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 Benzene derivatives

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 6220 L midge larvae N/I 1,2,3,4-Tetrachlorobenzene 634-66-2 N N/I N/I aqueous 12.5 µmol/L N/I N/I 0.0134 whole body mortality N/I N/I N/I N/I LD 10 N/I Leslie et al. 2002. Biomimetic solid‐phase microextraction t.... Environ Toxicol Chem 21:229-234.
Chironomus riparius 6221 L midge larvae N/I 1,2,3,4-Tetrachlorobenzene 634-66-2 N N/I N/I aqueous 12.5 µmol/L N/I N/I 0.0311 whole body mortality N/I N/I N/I N/I LD 50 N/I Leslie et al. 2002. Biomimetic solid‐phase microextraction t.... Environ Toxicol Chem 21:229-234.
Chironomus riparius 9957 L midge larvae N/I 1,2,3,4-Tetrachlorobenzene 634-66-2 N N/I N/I aqueous N/I N/I N/I 293.61 whole body mortality N/I N/I N/I N/I LD 50 CBR; BCF = 13.5; Used SPMEs Leslie et al. 2004. Chronic toxicity and body residues of th.... Environ Toxicol Chem 23:2022-2028.
Chironomus riparius 11218 L midge juvenile N/I 1,2,3-Trichlorobenzene 87-61-6 Y N/I N/I aqueous 1.88 µmol/L N/I N/I 95.99 whole body mortality N/I N/I N/I N/I LD 50 residue as total chlorobenzenes Leslie et al. 2004. Baseline toxicity of a chlorobenzene mix.... Environ Toxicol Chem 23:2019-2021.
Chironomus riparius 11219 L midge juvenile N/I 1,2,3-Trichlorobenzene 87-61-6 Y N/I N/I aqueous 1.88 µmol/L N/I N/I 70.58 whole body mortality N/I N/I N/I N/I LD 10 residue as total chlorobenzenes Leslie et al. 2004. Baseline toxicity of a chlorobenzene mix.... Environ Toxicol Chem 23:2019-2021.
Chironomus riparius 9494 L midge larvae N/I 1,2,4-Trichlorobenzene 120-82-1 N N/I N/I aqueous 9.2 µmol/L N/I N/I 63.6 whole body cellular N/I N/I N/I N/I LOEC Heat Output Penttinen and Kukkonen. 1998. Chemical stress and metabolic rate in aq.... Environ Toxicol Chem 17:883-890.
Chironomus tentans 14719 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 47.57 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 14721 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 82.61 whole body growth N/I N/I N/I N/I ED 27 N/I Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14722 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 127.67 whole body growth N/I N/I N/I N/I ED 54 N/I Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14723 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 127.67 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 14724 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 10.01 whole body reproduction N/I N/I N/I N/I ED 28 % pupation Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14725 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 25.03 whole body reproduction N/I N/I N/I N/I ED 40 % pupation Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14726 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 100.14 whole body reproduction N/I N/I N/I N/I ED 52 % pupation Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14727 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 5 whole body reproduction N/I N/I N/I N/I ED 73 % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14728 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 10.01 whole body reproduction N/I N/I N/I N/I ED 89 % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14729 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 17.52 whole body reproduction N/I N/I N/I N/I ED 88 % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14730 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 47.57 whole body reproduction N/I N/I N/I N/I ED 97 % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14731 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 100.14 whole body reproduction N/I N/I N/I N/I ED 72 % emergence Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14732 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 100.14 whole body reproduction N/I N/I N/I N/I NOEC eggs/female**variable data Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14733 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 5.01 whole body reproduction N/I N/I N/I N/I LOEC Larval development=LOER Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14734 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 5.01 whole body reproduction N/I N/I N/I N/I LOEC Emergence=LOER Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14735 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 47.57 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 14736 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 82.61 whole body growth N/I N/I N/I N/I LOEC N/I Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.
Chironomus tentans 14737 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 10.01 whole body mortality 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 14738 L midge adult N/I Pentachlorobenzene 608-93-5 N N/I FW aqueous N/I N/I N/I 202.78 whole body mortality N/I N/I N/I N/I LD 50 =LR50; MATR = 0.01 umol/g = 2.5 mg/kg tissue Schuler et al. 2007. Response spectrum of pentachlorobenzene .... Environ Toxicol Chem 26:1248-1257.