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 Pharm. Personal Care Products
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 | 14430 | L | Rainbow Trout | adult | N/I | 17alpha-Ethinylestradiol | 57-63-6 | N | N/I | N/I | aqueous | 125 ng/L | N/I | N/I | 0.08 | plasma | indice of condition | N/I | N/I | N/I | N/I | ED 233 | Hepatosomatic Index | Skillman et al. 2006. Dynamics of 17α‐Ethynylestradiol exposur.... Environ Toxicol Chem 25:2997-3005. |
Oncorhynchus mykiss | 14431 | L | Rainbow Trout | adult | N/I | 17alpha-Ethinylestradiol | 57-63-6 | N | N/I | N/I | aqueous | 125 ng/L | N/I | N/I | 0.08 | liver | physiological | N/I | N/I | N/I | N/I | IP 600 | VTG induction | Skillman et al. 2006. Dynamics of 17α‐Ethynylestradiol exposur.... Environ Toxicol Chem 25:2997-3005. |
Oncorhynchus mykiss | 14432 | L | Rainbow Trout | adult | N/I | 17alpha-Ethinylestradiol | 57-63-6 | N | N/I | N/I | aqueous | 125 ng/L | N/I | N/I | 0.08 | liver | physiological | N/I | N/I | N/I | N/I | IP 600 | VTG induction | Skillman et al. 2006. Dynamics of 17α‐Ethynylestradiol exposur.... Environ Toxicol Chem 25:2997-3005. |
Salmo trutta | 4333 | L | Sea Trout, Brown Trout | juvenile | C | 3,5-Dichlorocatechol | 13673-92-2 | N | Y | FW | aqueous | 2.9 mg/L | 1x | 24 hr | 6.4 | whole body | mortality | INC | N/R | 50% | N/R | LBR 50 | lethal body residue | Hattula et al. 1981. Acute toxicity of some chlorinated pheno.... B Environ Contam Tox 26:295-298. |
Salmo trutta | 4334 | L | Sea Trout, Brown Trout | juvenile | C | 4,5-Dichlorocatechol | 3428-24-8 | N | Y | FW | aqueous | 2.3 mg/L | 1x | 24 hr | 9.7 | whole body | mortality | INC | N/R | 50% | N/R | LBR 50 | lethal body residue | Hattula et al. 1981. Acute toxicity of some chlorinated pheno.... B Environ Contam Tox 26:295-298. |
Oncorhynchus mykiss | 4429 | L | Rainbow Trout | juvenile | C | 4-Hydroxybenzoic acid | 99-96-7 | N | Y | FW | aqueous | N/I | continuous | 4 d | 139 | 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 | 4447 | L | Rainbow Trout | immature | N/I | 4-Hydroxybenzoic acid | 99-96-7 | N | Y | FW | injection | N/I | N/I | 4 | 139 | 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 | 8245 | L | Rainbow Trout | adult | N/I | Diclofenac | 15307-86-5 | N | N/I | N/I | aqueous | 1 µg/L | N/I | N/I | 2.8 | liver | physiological | N/I | N/I | N/I | N/I | NOEC | Renal;pillar cells;respiratory cell necrosis | Schwaiger et al. 2004. Toxic effects of the non-steroidal anti-.... Aquat Toxicol 68:141-150. |
Oncorhynchus mykiss | 8246 | L | Rainbow Trout | adult | N/I | Diclofenac | 15307-86-5 | N | N/I | N/I | aqueous | 5 µg/L | N/I | N/I | 1.4 | kidney | physiological | N/I | N/I | N/I | N/I | LOEC | Renal;pillar cells;respiratory cell necrosis | Schwaiger et al. 2004. Toxic effects of the non-steroidal anti-.... Aquat Toxicol 68:141-150. |
Oncorhynchus mykiss | 8247 | L | Rainbow Trout | adult | N/I | Diclofenac | 15307-86-5 | N | N/I | N/I | aqueous | 5 µg/L | N/I | N/I | 1.05 | gill | physiological | N/I | N/I | N/I | N/I | LOEC | Renal;pillar cells;respiratory cell necrosis | Schwaiger et al. 2004. Toxic effects of the non-steroidal anti-.... Aquat Toxicol 68:141-150. |
Oncorhynchus mykiss | 4401 | L | Rainbow Trout | juvenile | C | p-Hydroxyanisole | 150-76-5 | N | Y | FW | aqueous | N/I | continuous | 4 d | 357 | 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 | 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... |
Oncorhynchus mykiss | 4439 | L | Rainbow Trout | immature | N/I | p-Hydroxyanisole | 150-76-5 | N | Y | FW | injection | N/I | N/I | 4 | 357 | 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. |