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; non-salmonid) and Mercury
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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Oryzias latipes | 21802 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 10 µg/L | daily | 16 d | 16 | whole body | reproduction | NEF | N | 58.3% | 46.7% | N/R | hatching % for exposure group not significantly different from the control | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21803 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 15 µg/L | daily | 16 d | 29 | whole body | reproduction | DEC | Y | 20.8% | 46.7% | N/R | hatching % significantly decreased for exposure group as compared to the control | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21804 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 20 µg/L | daily | 16 d | 54 | whole body | reproduction | DEC | Y | 0% | 46.7% | N/R | hatching % significantly decreased (no hatch at all) for exposure group as compared to the control | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21805 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 30 µg/L | daily | 16 d | 56 | whole body | reproduction | DEC | Y | 0% | 46.7% | N/R | hatching % significantly decreased (no hatch at all) for exposure group as compared to the control | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21806 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 10 µg/L | daily | 16 d | 16 | whole body | histopathology | NEF | N/R | 0% | no abromality | N/R | no abnormality in the 10 ppb exposure group or control group | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21807 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 15 µg/L | daily | 16 d | 29 | whole body | histopathology | INC | N/R | 79% | no abromality | N/R | 79% of exposure group eggs had abnormalities | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21808 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 20 µg/L | daily | 16 d | 54 | whole body | histopathology | INC | N/R | 100% | no abromality | N/R | 100% of exposure group eggs had abnormalities | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 21809 | L | Japanese rice fish | egg | C | Mercuric chloride | 7487-94-7 | N | Y | FW | aqueous | 30 µg/L | daily | 16 d | 56 | whole body | histopathology | INC | N/R | 100% | no abromality | N/R | 100% of exposure group eggs had abnormalities | Heisinger and Green. 1975. Mercuric chloride uptake by eggs of the .... B Environ Contam Tox 4:665-673. |
Oryzias latipes | 17154 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.01 µg/L | N/I | 210 d | 0.055 | whole body | behavior | NEF | N/I | None | normal | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17155 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.1 µg/L | N/I | 210 d | 14.23 | whole body | behavior | NEF | N/I | None | normal | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17156 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 1 µg/L | N/I | 210 d | 2.34 | whole body | behavior | NEF | N/I | None | normal | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17160 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.01 µg/L | N/I | 210 d | 0.055 | whole body | mortality | INC | N/I | 15% | 12.5% | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17161 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.1 µg/L | N/I | 210 d | 14.23 | whole body | mortality | INC | N/I | 25% | 12.5% | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17162 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 1 µg/L | N/I | 210 d | 2.34 | whole body | mortality | INC | N/I | 36.25% | 12.5% | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17166 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.01 µg/L | N/I | 210 d | 0.055 | whole body | development | N/I | N/I | 1 fish | 0 fish | N/I | vertebral abnormality; chemistry measured at 180 d; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17167 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.1 µg/L | N/I | 210 d | 14.23 | whole body | development | N/I | N/I | 2 fish | 0 fish | N/I | vertebral abnormality; chemistry measured at 180 d; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17168 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 1 µg/L | N/I | 210 d | 2.34 | whole body | development | N/I | N/I | 3 fish | 0 fish | N/I | vertebral abnormality; chemistry measured at 180 d; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17172 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.01 µg/L | N/I | 210 d | 0.055 | whole body | histopathology | N/I | N/I | N/R | normal | N/I | chemistry measured at 180 d; result 4250 ng/g; certified value 4470 ng/g; effect on liver | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17173 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.1 µg/L | N/I | 210 d | 14.23 | whole body | histopathology | N/I | N/I | N/R | normal | N/I | chemistry measured at 180 d; result 4250 ng/g; certified value 4470 ng/g; effect on liver | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17174 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 1 µg/L | N/I | 210 d | 2.34 | whole body | histopathology | N/I | N/I | N/R | normal | N/I | chemistry measured at 180 d; result 4250 ng/g; certified value 4470 ng/g; effect on liver | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17178 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.01 µg/L | N/I | 210 d | 0.055 | whole body | histopathology | N/I | N/I | N/R | gill, normal | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17179 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 0.1 µg/L | N/I | 210 d | 14.23 | whole body | histopathology | N/I | N/I | N/R | gill, normal | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |
Oryzias latipes | 17180 | L | Japanese rice fish | juvenile | C | Methylmercury Chloride | 115-09-3 | N | N/I | N/I | aqueous | 1 µg/L | N/I | 210 d | 2.34 | whole body | histopathology | N/I | N/I | N/R | gill, normal | N/I | accumulation data interpolated from graph; chemistry measured on day 180; verified Hg analysis; result 4250 ng/g; certified value 4470 ng/g | Liao et al. 2007. Interaction of methylmercury and seleniu... |