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 Chordata: Vert (fishes; salmonid) and (Miscellaneous)

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
Oncorhynchus mykiss 5022 L Rainbow Trout adult N/I Acrolein 107-02-8 N N/I N/I aqueous 0.0014 mmol/L N/I 0.85 5.3 whole body mortality N/I N/I N/I N/I LOEC N/I McKim and Schmieder. 1991. Bioaccumulation: Does it reflect toxici...
Oncorhynchus mykiss 5019 L Rainbow Trout adult N/I Benzaldehyde 100-52-7 N N/I N/I aqueous 0.36 mmol/L N/I 0.8 1400 whole body mortality N/I N/I N/I N/I LOEC N/I McKim and Schmieder. 1991. Bioaccumulation: Does it reflect toxici...
Oncorhynchus mykiss 4405 L Rainbow Trout juvenile C Carbon tetrachloride 56-23-5 N Y FW aqueous N/I continuous 4 d 2720 whole body mortality INC N/I N/I N/I LD 50 median lethal dose Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454.
Oncorhynchus mykiss 4414 L Rainbow Trout juvenile C Chloroform 67-66-3 N Y FW aqueous N/I continuous 4 d 504 whole body mortality INC N/I N/I N/I LD 50 median lethal dose Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454.
Oncorhynchus mykiss 4415 L Rainbow Trout juvenile C Dimethyl sulfoxide 67-68-5 N Y FW aqueous N/I continuous 4 d 10700 whole body mortality INC N/I N/I N/I LD 50 median lethal dose Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454.
Oncorhynchus mykiss 4416 L Rainbow Trout juvenile C Dimethylformamide 68-12-2 N Y FW aqueous N/I continuous 4 d 6620 whole body mortality INC N/I N/I N/I LD 50 median lethal dose Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454.
Oncorhynchus mykiss 9995 L Rainbow Trout juvenile N/I Propylparaben 94-13-3 Y N/I N/I aqueous 250 µg/L N/I N/I 0.87 muscle physiological N/I N/I N/I N/I IP 100 effect is vitellogenin synthesis Bjerregaard et al. 2003. Estrogenic effect of propylparaben (prop.... Comp Biochem Phys C 136:309-317.
Oncorhynchus mykiss 9996 L Rainbow Trout juvenile N/I Propylparaben 94-13-3 Y N/I N/I diet 1830 mg/kg N/I N/I 37 liver physiological N/I N/I N/I N/I IP 2000 effect is vitellogenin synthesis Bjerregaard et al. 2003. Estrogenic effect of propylparaben (prop.... Comp Biochem Phys C 136:309-317.
Oncorhynchus mykiss 9997 L Rainbow Trout juvenile N/I Propylparaben 94-13-3 Y N/I N/I aqueous 250 µg/L N/I N/I 7 liver physiological N/I N/I N/I N/I IP 100 effect is vitellogenin synthesis Bjerregaard et al. 2003. Estrogenic effect of propylparaben (prop.... Comp Biochem Phys C 136:309-317.
Oncorhynchus mykiss 4394 L Rainbow Trout juvenile C Pyridine 110-86-1 N Y FW aqueous N/I continuous 4 d 652 whole body mortality INC N/I N/I N/I LD 50 median lethal dose Hodson et al. 1988. Estimating the acute toxicity of waterbo.... Environ Toxicol Chem 7:443-454.
Salmo trutta 4335 L Sea Trout, Brown Trout juvenile C Tetrachlorocatechol 1198-55-6 N Y FW aqueous 1.1 mg/L 1x 24 hr 6.3 whole body mortality INC N/R 50% N/R LBR 50 lethal body residue Hattula et al. 1981. Acute toxicity of some chlorinated pheno.... B Environ Contam Tox 26:295-298.