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-fungicides
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 | 3449 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.3 µg/L | N/I | 28 | 4 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 3450 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.5 µg/L | N/I | 28 | 6.3 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 3451 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.7 µg/L | N/I | 28 | 14.8 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 3452 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 2 µg/L | N/I | 28 | 30.5 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 3453 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 3.8 µg/L | N/I | 28 | 46.5 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 1941 | L | fathead Minnow | juvenile | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 5 µg/L | N/I | 28 | 9.3 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | BCFs given for conc 0.3, 0.6, 1.2, 2.5, 5.0 ug/L | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 1945 | L | fathead Minnow | juvenile | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 5 µg/L | N/I | 28 | 9.3 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | BCFs given for conc 0.3, 0.6, 1.2, 2.5, 5.0 ug/L | Nebeker et al. 1989. Survival, reproduction and bioconcentrat.... Environ Toxicol Chem 8:601-611. |
Pimephales promelas | 5581 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.3 µg/L | N/I | 32 | 8 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5582 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.7 µg/L | N/I | 32 | 15 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5583 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 1.2 µg/L | N/I | 32 | 27 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5584 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 2.6 µg/L | N/I | 32 | 46 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5585 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 4.8 µg/L | N/I | 32 | 97 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5596 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.3 µg/L | N/I | 32 | 8 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5597 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 0.7 µg/L | N/I | 32 | 15 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5598 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 1.2 µg/L | N/I | 32 | 27 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5599 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 2.6 µg/L | N/I | 32 | 46 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 5600 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 4.8 µg/L | N/I | 32 | 97 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 2346 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | Y | FW | aqueous | 93 µg/g | N/I | 44 d | 138 | whole body | physiological | N/I | N/I | N/I | N/I | N/A | significantly different | Schuytema et al. 1988. Comparative uptake of hexachlorobenzene .... Environ Sci Tech 22:1035-1045. |
Pimephales promelas | 2347 | L | fathead Minnow | adult | N/I | Hexachlorobenzene | 118-74-1 | N | Y | FW | aqueous | 93 µg/g | N/I | 28 d | 190 | whole body | physiological | N/I | N/I | N/I | N/I | N/A | significantly different | Schuytema et al. 1988. Comparative uptake of hexachlorobenzene .... Environ Sci Tech 22:1035-1045. |
Pimephales promelas | 3066 | L | fathead Minnow | larvae | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 4.8 µg/L | N/I | 32d | 97 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 3072 | L | fathead Minnow | larvae | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 4.8 µg/L | N/I | 32d | 97 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |
Pimephales promelas | 3073 | L | fathead Minnow | embryo | N/I | Hexachlorobenzene | 118-74-1 | N | N/I | FW | aqueous | 4.8 µg/L | N/I | 32d | 97 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | hatch mortality | Carlson and Kosian. 1987. Toxicity of chlorinated benzenes to fath.... Arch Environ Con Tox 16:129-135. |