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Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
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 |
Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
no effect | capture rates between logged and burned units and the logged, burned and sprayed units during the year after spraying | Not Reported | Not Reported | Oregon Coast Range | 3 units/treatment | control or 1.3 kg/ha | TOX-POP - size effects | single | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|
MERCURIC CHLORIDE | 63.36 | 96 hour LC50 (95% Confidence Interval); based on measured concentrations | 37.02 - 108.30 (95% CI) | ug Hg/L | Not Reported | Not Reported | 10/dose | 0, 1.4, 3.9, 12.0, 110.0 and 487 ug Hg/L (mean daily measured concn.) | TOX-MORT - toxicity benchmarks | 96 hr | waterborne | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|
ARSENIC COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | increase at contaminated, relative to reference site | resting oxygen consumption at 25C, measured in the lab | ml O2/hr/tadpole | Not Reported | Tadpole | Savannah River | 8-11 | 80-d tadpole residue levels (ppm dry wt) at contaminated (C) vs reference (R) sites: Chromium, C=27.25 +/- 6.22, R=8.58 +/- 0.35; Copper, C=55.12 +/- 5.05, R=17.40 +/- 1.74; Arsenic C=25.95 +/- 3.08, R=0.75 +/- 0.20; Selenium, C=25.27 +/- 1.67, R=0.83 +/- | TOX-Non-Repro-Sublethal - whole animal | NR | site contamination | Toxicity Factor Datasets |
ARSENIC COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | decrease at contaminated, compared to reference site | % survival to 80 d posthatching | % | Not Reported | Tadpole | Savannah River | Not Reported | 80-d tadpole residue levels (ppm dry wt) at contaminated (C) vs reference (R) sites: Chromium, C=27.25 +/- 6.22, R=8.58 +/- 0.35; Copper, C=55.12 +/- 5.05, R=17.40 +/- 1.74; Arsenic C=25.95 +/- 3.08, R=0.75 +/- 0.20; Selenium, C=25.27 +/- 1.67, R=0.83 +/- | TOX-REPRO - reproductive success | NR | site contamination | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|
AMMONIUM NITRATE | 25.0 | 10-d LC50 value for embryos | 21.9-28.7 (95% CI) | mg/L as NH4-N | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.3, 3.3, 6.9, 13.3, 25.1, 50.9, 101.2 mg/L NH4-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
AMMONIUM NITRATE | 6.9 | LOAEL for body weight and length | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.3, 3.3, 6.9, 13.3, 25.1, 50.9, 101.2 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM NITRATE | 3.3 | NOAEL for body weight and length | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.3, 3.3, 6.9, 13.3, 25.1, 50.9, 101.2 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM CHLORIDE | 30.3 | 10-d LC50 for embryos | 27.0 - 33.4 (95% CI) | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.2, 2.8, 7.3, 12.8, 24.9, 49.7, 102.9 mg/L NH4-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
AMMONIUM CHLORIDE | 24.9 | LOAEL for body weight and length and deformities | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.2, 2.8, 7.3, 12.8, 24.9, 49.7, 102.9 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM CHLORIDE | 12.8 | NOAEL for body weight and length and deformities | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.2, 2.8, 7.3, 12.8, 24.9, 49.7, 102.9 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM SULFATE | 32.4 | 10-d LC50 for embryos | 29.7 - 35.4 (95% CI) | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.04, 2.6, 6.1, 11.7, 23.1, 45.4, 91.5 mg/L NH4-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
AMMONIUM SULFATE | 11.7 | LOAEL for body weight | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.04, 2.6, 6.1, 11.7, 23.1, 45.4, 91.5 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM SULFATE | 6.1 | NOAEL for body weight | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.04, 2.6, 6.1, 11.7, 23.1, 45.4, 91.5 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
NITRATE, SODIUM | 578.0 | 10-d LC50 for embryos | 459.0 - 726.5 (95% CI) | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.1, 24.8, 56.7, 111.0, 230.4, 470.4, 979.2, 2716 mg/L NO3-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
NITRATE, SODIUM | 111.0 | LOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.1, 24.8, 56.7, 111.0, 230.4, 470.4, 979.2, 2716 mg/L NO3-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
NITRATE, SODIUM | 56.7 | NOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.1, 24.8, 56.7, 111.0, 230.4, 470.4, 979.2, 2716 mg/L NO3-N, mean measured concentration | TOX-REPRO - development | 10 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increase | population size at contaminated vs reference sites | Both Male and Female | Both Adults and Juveniles | Rocky Mountain Arsenal National Wildlife Refuge | Not Reported | Average soil dieldrin concentrations (ppb) at Reference (4.6 - 5.1 ppb) and Contaminated (72.8 - 636.7 ppb) sites | TOX-POP - size effects | NR | site contamination | 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 | Rocky Mountain Arsenal National Wildlife Refuge | Not Reported | Average soil dieldrin concentrations (ppb) at Reference (4.6 - 5.1 ppb) and Contaminated (72.8 - 636.7 ppb) sites | TOX-REPRO - reproductive success | NR | site contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|
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 | mean liver butyltin residue levels in otters where disease was cause of death = 1570 (range = 40-5300 ng/g wet wt) compared to those that died of trauma = 220 (range = 92-480 ng/g wet wt) | TOX-MORT - mortality in the field | NR | site contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | increase | otters that died from infectious diseases contained higher liver DDTs concentrations that those that died of trauma | Both Male and Female | Adult | 4-8 | mean liver DDTs residues in otters where disease was cause of death = 2000 (range = 290-4700 ng/g wet wt) compared to those that died of trauma = 1400 (range = 280 - 3800 ng/g wet wt) | TOX-MORT - mortality in the field | NR | site contamination | 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, MERCURY COMPOUNDS, POLYCHLORINATED DIBENZO-P-DIOXINS, SELENIUM COMPOUNDS | no effect | half-peak coefficient of variation (HPCV) in DNA content vs. reference samples | Not Reported | Chick | Ferry Slip Island and South Pelican Island (33deg59'N,77deg57'W) | 15 | geometric means: 0.03 ppm As, 0.38 ppm Se, 0.34 ppm Hg, 4.5 pg/g TCDD-EQs, wet wt in eggs | TOX-Non-Repro-Sublethal - genetic effects | NR | habitat contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|
POLYCHLORINATED DIBENZO-P-DIOXINS | increased | P-450-dependent arachidonic acid metabolism by liver microsomes | Not Reported | Embryo | 3 | 100 ug/kg egg | TOX-EXP IND - biomarkers | 5-6 d | egg injection | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 95% | percent of eggs lost or broken before hatching in contaminated colonies | Not Reported | Embryo | Lake Huron | 235 eggs | mean ppm in 18 eggs, wet wt: 14.5 (DDE), 0.22 (DDT), 0.17 (DDD), 23.8 (PCBs), 0.33 (dieldrin), 0.04 (heptachlor epoxide), 0.01 (hexachlorobenzene), 0.46 (Hg) | TOX-REPRO - reproductive success | NR | in ovo | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 23.9% thinner | eggshell thickness compared with pre-1947 eggshells in contaminated colonies | Not Reported | Embryo | Lake Huron | 18 eggs | mean ppm in 18 eggs, wet wt: 14.5 (DDE), 0.22 (DDT), 0.17 (DDD), 23.8 (PCBs), 0.33 (dieldrin), 0.04 (heptachlor epoxide), 0.01 (hexachlorobenzene), 0.46 (Hg) | TOX-REPRO - physiology | NR | in ovo | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 2.4% | mean hatching success in contaminated colonies | Not Reported | Embryo | Lake Huron | 331 eggs | mean ppm in 18 eggs, wet wt: 14.5 (DDE), 0.22 (DDT), 0.17 (DDD), 23.8 (PCBs), 0.33 (dieldrin), 0.04 (heptachlor epoxide), 0.01 (hexachlorobenzene), 0.46 (Hg) | TOX-REPRO - reproductive success | NR | in ovo | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 0.06-0.11 (1972); 0.3 (1973) | fledging success (young/nest) in contaminated colonies | Not Reported | Embryo | Lake Huron | 42 (1973)-66 (1972) nests | mean ppm, wet wt: 14.5 (DDE), 0.22 (DDT), 0.17 (DDD), 23.8 (PCBs), 0.33 (dieldrin), 0.04 (heptachlor epoxide), 0.01 (hexachlorobenzene), 0.46 (Hg) | TOX-REPRO - reproductive success | NR | in ovo | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | incidence of embryonic deformities, depressed growth | Embryo, Juvenile | Not Reported | NR | TOX-REPRO - development | NR | NR | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS, POLYCHLORINATED DIBENZO-P-DIOXINS | review | enzyme induction | Not Reported | NR | TOX-EXP IND - biomarkers | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | incidence of reproductive effects | Both Adults and Juveniles, Embryo | Not Reported | NR | TOX-REPRO - reproductive success | NR | NR | 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 |
---|---|---|---|---|---|---|---|---|---|---|
FENTHION | increased @ all doses | mortality versus controls | Both Male and Female | Adult | 8 | 0,23.6,47.2,94.5,189.0 ppm in diet | TOX-MORT - dose-response data | 1 d | diet | Toxicity Factor Datasets |
CARBOFURAN | increased at 63.4, 126.8, 253.6 ppm | mortality versus controls | Both Male and Female | Adult | 8 | 0,31.7,63.4,126.8,253.6 ppm in diet | TOX-MORT - dose-response data | 1 d | diet | Toxicity Factor Datasets |
FENTHION | decreased to 10% of control levels | brain cholinesterase activity of birds that died | Both Male and Female | Adult | 8 | 0,23.6,47.2,94.5,189.0 ppm in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 1 d | diet | Toxicity Factor Datasets |
CARBOFURAN | decreased to 35% of controls | brain cholinesterase activity in birds that died | Both Male and Female | Adult | 8 | 0,31.7,63.4,126.8,253.6 ppm in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 1 d | diet | 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 |
---|---|---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | Y=1.132 + 0.801X (R^2 = 0.932) | relationship between Se concentrations in diet and blood | Both Male and Female | Adult | 9-10 pairs/group | 0,5,9 ppm, dry wt, in diet | TOX-EXP IND - accumulation | 77 d | diet | Toxicity Factor Datasets |
SELENIUM COMPOUNDS | 7.5 ppm Se, dry wt | maximum observed Se concentration in blood | Both Male and Female | Adult | 10 pairs/group | 8 ppm, dry wt, in contaminated prey species | TOX-EXP IND - accumulation | 77 d | diet | Toxicity Factor Datasets |
SELENOMETHIONINE | no effect | incidence of mortality or signs of toxicity | Both Male and Female | Adult | 9-10 pairs/group | 0,5,9 ppm, dry wt, in diet | TOX-MORT - dose-response data | 77 d | diet | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DICOFOL | decreased 5.45% (@ 5 mg/kg), 10.98% (@ 20 mg/kg) | eggshell thickness compared to controls | Female | Adult | 10/group | 0,5,20 mg/kg bw | TOX-REPRO - physiology | daily, throughout breeding season | gavage | Toxicity Factor Datasets |
DICOFOL | non-detectable (@ 5 mg/kg), 560 ng/g (@ 20 mg/kg) | mean concentration of metabolite dichlorobenzophenone in eggs | Female | Adult | 10/group | 0,5,20 mg/kg bw | TOX-EXP IND - accumulation | daily, throughout breeding season | gavage | Toxicity Factor Datasets |
DICOFOL | increased @ 5 and 20 mg/kg | incidence of abnormal embyronic gonads | Both Male and Female | Embryo | 10/group | 0,5,20 mg/kg bw | TOX-REPRO - development | daily, throughout breeding season | gavage | Toxicity Factor Datasets |