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). 

Source: Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268..

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 1250 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 3088 mg/kg N/I 56 636.6 liver biochemistry N/I N/I N/I N/I IP 1009 Increase of Cu in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1251 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 1585 mg/kg N/I 56 2256.4 liver biochemistry N/I N/I N/I N/I IP 1009 Increase of Cu in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1252 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 664 mg/kg N/I 112 288.2 liver growth N/I N/I N/I N/I ED 15 N/I Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1253 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 730 mg/kg N/I 56 177.2 liver biochemistry N/I N/I N/I N/I IP 1524 Increase of Cu in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1254 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 403 mg/kg N/I 112 209.2 liver biochemistry N/I N/I N/I N/I IP 335 Increase of Cu in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1255 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 511 mg/kg N/I 112 217 liver biochemistry N/I N/I N/I N/I IP 347 Increase of Copper in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1256 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 664 mg/kg N/I 112 288.2 liver biochemistry N/I N/I N/I N/I IP 462 Increase of Cu in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1257 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 730 mg/kg N/I 56 177.2 liver growth N/I N/I N/I N/I ED 56 N/I Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1258 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 730 mg/kg N/I 56 177.2 liver biochemistry N/I N/I N/I N/I IP 697 Increase of Cu in liver Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1259 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 1585 mg/kg N/I 56 256.4 liver growth N/I N/I N/I N/I ED 85 Avoidance of food evident Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1260 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 3088 mg/kg N/I 56 636.6 liver growth N/I N/I N/I N/I ED 93 Avoidance evident Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1261 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 1585 mg/kg N/I 56 256.4 liver growth N/I N/I N/I N/I ED 16 N/I Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1262 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 3088 mg/kg N/I 56 636.6 liver growth N/I N/I N/I N/I ED 27 Avoidance of food evident Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1263 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 664 mg/kg N/I 112 288.2 liver biochemistry N/I N/I N/I N/I NOEC Plasma copper Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1264 L Rainbow Trout fry N/I Copper 7440-50-8 Y N/I N/I diet 3088 mg/kg N/I 56 636.6 liver biochemistry NEF N/I N/I N/I NOEC N/I Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1265 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 664 mg/kg N/I 112 288.2 liver indice of condition N/I N/I N/I N/I NOEC hepatosomatic index Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.
Oncorhynchus mykiss 1266 L Rainbow Trout juvenile N/I Copper 7440-50-8 Y N/I N/I diet 664 mg/kg N/I 112 288.2 liver survival N/I N/I N/I N/I NOEC N/I Lanno et al. 1985. Maximum tolerable and toxicity levels of.... Aquaculture 49:257-268.