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Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
BENTAZON | 4530 mg/L | LC50 | NR | Tadpole | Experimental Frog Farm, São Paulo | 6 | 600, 1200, 2400, 4800, 9600 mg/L | TOX-MORT - toxicity benchmarks | 96 hr | Waterborne | Toxicity Factor Datasets |
PENOXSULAM | 7.52 mg/L | LC50 | NR | Tadpole | Experimental Frog Farm, São Paulo | 6 | (+ vegetable oil adjuvant): 2.88 + 55.80; 4.32 + 83.70; 5.76 + 111.60; 7.20 mg/L C 139.50; 8.64 + 167.40 | TOX-MORT - toxicity benchmarks | 96 hr | Waterborne | Toxicity Factor Datasets |
81.57 mg/L | LC50 | NR | Tadpole | Experimental Frog Farm, São Paulo | 6 | Vegetable oil: 55.80; 83.70; 111.60; 139.50; 167.40 mg/L | TOX-MORT - toxicity benchmarks | 96 hr | Waterborne | Toxicity Factor Datasets | |
PERMETHRIN | 0.10 mg/L | LC50 | NR | Tadpole | Experimental Frog Farm, São Paulo | 6 | 0.01, 0.03, 0.09, 0.27, 0.81 mg/L | TOX-MORT - toxicity benchmarks | 96 hr | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
NITRATE, SODIUM | No effect | % survival | NR | Embryo | Willamette Valley, OR | 10 | 0, 5, 20 mg/L | TOX-MORT - toxicity benchmarks | 3 w | Waterborne | Toxicity Factor Datasets |
NITRATE, SODIUM | No effect | % survival | NR | Embryo | Cascade Mountain, OR | 10 | 0, 10 mg/L | TOX-MORT - toxicity benchmarks | 3 w | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 2.7 [1.7-3.7 (84% CI)] ppb | LC10 | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 4 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 21.4 [17.0-27.0 (84%CI)] ppb | LC50 | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 4 d | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
ENDOSULFAN | 172 [117-283 (84% CI)] ppb | LC90 | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 4 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 7 ppb | LOEC | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 4 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 1.7 [1.1-2.4 (84% CI)] ppb | LC10 | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 8 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 13.9 [11.1-17.5 (84% CI)] ppb | LC50 | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 8 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 114 [79.0-187 (84% CI)] ppb | LC90 | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 8 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 7 | LOEC | NR | Embryo | Pymatuning Laboratory of Ecology, Pittsburgh, PA | 10 | 2, 6, 7, 35, 60, 296 ppb | TOX-MORT - toxicity benchmarks | 8 d | Waterborne | Toxicity Factor Datasets |
NITRATE, SODIUM | No effect | % survival | NR | Embryo | Oregon State University, Corvallis | 10 | 0, 5, 20 mg/L | TOX-MORT - toxicity benchmarks | 7 d | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
CYPERMETHRIN | No effect | % survival | NR | Embryo | Oregon State University, Corvallis | 10 | 0.0, 1.0, 5.0 µg/L | TOX-MORT - toxicity benchmarks | 48 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
CHLORPYRIFOS | Decreased | Survival | NR | Juvenile | University of Pittsburgh | 60 | Pesticide mixtures; Spring exp: 0, 2, 10 ppb; Summer exp: 0, 1, 5 ppb | TOX-MORT - toxicity benchmarks | 5 d | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 8279 mg/L | LC50 | NR | Tadpole | San Francisco State University | 144 | 0, 5700, 5800, 6900, 7000, 7900, 8800 mg/L | TOX-MORT - toxicity benchmarks | 24 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
GLYPHOSATE | 6392 mg/L | LC50 | NR | Tadpole | San Francisco State University | 144 | 0, 5700, 5800, 6900, 7000, 7900, 8800 mg/L | TOX-MORT - toxicity benchmarks | 48 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
GLYPHOSATE | 0.375 | % mortality | NR | Tadpole | San Francisco State University | 24 | 5700 mg/L | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 0.375 | % mortality | NR | Tadpole | San Francisco State University | 24 | 5800 mg/L | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 0.667 | % mortality | NR | Tadpole | San Francisco State University | 24 | 6900 mg/L | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 0.542 | % mortality | NR | Tadpole | San Francisco State University | 24 | 7000 mg/L | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 0.75 | % mortality | NR | Tadpole | San Francisco State University | 24 | 7900 mg/L | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 1 | % mortality | NR | Tadpole | San Francisco State University | 24 | 8800 mg/L | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 5092 mg/L | LC50 | NR | Tadpole | San Francisco State University | 24 | 0, 520 (440), 1900 (1319), 2700 (1758), 3100 (2198), 5100 (3077), 5200 (3736) mg/L glyphosate (surfactant) | TOX-MORT - toxicity benchmarks | 24 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
GLYPHOSATE | 0.5 | % mortality | NR | Tadpole | San Francisco State University | 24 | 5200 (3736) mg/L glyphosate (surfactant) | TOX-MORT - toxicity benchmarks | 24 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 0.125 | % mortality | NR | Tadpole | San Francisco State University | 24 | 520 (440) mg/L glyphosate (surfactant) | TOX-MORT - toxicity benchmarks | 48 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
GLYPHOSATE | No effect | % mortality | NR | Tadpole | San Francisco State University | 24 | 170 (132) mg/L glyphosate (surfactant) | TOX-MORT - toxicity benchmarks | 48 h | Waterborne | Toxicity Factor Datasets |
GLYPHOSATE | 0.042 | % mortality | NR | Tadpole | San Francisco State University | 24 | 370 (264) mg/L glyphosate (surfactant) | TOX-MORT - toxicity benchmarks | 48 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
ZINC SULFATE | 0.65 | % mortality | NR | Tadpole | Colorado Division of Wildlife Aquatic Toxicity Laboratory, Ft. Collins, CO | 80 | 1000 µg/L | TOX-MORT - toxicity benchmarks | 96 h | Waterborne | Toxicity Factor Datasets |
ZINC SULFATE | 1 | % mortality | NR | Tadpole | Colorado Division of Wildlife Aquatic Toxicity Laboratory, Ft. Collins, CO | 80 | 2000 µg/L | TOX-MORT - toxicity benchmarks | 96 h | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
ENDOSULFAN | 1,147 [623-2,726 (84% CI)] | LC90 | NR | Tadpole | University of Pittsburgh | 120 | 1, 5, 10, 50, 100, 500 ppb | TOX-MORT - toxicity benchmarks | 4 d | Waterborne | Toxicity Factor Datasets |
ENDOSULFAN | 7 | LOEC | NR | Tadpole | University of Pittsburgh | 120 | 1, 5, 10, 50, 100, 500 ppb | TOX-MORT - toxicity benchmarks | 4 d | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
HEXAHYDRO-1,3,5-TRINITRO-1,3,5-TRIAZINE | 72 mg/kg [49-106 (95% CI)] | LD50 | M | Adult | U.S. Army Center for Health Promotion and Preventive Medicine | 44 | 0, 20-200 mg/kg | TOX-MORT - toxicity benchmarks | Single dose | Oral gavage | Toxicity Factor Datasets |
HEXAHYDRO-1,3,5-TRINITRO-1,3,5-TRIAZINE | 88 mg/kg [65-119 (95% CI)] | LD50 | F | Adult | U.S. Army Center for Health Promotion and Preventive Medicine | 44 | 0, 20-200 mg/kg | TOX-MORT - toxicity benchmarks | Single dose | Oral gavage | Toxicity Factor Datasets |
HEXAHYDRO-1,3,5-TRINITRO-1,3,5-TRIAZINE | 3.25 d | Mean days of survival | M | Adult | U.S. Army Center for Health Promotion and Preventive Medicine | 42 | 0, 10, 20, 25, 30, 45, 60 mg/kg/d | TOX-MORT - toxicity benchmarks | 14 d | Oral gavage | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
HEXAHYDRO-1,3,5-TRINITRO-1,3,5-TRIAZINE | 19.33 d | Mean days of survival | M | Adult | U.S. Army Center for Health Promotion and Preventive Medicine | 60 | 0, 1, 2.5, 5, 8, 11 mg/kg/d | TOX-MORT - toxicity benchmarks | 60 d | Oral gavage | Toxicity Factor Datasets |
2-AMINO-4,6-DINITROTOLUENE | 1406 [947-2087 (95% CI)] | LD50 | M | Adult | 60 | 0, 200-3175 mg/kg | TOX-MORT - toxicity benchmarks | Single dose | Oral gavage | Toxicity Factor Datasets | |
2-AMINO-4,6-DINITROTOLUENE | 1867 [1076-3237 (95%CI)] | LD50 | F | Adult | 60 | 0, 200-5000 mg/kd | TOX-MORT - toxicity benchmarks | Single dose | Oral gavage | Toxicity Factor Datasets |