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 Arthropoda: Invert (insects, crustaceans) and Copper
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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Carcinus maenas | 11231 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 40 µmol/g | N/I | N/A | 190.6 | digestive gland | cellular | N/I | N/I | N/I | N/I | NOEC | Midgut Gland - Stress-70 Levels | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11232 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 3 µmol/g | N/I | N/A | 123.9 | digestive gland | cellular | N/I | N/I | N/I | N/I | LOEC | Midgut Gland - MT Concentration | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11233 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 3 µmol/g | N/I | N/A | 123.9 | digestive gland | cellular | N/I | N/I | N/I | N/I | IP 149 | Midgut Gland - MT Concentration | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11234 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 20 µmol/g | N/I | N/A | 133.5 | digestive gland | cellular | N/I | N/I | N/I | N/I | IP 122 | Midgut Gland - MT Concentration | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11235 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 40 µmol/g | N/I | N/A | 190.6 | digestive gland | cellular | N/I | N/I | N/I | N/I | IP 200 | Midgut Gland - MT Concentration | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11236 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 20 µmol/g | N/I | N/A | 133.45 | digestive gland | cellular | N/I | N/I | N/I | N/I | LOEC | Midgut Gland - Copper-bound to MT | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11237 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 20 µmol/g | N/I | N/A | 133.45 | digestive gland | cellular | N/I | N/I | N/I | N/I | IP 258 | Midgut Gland - Copper-bound to MT | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11238 | F | crab, green | adult | W | Copper | 7440-50-8 | Y | N | SW | in situ | 40 µmol/g | N/I | N/A | 190.638 | digestive gland | cellular | N/I | N/I | N/I | N/I | IP 293 | Midgut Gland - Copper-bound to MT | Pedersen et al. 1997. Field application of metallothionein and.... Aquat Toxicol 37:183-200. |
Carcinus maenas | 11589 | L | crab, green | adult | N/I | Copper | 7440-50-8 | N | N/I | SW | aqueous | 3 µg/L | N/I | N/I | 0.029 | gill | biochemistry | N/I | N/I | N/I | N/I | IP 600 | VTG induction | Martin-Diaz et al. 2005. An integrated approach using bioaccumula.... Chemosphere 58:615-626. |
Carcinus maenas | 11590 | L | crab, green | adult | N/I | Copper | 7440-50-8 | N | N/I | SW | aqueous | 3 µg/L | N/I | N/I | 0.008 | gut | biochemistry | N/I | N/I | N/I | N/I | IP 600 | VTG induction | Martin-Diaz et al. 2005. An integrated approach using bioaccumula.... Chemosphere 58:615-626. |
Carcinus maenas | 11591 | L | crab, green | adult | N/I | Copper | 7440-50-8 | N | N/I | SW | aqueous | 3 µg/L | N/I | N/I | 0.011 | muscle | biochemistry | N/I | N/I | N/I | N/I | IP 600 | VTG induction | Martin-Diaz et al. 2005. An integrated approach using bioaccumula.... Chemosphere 58:615-626. |
Callinectes sapidus | 16988 | L | crab, blue | juvenile | N/R | Copper chloride | 7447-39-4 | N | Y | N/I | aqueous | 6.4 N/I | 1x/24hr | 4 d | 22.24 | gill | mortality | INC | N | N/R | N/I | LC 50 | 2 ppt salinity | Martins et al. 2011. Acute toxicity, accumulation and tissue .... Aquat Toxicol 101:88-99. |
Callinectes sapidus | 16989 | L | crab, blue | juvenile | N/R | Copper chloride | 7447-39-4 | N | Y | N/I | aqueous | 63.23 N/I | 1x/24hr | 4 d | 14.616 | gill | mortality | INC | Y | N/R | N/I | LC 50 | 30 ppt salinity, sig different from 2 ppt | Martins et al. 2011. Acute toxicity, accumulation and tissue .... Aquat Toxicol 101:88-99. |
Orconectes rusticus | 22144 | L | crayfish, rusty | adult | W | Copper(II) Sulfate | 7758-98-7 | N | Y | FW | aqueous | 0.1 mg/L | 1x | 48 hr | 26 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | all crayfish survived the 48 h exposure period; control had 24 mg/kg whole body copper | Evans. 1980. Copper accumulation in the crayfish (Orc.... B Environ Contam Tox 24:916-920. |
Orconectes rusticus | 22145 | L | crayfish, rusty | adult | W | Copper(II) Sulfate | 7758-98-7 | N | Y | FW | aqueous | 0.5 mg/L | 1x | 48 hr | 34 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | all crayfish survived the 48 h exposure period; control had 24 mg/kg whole body copper | Evans. 1980. Copper accumulation in the crayfish (Orc.... B Environ Contam Tox 24:916-920. |
Orconectes rusticus | 22146 | L | crayfish, rusty | adult | W | Copper(II) Sulfate | 7758-98-7 | N | Y | FW | aqueous | 1 mg/L | 1x | 48 hr | 36 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | all crayfish survived the 48 h exposure period; control had 24 mg/kg whole body copper | Evans. 1980. Copper accumulation in the crayfish (Orc.... B Environ Contam Tox 24:916-920. |
Orconectes rusticus | 22147 | L | crayfish, rusty | adult | W | Copper(II) Sulfate | 7758-98-7 | N | Y | FW | aqueous | 2 mg/L | 1x | 48 hr | 44 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | all crayfish survived the 48 h exposure period; control had 24 mg/kg whole body copper | Evans. 1980. Copper accumulation in the crayfish (Orc.... B Environ Contam Tox 24:916-920. |
Orconectes rusticus | 22148 | L | crayfish, rusty | adult | W | Copper(II) Sulfate | 7758-98-7 | N | Y | FW | aqueous | 3 mg/L | 1x | 48 hr | 50 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | all crayfish survived the 48 h exposure period; control had 24 mg/kg whole body copper | Evans. 1980. Copper accumulation in the crayfish (Orc.... B Environ Contam Tox 24:916-920. |