Toxicokinetics of 2,3,7,8-TCDF and 2,3,4,7,8-PeCDF in mink (Mustela vison) at ecologically relevant exposures.
Wild mink (Mustela vison) living along the Tittabawassee River in central Michigan exhibit elevated hepatic and dietary polychlorinated dibenzofuran (PCDF) concentrations exceeding mink-specific, literature-reported toxicity reference values (TRVs) on a toxicity equivalents basis. However, no apparent effects on individuals or population are evident, suggesting that available TRVs may overpredict risk for the site-specific mix of congeners. To investigate this discrepancy, a 180-day spiked feed study was conducted to assess: (1) the dosages of key congeners necessary to achieve liver concentrations bracketing those observed in wild mink, (2) time to achieve steady-state concentrations, and (3) effect of coadministration of 2,3,7,8-tetrachlorodibenzofuran (TCDF) and 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF) on the toxicokinetics and distribution of each congener. Adipose and hepatic PCDF concentrations were measured at 0, 90, and 180 days. PCDF concentrations in mink scat were determined at several time points and indicated nearly complete absorption of both TCDF and 4-PeCDF from the diet. Elimination half-times of TCDF were < 15 h and were inversely proportional to dose, while those for 4-PeCDF were approximately 7-9 days with no clear dose dependency in the tested dose range. Coadministration of 4-PeCDF and TCDF accelerated clearance of TCDF compared to administration of TCDF alone. Clearance of 4-PeCDF was not affected by TCDF coadministration. Distribution of 4-PeCDF, but not TCDF, demonstrated increased hepatic sequestration with increasing dose. 4-PeCDF toxicokinetics were described using a previously published two-compartment model. Overall, the toxicokinetic information gathered here illustrates the impact of CYP1A1 induction on bioaccumulation and toxicity potential of TCDF and 4-PeCDF. This information may provide insight into why the current TRVs do not appear to correctly characterize the risk for these two congeners when they are the primary components of an environmental mixture.
Zwiernik
Matthew J
MJ
Aquatic Toxicology Laboratory, National Food Safety and Toxicology Center, Michigan State University, East Lansing, Michigan 48824, USA. zwiernik@msu.edu
Bursian
Steven
S
Aylward
Lesa L
LL
Kay
Denise P
DP
Moore
Jeremy
J
Rowlands
Craig
C
Woodburn
Kent
K
Shotwell
Melissa
M
Khim
Jong Seong
JS
Giesy
John P
JP
Budinsky
Robert A
RA
D000273:Adipose Tissue / Q000378:metabolism; D000818:Animals; D001572:Benzofurans / Q000493:pharmacokinetics* / Q000633:toxicity; D004463:Ecology; D005260:Female; D008099:Liver / Q000378:metabolism; D008907:Mink / Q000378:metabolism*; D008954:Models, Biological
D001572:Benzofurans; C038890:2,3,4,7,8-pentachlorodibenzofuran; C014211:2,3,7,8-tetrachlorodibenzofuran