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). |
Source: Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434..
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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Crassostrea virginica | 3605 | L | eastern oyster | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 0.23 µg/L | continuous | 96 hr | 4.95 | whole body | growth | DEC | N/R | 18% | 0% | N/R | reduction in shell growth | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Crassostrea virginica | 3606 | L | eastern oyster | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 5.8 µg/L | continuous | 96 hr | 13.85 | whole body | growth | NEF | N/R | 0% | 0% | N/R | no effect on shell growth | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Crassostrea virginica | 3607 | L | eastern oyster | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 6.7 µg/L | continuous | 96 hr | 20 | whole body | growth | DEC | N/R | 24% | 0% | N/R | reduction in shell growth | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Crassostrea virginica | 3608 | L | eastern oyster | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 13 µg/L | continuous | 96 hr | 80.5 | whole body | growth | DEC | N/R | 61% | 0% | N/R | reduction in shell growth | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Farfantepanaeus duorarum | 3609 | L | shrimp, penaeid | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 0.014 µg/L | continuous | 96 hr | 0.01 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | no effect on mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Farfantepanaeus duorarum | 3610 | L | shrimp, penaeid | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 0.19 µg/L | continuous | 96 hr | 0.08 | whole body | mortality | INC | N/R | 25% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Farfantepanaeus duorarum | 3611 | L | shrimp, penaeid | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 0.9 µg/L | continuous | 96 hr | 0.25 | whole body | mortality | INC | N/R | 55% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Farfantepanaeus duorarum | 3612 | L | shrimp, penaeid | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 2.5 µg/L | continuous | 96 hr | 0.76 | whole body | mortality | INC | N/R | 70% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Palaemonetes pugio | 3613 | L | shrimp, daggerblade grass | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 2.8 µg/L | continuous | 96 hr | 2.1 | whole body | mortality | INC | N/R | 20% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Palaemonetes pugio | 19733 | L | shrimp, daggerblade grass | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 7.1 µg/L | continuous | 96 hr | 3.32 | whole body | mortality | INC | N/R | 30% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Cyprinodon variegatus | 19734 | L | Sheepshead minnow | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 0.52 µg/L | continuous | 96 hr | 3.8 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | no effect on mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Cyprinodon variegatus | 19735 | L | Sheepshead minnow | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 2.2 µg/L | continuous | 96 hr | 12.8 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | no effect on mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Cyprinodon variegatus | 19736 | L | Sheepshead minnow | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 6 µg/L | continuous | 96 hr | 34 | whole body | mortality | INC | N/R | 10% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |
Cyprinodon variegatus | 19737 | L | Sheepshead minnow | N/R | W | Dieldrin | 60-57-1 | N | Y | SW | aqueous | 17.6 µg/L | continuous | 96 hr | 62.4 | whole body | mortality | INC | N/R | 65% | 0% | N/R | increase in mortality | Parrish et al. 1974. Dieldrin: effects on several estuarine o.... Proc 27th SEAFWA 27:427-434. |