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Exposure Endpoint Type | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Clutch or Litter Size | 191 - 315 | eggs/female | Female | Adult | Palouse grasslands, Pullman | 11 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Error | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 4.63 | 0.07 SE | g | Male | Adult | Moscow, Latah County | 134 | Exposure Factor Datasets |
Body Weight - Mean | 6.02 | 0.04 SE | g | Female | Adult | Moscow, Latah County | 134 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Feb. - Apr. | time of breeding | Both Male and Female | Adult | Lindsey Creek, Perce County (elev., 420m) | Not Reported | Exposure Factor Datasets | |||
Clutch or Litter Size | 166.5 | eggs/cluster averaged 16.7 | 59.7 SD | eggs/female | Female | Adult | Lindsey Creek, Perce County (elev., 420m) | 25 | Exposure Factor Datasets | |
Growth Rate | increase in snout-vent length | 0.12 - 0.17 | mm/d | Both Male and Female | Juvenile | Lindsey Creek, Perce County (elev., 420m) | 223 | Exposure Factor Datasets | ||
Time of Mating/ Laying | Apr.-May | time of breeding | Both Male and Female | Adult | Bear Wallow, Baker County (elev., 1140m) | Not Reported | Exposure Factor Datasets | |||
Clutch or Litter Size | 105.3 | eggs/cluster averaged 14.8 | 31.03 SD | eggs/female | Female | Adult | Bear Wallow, Baker County (elev., 1140m) | 16 | Exposure Factor Datasets | |
Growth Rate | increase in snout-vent length | 0.32 - 0.39 | mm/d | Both Male and Female | Juvenile | Bear Wallow, Baker County (elev., 1140m) | Not Reported | Exposure Factor Datasets | ||
Time of Mating/ Laying | June - July | time of breeding | Both Male and Female | Adult | Wallowa County (elev., 2470m) | Not Reported | Exposure Factor Datasets | |||
Clutch or Litter Size | 90.1 | 48.87 SD | eggs/female | Female | Adult | Wallowa County (elev., 2470m) | 7 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Cast skin (10.4%); Annelida (6.5%); Mollusca (7.8%); Chilopoda (3.9%); Isopoda (46.8%); Araneida (1.3%); Collembola (2.6%); Lepidoptera (2.6%); Diptera (2.6%); Orthoptera (6.5%); Coleoptera (14.2%); Unidentified (1.3%) | % of total number of items in stomach contents | % | Not Reported | Adult | Ellicott Pond | 38 | Exposure Factor Datasets |
Dietary Composition | Cladocera (1.12%); Copepoda (0.22%); Ostracoda (12.64%); Chironomidae (23.79%); Corixidae (1.56%); Snails (5.58%); Leeches (4.46%); Oligochaeta (22.30%) and Tadpoles (27.88%) | % by weight of food item in stomach contents | % | Not Reported | Juvenile | Ellicott Pond | 20 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Jan. - Feb. | time of breeding | Both Male and Female | Adult | Valencia Lagoon, Rio Del Mar | Not Reported | Exposure Factor Datasets | ||
Age at Sexual Maturity | 2 | yr | Both Male and Female | Adult | Valencia Lagoon, Rio Del Mar | Not Reported | Exposure Factor Datasets | ||
Clutch or Litter Size | 307 | 215-411 | eggs/clutch | Female | Adult | Valencia Lagoon, Rio Del Mar | 5 | Exposure Factor Datasets | |
Growth Rate | see citation | figure of seasonal changes in total length | Both Male and Female | Juvenile | Valencia Lagoon, Rio Del Mar | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Cast skin (2.1%); Isopoda (0.7%); Araneida (10.4%); Collembola (10.4%); Diptera (57.0%); Orthoptera (3.5%); Coleoptera (11.9%); Unidentified (4.2%) | % of total number of items in stomach contents | % | Not Reported | Adult | Mosquito Lakes (elev., 8050 ft) | 20 | Exposure Factor Datasets |
Dietary Composition | Mollusca (2.7%); Cladocera (36.7%); Copepoda (20.8%); Ostracoda (11.5%); Hydracarina (0.4%); Chironomidae (17.9%); Mosquitoes (5.1%); Coleoptera (2.1); Trichoptera (0.3) and Unidentified (0.14%) | % of total number of items in stomach contents | % | Not Reported | Juvenile | Mosquito Lakes (elev., 8050 ft) | 60 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | May - June | time of breeding | Both Male and Female | Adult | Big Meadow (elev., 1980m) and Mosquito Lakes (elev., 2450 m) | Not Reported | Exposure Factor Datasets | |
Growth Rate | see citation | figure of seasonal changes in total length | Both Male and Female | Juvenile | Big Meadow (elev., 1980m) and Mosquito Lakes (elev., 2450 m) | Not Reported | Exposure Factor Datasets | |
Age at Sexual Maturity | 3 | yrs | Both Male and Female | Adult | Big Meadow (elev., 1980m) and Mosquito Lakes (elev., 2450 m) | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Age at Sexual Maturity | 2 | yrs | Not Reported | Adult | Bow Valley (elev., 1290-1375m), [lat.,51^o05'N; long., 115^o4'W] | 170 | Exposure Factor Datasets | |
Longevity | 10 | maximum lifespan | yr | Not Reported | Adult | Bow Valley (elev., 1290-1375m), [lat.,51^o05'N; long., 115^o4'W] | 170 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Time of Mating/ Laying | May - July | time of laying | Female | Adult | Crater Lake, Munson Oxbow Pond, Aant Point Pond, Whitehorse Bluff ponds and Lake West | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|
Inhalation Rate | see citation | tidal volume and breathing rate data | Not Reported | Not Reported | Not Reported | Exposure Factor Datasets | |
Metabolic Rate | see citation | figure of pulmonary and cutaneous oxygen consumption | ul O2/g/hr | Not Reported | Not Reported | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | 281.0 | mean oxygen consumption following activity, measured at 25C | 19.5 SE | ul O2/g/hr | Not Reported | Not Reported | 6 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Population Density | range of larval density estimates in 8 fishless lakes utilizing 3 survey methodologies during day and night | 0 - 383 | larvae/100 m shoreline | Both Male and Female | Juvenile | North Cascades National Park Service Complex | Not Reported | Exposure Factor Datasets | |
Dietary Composition | Benthic macroinvertebrates (75%): Diptera (66.7); Chironomidae (41.7%); Coleoptera (58.3%); Trichoptera (50%); Ephemeroptera (25%); Amphipoda (16.7%); Plecoptera (8.3%); Pelecypoda (8.3%); Crustacean zooplankton (41.7%): Cladocerans (41.7%); Unidentified (41.7%); Imm. Daphnids (25.0%); Daphnia rosea (25%); Ceriodaphnia quadrangula (16.7%); Chydorus spaericus (8.3%); Copepods (16.7%); Cylopoids (16.7%); Calanoids (8.3%); Harpactacoids (8.3%) | % larvae stomachs that contained prey item | % | Not Reported | Juvenile | North Cascades National Park Service Complex | 13 | Exposure Factor Datasets |
Chemical | Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 15.4 | 0.3 SE | mg | Not Reported | Juvenile | 3 | Exposure Factor Datasets | ||||||
METHOXYCHLOR | no appreciable mortality | embryo and larvae (10 d post-hatch) mortality | Not Reported | Embryo, Juvenile | 30-34 eggs/dose | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-MORT - dose-response data | 45 d | waterborne | Toxicity Factor Datasets | |||
METHOXYCHLOR | decrease @ 0.1, 0.3, 1, 3, 10 mg/L | mean day of hatch, compared to controls | Not Reported | Embryo, Juvenile | 30-34 eggs/dose | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-REPRO - development | 35 d | waterborne | Toxicity Factor Datasets | |||
METHOXYCHLOR | decrease @ 0.3, 1, 3, 10 mg/l | responsiveness to startle and distance travelled post-startle in larvae | Not Reported | Juvenile | 30-34 eggs exposed/dose; 14-27 larvae tested/dose | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-REPRO - behavior | 45 d | waterborne | Toxicity Factor Datasets | |||
METHOXYCHLOR | decrease @ 0.3 and 10 mg/L | mean body weight of larvae | Not Reported | Embryo, Juvenile | 30-38 eggs/dose | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-Non-Repro-Sublethal - whole animal | 37 d | waterborne | Toxicity Factor Datasets |