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 Polyaromatic Hydrocarbons (PAHs)

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
Elliptio complanata 6364 L Eastern elliptio N/I N/I Anthracene 120-12-7 N N/I FW aqueous N/I N/I N/I 2.6 gill cellular N/I N/I N/I N/I ED 64 Excised gill tissue was cultured with PAH Cheney et al. 2001. Uptake and diverse effects of polycyclic.... Environ Toxicol Chem 20:1031-1036.
Dreissena polymorpha 4046 F zebra mussel adult W Benz[a]anthracene 56-55-3 Y N FW in situ 8.49 mg/kg N/I 34 d 0.6 whole body survival N/I N/I N/I N/I NOEC N/I Roper et al. 1997. Bioaccumulation of PAHs in the zebra mus.... Environ Monit Assess 46:267-277.
Sphaerium corneum 5446 L clam, European fingernailclam adult N/I Benzo[a]pyrene 50-32-8 N N/I FW sediment 10 µg/g N/I 5 1.25 whole body mortality NEF N/I N/I N/I NOEC Residue measured at end of exposure period Borchert et al. 1997. Uptake and metabolism of benzo (a) pyren.... B Environ Contam Tox 58:158-165.
Mercenaria mercenaria 20786 L hard-shell clam N/R N/R Benzo[a]pyrene 50-32-8 N Y SW aqueous <0.001 ppb N/R 18 wk 0.003 whole body mortality NEF N/R N/R N/R N/R no increased mortality Anderson et al. 1991. Effects of environmental pollutants on i.... Aquat Toxicol 1:187-195.
Pisidium amnicum 8154 L clam, greater European peaclam adult N/I Benzo[a]pyrene 50-32-8 Y N/I FW aqueous 21.04 µg/L N/I N/I 0.024 whole body mortality N/I N/I N/I N/I NOEC 21 ug/l TCP and 4 ng/l BaP, Uninfected, 20 C Heinonen et al. 1999. The effects of parasites and temperature.... J Appl Ecol 9:475-481.
Pisidium amnicum 8155 L clam, greater European peaclam adult N/I Benzo[a]pyrene 50-32-8 Y N/I FW aqueous 21.04 µg/L N/I N/I 0.028 whole body mortality N/I N/I N/I N/I NOEC Infected with Bunodera luciopercae, 20 C Heinonen et al. 1999. The effects of parasites and temperature.... J Appl Ecol 9:475-481.
Pisidium amnicum 8160 L clam, greater European peaclam adult N/I Benzo[a]pyrene 50-32-8 Y N/I FW aqueous 21.04 µg/L N/I N/I 0.001 whole body mortality N/I N/I N/I N/I NOEC 21 ug/l TCP and 4 ng/l BaP Uninfected, 4 C Heinonen et al. 1999. The effects of parasites and temperature.... J Appl Ecol 9:475-481.
Pisidium amnicum 8161 L clam, greater European peaclam adult N/I Benzo[a]pyrene 50-32-8 Y N/I FW aqueous 21.04 µg/L N/I N/I 0.016 whole body mortality N/I N/I N/I N/I NOEC Infected with Palaeorchis crassus, 20 C Heinonen et al. 1999. The effects of parasites and temperature.... J Appl Ecol 9:475-481.
Pisidium amnicum 8164 L clam, greater European peaclam adult N/I Benzo[a]pyrene 50-32-8 Y N/I FW aqueous 21.04 µg/L N/I N/I 0.016 whole body mortality N/I N/I N/I N/I NOEC Infected with Phyllodistomum elongatum, 4 C Heinonen et al. 1999. The effects of parasites and temperature.... J Appl Ecol 9:475-481.
Pisidium amnicum 8165 L clam, greater European peaclam adult N/I Benzo[a]pyrene 50-32-8 Y N/I FW aqueous 21.04 µg/L N/I N/I 0.024 whole body mortality N/I N/I N/I N/I NOEC Infected with Bunodera luciopercae, 4 C Heinonen et al. 1999. The effects of parasites and temperature.... J Appl Ecol 9:475-481.
Dreissena polymorpha 4045 F zebra mussel adult W Chrysene 218-01-9 Y N FW in situ 9.32 mg/kg N/I 34 d 0.93 whole body survival N/I N/I N/I N/I NOEC N/I Roper et al. 1997. Bioaccumulation of PAHs in the zebra mus.... Environ Monit Assess 46:267-277.
Dreissena polymorpha 4044 F zebra mussel adult W Fluoranthene 206-44-0 Y N FW in situ 25.12 mg/kg N/I 34 d 1.29 whole body survival N/I N/I N/I N/I NOEC EPA method cited has standards Roper et al. 1997. Bioaccumulation of PAHs in the zebra mus.... Environ Monit Assess 46:267-277.
Macoma balthica 10681 L Baltic macoma adult N/I Fluoranthene 206-44-0 Y N/I SW aqueous N/I N/I N/I 140 whole body behavior N/I N/I N/I N/I ED 50 re-burying effect Ahrens et al. 2002. Sensitivity of juvenile Macomona liliana.... Environ Toxicol 17:567-577.
Macoma balthica 10682 L Baltic macoma adult N/I Fluoranthene 206-44-0 Y N/I SW aqueous N/I N/I N/I 460 whole body behavior N/I N/I N/I N/I ED 50 re-burying effect Ahrens et al. 2002. Sensitivity of juvenile Macomona liliana.... Environ Toxicol 17:567-577.
Macoma balthica 10683 L Baltic macoma adult N/I Fluoranthene 206-44-0 Y N/I SW aqueous N/I N/I N/I 150 whole body behavior N/I N/I N/I N/I NOEC re-burying effect Ahrens et al. 2002. Sensitivity of juvenile Macomona liliana.... Environ Toxicol 17:567-577.
Macoma balthica 10684 L Baltic macoma adult N/I Fluoranthene 206-44-0 Y N/I SW aqueous N/I N/I N/I 30 whole body behavior N/I N/I N/I N/I NOEC re-burying effect Ahrens et al. 2002. Sensitivity of juvenile Macomona liliana.... Environ Toxicol 17:567-577.
Dreissena polymorpha 4043 F zebra mussel adult W Pyrene 129-00-0 Y N FW in situ 18.22 mg/kg N/I 34 d 1.08 whole body survival N/I N/I N/I N/I NOEC Reps in EPA method Roper et al. 1997. Bioaccumulation of PAHs in the zebra mus.... Environ Monit Assess 46:267-277.