DOTS

ERED

Environmental Residue-Effects Database

US Army Corps of Engineers ERDC Dredging Operations Technical Support

USACE


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: Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166..

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
Saccostrea cucullata 15247 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.88 whole body physiological N/I N/I N/I N/I IP 82 Cd partitioning- % heat sensitive protein Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15249 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.54 whole body physiological N/I N/I N/I N/I IP 86 Cd partitioning- % heat sensitive protein Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15254 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.88 whole body physiological N/I N/I N/I N/I IP 55 MT concentration in leiblain gland, Cd exposure Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15255 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 5.82 whole body physiological N/I N/I N/I N/I IP 73 MT concentration in leiblain gland, Cd exposure Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15256 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.54 whole body physiological N/I N/I N/I N/I IP 47 MT concentration in leiblain gland Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15258 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.88 whole body physiological N/I N/I N/I N/I IP 85 Cd-MT isoform concentration in leiblain gland Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15259 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 5.82 whole body physiological N/I N/I N/I N/I IP 58 Cd-MT isoform concentration in leiblain gland Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15260 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.54 whole body physiological N/I N/I N/I N/I IP 106 Cd-MT isoform concentration in leiblain gland Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15252 L oyster adult N/I Cadmium 7440-43-9 N/I N/I SW diet 150 µg/L N/I N/I 2.54 whole body physiological N/I N/I N/I N/I IP 626 Zn partitioning- % MTLP, Cd + Zn exposure Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15253 L oyster adult N/I Zinc 7440-66-6 N/I N/I SW diet 200 µg/L N/I N/I 500 whole body physiological N/I N/I N/I N/I IP 626 Zn partitioning- % MTLP), Zn + Cd exposure Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15261 L oyster adult N/I Zinc 7440-66-6 N/I N/I SW diet 200 µg/L N/I N/I 500 whole body physiological N/I N/I N/I N/I IP 106 Cd-MT isoform concentration in leiblain gland Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15257 L oyster adult N/I Zinc 7440-66-6 N/I N/I SW diet 200 µg/L N/I N/I 500 whole body physiological N/I N/I N/I N/I IP 47 MT concentration in leiblain gland Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15250 L oyster adult N/I Zinc 7440-66-6 N/I N/I SW diet 200 µg/L N/I N/I 500 whole body physiological N/I N/I N/I N/I IP 86 Cd partitioning- % heat sensitive protein Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15251 L oyster adult N/I Zinc 7440-66-6 N/I N/I SW diet 200 µg/L N/I N/I 460 whole body physiological N/I N/I N/I N/I IP 640 Zn partitioning- % MTLP, Zn exposure Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.
Saccostrea cucullata 15248 L oyster adult N/I Zinc 7440-66-6 N/I N/I SW diet 200 µg/L N/I N/I 460 whole body physiological N/I N/I N/I N/I IP 87 Cd partitioning- % heat sensitive protein Cheung and Wang. 2008. Uses of subcellular metal distribution i.... Environ Toxicol Chem 27:1160-1166.