DOTS

ERED

Environmental Residue-Effects Database

US Army Corps of Engineers ERDC Dredging Operations Technical Support

USACE


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; non-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
Pimephales promelas 20507 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 5.04 µmol/L 1x 2 hr 74.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20508 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 2.52 µmol/L 1x 4 hr 69.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20509 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 2.27 µmol/L 1x 6 hr 85.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20510 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.58 µmol/L 1x 10 hr 82.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20511 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.42 µmol/L 1x 16 hr 90.5 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20512 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.2 µmol/L 1x 24 hr 85.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20513 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.11 µmol/L 1x 48 hr 85.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20514 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.07 µmol/L 1x 96 hr 82.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20515 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 0.97 µmol/L 1x 144 hr 74.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20516 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 3.51 µmol/L 6 h interval, 3 pulse 24 hr 82.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20517 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 3 µmol/L 6 h interval, 15 pulse 120 hr 74.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20518 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 4.4 µmol/L 14 h interval, 3 pulse 48 hr 77.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20519 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 3.91 µmol/L 14 h interval, 8 pulse 128 hr 69.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20520 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 5.04 µmol/L 22 h interval, 3 pulse 72 hr 79.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20521 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.89 µmol/L 6 h interval, 3 pulse 30 hr 74.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20522 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.64 µmol/L 6 h interval, 12 pulse 120 hr 66.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20523 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 2.05 µmol/L 16 h interval, 3 pulse 60 hr 61.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20524 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.51 µmol/L 16 h interval, 8 pulse 160 hr 45.3 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20525 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 2.18 µmol/L 6 h interval, 2 pulse 24 hr 103.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20526 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.7 µmol/L 6 h interval, 10 pulse 120 hr 85.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20527 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 2.2 µmol/L 18 h interval, 2 pulse 48 hr 87.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20528 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.91 µmol/L 18 h interval, 5 pulse 120 hr 77.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20529 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.18 µmol/L 6 h interval, 2 pulse 32 hr 71.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20530 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.11 µmol/L 6 h interval, 9 pulse 144 hr 69.2 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20531 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.42 µmol/L 22 h interval, 2 pulse 64 hr 74.6 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20532 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.35 µmol/L 22 h interval, 3 pulse 96 hr 71.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20533 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.23 µmol/L 24 h interval, 2 pulse 96 hr 87.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20534 L fathead Minnow larvae C Pentachlorophenol 87-86-5 N Y FW aqueous 1.21 µmol/L 24 h interval, 3 pulse 144 hr 87.9 whole body mortality INC N/I 50% >90% LC 50 exposure: time interval b/w pulses & no. pulses Hickie et al. 1995. A residue‐based toxicokinetic model for .... Environ Toxicol Chem 14:2187-2197.
Pimephales promelas 20825 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 3.1 µg/L continuous 32 d 2.8 whole body survival NEF N 96% 91% N/R pH=6.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20826 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.1 µg/L continuous 32 d 5 whole body survival NEF N 91% 91% N/R pH=6.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20827 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 8.9 µg/L continuous 32 d 9.6 whole body survival NEF N 95% 91% N/R pH=6.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20828 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 16.5 µg/L continuous 32 d 21.5 whole body survival NEF N 95% 91% N/R pH=6.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20829 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 34.6 µg/L continuous 32 d 45.9 whole body survival DEC Y 23% 91% N/R pH=6.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20830 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.6 µg/L continuous 32 d 2.5 whole body survival NEF N 91% 90% N/R pH=7.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20831 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.2 whole body survival NEF N 88% 90% N/R pH=7.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20832 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 27.6 µg/L continuous 32 d 12.3 whole body survival NEF N 98% 90% N/R pH=7.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20833 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 58.2 µg/L continuous 32 d 25.1 whole body survival NEF N 84% 90% N/R pH=7.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20834 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 124 µg/L continuous 32 d N/R survival DEC Y 0% 90% N/R pH=7.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20835 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.8 whole body survival NEF N 88% 88% N/R pH=8.0 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20836 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 32 µg/L continuous 32 d 12.6 whole body survival NEF N 91% 88% N/R pH=8.0 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20837 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 75 µg/L continuous 32 d 22.1 whole body survival NEF N 92% 88% N/R pH=8.0 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20838 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 161 µg/L continuous 32 d 53.8 whole body survival DEC Y 29% 88% N/R pH=8.0 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20839 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 327 µg/L continuous 32 d N/R survival DEC Y 0% 88% N/R pH=8.0 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20840 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 29.3 µg/L continuous 32 d 8.3 whole body survival NEF N 93% 93% N/R pH=8.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20841 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 63.7 µg/L continuous 32 d 17.8 whole body survival NEF N 92% 93% N/R pH=8.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20842 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 125 µg/L continuous 32 d 35.1 whole body survival DEC Y 75% 93% N/R pH=8.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20843 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 237 µg/L continuous 32 d 69 whole body survival DEC Y 75% 93% N/R pH=8.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20844 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 451 µg/L continuous 32 d N/R survival DEC Y 13% 93% N/R pH=8.5 Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20845 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 3.1 µg/L continuous 32 d 2.8 whole body reproduction NEF N 98% 100% N/R pH=6.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20846 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.1 µg/L continuous 32 d 5 whole body reproduction NEF N 100% 100% N/R pH=6.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20847 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 8.9 µg/L continuous 32 d 9.6 whole body reproduction NEF N 100% 100% N/R pH=6.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20848 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 16.5 µg/L continuous 32 d 21.5 whole body reproduction NEF N 100% 100% N/R pH=6.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20849 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 34.6 µg/L continuous 32 d 45.9 whole body reproduction NEF N 100% 100% N/R pH=6.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20850 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.6 µg/L continuous 32 d 2.5 whole body reproduction NEF N 100% 100% N/R pH=7.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20851 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.2 whole body reproduction NEF N 100% 100% N/R pH=7.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20852 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 27.6 µg/L continuous 32 d 12.3 whole body reproduction NEF N 100% 100% N/R pH=7.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20853 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 58.2 µg/L continuous 32 d 25.1 whole body reproduction NEF N 100% 100% N/R pH=7.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20854 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 124 µg/L continuous 32 d N/R reproduction DEC Y 82% 100% N/R pH=7.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20855 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.8 whole body reproduction NEF N 98% 100% N/R pH=8.0; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20856 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 32 µg/L continuous 32 d 12.6 whole body reproduction NEF N 100% 100% N/R pH=8.0; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20857 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 75 µg/L continuous 32 d 22.1 whole body reproduction NEF N 95% 100% N/R pH=8.0; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20858 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 161 µg/L continuous 32 d 53.8 whole body reproduction NEF N 95% 100% N/R pH=8.0; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 6371 L fathead Minnow juvenile N/I Pentachlorophenol 87-86-5 N N/I FW aqueous N/I N/I N/I 70.58 whole body mortality N/I N/I N/I N/I LD 50 N/I McCarty et al. 1993. Residue‐based interpretation of toxicity.... Ecotox Environ Safe 25:253-270.
Carassius auratus 1186 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.27 mg/L 1x/8hr 24 hr 95 whole body mortality INC N/I 50% N/R LC 50 lethal concentration Kobayashi et al. 1979. Relation between toxicity and accumulati.... B Jpn Soc Sci Fish 45:173-175.
Carassius auratus 1194 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.2 mg/L N/I 5 hr 58 whole body mortality N/I N/I N/I N/I LD 100 Survivors residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1195 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.3 mg/L N/I 5 hr 69 whole body mortality N/I N/I N/I N/I LD 100 Survivors residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1196 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.5 mg/L N/I 5 hr 73 whole body mortality N/I N/I N/I N/I LD 100 Survivors residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1197 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.2 mg/L N/I 5 hr 82 whole body mortality N/I N/I N/I N/I LD 100 Dead fish residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1198 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 3 mg/L N/I 5 hr 86 whole body mortality N/I N/I N/I N/I LD 100 Dead fish residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1199 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.3 mg/L N/I 5 hr 88 whole body mortality N/I N/I N/I N/I LD 100 Dead fish residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1200 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.5 mg/L N/I 5 hr 92 whole body mortality N/I N/I N/I N/I LD 100 Dead fish residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1201 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 1 mg/L N/I 5 hr 102 whole body mortality N/I N/I N/I N/I LD 100 Dead fish residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 1202 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 3 mg/L N/I 5 hr 18 whole body mortality N/I N/I N/I N/I NOEC Survivors residue measurement Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4744 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.2 mg/L N/I 0.21 82 whole body mortality N/I N/I N/I N/I LD 100 Exposure at pH 5.5. 100% mortality in 5 hr. Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4745 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 3 mg/L N/I 0.21 86 whole body mortality N/I N/I N/I N/I LD 100 Exposure at pH 9. 100% mortality in 5 hr. Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4746 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.3 mg/L N/I 0.21 88 whole body mortality N/I N/I N/I N/I LD 100 Exposure at pH 6. 100% mortality in 5 hr. Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4747 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.5 mg/L N/I 0.21 92 whole body mortality N/I N/I N/I N/I LD 100 Exposure at pH 7. 100% mortality in 5 hr. Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4748 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 1 mg/L N/I 0.21 102 whole body mortality N/I N/I N/I N/I LD 100 Exposure at pH 8. 100% mortality in 5 hr. Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4749 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 3 mg/L N/I 0.21 20 whole body mortality N/I N/I N/I N/I NOEC No increase in mortality in 5 hr Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4750 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.1 mg/L N/I 0.21 60 whole body mortality N/I N/I N/I N/I NOEC No increase in mortality in 5 hr Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4751 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 2 mg/L N/I 0.21 60 whole body mortality N/I N/I N/I N/I NOEC No increase in mortality in 5 hr Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4752 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.1 mg/L N/I 0.21 65 whole body mortality N/I N/I N/I N/I NOEC No increase in mortality in 5 hr Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4753 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.5 mg/L N/I 0.21 70 whole body mortality N/I N/I N/I N/I NOEC No increase in mortality in 5 hr Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Carassius auratus 4754 L goldfish N/I N/I Pentachlorophenol 87-86-5 N N/I FW aqueous 0.3 mg/L N/I 0.21 80 whole body mortality N/I N/I N/I N/I NOEC No increase in mortality in 5 hr Kobayashi and Kishino. 1980. Effect of pH on the toxicity and accumul.... B Jpn Soc Sci Fish 46:167-170.
Pimephales promelas 20859 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 327 µg/L continuous 32 d N/R reproduction DEC Y 54% 100% N/R pH=8.0; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20860 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 29.3 µg/L continuous 32 d 8.3 whole body reproduction NEF N 100% 100% N/R pH=8.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20861 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 63.7 µg/L continuous 32 d 17.8 whole body reproduction NEF N 98% 100% N/R pH=8.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20862 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 125 µg/L continuous 32 d 35.1 whole body reproduction NEF N 100% 100% N/R pH=8.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20863 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 237 µg/L continuous 32 d 69 whole body reproduction NEF N 100% 100% N/R pH=8.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20864 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 451 µg/L continuous 32 d N/R reproduction DEC Y 82% 100% N/R pH=8.5; hatchability Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20865 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 3.1 µg/L continuous 32 d 2.8 whole body reproduction NEF N 98% 100% N/R pH=6.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20866 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.1 µg/L continuous 32 d 5 whole body reproduction NEF N 100% 100% N/R pH=6.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20867 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 8.9 µg/L continuous 32 d 9.6 whole body reproduction NEF N 100% 100% N/R pH=6.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20868 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 16.5 µg/L continuous 32 d 21.5 whole body reproduction NEF N 100% 100% N/R pH=6.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20869 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 34.6 µg/L continuous 32 d 45.9 whole body reproduction DEC Y 0% 100% N/R pH=6.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20870 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.6 µg/L continuous 32 d 2.5 whole body reproduction NEF N 95% 95% N/R pH=7.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20871 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.2 whole body reproduction NEF N 95% 95% N/R pH=7.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20872 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 27.6 µg/L continuous 32 d 12.3 whole body reproduction NEF N 93% 95% N/R pH=7.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20873 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 58.2 µg/L continuous 32 d 25.1 whole body reproduction NEF N 100% 95% N/R pH=7.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20874 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 124 µg/L continuous 32 d N/R reproduction DEC Y 88% 95% N/R pH=7.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20875 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.8 whole body reproduction NEF N 0% 97% N/R pH=8.0; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20876 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 32 µg/L continuous 32 d 12.6 whole body reproduction NEF N 97% 97% N/R pH=8.0; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20877 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 75 µg/L continuous 32 d 22.1 whole body reproduction NEF N 95% 97% N/R pH=8.0; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20878 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 161 µg/L continuous 32 d 53.8 whole body reproduction DEC Y 0% 97% N/R pH=8.0; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20879 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 327 µg/L continuous 32 d N/R reproduction DEC Y 0% 97% N/R pH=8.0; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20880 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 29.3 µg/L continuous 32 d 8.3 whole body reproduction NEF N 100% 97% N/R pH=8.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20881 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 63.7 µg/L continuous 32 d 17.8 whole body reproduction NEF N 97% 97% N/R pH=8.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20882 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 125 µg/L continuous 32 d 35.1 whole body reproduction NEF N 100% 97% N/R pH=8.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20883 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 237 µg/L continuous 32 d 69 whole body reproduction DEC Y 0% 97% N/R pH=8.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20884 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 451 µg/L continuous 32 d N/R reproduction DEC Y 0% 97% N/R pH=8.5; normal larvae at hatch Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20885 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 3.1 µg/L continuous 32 d 2.8 whole body growth NEF N 74 mg 81 mg N/R pH=6.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20886 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.1 µg/L continuous 32 d 5 whole body growth NEF N 80 mg 81 mg N/R pH=6.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20887 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 8.9 µg/L continuous 32 d 9.6 whole body growth NEF N 74 mg 81 mg N/R pH=6.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20888 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 16.5 µg/L continuous 32 d 21.5 whole body growth NEF N 74 mg 81 mg N/R pH=6.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20889 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 34.6 µg/L continuous 32 d 45.9 whole body growth NEF N 88 mg 81 mg N/R pH=6.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20890 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 5.6 µg/L continuous 32 d 2.5 whole body growth NEF N 103 mg 98 mg N/R pH=7.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20891 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.2 whole body growth NEF N 102 mg 98 mg N/R pH=7.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20892 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 27.6 µg/L continuous 32 d 12.3 whole body growth NEF N 90 mg 98 mg N/R pH=7.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20893 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 58.2 µg/L continuous 32 d 25.1 whole body growth DEC Y 81 mg 98 mg N/R pH=7.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20894 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 12.7 µg/L continuous 32 d 5.8 whole body growth NEF N 108 mg 100 mg N/R pH=8.0; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20895 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 32 µg/L continuous 32 d 12.6 whole body growth NEF N 109 mg 100 mg N/R pH=8.0; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20896 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 75 µg/L continuous 32 d 22.1 whole body growth DEC Y 90 mg 100 mg N/R pH=8.0; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20897 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 161 µg/L continuous 32 d 53.8 whole body growth DEC Y 88 mg 100 mg N/R pH=8.0; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20898 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 29.3 µg/L continuous 32 d 8.3 whole body growth NEF N 104 mg 108mg N/R pH=8.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20899 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 63.7 µg/L continuous 32 d 17.8 whole body growth NEF N 107 mg 108mg N/R pH=8.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20900 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 125 µg/L continuous 32 d 35.1 whole body growth NEF N 104 mg 108mg N/R pH=8.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20901 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 237 µg/L continuous 32 d 69 whole body growth DEC Y 88 mg 108mg N/R pH=8.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Pimephales promelas 20902 L fathead Minnow embryo C Pentachlorophenol 87-86-5 N Y FW aqueous 451 µg/L continuous 32 d N/R growth DEC Y 7 mg 108mg N/R pH=8.5; mean weight Spehar et al. 1985. Pentachlorophenol toxicity to amphipods .... Environ Toxicol Chem 4:389-397.
Carassius auratus 21810 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.1 mg/L 1x 5 hr 66 whole body survival N/I N/R 100% no ctrl N/R pH 5.5; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21811 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.2 mg/L 1x 5 hr 57 whole body survival N/I N/R 0% no ctrl N/R pH 5.5; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21812 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.3 mg/L 1x 5 hr 70 whole body survival N/I N/R 90% no ctrl N/R pH 5.5; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21813 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.5 mg/L 1x 5 hr 44 whole body survival N/I N/R 0% no ctrl N/R pH 5.5; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21814 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.7 mg/L 1x 5 hr 62 whole body survival N/I N/R 0% no ctrl N/R pH 5.5; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21815 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 1 mg/L 1x 5 hr 76 whole body survival N/I N/R 0% no ctrl N/R pH 5.5; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21822 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.1 mg/L 1x 5 hr 58 whole body survival N/I N/R 100% no ctrl N/R pH 6; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21823 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.2 mg/L 1x 5 hr 88 whole body survival N/I N/R 55% no ctrl N/R pH 6; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21824 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.3 mg/L 1x 5 hr 70 whole body survival N/I N/R 0% no ctrl N/R pH 6; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21825 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.5 mg/L 1x 5 hr 101 whole body survival N/I N/R 10% no ctrl N/R pH 6; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21826 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.7 mg/L 1x 5 hr 60 whole body survival N/I N/R 0% no ctrl N/R pH 6; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21827 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 1 mg/L 1x 5 hr 82 whole body survival N/I N/R 0% no ctrl N/R pH 6; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21828 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.1 mg/L 1x 5 hr 30 whole body survival N/I N/R 100% no ctrl N/R pH 7; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21829 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.2 mg/L 1x 5 hr 56 whole body survival N/I N/R 100% no ctrl N/R pH 7; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21830 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.3 mg/L 1x 5 hr 82 whole body survival N/I N/R 100% no ctrl N/R pH 7; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21831 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.5 mg/L 1x 5 hr 74 whole body survival N/I N/R 0% no ctrl N/R pH 7; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21832 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.7 mg/L 1x 5 hr 86 whole body survival N/I N/R 30% no ctrl N/R pH 7; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21833 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 1 mg/L 1x 5 hr 100 carcass survival N/I N/R 0% no ctrl N/R pH 7; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21834 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.1 mg/L 1x 5 hr 11 whole body survival N/I N/R 100% no ctrl N/R pH 8; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21835 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.2 mg/L 1x 5 hr 22 whole body survival N/I N/R 100% no ctrl N/R pH 8; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21836 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.3 mg/L 1x 5 hr 37 whole body survival N/I N/R 100% no ctrl N/R pH 8; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21837 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.5 mg/L 1x 5 hr 68 whole body survival N/I N/R 100% no ctrl N/R pH 8; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21838 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.7 mg/L 1x 5 hr 86 whole body survival N/I N/R 91% no ctrl N/R pH 8; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21839 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 1 mg/L 1x 5 hr 68 whole body survival N/I N/R 9% no ctrl N/R pH 8; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21840 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.1 mg/L 1x 5 hr 3 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21841 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.2 mg/L 1x 5 hr 8 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21842 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.3 mg/L 1x 5 hr 11 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21843 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.5 mg/L 1x 5 hr 18 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21844 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.7 mg/L 1x 5 hr 25 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21845 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 1 mg/L 1x 5 hr 32 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21846 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 2 mg/L 1x 5 hr 56 whole body survival N/I N/R 100% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21847 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 3 mg/L 1x 5 hr 82 whole body survival N/I N/R 10% no ctrl N/R pH 9; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21848 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.1 mg/L 1x 5 hr 1 whole body survival N/I N/R 100% no ctrl N/R pH 10; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21849 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 0.5 mg/L 1x 5 hr 7 whole body survival N/I N/R 100% no ctrl N/R pH 10; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21850 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 2 mg/L 1x 5 hr 12 whole body survival N/I N/R 100% no ctrl N/R pH 10; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.
Carassius auratus 21851 L goldfish N/R N/R Pentachlorophenol 87-86-5 N Y FW aqueous 3 mg/L 1x 5 hr 16 whole body survival N/I N/R 100% no ctrl N/R pH 10; relation between acute toxicity and accumulation of chlorophenols exposed at various pH Kishino and Kobayashi. 1995. Relation between toxicity and accumulati.... Water Res 29:431-442.