DATA ASSOCIATED WITH 'POLAR BEAR SUBPOPULATION DECLINES DUE TO LEGACY PERSISTENT ORGANIC POLLUTANTS – TEMPORAL AND SPATIAL TRENDS’

• Main Authors: Hoondert, R.P.J., Ragas, A.M.J., Hendriks, A.J.
• Format: Dataset
• Language: unknown
• Published: DANS EASY 2020
• Subjects: Ecotoxicology; Polar bear populations; SSDs; POPs; Environmental Sciences; Arctic; Erignathus barbatus; Monodon monoceros; Odobenus rosmarus; Phoca groenlandica; Phoca hispida; ringed seal; Ursus maritimus
• Online Access: https://hdl.handle.net/2066/226559; https://doi.org/10.1016/j.scitotenv.2020.142380

Item does not contain fulltext Although concentrations of many conventional POPs have decreased in the Arctic over the past few decades, levels of most POPs remain high in Arctic areas, especially in top predators like polar bears (Ursus maritimus). So far, studies generally focused on individual effects only. In the study associated to these data we therefore aimed to estimate the (combined and individual) effect of legacy POPs and mercury on population growth rate of nineteen polar bear subpopulations. We modelled polar bear population development in three scenarios, based on SSDs derived for POPs based on ecotoxicity data for endothermic species. Exposure data. Data on POP residues in marine mammal species (mainly Phoca hispida, Phoca largha, Phoca groenlandica, Crystophora cristata , Erignathus barbatus, Odobenus rosmarus and Monodon monoceros), assumed to be the main prey of polar bears in the Arctic, were compiled to calculate potential changes in intrinsic growth rates of polar bear populations. POP concentrations (transformed to mg/kg wet weight (w.w.)) were obtained from a literature search using the Web of Knowledge and Google Scholar. Search strings used in queries included POPs (specific compound names (e.g. “p,p’-DDE”, or “CB-153”) or compound groups (e.g. “PCBs” or “DDTs”)) on one side, combined with Arctic species’ names (both scientific (e.g. “Phoca hispida”) and common names (e.g. “ringed seal”)) on the other. Concentrations on lipid basis were converted to wet weight (w.w.) basis, based on the reported lipid content. If no lipid concentration was reported, a lipid content of 85% was assumed for marine mammal blubber samples. To calculate the toxic equivalency of PCBs, we assumed that the planar PCB composition in marine mammal blubber was similar across all sampled individuals. In the present study, the planar PCB composition in blubber was taken from Savinov et al. 2011. All concentration data used in our simulations were collected between 1972 and 2018. Ecotoxicity data were taken from the ...