| 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: Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben....
| 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 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Oncorhynchus mykiss | 4589 | L | Rainbow Trout | N/I | N/I | 1,2,3,4-Tetrachlorobenzene | 634-66-2 | N | Y | FW | injection | N/I | N/I | 96 hr | 1060 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4590 | L | Rainbow Trout | N/I | N/I | 1,2,3,5-Tetrachlorobenzene | 634-90-2 | N | Y | FW | injection | N/I | N/I | 96 hr | 1680 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4592 | L | Rainbow Trout | N/I | N/I | 1,2,3-Trichlorobenzene | 87-61-6 | N | Y | FW | injection | N/I | N/I | 96 hr | 1620 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4595 | L | Rainbow Trout | N/I | N/I | 1,2,4,5-Tetrachlorobenzene | 95-94-3 | N | Y | FW | injection | N/I | N/I | 96 hr | 5060 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4601 | L | Rainbow Trout | N/I | N/I | 1,2,4-Trichlorobenzene | 120-82-1 | N | Y | FW | injection | N/I | N/I | 96 hr | 706 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4584 | L | Rainbow Trout | N/I | N/I | 1,2,4-Trichlorobenzene | 120-82-1 | N | Y | FW | injection | N/I | N/I | 96 hr | 1770 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4594 | L | Rainbow Trout | N/I | N/I | 1,2-Dichlorobenzene | 95-50-1 | N | Y | FW | injection | N/I | N/I | 96 hr | 1090 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4580 | L | Rainbow Trout | N/I | N/I | 1,3,5-Trichlorobenzene | 108-70-3 | N | Y | FW | injection | N/I | N/I | 96 hr | 5480 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4587 | L | Rainbow Trout | N/I | N/I | 1,3-Dichlorobenzene | 541-73-1 | N | Y | FW | injection | N/I | N/I | 96 hr | 1470 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4578 | L | Rainbow Trout | N/I | N/I | 1,4-Dichlorobenzene | 106-46-7 | N | Y | FW | injection | N/I | N/I | 96 hr | 1500 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4597 | L | Rainbow Trout | N/I | N/I | 1,4-Dichlorobenzene | 106-46-7 | N | Y | FW | injection | N/I | N/I | 96 hr | 387 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4585 | L | Rainbow Trout | N/I | N/I | 2,4-Dichlorophenol | 120-83-2 | N | Y | FW | injection | N/I | N/I | 96 hr | 649 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4593 | L | Rainbow Trout | N/I | N/I | 2,6-Dichlorophenol | 87-65-0 | N | Y | FW | injection | N/I | N/I | 96 hr | 1450 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4579 | L | Rainbow Trout | N/I | N/I | 4-Chlorophenol | 106-48-9 | N | Y | FW | injection | N/I | N/I | 96 hr | 435 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4598 | L | Rainbow Trout | N/I | N/I | 4-Chlorophenol | 106-48-9 | N | Y | FW | injection | N/I | N/I | 96 hr | 5.6 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4596 | L | Rainbow Trout | N/I | N/I | 4-Methylphenol | 106-44-5 | N | Y | FW | injection | N/I | N/I | 96 hr | 16.3 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4577 | L | Rainbow Trout | N/I | N/I | 4-Methylphenol | 106-44-5 | N | Y | FW | injection | N/I | N/I | 96 hr | 76.5 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4576 | L | Rainbow Trout | N/I | N/I | 4-Nitrophenol | 100-02-7 | N | Y | FW | injection | N/I | N/I | 96 hr | 75 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4591 | L | Rainbow Trout | N/I | N/I | Benzene | 71-43-2 | N | Y | FW | injection | N/I | N/I | 96 hr | 1950 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4602 | L | Rainbow Trout | N/I | N/I | Benzene | 71-43-2 | N | Y | FW | injection | N/I | N/I | 96 hr | 409 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4599 | L | Rainbow Trout | N/I | N/I | Chlorobenzene | 108-90-7 | N | Y | FW | injection | N/I | N/I | 96 hr | 159 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4581 | L | Rainbow Trout | N/I | N/I | Chlorobenzene | 108-90-7 | N | Y | FW | injection | N/I | N/I | 96 hr | 1070 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4583 | L | Rainbow Trout | N/I | N/I | Hexachlorobenzene | 118-74-1 | N | Y | FW | injection | N/I | N/I | 96 hr | 4950 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4588 | L | Rainbow Trout | N/I | N/I | Pentachlorobenzene | 608-93-5 | N | Y | FW | injection | N/I | N/I | 96 hr | 1440 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4582 | L | Rainbow Trout | N/I | N/I | Phenol | 108-95-2 | N | Y | FW | injection | N/I | N/I | 96 hr | 420 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4600 | L | Rainbow Trout | N/I | N/I | Phenol | 108-95-2 | N | Y | FW | injection | N/I | N/I | 96 rr | 16 | whole body | biochemistry | N/I | N/I | N/I | N/I | LOEC | threshold; induction serum sorbitol dehydrogenase | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |
| Oncorhynchus mykiss | 4586 | L | Rainbow Trout | N/I | N/I | p-Hydroxyanisole | 150-76-5 | N | Y | FW | injection | N/I | N/I | 96 hr | 358 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Estimated LD50. Residue is injected dose. | Kaiser et al. 1984. QSAR studies on chlorophenols, chloroben... |