| 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 Polychlorinated Biphenyls (PCBs)
| 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 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Limanda limanda | 21100 | L | Dab | adult | W | Clophen A40 | N | Y | SW | gavage | 1 mg | 3x | 101 d | 18.1 | muscle | mortality | NEF | N | 0% | 0% | N/R | no mortality during experiment | Sleiderink et al. 1995. Hepatic cytochrome P4501A induction in D.... Environ Toxicol Chem 14:679-687. | |
| Limanda limanda | 21101 | L | Dab | adult | W | Clophen A40 | N | Y | SW | gavage | 1 mg | 3x | 101 d | 41.5 | muscle | mortality | NEF | N | 0% | 0% | N/R | no mortality during experiment | Sleiderink et al. 1995. Hepatic cytochrome P4501A induction in D.... Environ Toxicol Chem 14:679-687. | |
| Limanda limanda | 21102 | L | Dab | adult | W | Clophen A40 | N | Y | SW | gavage | 1 mg | 3x | 101 d | 55.9 | muscle | mortality | NEF | N | 0% | 0% | N/R | no mortality during experiment | Sleiderink et al. 1995. Hepatic cytochrome P4501A induction in D.... Environ Toxicol Chem 14:679-687. | |
| Limanda limanda | 21103 | L | Dab | adult | W | Clophen A40 | N | Y | SW | gavage | 1 mg | 3x | 101 d | 18.1 | muscle | growth | NEF | N | 105 g | 93 g | N/R | no difference in weight, length, condition indice | Sleiderink et al. 1995. Hepatic cytochrome P4501A induction in D.... Environ Toxicol Chem 14:679-687. | |
| Limanda limanda | 21104 | L | Dab | adult | W | Clophen A40 | N | Y | SW | gavage | 1 mg | 3x | 101 d | 41.5 | muscle | growth | NEF | N | 105 g | 93 g | N/R | no difference in weight, length, condition indice | Sleiderink et al. 1995. Hepatic cytochrome P4501A induction in D.... Environ Toxicol Chem 14:679-687. | |
| Limanda limanda | 21105 | L | Dab | adult | W | Clophen A40 | N | Y | SW | gavage | 1 mg | 3x | 101 d | 55.9 | muscle | growth | NEF | N | 105 g | 93 g | N/R | no difference in weight, length, condition indice | Sleiderink et al. 1995. Hepatic cytochrome P4501A induction in D.... Environ Toxicol Chem 14:679-687. | |
| Pseudopleuronectes americanus | 21192 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.27 | whole body | growth | DEC | Y | 0.019 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21193 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.67 | whole body | growth | DEC | Y | 0.019 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21194 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.29 | whole body | growth | DEC | Y | 0.021 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21195 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.39 | whole body | growth | DEC | Y | 0.021 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21196 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.33 | whole body | growth | DEC | Y | 0.022 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21197 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.28 | whole body | growth | DEC | Y | 0.024 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21198 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.41 | whole body | growth | DEC | Y | 0.024 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21199 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 0.39 | whole body | growth | DEC | Y | 0.025 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21200 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 3.15 | whole body | growth | DEC | Y | 0.027 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21201 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 4.1 | whole body | growth | DEC | Y | 0.026 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21202 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 4.89 | whole body | growth | DEC | Y | 0.025 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21203 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 4.14 | whole body | growth | DEC | Y | 0.021 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21204 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 3.37 | whole body | growth | DEC | Y | 0.015 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21205 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 11.08 | whole body | growth | DEC | Y | 0.011 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21206 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 11.32 | whole body | growth | DEC | Y | 0.016 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21207 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 11.64 | whole body | growth | DEC | Y | 0.016 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21208 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 11.48 | whole body | growth | DEC | Y | 0.024 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Pseudopleuronectes americanus | 21209 | L | winter flounder | egg | W | PCBs (total) | 1336-36-3 | N | N | SW | aqueous | N/R | field | N/A | 14.3 | whole body | growth | DEC | Y | 0.012 mg | N/A | N/R | significant inverse relationship between PCB content of the egg and length or weight at hatch | Black et al. 1988. The effect of inherited contamination on.... Mar Environ Res 25:45-62. |
| Parophrys vetulus | 21272 | F | English sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3.7 | liver | biochemistry | INC | Y | 140 | 35 | N/R | hydrophobic DNA xenobiotic adducts | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Parophrys vetulus | 21273 | F | English sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3.7 | liver | biochemistry | INC | Y | 660 | 110 | N/R | hepatic aryl hydrocarbon hydroxylase | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Parophrys vetulus | 21274 | F | English sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3.7 | liver | biochemistry | INC | Y | 510 | 35 | N/R | ethoxyresorufin 0 deethylase | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Parophrys vetulus | 21275 | F | English sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3.7 | liver | biochemistry | INC | Y | 4,100 | 370 | N/R | total hepatic GSH | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Lepidopsetta bilineata | 21276 | F | Rock sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3 | liver | biochemistry | NEF | N | 100 | 67 | N/R | hydrophobic DNA xenobiotic adducts | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Lepidopsetta bilineata | 21277 | F | Rock sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3 | liver | biochemistry | INC | Y | 630 | 380 | N/R | hepatic aryl hydrocarbon hydroxylase | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Lepidopsetta bilineata | 21278 | F | Rock sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3 | liver | biochemistry | INC | Y | 540 | 270 | N/R | ethoxyresorufin 0 deethylase | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Lepidopsetta bilineata | 21279 | F | Rock sole | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 3 | liver | biochemistry | INC | Y | 2600 | 1,600 | N/R | total hepatic GSH | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Platichthys stellatus | 21280 | F | starry flounder | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 1.9 | liver | biochemistry | INC | Y | 180 | 20 | N/R | hydrophobic DNA xenobiotic adducts | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Platichthys stellatus | 21281 | F | starry flounder | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 1.9 | liver | biochemistry | INC | Y | 370 | 95 | N/R | hepatic aryl hydrocarbon hydroxylase | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Platichthys stellatus | 21282 | F | starry flounder | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 1.9 | liver | biochemistry | INC | Y | 210 | 58 | N/R | ethoxyresorufin 0 deethylase | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |
| Platichthys stellatus | 21283 | F | starry flounder | juvenile | W | PCBs (total) | 1336-36-3 | Y | N | SW | in situ | 570 ng/g | field | N/A | 1.9 | liver | biochemistry | INC | Y | 2,500 | 1,300 | N/R | total hepatic GSH | Stein et al. 1992. Bioindicators of contaminant exposure an.... Environ Toxicol Chem 11:701-714. |