| Autor: |
Sonne C; Aarhus University, Faculty of Science and Technology, Department of Bioscience, Arctic Research Centre, Frederiksborgvej, 399, P.O. Box 358, DK-4000 Roskilde, Denmark. Electronic address: cs@bios.au.dk., Gustavson K; Aarhus University, Faculty of Science and Technology, Department of Bioscience, Arctic Research Centre, Frederiksborgvej, 399, P.O. Box 358, DK-4000 Roskilde, Denmark., Letcher RJ; Ecotoxicology and Wildlife Health Division, Wildlife and Landscape Science Directorate, Environment Canada, National Wildlife Research Centre, Carleton University, Ottawa, ON K1A 0H3, Canada., Dietz R; Aarhus University, Faculty of Science and Technology, Department of Bioscience, Arctic Research Centre, Frederiksborgvej, 399, P.O. Box 358, DK-4000 Roskilde, Denmark. |
| Abstrakt: |
We used PBPK (physiologically-based pharmacokinetic) modelling to investigate distribution, bioaccumulation and excretion of the seven POPs (persistent organic pollutants) CB-99, CB-153, HCB, oxychlordane, p,p'-DDE, BDE-47 and BDE-99 in 4 adult captive Greenland sledge dog (Canis familiaris) bitches fed minke whale (Balaenoptera acuterostrata) blubber for 500-635 days. The PBPK modelled POP concentrations in adipose tissue, liver, kidney and plasma were mostly within a factor 2 of actual measured tissue levels even for those at the lower concentration end. The excretion route for oxychlordane and CB-153 was modelled to be via faeces while lung alveolar excretion dominated for BDE-47, BDE-99, HCB, p,p'-DDE and CB-99. Furthermore the model suggested the retained mass of POPs after 500 and 635 days of exposure, respectively, to be relatively low despite these POPs being highly recalcitrant. The retention increased in the following order (% of total intake); p,p'-DDE (1%) (Copyright © 2015 Elsevier Inc. All rights reserved.) |
Full Text from ScienceDirect