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Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|
Metabolic Rate | see citation | figures of oxygen consumption of submerged tadpoles measured at various oxygen tensions and pre-metamorphic stages | ul/g/hr | Not Reported | Tadpole | 10/group | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Decapoda: Astacidae (47.7%); Lepidoptera (19.0%); Coleoptera: Lampryidae (5.8%); Chrysomelidae (5.8%); Carabidae (4.1%); Curculionidae (0.3%); Chilopoda (7.7%); sand, gravel (1.2%); unidentified (1%) | % volume of stomach contents | % | Not Reported | Not Reported | Breathitt and Perry counties | 18 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | frogs (12.1%); goldfish (30.3%); gastropods (12.4%); crayfish (9.3%); arachnida (4.4%); coleoptera adult (10.6%); hemiptera (8.2%); orthoptera (8.7%) | % of stomachs containing major (>4%) food items | % | Not Reported | Adult | goldfish pond, Richland | 772 | Exposure Factor Datasets |
Dietary Composition | frogs (13.0%); shiners (27.5%); gastropods (16.1%); crayfish (16.3%); arachnida (4.5%); coleoptera adult (10.5%); hemiptera (13.5%); orthoptera (5.8%); lepidoptera larvae (4.5%); odonata adult (4.2%) | % of stomachs containing major (>4%) food items | % | Not Reported | Adult | bait minnow pond, Richland | 553 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 175.9 | 8.16 SE | g | Both Male and Female | Adult | 30 | Exposure Factor Datasets | |
Inhalation Rate | see citation | figure of breathing frequency (breaths/min) at various seasons, temperatures and oxygen levels | Both Male and Female | Adult | 6/group | Exposure Factor Datasets | ||
Metabolic Rate | see citation | figure of oxygen consumption at various body temperatures within seasons | Both Male and Female | Adult | 6/group | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | 0.1582 | resting oxygen consumption at 23C | 0.009 SE | ml O2/hr/tadpole | Not Reported | Tadpole | 19 | Exposure 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 |
---|---|---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | Not Reported | Tadpole | 15 animals/group | 0, 25, 50,100, 200, 1000 ug/kg body weight | TOX-MORT - dose-response data | single | intraperitoneal | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | incidence of morphological abnormalities | Not Reported | Tadpole | 15 animals/group | 0, 25, 50,100, 200, 1000 ug/kg body weight | TOX-REPRO - development | single | intraperitoneal | Toxicity Factor Datasets |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | Both Male and Female | Adult | 5 animals/group | 0, 25, 50,100, 250, 500 ug/kg body weight | TOX-MORT - dose-response data | single | intraperitoneal | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | histopathological changes in liver, kidney, lung, heart and gonads | Both Male and Female | Adult | 5 animals/group | 0, 25, 50,100, 250, 500 ug/kg body weight | TOX-Non-Repro-Sublethal - cellular/biochemical effects | single | intraperitoneal | 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 |
---|---|---|---|---|---|---|---|---|---|---|
FENITROTHION | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | 0.5, 1.0, 2.0, 4.0, 8.0 mg/l (nominal) | TOX-REPRO - reproductive success | 24 hr | waterborne | Toxicity Factor Datasets |
FENITROTHION | no effect | avoidance response assessed by daily prodding of newly hatched tadpoles | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | 0.5, 1.0, 2.0, 4.0, 8.0 mg/l (nominal) | TOX-REPRO - behavior | 24 hr | waterborne | Toxicity Factor Datasets |
TRICLOPYR | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | 0.6, 1.2, 2.4, 4.8 mg/l (nominal) | TOX-REPRO - reproductive success | 48 hr | waterborne | Toxicity Factor Datasets |
TRICLOPYR | no effect | avoidance response assessed by daily prodding of newly hatched tadpoles | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | 0.6, 1.2, 2.4, 4.8 mg/l (nominal) | TOX-REPRO - behavior | 48 hr | waterborne | Toxicity Factor Datasets |
HEXAZINONE | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | 100 mg/l (nominal) | TOX-REPRO - reproductive success | 8 d | waterborne | Toxicity Factor Datasets |
HEXAZINONE | no effect | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | 100 mg/l (nominal) | TOX-MORT - dose-response data | 9 d | waterborne | Toxicity Factor Datasets | |
TRICLOPYR | increase at 2.4 and 4.8 mg/l | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | 0.6, 1.2, 2.4, 4.8 mg/l (nominal) | TOX-MORT - dose-response data | 48 hr | waterborne | Toxicity Factor Datasets | |
TRICLOPYR | decrease response at 1.2 mg/l | avoidance response assessed by daily prodding | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | 0.6, 1.2, 2.4, 4.8 mg/l (nominal) | TOX-REPRO - behavior | 48 hr | waterborne | Toxicity Factor Datasets |
FENITROTHION | decrease response at 0.5 - 8 mg/l | avoidance response assessed by daily prodding | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | 0.5, 1.0, 2.0, 4.0, 8.0 mg/l (nominal) | TOX-REPRO - behavior | 24 hr | waterborne | Toxicity Factor Datasets |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
FENITROTHION | increase at 9 mg/l | Not Reported | Tadpole | 10/replicate; 3 replicates/dose | 1, 2, 5, 9 mg/l (nominal) | TOX-MORT - dose-response data | 24 hr | waterborne | Toxicity Factor Datasets |
FENITROTHION | increase at 9 mg/l | Not Reported | Tadpole | 10/replicate; 3 replicates/dose | 1, 2, 5, 9 mg/l (nominal) | TOX-MORT - dose-response data | 24 hr | waterborne | 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 |
---|---|---|---|---|---|---|---|---|---|---|
SULFURIC ACID | significant decrease at pH 3.5 and 4.0 | hatching success | Not Reported | 50 eggs/replicate, 6 replicates/group (n=294-312) | pH = 3.5, 4.0, 4.5, 5.0, 6.3 | TOX-REPRO - reproductive success | NR | waterborne | Toxicity Factor Datasets | |
SULFURIC ACID | significant increase at pH 3.5 and 4.0 | Not Reported | Tadpole | 120 animals/dose | pH = 3.5, 4.0, 4.5, 5.0, 6.3 | TOX-MORT - dose-response data | 3 wk | waterborne | Toxicity Factor Datasets |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
PARATHION | no effect | Not Reported | Tadpole | 30 animals/dose | 0, 1 mg/l (nominal) | TOX-MORT - dose-response data | 96 hr | waterborne | 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 |
---|---|---|---|---|---|---|---|---|---|---|
TOXAPHENE (POLYCHLORINATED CAMPHENES) | 99 ug/l (95% CL: 71-116 ug/l) | LC50 | Not Reported | Tadpole | 220 animals | 6 unspecified concentrations | TOX-MORT - toxicity benchmarks | 96 hr | waterborne | Toxicity Factor Datasets |
ENDRIN | 2 ug/l (95% CL: 1-5 ug/l) | LC50 | Not Reported | Tadpole | 220 animals | 6 unspecified concentrations | TOX-MORT - toxicity benchmarks | 96 hr | waterborne | Toxicity Factor Datasets |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | 312 ug/l (95% CL: 225-435 ug/l) | EC50; Loss of equilibrium | Not Reported | Tadpole | 220 animals | 6 unspecified concentrations | TOX-REPRO - behavior | 96 hr | waterborne | Toxicity Factor Datasets |
ENDRIN | > 40 ug/l | EC50; Loss of equilibrium | Not Reported | Tadpole | 220 animals | 6 unspecified concentrations | TOX-REPRO - behavior | 96 hr | waterborne | 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 |
---|---|---|---|---|---|---|---|---|---|---|
PERMETHRIN | 7,033 ug/l (95% CL: 4,129-8,735 ug/l) | LC50 | Not Reported | Tadpole | 10 animals/replicate; 4 replicates/dose | NR | TOX-MORT - toxicity benchmarks | 96 hr | waterborne | Toxicity Factor Datasets |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
CHLORDANE | no effect | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | Toxicity Factor Datasets |
CHLORDANE | increase at 0.5 lb/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | Toxicity Factor Datasets |
ENDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | Toxicity Factor Datasets |
DIELDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | Toxicity Factor Datasets |
ALDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | Toxicity Factor Datasets |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | increase at 0.5 lbs/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | Toxicity Factor Datasets |
LINDANE | increase at 0.5 lbs/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | 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, BARIUM COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | increase | incidence of oral deformities at coal ash contaminated site, relative to reference site | Not Reported | Tadpole | Savannah River, Aiken | 575-1048 | mean whole body concn. at contaminated (C) compared to reference (R) site: As, C=48.9 +/- 2.6SE, R=2.5 +/-0.2SE; Ba, C=211.5 +/- 14.9SE, R=81.2 +/- 5.2SE; Cd, C=1.71 +/- 0.5SE, R=0.15 +/- 0.04SE; Cr, C=17.2 +/- 0.5SE, R=1.4 +/- 0.3SE; Cu, C=31.4 +/- 1.5SE | TOX-REPRO - development | NR | site contamination | Toxicity Factor Datasets |
ARSENIC COMPOUNDS, BARIUM COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | increase at contaminated (C) compared to reference (R) site: Arsenic, C=48.9 +/- 2.6SE, R=2.5 +/-0.2SE; Barium, C=211.5 +/- 14.9SE, R=81.2 +/- 5.2SE; Cadmium, C=1.71 +/- 0.5SE, R=0.15 +/- 0.04SE; Chromium, C=17.2 +/- 0.5SE, R=1.4 +/- 0.3SE; Copper, C=31.4 +/- 1.5SE, R=17.5 +/- 6.6SE; Selenium, C=25.70 +/- 3.60SE, R=3.37 +/- 0.09SE. | mean whole body metal concentrations (ppm, dry mass) | Not Reported | Tadpole | Savannah River, Aiken | 3 animals/site | sediment concn. at contaminated (C) compared to reference (R) site: As, C=70.8 +/- 12.5SE, R=<1.0; Ba, C=418.7 +/- 34.0SE, R=11.8 +/- 0.6SE; Cd, C=0.57 +/- 0.05SE, R=0.03 +/- 0.00SE; Cr, C=70.8 +/- 12.5SE, R=<1.0; Cu, C=71.8 +/- 12.3SE, R=<1.0; Se, C=6.21 | TOX-EXP IND - accumulation | NR | site contamination | Toxicity Factor Datasets |