| Population Density | # of animals live-trapped in 3 grids (2 - 4 ha) from May to Oct. (1979 - 1981) | #/ha | Both Male and Female | Both Adults and Juveniles | 3 grids | Kananaskis Valley, Alberta [lat., 51 N] | Exposure Factor Datasets | CANADA |
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 | 0.24 | mean dry stomach content mass | g | Female | Adult | 60 | Tule Lake National Wildlife Refuge (1230 m) | Exposure Factor Datasets | Siskiyou | 0.03 SE |
| Time of Mating/ Laying | January, August-October | annual reproductive peaks | Female | Adult | 1085 | Tule Lake National Wildlife Refuge (1230 m) | Exposure Factor Datasets | Siskiyou |
Deer Mouse (Peromyscus maniculatus ssp. nebrascensis)
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 7.3 | g | Both Male and Female | Juvenile | 90 | captured in Nebraska | Exposure Factor Datasets | 14 d | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Food Ingestion Rate | 0.17 | average daily food intake | g/g/d | Female | Adult | 49 | captured in Alberta, Canada | Exposure Factor Datasets | non-breeding | Laboratory |
Deer Mouse (Peromyscus maniculatus ssp. nubiterrae)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
|---|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 3.4 | based on embryo counts | #/litter | Female | Adult | 52 | Mountain Lake Biological Station, Giles County [lat., 37^010'N; long., 80^o30' W] | Exposure Factor Datasets | 0.07 SE |
Deer Mouse (Peromyscus maniculatus ssp. sonoriensis)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
|---|---|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 4.88 | potential litter size; estimated using the larger of corpora lutea count or embryo sites | #/litter | Female | Adult | 26 | White Mountain (elev.,12,400 ft) | Exposure Factor Datasets | Mono | 0.46 SE |
Audubon's Cottontail (Sylvilagus audubonii ssp. arizonae)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 2.9 | estimated by embryo counts | young/litter | Female | Adult | 56 | southern portion of state | Exposure Factor Datasets |
Audubon's Cottontail (Sylvilagus audubonii ssp. vallicola)
| Exposure Endpoint Type | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| Home Range | acres | Both Male and Female | Both Adults and Juveniles | Not Reported | San Joaquin Experimental Range | Exposure Factor Datasets |
Brush Rabbit (Sylvilagus bachmani ssp. ubericolor)
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 732.25 | g | Female | Adult | 45 | E.E. Wilson Game Management Area, Corvallis | Exposure Factor Datasets | 80.85 SD |
Ornate Shrew (Sorex ornatus)
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Duration of Incubation or Gestation | 21 | d | Female | Adult | Not Reported | San Francisco Bay region | Exposure Factor Datasets |
Kit Fox (Vulpes macrotis)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Food Ingestion Rate | 101 | estimated daily food intake based on a desert kangaroo diet (7.38 kJ/g wet wt) and calculated daily energy requirements (see Golightly, 1981) | g/d | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets | Laboratory |
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