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Accumulation of 2,3,7,8‐tetrachlorodibenzo‐ p ‐dioxin by rainbow trout ( Onchorhynchus mykiss ) at environmentally relevant dietary concentrations
Author(s) -
Jones, Paul D.,
Kannan Kurunthachalam,
Newsted John I.,
Tillitt Donald E.,
Williams Lisa L.,
Giesy John P.
Publication year - 2001
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.5620200215
Subject(s) - rainbow trout , tetrachlorodibenzo p dioxin , chemistry , toxicity , endocrinology , bioconcentration , medicine , biomagnification , toxicokinetics , toxic equivalency factor , trout , bioaccumulation , zoology , metabolism , biology , persistent organic pollutant , environmental chemistry , fish <actinopterygii> , pollutant , fishery , organic chemistry
Rainbow trout were fed a diet containing 1.8, 18, or 90 pg/g 3 H‐2,3,7,8‐tetrachlorodibenzo‐ p ‐dioxin (TCDD) for up to 320 d. Concentrations of TCDD were determined in muscle, liver, and ovaries at 100, 150, 200, and 250 d. Concentrations of TCDD reached an apparent steady‐state concentration in liver after 100 d of exposure, whereas concentrations in other tissues continued to increase until 150 d of exposure. The greatest portion of the total mass of TCDD was present in the muscle tissue with lesser proportions in other organs. As the ovaries developed before spawning, an increase occurred in the total mass of TCDD present in this tissue. The assimilation rate of TCDD during the initial 100 d of the exposure was determined to be between 10 and 30%. This is somewhat less than estimates derived based on both uptake and elimination constants determined during shorter exposures. Biomagnification factors (BMFs) were estimated for all tissues and exposure concentrations, and at all exposure periods. Lipid‐normalized BMFs for muscle ranged from 0.38 to 1.51, which is consistent with the value of 1.0 predicted from fugacity theory. Uptake and depuration rate constants were determined and used to predict individual organ TCDD concentrations. Comparison with observed values indicated that the model could be used to predict tissue concentrations from the known concentrations of TCDD in food. This model will allow more refined risk assessments by predicting TCDD concentrations in sensitive tissues such as developing eggs.