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: Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158..

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
Lepomis macrochirus 4828 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body behavior DEC N/I Yes N/I LOEC behavior (feeding) Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4829 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body biochemistry DEC N/I Yes N/I LOEC hemoglobin and red blood cells Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4830 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body cellular N/I N/I N/I N/I LOEC Swelling and distortion in gill tissue Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4831 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body growth DEC N/I Yes N/I LOEC growth (weight/length ratio) Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4832 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.6 whole body mortality N/I N/I 35% N/I LOEC N/I Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4833 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body physiological INC N/I Yes N/I LOEC oxygen consumption and lipid depletion Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4834 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body physiological INC N/I Yes N/I LOEC oxygen consumption Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4835 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.6 whole body cellular NEF N/I N/I N/I NOEC liver, kidney, heart, spleen tissue Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4836 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.2 whole body growth NEF N/I N/I N/I NOEC growth (weight to length ratio) Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.
Lepomis macrochirus 4837 L Bluegill immature W Selenium 7782-49-2 N Y FW aqueous/diet 5.1 µg/g N/I 180 1.6 whole body mortality NEF N/I N/I N/I NOEC N/I Lemly. 1993. Metabolic stress during winter increases.... Aquat Toxicol 27:133-158.