Field Name | Description |
---|---|
% Effect | The magnitude of the effect (e.g., % mortality; change in weight; change in length; percent hatch; etc.). |
Analyte | The chemical substance used to create the exposure. |
CAS | CAS registry number is a unique numerical identifier assigned by Chemical Abstract Service (CAS) to a chemical substance. |
COLL | Where the animal was obtained: C (cultured-reared in laboratory); W (collected from wild); N/I (No Information); N/R (Not Reported). |
Comments | Commonly supports the effects data. |
Common name | Common name of the test animal. |
Control | The control response for the observed effect (e.g., survival, growth, reproduction; etc.). |
Dose | The frequency with which the contaminant was applied during the test. |
Duration | The duration of the exposure period: hr (hours); d (days) wk (weeks), mo (months), yr (years). |
Effect | The type of toxicological effect observed in the test animal (e.g., survival, growth, reproduction). |
ERED ID | Unique identification number autogenerated by database. |
ExpConc | The exposure concentration and units. |
Fraction | The test animal tissue used to determine tissue residue (e.g., whole body, soft tissue, liver, etc.). |
Genus Species | Scientific name of the test animal. |
Media | Type of water used to test animal: FW (freshwater); SW (saltwater) |
Mix | Whether the analyte was tested as part of a mixture of analytes or individually: yes (part of mixture), no (single), or N/I (No information). |
Risk | Summary of the risk (e.g., ED, NOED, LOED) an analyte might pose to the test animal. Previously, many risk numbers were assigned to results. Going forward ERED will not report a risk number unless it is reported in the study. |
Route | The route by which the analyte was intended to enter the body: aquatic; diet; injection. |
Signif | Whether the effect was significantly different, usually compared to the control for laboratory studies: Yes (significant); No (not significant). |
Source | Reference from which data was obtained. |
Spiked | Whether the analyte was spiked into the route (aquatic, diet, sediment, injection): yes (analyte spiked), no (analyte not spiked) |
ST | Study type: L (Lab); F (Field); L/F (Lab/Field); Meso (Mesocosm); Micro (Microcosm); N/I (No Information). |
Stage | Life stage of the test animal (e.g., egg, larval, juvenile, adult). |
Tissue ww (mg/kg) | Tissue residue of analyte in the test animal tissue (mg/kg wet weight). |
Trend | The trend of the effect, usually compared to the control for laboratory studies: INC (increase); DEC (decrease), NEF (No effect). |
You are viewing Chordata: Vert (fishes; salmonid) and Pesticides-PCP
Genus Species | ERED ID | ST | Common | Stage | COLL | Analyte | CAS | MX | SPK | H2O | Route | CONC | Dose | DUR | Residue mg/kg ww |
Fraction | Effect | Trend | Signif | % Effect | Control | Risk | Comments | Source |
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Oncorhynchus mykiss | 1991 | L | Rainbow Trout | immature | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | diet | 3 mg/kg | N/I | 110 | 0.04 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Niimi and Cho. 1983. Laboratory and field analysis of pentach.... Water Res 17:1791-1795. |
Salmo trutta | 4331 | L | Sea Trout, Brown Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 0.2 mg/L | 1x | 24 hr | 200 | whole body | mortality | INC | N/R | 50% | N/R | LBR 50 | lethal body residue | Hattula et al. 1981. Acute toxicity of some chlorinated pheno.... B Environ Contam Tox 26:295-298. |
Oncorhynchus tshawytscha | 2280 | L | Chinook Salmon | juvenile | N/I | Pentachlorophenol | 87-86-5 | Y | N/I | N/I | aqueous | 3.11 µg/L | N/I | 62d | 2.323 | whole body | behavior | N/I | N/I | N/I | N/I | NOEC | N/I | Rogers et al. 1988. Bioconcentration of chlorophenols by juv.... Water Qual Res J Can 23:100-113. |
Oncorhynchus tshawytscha | 2282 | L | Chinook Salmon | juvenile | N/I | Pentachlorophenol | 87-86-5 | Y | N/I | N/I | aqueous | 3.11 µg/L | N/I | 62d | 2.323 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | growth (weight) | Rogers et al. 1988. Bioconcentration of chlorophenols by juv.... Water Qual Res J Can 23:100-113. |
Oncorhynchus tshawytscha | 2284 | L | Chinook Salmon | juvenile | N/I | Pentachlorophenol | 87-86-5 | Y | N/I | N/I | aqueous | 3.11 µg/L | N/I | 62d | 2.323 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Rogers et al. 1988. Bioconcentration of chlorophenols by juv.... Water Qual Res J Can 23:100-113. |
Oncorhynchus gorbuscha | 2356 | L | Pink Salmon | egg | N/I | Pentachlorophenol | 87-86-5 | Y | N/I | N/I | aqueous | 3.11 µg/L | N/I | 96 hr | 1.089 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | N/I | Servizi and Gordon. 1988. Bioconcentration of chlorophenols by ear.... Water Qual Res J Can 23:86-99. |
Oncorhynchus mykiss | 4422 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | N/I | continuous | 4 d | 34.6 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
Oncorhynchus mykiss | 4446 | L | Rainbow Trout | immature | N/I | Pentachlorophenol | 87-86-5 | N | Y | FW | injection | N/I | N/I | 4 | 37.3 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
Salmo salar | 15339 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.13 µmol/L | N/I | N/I | 3.995 | whole body | physiological | N/I | N/I | N/I | N/I | ED 117 | 7 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15340 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.25 µmol/L | N/I | N/I | 7.457 | whole body | physiological | N/I | N/I | N/I | N/I | ED 145 | 7 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15341 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.25 µmol/L | N/I | N/I | 17.845 | whole body | physiological | N/I | N/I | N/I | N/I | ED 226 | 7 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15342 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.25 µmol/L | N/I | N/I | 22.372 | whole body | physiological | N/I | N/I | N/I | N/I | ED 188 | 7 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15343 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.44 µmol/L | N/I | N/I | 7.457 | whole body | physiological | N/I | N/I | N/I | N/I | ED 150 | 7 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15344 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.55 µmol/L | N/I | N/I | 11.719 | whole body | physiological | N/I | N/I | N/I | N/I | ED 235 | 1 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15345 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.55 µmol/L | N/I | N/I | 35.157 | whole body | physiological | N/I | N/I | N/I | N/I | ED 313 | 1 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15346 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.55 µmol/L | N/I | N/I | 41.282 | whole body | physiological | N/I | N/I | N/I | N/I | ED 207 | 1 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15347 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 0.82 µmol/L | N/I | N/I | 15.448 | whole body | physiological | N/I | N/I | N/I | N/I | ED 225 | 1 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 15348 | L | Atlantic Salmon | alevin | N/I | Pentachlorophenol | 87-86-5 | N/I | N/I | N/I | aqueous | 1.04 µmol/L | N/I | N/I | 22.372 | whole body | physiological | N/I | N/I | N/I | N/I | ED 284 | 1 d old Alevins | Penttinen and JVK. 2006. Body residues as dose for sublethal resp.... Environ Toxicol Chem 25:1088-1093. |
Salmo salar | 9616 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.263 µmol/L | N/I | N/I | 7.72 | whole body | physiological | N/I | N/I | N/I | N/I | NOEC | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9618 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.263 µmol/L | N/I | N/I | 2.65 | yolk | physiological | N/I | N/I | N/I | N/I | NOEC | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9619 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.263 µmol/L | N/I | N/I | 1.8 | egg shell | physiological | N/I | N/I | N/I | N/I | NOEC | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9620 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.497 µmol/L | N/I | N/I | 12.8 | whole body | physiological | N/I | N/I | N/I | N/I | LOEC | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9621 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.497 µmol/L | N/I | N/I | 3.9 | yolk | physiological | N/I | N/I | N/I | N/I | LOEC | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9622 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.497 µmol/L | N/I | N/I | 1.8 | egg shell | physiological | N/I | N/I | N/I | N/I | LOEC | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9623 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.497 µmol/L | N/I | N/I | 1.8 | egg shell | physiological | N/I | N/I | N/I | N/I | IP 152 | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9624 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.497 µmol/L | N/I | N/I | 3.9 | yolk | physiological | N/I | N/I | N/I | N/I | IP 152 | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9625 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.497 µmol/L | N/I | N/I | 12.8 | whole body | physiological | N/I | N/I | N/I | N/I | IP 152 | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9626 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.992 µmol/L | N/I | N/I | 25.8 | whole body | physiological | N/I | N/I | N/I | N/I | IP 225 | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9627 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.992 µmol/L | N/I | N/I | 8.6 | yolk | physiological | N/I | N/I | N/I | N/I | IP 225 | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Salmo salar | 9628 | L | Atlantic Salmon | embryo | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.992 µmol/L | N/I | N/I | 5.9 | egg shell | physiological | N/I | N/I | N/I | N/I | IP 225 | effect of PCP on embryo ability to dissipate heat | Maenpaa et al. 2004. Pentachlorophenol (PCP) bioaccumulation .... Aquat Toxicol 68:75-85. |
Oncorhynchus mykiss | 5030 | L | Rainbow Trout | adult | N/I | Pentachlorophenol | 87-86-5 | N | N/I | N/I | aqueous | 0.0003 mmol/L | N/I | 1.33 | 13.8 | whole body | mortality | N/I | N/I | N/I | N/I | LOEC | N/I | McKim and Schmieder. 1991. Bioaccumulation: Does it reflect toxici... |
Oncorhynchus mykiss | 20903 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 271 µg/L | continuous | 144 hr | 24.8 | whole body | mortality | N/R | N/A | 5.15 h | N/A | N/R | median time to death; high fat diet; no control | van den Huevel et al. 1991. Effect of total body lipid on the toxici.... Aquat Toxicol 20:235-252. |
Oncorhynchus mykiss | 20904 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 271 µg/L | continuous | 144 hr | 21.8 | whole body | mortality | N/R | N/A | 4.99 h | N/A | N/R | median time to death; low fat diet; no control | van den Huevel et al. 1991. Effect of total body lipid on the toxici.... Aquat Toxicol 20:235-252. |
Oncorhynchus mykiss | 20905 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 122 µg/L | continuous | 144 hr | 39.4 | whole body | mortality | N/R | N/A | 18.9 h | N/A | N/R | median time to death; high fat diet; no control | van den Huevel et al. 1991. Effect of total body lipid on the toxici.... Aquat Toxicol 20:235-252. |
Oncorhynchus mykiss | 20906 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 122 µg/L | continuous | 144 hr | 29.8 | whole body | mortality | N/R | N/A | 15.2 h | N/A | N/R | median time to death; low fat diet; no control | van den Huevel et al. 1991. Effect of total body lipid on the toxici.... Aquat Toxicol 20:235-252. |
Oncorhynchus mykiss | 20907 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 91 µg/L | continuous | 144 hr | 37.5 | whole body | mortality | N/R | N/A | >144 h | N/A | N/R | median time to death; high fat diet; no control | van den Huevel et al. 1991. Effect of total body lipid on the toxici.... Aquat Toxicol 20:235-252. |
Oncorhynchus mykiss | 20908 | L | Rainbow Trout | juvenile | C | Pentachlorophenol | 87-86-5 | N | Y | FW | aqueous | 91 µg/L | continuous | 144 hr | 43.9 | whole body | mortality | N/R | N/A | >144 h | N/A | N/R | median time to death; low fat diet; no control | van den Huevel et al. 1991. Effect of total body lipid on the toxici.... Aquat Toxicol 20:235-252. |