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 Arthropoda: Invert (insects, crustaceans) 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
Chironomus riparius 5447 L midge larvae N/I Benzo[a]pyrene 50-32-8 N N/I N/I sediment 10 µg/g N/I 5 1.9 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.
Chironomus tentans 10315 L midge adult N/I Fluoranthene 206-44-0 Y N/I FW aqueous N/I N/I N/I 87 whole body mortality N/I N/I N/I N/I LD 50 N/I Schuler et al. 2004. Time-dependent toxicity of fluoranthene .... Environ Sci Tech 38:6247-6255.
Chironomus tentans 10316 L midge adult N/I Fluoranthene 206-44-0 Y N/I FW aqueous N/I N/I N/I 50.6 whole body mortality N/I N/I N/I N/I LD 50 N/I Schuler et al. 2004. Time-dependent toxicity of fluoranthene .... Environ Sci Tech 38:6247-6255.
Chironomus tentans 10317 L midge adult N/I Fluoranthene 206-44-0 Y N/I FW aqueous N/I N/I N/I 34.4 whole body mortality N/I N/I N/I N/I LD 50 N/I Schuler et al. 2004. Time-dependent toxicity of fluoranthene .... Environ Sci Tech 38:6247-6255.
Chironomus tentans 10318 L midge adult N/I Fluoranthene 206-44-0 Y N/I FW aqueous N/I N/I N/I 52.6 whole body mortality N/I N/I N/I N/I LD 50 N/I Schuler et al. 2004. Time-dependent toxicity of fluoranthene .... Environ Sci Tech 38:6247-6255.
Chironomus tentans 10321 L midge adult N/I Fluoranthene 206-44-0 Y N/I FW aqueous N/I N/I N/I 40.5 whole body mortality N/I N/I N/I N/I LD 50 N/I Schuler et al. 2004. Time-dependent toxicity of fluoranthene .... Environ Sci Tech 38:6247-6255.
Chironomus tentans 10485 L midge larvae N/I Fluoranthene 206-44-0 N N/I FW sediment 204 µg/g N/I N/I 14.56 whole body mortality N/I N/I N/I N/I NOEC animals exposed to sed survived longer Bell et al. 2004. Evaluation of bioaccumulation and photo-.... Arch Environ Con Tox 47:297-303.
Chironomus tentans 10486 L midge larvae N/I Fluoranthene 206-44-0 N N/I FW sediment 204 µg/g N/I N/I 14.56 whole body mortality N/I N/I N/I N/I LD 100 animals exposed to sed survived longer Bell et al. 2004. Evaluation of bioaccumulation and photo-.... Arch Environ Con Tox 47:297-303.
Chironomus tentans 10487 L midge larvae N/I Fluoranthene 206-44-0 N N/I FW sediment 170 µg/g N/I N/I 6.7 whole body mortality N/I N/I N/I N/I NOEC animals exposed to sed survived longer Bell et al. 2004. Evaluation of bioaccumulation and photo-.... Arch Environ Con Tox 47:297-303.
Chironomus tentans 10488 L midge larvae N/I Fluoranthene 206-44-0 N N/I FW sediment 53.6 µg/g N/I N/I 1.92 whole body mortality N/I N/I N/I N/I NOEC animals exposed to sed survived longer Bell et al. 2004. Evaluation of bioaccumulation and photo-.... Arch Environ Con Tox 47:297-303.
Chironomus tentans 14451 L midge N/I N/I Fluoranthene 206-44-0 N N/I FW aqueous N/I N/I N/I 44.496 whole body mortality N/I N/I Yes N/I LD 50 mortality is LBR50 Lee and Landrum. 2006. Application of multi-component damage as.... Environ Sci Tech 40:1350-1357.
Chironomus tentans 14755 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 28.32 whole body growth N/I N/I N/I N/I NOEC dry mass Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14756 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 42.48 whole body growth N/I N/I N/I N/I ED 50 dry mass Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14757 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 30.34 whole body reproduction N/I N/I N/I N/I NOEC % pupation Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14758 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 52.59 whole body reproduction N/I N/I N/I N/I ED 33 % pupation Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14759 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 30.34 whole body reproduction N/I N/I N/I N/I NOEC % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14760 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 52.59 whole body reproduction N/I N/I N/I N/I ED 68 % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14761 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 141.58 whole body reproduction N/I N/I N/I N/I NOEC # eggs/female Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14762 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 30.34 whole body reproduction N/I N/I N/I N/I ED 37 # eggs/female Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14763 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 14.16 whole body reproduction N/I N/I N/I N/I NOEC N/I Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14764 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 30.34 whole body reproduction N/I N/I N/I N/I LOEC =LOER; development Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14765 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 30.34 whole body reproduction N/I N/I N/I N/I NOEC =LOER; pupation Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14766 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 28.32 whole body growth N/I N/I N/I N/I NOEC N/I Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14767 L midge adult N/I Fluorene 86-73-7 N N/I FW aqueous N/I N/I N/I 30.34 whole body growth N/I N/I N/I N/I LD 50 =LR50; MATR =0.11 umol/g = 22.25 mg/kg tissue Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.