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 Organotin

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
Hyalella azteca 10143 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 78 ng/L 3x 28 d 0.568 whole body survival DEC N/I N/I N/I LD 25 N/I Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10144 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 145 ng/L 3x 28 d 0.86 whole body survival DEC N/I N/I N/I LD 50 N/I Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10145 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 40 ng/L 3x 70 d 0.328 whole body survival DEC N/I N/I N/I LD 25 N/I Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10146 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 76 ng/L 3x 70 d 0.558 whole body survival DEC N/I N/I N/I LD 50 N/I Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10147 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 89 ng/L 3x 28 d 0.616 whole body growth N/I N/I N/I N/I ED 25 based on biomass; indiv growth not affected so was actually an effect on survival Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10148 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 152 ng/L 3x 28 d 0.812 whole body growth N/I N/I N/I N/I ED 50 based on biomass; indiv growth not affected so was actually an effect on survival Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10149 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 86 ng/L 3x 70 d 0.6 whole body growth N/I N/I N/I N/I ED 25 based on biomass; indiv growth not affected so was actually an effect on survival Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10150 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 124 ng/L 3x 70 d 0.768 whole body growth N/I N/I N/I N/I ED 50 based on biomass; indiv growth not affected so was actually an effect on survival Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Hyalella azteca 10151 L freshwater amphipod life cycle C Tributyltin chloride 56573-85-4 N Y FW sediment 22 ng/L 3x 70 d 0.158 whole body reproduction N/I N/I N/I N/I ED 50 reproduction results variable Bartlett et al. 2004. Accumulation of tributyltin in Hyalella .... Environ Toxicol Chem 23:2878-2888.
Rhepoxynius abronius 19089 L amphipod N/R W Tributyltin chloride 1461-22-9 Y Y SW aqueous 27 ng/ml daily 10 d 10.8 whole body mortality INC N/I N/I N/I LC 50 LC50 predicted for given time Meador. 1997. Comparative toxicokinetics of tributylti.... Aquat Toxicol 37:307-326.
Rhepoxynius abronius 1730 L amphipod N/R W Tributyltin chloride 1461-22-9 N Y SW aqueous 173 ng/ml 1x/24hr 4 d 14.3 whole body mortality INC N/I 50% 2% LD 50 acclimated 6 d; TBT conc that caused 50% mortality Meador. 1993. The effect of laboratory holding on the .... J Exp Mar Biol Ecol 174:227-242.
Rhepoxynius abronius 1731 L amphipod N/R W Tributyltin chloride 1461-22-9 N Y SW aqueous 51 ng/ml 1x/24hr 4 d 5.84 whole body mortality INC N/I 50% 13% LD 50 acclimated 68 d; TBT conc that caused 50% mortality Meador. 1993. The effect of laboratory holding on the .... J Exp Mar Biol Ecol 174:227-242.
Eohaustorius estuarius 1732 L amphipod N/R W Tributyltin chloride 1461-22-9 N Y SW aqueous 2 ng/ml 1x/24hr 10 d 11.8 whole body mortality INC N/I 50% 2.5% LD 50 acclimated 11 d; TBT conc that caused 50% mortality Meador. 1993. The effect of laboratory holding on the .... J Exp Mar Biol Ecol 174:227-242.
Eohaustorius estuarius 1733 L amphipod N/R W Tributyltin chloride 1461-22-9 N Y SW aqueous 1.5 ng/ml 1x/24hr 10 d 7.1 whole body mortality INC N/I 50% 8.5% LD 50 acclimated 98 d; TBT conc that caused 50% mortality Meador. 1993. The effect of laboratory holding on the .... J Exp Mar Biol Ecol 174:227-242.