| 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: de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863..
| 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 | 
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Poecilia reticulata | 7864 | L | guppy | N/I | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 2.2 µmol/L | N/I | N/I | 0.7 | whole body | mortality | N/I | N/I | N/I | N/I | LOEC | N/I | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. | 
| Poecilia reticulata | 95 | L | guppy | yearling | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 854.4 µg/L | N/I | 48 hr | 161.6 | whole body | mortality | N/I | N/I | N/I | N/I | LD 100 | tissue residue is the average | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. | 
| Poecilia reticulata | 96 | L | guppy | yearling | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 854.4 µg/L | N/I | 48 hr | 3463.6 | whole body | mortality | N/I | N/I | N/I | N/I | LD 100 | tissue residue is the average | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. | 
| Poecilia reticulata | 97 | L | guppy | yearling | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 854.4 µg/L | N/I | 48 hr | 415.6 | whole body | mortality | N/I | N/I | N/I | N/I | LD 55 | tissue residue is the average | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. | 
| Poecilia reticulata | 98 | L | guppy | yearling | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 854.4 µg/L | N/I | 48 hr | 629.7 | whole body | mortality | N/I | N/I | N/I | N/I | LD 55 | tissue residue is the average | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. | 
| Poecilia reticulata | 99 | L | guppy | yearling | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 461.8 µg/L | N/I | 14d | 161.6 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | Hypoactive, lack of feeding, loss of equilibrium | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. | 
| Poecilia reticulata | 100 | L | guppy | yearling | N/I | 2,3,4,5-Tetrachlorocebenamine | 634-83-3 | N | N/I | N/I | aqueous | 461.8 µg/L | N/I | 14d | 3463.6 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | Hypoactive, lack of feeding, loss of equilibrium | de Wolf et al. 1992. Bioconcentration and lethal body burden .... Chemosphere 25:853-863. |