| 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: Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno....
| 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 | 21552 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.09 µg/L | daily | 28 d | 2.2 | whole body | mortality | NEF | N/R | 13% | 7% | N/R | mortality reported as negligible | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21553 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.14 µg/L | daily | 28 d | 9.5 | whole body | mortality | NEF | N/R | 7% | 7% | N/R | mortality reported as negligible | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21554 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.39 µg/L | daily | 28 d | 25 | whole body | mortality | NEF | N/R | 10% | 7% | N/R | mortality reported as negligible | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21555 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 1.1 µg/L | daily | 28 d | 49 | whole body | mortality | NEF | N/R | 3% | 7% | N/R | mortality reported as negligible | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21556 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 5.6 µg/L | daily | 28 d | N/R | mortality | INC | N/R | 95% | 7% | N/R | mortality increase substantially; no tissue conc reported | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... | |
| Cyprinodon variegatus | 21557 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.09 µg/L | daily | 28 d | 0.88 | egg | survival | NEF | N | 88% | 93% | N/R | no effect on survival of embryo to hatch in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21558 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.14 µg/L | daily | 28 d | 5.1 | egg | survival | NEF | N | 80% | 93% | N/R | no effect on survival of embryo to hatch in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21559 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.39 µg/L | daily | 28 d | 11 | egg | survival | NEF | N | 98% | 93% | N/R | no effect on survival of embryo to hatch in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21560 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 1.1 µg/L | daily | 28 d | 27 | egg | survival | NEF | N | 85% | 93% | N/R | no effect on survival of embryo to hatch in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21561 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 5.6 µg/L | daily | 28 d | 170 | egg | survival | DEC | Y | 72% | 93% | N/R | decreased survival of embryo to hatch in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21562 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.09 µg/L | daily | 28 d | 0.88 | egg | survival | NEF | N | 97% | 95% | N/R | no effect on week 1 survival of fry in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21563 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.14 µg/L | daily | 28 d | 5.1 | egg | survival | DEC | Y | 77% | 95% | N/R | decrease in week 1 survival of fry in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21564 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.39 µg/L | daily | 28 d | 11 | egg | survival | DEC | Y | 26% | 95% | N/R | decrease in week 1 survival of fry in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21565 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 1.1 µg/L | daily | 28 d | 27 | egg | survival | DEC | Y | 23% | 95% | N/R | decrease in week 1 survival of fry in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21566 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 5.6 µg/L | daily | 28 d | 170 | egg | survival | DEC | Y | 0% | 95% | N/R | decrease in week 1 survival of fry in exposure group as compared to control | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21567 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.09 µg/L | daily | 28 d | 2.2 | whole body | reproduction | NEF | N/R | 121 eggs | 97 eggs | N/R | no alteration of fecundity for surviving fish | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21568 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.14 µg/L | daily | 28 d | 9.5 | whole body | reproduction | NEF | N/R | 110 eggs | 97 eggs | N/R | no alteration of fecundity for surviving fish | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21569 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 0.39 µg/L | daily | 28 d | 25 | whole body | reproduction | NEF | N/R | 127 eggs | 97 eggs | N/R | no alteration of fecundity for surviving fish | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21570 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 1.1 µg/L | daily | 28 d | 49 | whole body | reproduction | NEF | N/R | 152 eggs | 97 eggs | N/R | no alteration of fecundity for surviving fish | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |
| Cyprinodon variegatus | 21571 | L | Sheepshead minnow | adult | C | Aroclor 1254 | 11097-69-1 | N | Y | SW | aqueous | 5.6 µg/L | daily | 28 d | N/R | reproduction | NEF | N/R | 138 eggs | 97 eggs | N/R | no alteration of fecundity for surviving fish | Hansen et al. 1973. Aroclor 1254 in eggs of sheepshead minno... |