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Toxicity and bioconcentration of 2,3,7,8‐tetrachlorodibenzodioxin and 2,3,7,8‐tetrachlorodibenzofuran in rainbow trout
Author(s) -
Mehrle Paul M.,
Buckler Denny R.,
Little Edward E.,
Smith Larry M.,
Petty Jim D.,
Peterman Paul H.,
Stalling David L.,
De Graeve G. M.,
Coyle James J.,
Adams William J.
Publication year - 1988
Publication title -
environmental toxicology and chemistry
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.1
H-Index - 171
eISSN - 1552-8618
pISSN - 0730-7268
DOI - 10.1002/etc.5620070108
Subject(s) - bioconcentration , salmo , rainbow trout , chemistry , toxicity , trout , fish <actinopterygii> , environmental chemistry , polychlorinated dibenzodioxins , zoology , bioaccumulation , fishery , biology , organic chemistry
Among the most toxic isomers of polychlorinated dibenzodioxins and polychlorinated dibenzofurans, two groups of toxic aromatic compounds, are 2,3,7,8‐tetrachlorodibenzodioxin (TCDD) and 2,3,7,8‐tetrachlorodibenzofuran (TCDF). We examined the chronic toxicity of these compounds to rainbow trout ( Salmo gairdneri ). The fish (0.38 ± 0.09 g) were continuously exposed in an intermittent‐flow proportional diluter for 28 d to 0, 38, 79, 176, 382, and 789 pg TCDD/L (parts per quadrillion) or to 0, 0.41, 0.90, 1.79, 3.93, and 8.78 ng TCDF/L (parts per trillion); exposures to each chemical were followed by a 28‐d depuration phase. TCDD had significant effects on survival, growth, and behavior during the exposure and depuration phases. The no observed effect concentration was lower than the lowest exposure concentration of 38 pg/L. The average measured BCF at 28 days was 26,707. The estimated bioconcentration factor at steady‐state equilibrium was 39,000 in the lowest exposure concentration where fish were least affected. TCDF, like TCDD, induced similar effects on survival, growth and behavior. The no observed effect concentration, based on survival, was 1.79 ng/L; that based on growth was 0.41 ng/L. The measured bioconcentration factor was 6,049 in fish exposed to 0.41 ng/L, and 2,455 in fish exposed to 3.93 ng/L for 28 d.