| 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). |
You are viewing Chordata: Vert (fishes; salmonid) and Benzene derivatives
| 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 | 4410 | L | Rainbow Trout | juvenile | C | 1,2,3,4-Tetrachlorobenzene | 634-66-2 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1100 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| 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 | 4411 | L | Rainbow Trout | juvenile | C | 1,2,3,5-Tetrachlorobenzene | 634-90-2 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1660 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| 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 | 4420 | L | Rainbow Trout | juvenile | C | 1,2,3-Trichlorobenzene | 87-61-6 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1620 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 4445 | L | Rainbow Trout | immature | N/I | 1,2,3-Trichlorobenzene | 87-61-6 | N | Y | FW | injection | N/I | N/I | 4 | 1620 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
| 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 | 5482 | L | Rainbow Trout | immature | N/I | 1,2,4,5-Tetrachlorobenzene | 95-94-3 | N | N/I | N/I | aqueous | 125 µg/L | N/I | 3 | 220 | whole body | mortality | INC | N/I | Yes | N/I | LOEC | mortality | Brauner et al. 1994. The effect of exposure to 1, 2, 4, 5‐tet.... Environ Toxicol Chem 13:1813-1820. |
| Oncorhynchus mykiss | 5483 | L | Rainbow Trout | immature | N/I | 1,2,4,5-Tetrachlorobenzene | 95-94-3 | N | N/I | N/I | aqueous | 125 µg/L | N/I | 3 | 220 | whole body | physiological | N/I | N/I | Yes | N/I | LOEC | maintain equilib, physical distress, dark color | Brauner et al. 1994. The effect of exposure to 1, 2, 4, 5‐tet.... Environ Toxicol Chem 13:1813-1820. |
| Oncorhynchus mykiss | 5484 | L | Rainbow Trout | immature | N/I | 1,2,4,5-Tetrachlorobenzene | 95-94-3 | N | N/I | N/I | aqueous | 250 µg/L | N/I | 3 | 467 | whole body | physiological | NEF | N/I | N/I | N/I | NOEC | critical swimming velocity. | Brauner et al. 1994. The effect of exposure to 1, 2, 4, 5‐tet.... Environ Toxicol Chem 13:1813-1820. |
| Oncorhynchus mykiss | 4395 | L | Rainbow Trout | juvenile | C | 1,2,4-Trichlorobenzene | 120-82-1 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1780 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| 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 | 4436 | L | Rainbow Trout | immature | N/I | 1,2,4-Trichlorobenzene | 120-82-1 | N | Y | FW | injection | N/I | N/I | 4 | 1780 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
| 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 | 20817 | L | Rainbow Trout | juvenile | C | 1,2-Dibromobenzene | 583-53-9 | N | Y | FW | aqueous | 111 µmol/L | 1x | 0.8-1.7 hr | 425 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20818 | L | Rainbow Trout | juvenile | C | 1,2-Dibromobenzene | 583-53-9 | N | Y | FW | aqueous | 57 µmol/L | 1x | 1.7-3.6 hr | 448 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20822 | L | Rainbow Trout | juvenile | C | 1,2-Dibromobenzene | 583-53-9 | N | Y | FW | aqueous | 107 µmol/L | 1x | 0.4-0.6 hr | 134 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20823 | L | Rainbow Trout | juvenile | C | 1,2-Dibromobenzene | 583-53-9 | N | Y | FW | aqueous | 74.5 µmol/L | 1x | 1.3-5.5 hr | 566 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20820 | L | Rainbow Trout | juvenile | C | 1,2-Dichlorobenzene | 95-50-1 | N | Y | FW | aqueous | 40.9 µmol/L | 1x | 3-4.7 hr | 138 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20821 | L | Rainbow Trout | juvenile | C | 1,2-Dichlorobenzene | 95-50-1 | N | Y | FW | aqueous | 16.2 µmol/L | 1x | 3.5-8.2 hr | 147 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| 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 | 4426 | L | Rainbow Trout | juvenile | C | 1,2-Dichlorobenzene | 95-50-1 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1100 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 20807 | L | Rainbow Trout | juvenile | C | 1,2-Difluorobenzene | 367-11-3 | N | Y | FW | aqueous | 189 µmol/L | 1x | 7-21 hr | 112 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20812 | L | Rainbow Trout | juvenile | C | 1,2-Difluorobenzene | 367-11-3 | N | Y | FW | aqueous | 132 µmol/L | 1x | 7-21 hr | 74 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 4390 | L | Rainbow Trout | juvenile | C | 1,3,5-Trichlorobenzene | 108-70-3 | N | Y | FW | aqueous | N/I | continuous | 4 d | 5540 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 4433 | L | Rainbow Trout | immature | N/I | 1,3,5-Trichlorobenzene | 108-70-3 | N | Y | FW | injection | N/I | N/I | 4 | 5540 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
| 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 | 4404 | L | Rainbow Trout | juvenile | C | 1,3-Dichlorobenzene | 541-73-1 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1440 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 20819 | L | Rainbow Trout | juvenile | C | 1,4-Dibromobenzene | 106-37-6 | N | Y | FW | aqueous | 54.4 µmol/L | 1x | 0.7-1.4 hr | 205 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20824 | L | Rainbow Trout | juvenile | C | 1,4-Dibromobenzene | 106-37-6 | N | Y | FW | aqueous | 20.2 µmol/L | 1x | 2.9-4.8 hr | 184 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 344 | L | Rainbow Trout | egg | N/I | 1,4-Dichlorobenzene | 106-46-7 | N | N/I | N/I | aqueous | 16.4 µg/L | N/I | 2(1) | 52 | egg | development | NEF | N/I | N/I | N/I | NOEC | No abnormalities; no teratogenic effects | Galassi et al. 1982. Uptake and release of p-dichlorobenzene .... Ecotox Environ Safe 6:439-447. |
| Oncorhynchus mykiss | 345 | L | Rainbow Trout | egg | N/I | 1,4-Dichlorobenzene | 106-46-7 | N | N/I | N/I | aqueous | 79.5 µg/L | N/I | 2(1) | 200 | egg | development | NEF | N/I | N/I | N/I | NOEC | No abnormalities; no teratogenic effects | Galassi et al. 1982. Uptake and release of p-dichlorobenzene .... Ecotox Environ Safe 6:439-447. |
| Oncorhynchus mykiss | 346 | L | Rainbow Trout | egg | N/I | 1,4-Dichlorobenzene | 106-46-7 | N | N/I | N/I | aqueous | 16.4 µg/L | N/I | 2(1) | 303 | egg | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Galassi et al. 1982. Uptake and release of p-dichlorobenzene .... Ecotox Environ Safe 6:439-447. |
| Oncorhynchus mykiss | 347 | L | Rainbow Trout | egg | N/I | 1,4-Dichlorobenzene | 106-46-7 | N | N/I | N/I | aqueous | 79.5 µg/L | N/I | 2(1) | 1355 | egg | survival | N/I | N/I | N/I | N/I | NOEC | N/I | Galassi et al. 1982. Uptake and release of p-dichlorobenzene .... Ecotox Environ Safe 6:439-447. |
| Oncorhynchus mykiss | 4386 | L | Rainbow Trout | juvenile | C | 1,4-Dichlorobenzene | 106-46-7 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1490 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 20815 | L | Rainbow Trout | juvenile | C | 1,4-Dichlorobenzene | 106-46-7 | N | Y | FW | aqueous | 25.5 µmol/L | 1x | 0.8-1.2 hr | 47 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20816 | L | Rainbow Trout | juvenile | C | 1,4-Dichlorobenzene | 106-46-7 | N | Y | FW | aqueous | 6.35 µmol/L | 1x | 2.3-20 hr | 69 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| 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 | 20813 | L | Rainbow Trout | juvenile | C | 1,4-Difluorobenzene | 540-36-3 | N | Y | FW | aqueous | 136 µmol/L | 1x | 0.6-1.6 hr | 43 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 20814 | L | Rainbow Trout | juvenile | C | 1,4-Difluorobenzene | 540-36-3 | N | Y | FW | aqueous | 64 µmol/L | 1x | 3.3-4 hr | 33 | whole body | mortality | INC | N/R | 100% | N/R | N/R | 100% mortality | van Wezel et al. 1995. Use of lethal body burdens to indicate s.... Chemosphere 31:3201-3209. |
| Oncorhynchus mykiss | 4398 | L | Rainbow Trout | juvenile | C | 1,4-Dihydroxybenzene | 123-31-9 | N | Y | FW | aqueous | N/I | continuous | 4 d | 18.6 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 4437 | L | Rainbow Trout | immature | N/I | 1,4-Dihydroxybenzene | 123-31-9 | N | Y | FW | injection | N/I | N/I | 4 | 24.2 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
| Oncorhynchus mykiss | 4442 | L | Rainbow Trout | immature | N/I | Benzene | 71-43-2 | N | Y | FW | injection | N/I | N/I | 4 | 2020 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
| 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 | 4417 | L | Rainbow Trout | juvenile | C | Benzene | 71-43-2 | N | Y | FW | aqueous | N/I | continuous | 4 d | 2020 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 5642 | L | Rainbow Trout | immature | C | Chlorobenzene | 108-90-7 | N | Y | FW | injection | 9.8 mmol/kg | N/I | 4 | 1100 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | Hyperactive, erratic swim, loss of equilib | Dalich et al. 1982. Acute and chronic toxicity studies with .... Aquat Toxicol 2:127-142. |
| Oncorhynchus mykiss | 5643 | L | Rainbow Trout | immature | C | Chlorobenzene | 108-90-7 | N | Y | FW | injection | 9.8 mmol/kg | N/I | 4 | 1100 | whole body | biochemistry | INC | N/I | 70 | N/I | LOEC | in plasma alananine aminotransferase activity | Dalich et al. 1982. Acute and chronic toxicity studies with .... Aquat Toxicol 2:127-142. |
| Oncorhynchus mykiss | 4392 | L | Rainbow Trout | juvenile | C | Chlorobenzene | 108-90-7 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1090 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 1993 | L | Rainbow Trout | N/I | N/I | Chlorobenzene | 108-90-7 | N | N/I | N/I | aqueous | 2350 ng/L | N/I | 75d | 3 | whole body | physiological | N/I | N/I | N/I | N/I | LOEC | Hemoglobin Content | Niimi and Jinde. 1984. Differential blood cell ratios of rainbo.... Arch Environ Con Tox 13:303-311. |
| Oncorhynchus mykiss | 1994 | L | Rainbow Trout | N/I | N/I | Chlorobenzene | 108-90-7 | N | N/I | N/I | aqueous | 2350 ng/L | N/I | 75d | 3 | whole body | physiological | N/I | N/I | N/I | N/I | NOEC | Red/White Blood Cell ratio | Niimi and Jinde. 1984. Differential blood cell ratios of rainbo.... Arch Environ Con Tox 13:303-311. |
| Oncorhynchus mykiss | 1997 | L | Rainbow Trout | N/I | N/I | Chlorobenzene | 108-90-7 | N | N/I | N/I | aqueous | 2350 ng/L | N/I | 75d | 34.3 | whole body | survival | N/I | N/I | N/I | N/I | NOEC | Mixed Chlorobenzenes | Niimi and Jinde. 1984. Differential blood cell ratios of rainbo.... Arch Environ Con Tox 13:303-311. |
| 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 | 4434 | L | Rainbow Trout | immature | N/I | Chlorobenzene | 108-90-7 | N | Y | FW | injection | N/I | N/I | 4 | 1090 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | internal dose used for tissue conc | Hodson et al. 1984. Measurement of median lethal dose as a r.... Environ Toxicol Chem 3:243-254. |
| Oncorhynchus mykiss | 4402 | L | Rainbow Trout | juvenile | C | Hexafluorobenzene | 392-56-3 | N | Y | FW | aqueous | N/I | continuous | 4 d | 3550 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| Oncorhynchus mykiss | 4408 | L | Rainbow Trout | juvenile | C | Pentachlorobenzene | 608-93-5 | N | Y | FW | aqueous | N/I | continuous | 4 d | 1450 | whole body | mortality | INC | N/I | N/I | N/I | LD 50 | median lethal dose | Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454. |
| 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... |