| 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 Arthropoda: Invert (insects, crustaceans) 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 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Palaemonetes pugio | 4233 | L | shrimp, daggerblade grass | N/R | W | Aroclor 1016 | 12674-11-2 | N | Y | SW | aqueous | 9.4 µg/L | continuous | 96 hr | 22 | whole body | mortality | INC | N/R | 38% | 8% | N/R | 38% mortality | Hansen et al. 1974. Aroclor 1016: Toxicity to and uptake by .... Environ Res 7:363-373. |
| Farfantepanaeus aztecus | 4234 | L | shrimp, brown | N/I | W | Aroclor 1016 | 12674-11-2 | N | Y | SW | aqueous | 8.9 µg/L | continuous | 96 hr | 42 | whole body | mortality | INC | N/R | 43% | 0% | N/R | 43% mortality | Hansen et al. 1974. Aroclor 1016: Toxicity to and uptake by .... Environ Res 7:363-373. |
| Palaemonetes pugio | 4242 | L | shrimp, daggerblade grass | N/R | W | Aroclor 1016 | 12674-11-2 | N | Y | SW | aqueous | 38 µg/L | continuous | 96 hr | 44 | whole body | mortality | INC | N/R | 93% | 8% | N/R | 93% mortality | Hansen et al. 1974. Aroclor 1016: Toxicity to and uptake by .... Environ Res 7:363-373. |
| Palaemonetes pugio | 4252 | L | shrimp, daggerblade grass | N/R | W | Aroclor 1016 | 12674-11-2 | N | Y | SW | aqueous | 0.4 µg/L | continuous | 96 hr | 1.1 | whole body | mortality | INC | N/R | 33% | 8% | N/R | 33% mortality | Hansen et al. 1974. Aroclor 1016: Toxicity to and uptake by .... Environ Res 7:363-373. |
| Farfantepanaeus aztecus | 4253 | L | shrimp, brown | N/I | W | Aroclor 1016 | 12674-11-2 | N | Y | SW | aqueous | 0.9 µg/L | continuous | 96 hr | 3.8 | whole body | mortality | INC | N/R | 8% | 0% | N/R | 8% mortality | Hansen et al. 1974. Aroclor 1016: Toxicity to and uptake by .... Environ Res 7:363-373. |
| Farfantepanaeus aztecus | 19759 | L | shrimp, brown | N/R | W | Aroclor 1016 | 12674-11-2 | N | Y | SW | aqueous | 33 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 100% | 0% | N/R | 100% mortality; no residue reported | Hansen et al. 1974. Aroclor 1016: Toxicity to and uptake by .... Environ Res 7:363-373. | |
| Palaemonetes kadiakensis | 19936 | L | shrimp, Mississippi grass | mature | W | Aroclor 1254 | 11097-69-1 | Y | Y | FW | aqueous | 1.3 µg/L | continuous | 4 d | 3.2 | whole body | mortality | NEF | N/R | <10% | <10% | N/R | mortality <10% for test and control animals | Sanders and Chandler. 1972. Biological magnification of a polychlori.... B Environ Contam Tox 7:257-263. |
| Orconectes nais | 19939 | L | crayfish, water nymph | mature | W | Aroclor 1254 | 11097-69-1 | Y | Y | FW | aqueous | 1.2 µg/L | continuous | 4 d | 0.04 | whole body | mortality | NEF | N/R | <10% | <10% | N/R | mortality <10% for test and control animals | Sanders and Chandler. 1972. Biological magnification of a polychlori.... B Environ Contam Tox 7:257-263. |
| Palaemonetes pugio | 19982 | L | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | Y | SW | aqueous | 0.17 µg/L | continuous | 7 d | 1.3 | whole body | mortality | NEF | N | 8% | 4% | N/R | no effect on mortality | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19983 | L | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | Y | SW | aqueous | 0.62 µg/L | continuous | 7 d | 5.4 | whole body | mortality | NEF | N | 4% | 4% | N/R | no effect on mortality | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19984 | L | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | Y | SW | aqueous | 9.1 µg/L | continuous | 7 d | 65 | whole body | mortality | INC | Y | 60% | 4% | N/R | mortality increased significantly | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19985 | L | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | Y | SW | aqueous | 1.3 µg/L | continuous | 16 d | 18 | whole body | mortality | NEF | N | 40% | 25% | N/R | no effect on mortality | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19986 | L | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | Y | SW | aqueous | 4 µg/L | continuous | 16 d | 27 | whole body | mortality | INC | Y | 45% | 25% | N/R | mortality increased significantly | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19987 | L | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | Y | SW | aqueous | 12.5 µg/L | continuous | 16 d | 46 | whole body | mortality | INC | Y | 55% | 25% | N/R | mortality increased significantly | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19988 | F | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | N | SW | in situ | 5 mg/kg | continuous | 1 mo | 0.41 | whole body | mortality | NEF | N | N/R | N/R | N/R | no effect on mortality | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Palaemonetes pugio | 19989 | F | shrimp, daggerblade grass | N/R | N/R | Aroclor 1254 | 11097-69-1 | Y | N | SW | in situ | 5 mg/kg | continuous | 3 mo | 0.42 | whole body | mortality | NEF | N | N/R | N/R | N/R | no effect on mortality | Nimmo et al. 1974. Accumulation of Aroclor® 1254 in grass s.... B Environ Contam Tox 11:303-308. |
| Farfantepanaeus duorarum | 19750 | L | shrimp, penaeid | juvenile | W | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 100 µg/L | continuous | 48 hr | 3.9 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | Duke et al. 1970. A polychlorinated biphenyl (aroclor 1254.... B Environ Contam Tox 5:171-180. |
| Farfantepanaeus duorarum | 19751 | L | shrimp, penaeid | juvenile | W | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 10 µg/L | continuous | 48 hr | 1.3 | whole body | mortality | NEF | N/R | 0% | N/R | N/R | no effect on mortality | Duke et al. 1970. A polychlorinated biphenyl (aroclor 1254.... B Environ Contam Tox 5:171-180. |
| Farfantepanaeus duorarum | 19752 | L | shrimp, penaeid | juvenile | W | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 1 µg/L | continuous | 48 hr | 0.14 | whole body | mortality | NEF | N/R | 0% | N/R | N/R | no effect on mortality | Duke et al. 1970. A polychlorinated biphenyl (aroclor 1254.... B Environ Contam Tox 5:171-180. |
| Farfantepanaeus duorarum | 19756 | L | shrimp, penaeid | juvenile | W | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 4.2 µg/L | continuous | 20 d | 33 | whole body | mortality | INC | N/R | 72% | 0% | N/R | mortality increased to 72% (18 of 25 shrimp) | Duke et al. 1970. A polychlorinated biphenyl (aroclor 1254.... B Environ Contam Tox 5:171-180. |
| Callinectes sapidus | 19757 | L | crab, blue | juvenile | W | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 4.2 µg/L | continuous | 20 d | 23 | whole body | mortality | INC | N/R | 5% | 5% | N/R | mortality was 5% (1 of 20 crabs) | Duke et al. 1970. A polychlorinated biphenyl (aroclor 1254.... B Environ Contam Tox 5:171-180. |