| 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: Goodman et al. 1977. Effects of heptachlor and toxaphene on l....
| 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 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Cyprinodon variegatus | 5864 | L | Sheepshead minnow | embryo | N/I | Chlordane | 57-74-9 | Y | N/I | SW | aqueous | N/I | N/I | 28 | 3.6 | whole body | behavior | DEC | N/I | Yes | N/I | LOEC | swimming activity | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5865 | L | Sheepshead minnow | embryo | N/I | Chlordane | 57-74-9 | Y | N/I | SW | aqueous | N/I | N/I | 28 | 5.6 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | Hyperkinetic activity followed by temp. paralysis | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5870 | L | Sheepshead minnow | embryo | N/I | Chlordane | 57-74-9 | Y | N/I | SW | aqueous | N/I | N/I | 28 | 11.7 | whole body | mortality | N/I | N/I | 39% | N/I | LOEC | Exposure to technical grade heptachlor | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5875 | L | Sheepshead minnow | embryo | N/I | Chlordane | 57-74-9 | Y | N/I | SW | aqueous | N/I | N/I | 28 | 5.6 | whole body | cellular | NEF | N/I | N/I | N/I | NOEC | liver, kidney, pancreas, digestive tract | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5878 | L | Sheepshead minnow | embryo | N/I | Chlordane | 57-74-9 | Y | N/I | SW | aqueous | N/I | N/I | 28 | 11.7 | whole body | growth | NEF | N/I | N/I | N/I | NOEC | growth (length) | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5882 | L | Sheepshead minnow | embryo | N/I | Chlordane | 57-74-9 | Y | N/I | SW | aqueous | N/I | N/I | 28 | 5.6 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | Exposure to technical grade heptachlor | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5883 | L | Sheepshead minnow | embryo | N/I | Heptachlor | 76-44-8 | Y | N/I | SW | aqueous | 2.04 µg/L | N/I | 28 | 4.8 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | Exposure to technical grade heptachlor | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5879 | L | Sheepshead minnow | embryo | N/I | Heptachlor | 76-44-8 | Y | N/I | SW | aqueous | 2.2 µg/L | N/I | 28 | 10.4 | whole body | growth | NEF | N/I | N/I | N/I | NOEC | growth (length) | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5876 | L | Sheepshead minnow | embryo | N/I | Heptachlor | 76-44-8 | Y | N/I | SW | aqueous | 2.04 µg/L | N/I | 28 | 4.8 | whole body | cellular | NEF | N/I | N/I | N/I | NOEC | liver, kidney, pancreas, digestive tract | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5871 | L | Sheepshead minnow | embryo | N/I | Heptachlor | 76-44-8 | Y | N/I | SW | aqueous | 2.24 µg/L | N/I | 28 | 10.4 | whole body | mortality | N/I | N/I | 39% | N/I | LOEC | Exposure to technical grade heptachlor | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5866 | L | Sheepshead minnow | embryo | N/I | Heptachlor | 76-44-8 | Y | N/I | SW | aqueous | 1.22 µg/L | N/I | 28 | 4.5 | whole body | behavior | DEC | N/I | Yes | N/I | LOEC | swimming activity | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5867 | L | Sheepshead minnow | embryo | N/I | Heptachlor | 76-44-8 | Y | N/I | SW | aqueous | 2.04 µg/L | N/I | 28 | 4.8 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | Hyperkinetic activity followed by temp. paralysis | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5877 | L | Sheepshead minnow | embryo | N/I | Heptachlor epoxide | 1024-57-3 | Y | N/I | SW | aqueous | 2.2 µg/L | N/I | 28 | 8 | whole body | growth | NEF | N/I | N/I | N/I | NOEC | growth (length) | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5862 | L | Sheepshead minnow | embryo | N/I | Heptachlor epoxide | 1024-57-3 | Y | N/I | SW | aqueous | 1.22 µg/L | N/I | 28 | 3.6 | whole body | behavior | DEC | N/I | Yes | N/I | LOEC | swimming activity | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5863 | L | Sheepshead minnow | embryo | N/I | Heptachlor epoxide | 1024-57-3 | Y | N/I | SW | aqueous | 2.04 µg/L | N/I | 28 | 4.2 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | Hyperkinetic activity followed by temp. paralysis | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5869 | L | Sheepshead minnow | embryo | N/I | Heptachlor epoxide | 1024-57-3 | Y | N/I | SW | aqueous | 2.24 µg/L | N/I | 28 | 8 | whole body | mortality | N/I | N/I | 39% | N/I | LOEC | Exposure to technical grade heptachlor | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5874 | L | Sheepshead minnow | embryo | N/I | Heptachlor epoxide | 1024-57-3 | Y | N/I | SW | aqueous | 2.04 µg/L | N/I | 28 | 4.2 | whole body | cellular | NEF | N/I | N/I | N/I | NOEC | liver, kidney, pancreas, digestive tract | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5881 | L | Sheepshead minnow | embryo | N/I | Heptachlor epoxide | 1024-57-3 | Y | N/I | SW | aqueous | 2.04 µg/L | N/I | 28 | 4.2 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | Exposure to technical grade heptachlor | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5884 | L | Sheepshead minnow | embryo | N/I | Toxaphene | 8001-35-2 | N | N/I | SW | aqueous | 1.1 µg/L | N/I | 28 | 10 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5880 | L | Sheepshead minnow | embryo | N/I | Toxaphene | 8001-35-2 | N | N/I | SW | aqueous | 2.5 µg/L | N/I | 28 | 36 | whole body | growth | NEF | N/I | N/I | N/I | NOEC | growth (length) | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5868 | L | Sheepshead minnow | embryo | N/I | Toxaphene | 8001-35-2 | N | N/I | SW | aqueous | 1.1 µg/L | N/I | 28 | 10 | whole body | behavior | DEC | N/I | Yes | N/I | LOEC | hyperactive followed by temporary paralysis | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5872 | L | Sheepshead minnow | embryo | N/I | Toxaphene | 8001-35-2 | N | N/I | SW | aqueous | 2.5 µg/L | N/I | 28 | 36 | whole body | mortality | N/I | N/I | 90% | N/I | LOEC | N/I | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |
| Cyprinodon variegatus | 5873 | L | Sheepshead minnow | embryo | N/I | Toxaphene | 8001-35-2 | N | N/I | SW | aqueous | 0.62 µg/L | N/I | 28 | 3.8 | whole body | behavior | NEF | N/I | N/I | N/I | NOEC | behavior (swimming) | Goodman et al. 1977. Effects of heptachlor and toxaphene on l... |