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). 

You are viewing Mollusca: Invert (molluscs) and Lead

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
Dreissena polymorpha 2094 L zebra mussel immature N/I Lead 7439-92-1 N N/I FW aqueous 370 µg/L N/I 48 hr 12 other behavior N/I N/I N/I N/I ED 50 filtration rate fraction= soft tissues Bleeker et al. 1992. Ecotoxicity of lead to the zebra musselD.... Hydrobiol Bull 25:233-235.
Dreissena polymorpha 2095 L zebra mussel immature N/I Lead 7439-92-1 N N/I FW aqueous 116 µg/L N/I 48 hr 4.4 other behavior N/I N/I N/I N/I NOEC filtration rate fraction= soft tissues Bleeker et al. 1992. Ecotoxicity of lead to the zebra musselD.... Hydrobiol Bull 25:233-235.
Dreissena polymorpha 2096 L zebra mussel immature N/I Lead 7439-92-1 N N/I FW aqueous 1700 µg/L N/I 48 hr 40 other mortality N/I N/I N/I N/I NOEC filtration rate fraction= soft tissues Bleeker et al. 1992. Ecotoxicity of lead to the zebra musselD.... Hydrobiol Bull 25:233-235.
Dreissena polymorpha 1230 L zebra mussel N/I N/I Lead 7439-92-1 N N/I FW aqueous 382 µg/L N/I 10 wk 200 soft tissue behavior N/I N/I N/I N/I ED 77 behavior (filtration rate) Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 1233 L zebra mussel N/I N/I Lead 7439-92-1 N N/I FW aqueous 38 µg/L N/I 10 wk 6 soft tissue behavior N/I N/I N/I N/I NOEC behavior (filtration rate) Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 1235 L zebra mussel N/I N/I Lead 7439-92-1 N N/I FW aqueous 85 µg/L N/I 10 wk 34 soft tissue mortality N/I N/I N/I N/I NOEC Bioconcen. Measured as Musssels dies Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4779 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 358 µg/L N/I 70 200 whole body physiological N/I N/I N/I N/I ED 100 decr filtration rate; eventual cessation Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4780 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 358 µg/L N/I 70 200 whole body growth DEC N/I Yes N/I LOEC growth rate Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4781 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 358 µg/L N/I 70 200 whole body mortality N/I N/I 52% N/I LOEC N/I Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4783 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 85 µg/L N/I 70 35 whole body physiological DEC N/I 19 N/I LOEC in filtration rate Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4785 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 85 µg/L N/I 70 35 whole body growth NEF N/I N/I N/I NOEC growth (weight) Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4787 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 85 µg/L N/I 70 35 whole body mortality N/I N/I N/I N/I NOEC N/I Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Dreissena polymorpha 4789 L zebra mussel adult N/I Lead 7439-92-1 N N/I FW aqueous 38 µg/L N/I 70 7 whole body physiological NEF N/I N/I N/I NOEC Filtration Rate Kraak et al. 1994. Chronic ecotoxicity of Zn and Pb to the .... Aquat Toxicol 30:77-89.
Pyganodon grandis 2041 L giant floater mussel adult N/I Lead nitrate 10099-74-8 N N/I FW aqueous 5000 µg/L N/I 28 18 adductor muscle growth NEF N/I N/I N/I NOEC growth (weight or length) Black et al. 1996. DNA strand breakage in freshwater mussel.... Environ Toxicol Chem 15:802-808.
Pyganodon grandis 2042 L giant floater mussel adult N/I Lead nitrate 10099-74-8 N N/I FW aqueous 5000 µg/L N/I 28 48 mantle growth NEF N/I N/I N/I NOEC growth (weight or length) Black et al. 1996. DNA strand breakage in freshwater mussel.... Environ Toxicol Chem 15:802-808.
Pyganodon grandis 2043 L giant floater mussel adult N/I Lead nitrate 10099-74-8 N N/I FW aqueous 5000 µg/L N/I 28 48 foot growth NEF N/I N/I N/I NOEC growth (weight or length) Black et al. 1996. DNA strand breakage in freshwater mussel.... Environ Toxicol Chem 15:802-808.