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Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | 0.619 | resting metabolic rate at 30C | 0.099 SD | ml O2/min | Not Reported | Adult | 30 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 37.4 | 5.0 SD | g | Both Male and Female | Adult | Great Basin Desert, near Reno | 13 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 7.4 | 1.1 SD | g | Both Male and Female | Adult | Great Basin Desert, near Reno | 8 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Population Density | range of densities for entire study area for 2 yrs | 3.57 - 19.07 | #/km2 | Both Male and Female | Both Adults and Juveniles | Elkhorn Slough | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Home Range | daily home range, estimated from hourly trangulations during 24-hr watches using the minimum convex polygon method | 7 - 223 | ha | Male | Adult | Monterey to San Luis Obispo | 9 animals | Exposure Factor Datasets |
Home Range | daily home range, estimated from hourly trangulations during 24-hr watches using the minimum convex polygon method | 221 - 759 | ha | Male | Juvenile | Monterey to San Luis Obispo | 5 animals | Exposure Factor Datasets |
Home Range | daily home range, estimated from hourly trangulations during 24-hr watches using the minimum convex polygon method | 10 - 1166 | ha | Female | Adult | Monterey to San Luis Obispo | 16 animals | Exposure Factor Datasets |
Home Range | daily home range, estimated from hourly trangulations during 24-hr watches using the minimum convex polygon method | 32 - 214 | ha | Female | Juvenile | Monterey to San Luis Obispo | 10 animals | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Home Range | 4.3 | average home range | km2 | Both Male and Female | Both Adults and Juveniles | Naval Petroleum Reserves in California, Bakersfield | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|
Population Density | review | #/km2 | Not Reported | Not Reported | Not Reported | Exposure Factor Datasets |
Survival/ Mortality | review | Not Reported | Adult | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Time of Hatching or Parturition | March to early April | time of whelping | Female | Adult | Tooele County, west. UT, elev. 4300-4800 ft | Not Reported | Exposure Factor Datasets | |
Population Density | 3.6 | pairs/square mile | Both Male and Female | Adult | Tooele County, west. UT, elev. 4300-4800 ft | 9 individuals | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 4.55 | mean body weight | 3.8-5.5 | lbs | Male | Adult | Tooele County, west. UT | 10 | Exposure Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
GLYPHOSATE | decrease | number of hardwood trees in study area | Both Male and Female | Both Adults and Juveniles | Maple Ridge, BC | 1 study area | 2.2 kg/ha | TOX-Non-Repro-Sublethal - indirect effects | NR | field application | Toxicity Factor Datasets |
GLYPHOSATE | no effect | proportion of trapped animals in breeding condition | Both Male and Female | Both Adults and Juveniles | Maple Ridge, BC | 151 | 2.2 kg/ha | TOX-REPRO - physiology | NR | field application | Toxicity Factor Datasets |
GLYPHOSATE | increase | survival over summer and winter | Both Male and Female | Both Adults and Juveniles | Maple Ridge, BC | 545 | 2.2 kg/ha | TOX-MORT - mortality in the field | NR | field application | Toxicity Factor Datasets |
GLYPHOSATE | no effect | juvenile growth rate (summer and fall) | Both Male and Female | Both Adults and Juveniles | Maple Ridge, BC | 283 | 2.2 kg/ha | TOX-REPRO - physiology | NR | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
GLYPHOSATE | 0.29 | relative density (vs. control) in sprayed area | Both Male and Female | Both Adults and Juveniles | Vancouver Island | 285 | 1.1-1.2 kg/ha application | TOX-POP - size effects | field application | Toxicity Factor Datasets |
GLYPHOSATE | decrease | percent vegetation cover (vs control) in study area | Both Male and Female | Both Adults and Juveniles | Vancouver Island | 285 | 1.1-1.2 kg/ha application | TOX-Non-Repro-Sublethal - indirect effects | field application | Toxicity Factor Datasets |
GLYPHOSATE | no effect | adult sex ratios | Both Male and Female | Both Adults and Juveniles | Vancouver Island | 285 | 1.1-1.2 kg/ha application | TOX-POP - size effects | field application | Toxicity Factor Datasets |
GLYPHOSATE | no effect | age structure as indicated by number of juveniles trapped | Both Male and Female | Both Adults and Juveniles | Vancouver Island | 285 | 1.1-1.2 kg/ha application | TOX-POP - age distribution effects | field application | Toxicity Factor Datasets |
GLYPHOSATE | increase | mean number of foeti in trapped females | Both Male and Female | Both Adults and Juveniles | Vancouver Island | 285 | 1.1-1.2 kg/ha application | TOX-REPRO - reproductive success | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
CHLOROCHOLINE CHLORIDE | increase @ 1, 20, 80 mg/kg bw/d | liver weight to bw ratio | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - organ/system effects | 28 d | diet | Toxicity Factor Datasets |
CHLOROCHOLINE CHLORIDE | increase @ 1-80 mg/kg | thymus weight to bw ratios | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - organ/system effects | 28 d | Diet | Toxicity Factor Datasets |
CHLOROCHOLINE CHLORIDE | increase @ 80 mg/kg bw/d | white blood cell counts | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 28 d | Diet | Toxicity Factor Datasets |
CHLOROCHOLINE CHLORIDE | increase @ 80 mg/kg bw/d | plaque forming cells/g spleen | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 28 d | Diet | Toxicity Factor Datasets |
CHLOROCHOLINE CHLORIDE | decrease @ 80 mg/kg bw/d | reciprocal of hemolysin titers (against sheep rbc) | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 28 d | Diet | Toxicity Factor Datasets |
GLYPHOSATE | increase @ 20, 80 mg/kg bw/d | liver weight to body weight ratio | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - organ/system effects | 28 d | Diet | Toxicity Factor Datasets |
GLYPHOSATE | increased @ 1-80 mg/kg | thymus weight to bw ratio | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - organ/system effects | 28 d | Diet | Toxicity Factor Datasets |
GLYPHOSATE | increase@ 80 mg/kg bw/d | white blood cell count | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 28 d | Diet | Toxicity Factor Datasets |
GLYPHOSATE | increase @ 80 mg/kg bw/d | plaque forming cell count/g spleen | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 28 d | Diet | Toxicity Factor Datasets |
GLYPHOSATE | no effect | reciprocal of hemolysin titer (against sheep rbc) | Female | Adult | 12/dose | 0, 1, 10, 20, 40, 80 mg/kg bw/d | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 28 d | Diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DICHLOROPHENOXY-ACETIC ACID (2,4-) | no effect | changes in population density; treated versus control site | Not Reported | Both Adults and Juveniles | Gunnison County and Saquache County, (elev., 8500 - 9300 ft.) | 6 study areas/dose | 0, 2-3 lbs/acre | TOX-POP - size effects | single | field application | Toxicity Factor Datasets |
DICHLOROPHENOXY-ACETIC ACID (2,4-) | no effect | mean litter size, based upon number of viable embryos or placental scars | Female | Adult | Gunnison County and Saquache County, (elev., 8500 - 9300 ft.) | 66-77 animals | 0, 2-3 lbs/acre | TOX-REPRO - reproductive success | single | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
DIPHACINONE | increase at 0.0025% | Both Male and Female | Not Reported | 10 animals/dose | 0.00125, 0.0025, 0.005, 0.01, 0.02% | TOX-MORT - dose-response data | 2 d | diet | Toxicity Factor Datasets |
CHLOROPHACINONE | increase at 0.00125% | Both Male and Female | Not Reported | 10 animals/dose | 0.00125, 0.0025, 0.005, 0.01, 0.02% | TOX-MORT - dose-response data | 2 d | diet | Toxicity Factor Datasets |
DIPHACINONE | increase @ 0.00125- 0.02% | Both Male and Female | Not Reported | 10 animals/dose | 0.00125, 0.0025, 0.005, 0.01, 0.02% | TOX-MORT - dose-response data | 4 d | diet | Toxicity Factor Datasets |
CHLOROPHACINONE | increase @ 0.00125-0.02% | Both Male and Female | Not Reported | 10 animals/dose | 0.00125, 0.0025, 0.005, 0.01, 0.02% | TOX-MORT - dose-response data | 4 d | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | 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 | Milltown Reservoir, Missoula | 8 animals | Mining waste; Mean soil concentrations (n=8): Arsenic, 52.5 +/- 6.2; Cadmium, 7.8 +/- 0.7; Copper, 532.2 +/- 69.4; Lead, 65.7 +/- 6.4; Zinc, 1,908.9 +/- 392.9SE ug/g | TOX-EXP IND - accumulation | NR | site contamination | Toxicity Factor Datasets |