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dc.contributor.authorAlfaro Garcia, Laura Andrea
dc.contributor.authorDescamps, Sebastien
dc.contributor.authorHerzke, Dorte
dc.contributor.authorChastel, Olivier
dc.contributor.authorCarravieri, Alice
dc.contributor.authorCherel, Yves
dc.contributor.authorLabadie, Pierre
dc.contributor.authorBudzinski, Helene
dc.contributor.authorMunoz, Gabriel
dc.contributor.authorBustamante, Paco
dc.contributor.authorPolder, Anuschka
dc.contributor.authorGabrielsen, Geir Wing
dc.contributor.authorBustnes, Jan Ove
dc.contributor.authorBorgå, Katrine
dc.date.accessioned2023-03-27T09:20:50Z
dc.date.available2023-03-27T09:20:50Z
dc.date.created2022-04-26T15:36:19Z
dc.date.issued2022
dc.identifier.citationFrontiers in Marine Science. 2022, 9 .en_US
dc.identifier.issn2296-7745
dc.identifier.urihttps://hdl.handle.net/11250/3060526
dc.description.abstractPer and polyfluoroalkyl substances (PFASs) are found in Antarctic wildlife, with high levels in the avian top predator south polar skua (Catharacta maccormicki). As increasing PFAS concentrations were found in the south polar skua during the breeding season in Antarctica, we hypothesised that available prey during the breeding period contributes significantly to the PFAS contamination in skuas. To test this, we compared PFAS in south polar skuas and their main prey from two breeding sites on opposite sides of the Antarctic continent: Antarctic petrel (Thalassoica antarctica) stomach content, eggs, chicks, and adults from Svarthamaren in Dronning Maud Land and Adélie penguin chicks (Pygoscelis adeliae) from Dumont d’Urville in Adélie Land. Of the 22 PFAS analysed, seven were present in the majority of samples, except petrel stomach content [only perfluoroundecanoate (PFUnA) present] and Adélie penguins (only four compounds present), with increasing concentrations from the prey to the skuas. The biomagnification factors (BMFs) were higher at Dumont d’Urville than Svarthamaren. When adjusted to reflect one trophic level difference, the BMFs at Svarthamaren remained the same, whereas the ones at Dumont d’Urville doubled. At both the colonies, the skua PFAS pattern was dominated by perfluorooctanesulfonic acid (PFOS), followed by PFUnA, but differed with the presence of branched PFOS and perfluorotetradecanoate (PFTeA) and lack of perfluorononanoate (PFNA) and perfluorodecanoate (PFDA) at Dumont d’Urville. At Svarthamaren, the pattern in the prey was comparable to the skuas, but with a higher relative contribution of PFTeA in prey. At Dumont d’Urville, the pattern in the prey differed from the skuas, with the domination of PFUnA and the general lack of PFOS in prey. Even though the PFAS levels are low in Antarctic year-round resident prey, the three lines of evidence (pattern, BMF difference, and BMF adjusted to one trophic level) suggest that the Antarctic petrel are the significant source of PFAS in the Svarthamaren skuas, whereas the skuas in Dumont d’Urville have other important sources to PFAS than Adélie penguin, either in the continent or external on the inter-breeding foraging grounds far from Antarctica.
dc.description.abstractBioaccumulation of Per and Polyfluoroalkyl Substances in Antarctic Breeding South Polar Skuas (Catharacta maccormicki) and Their Prey
dc.language.isoengen_US
dc.subjectMiljøgifter
dc.subjectEnvironmental pollution
dc.subjectAntarktis
dc.subjectAntarctica
dc.subjectSjøfugl
dc.subjectSeabirds
dc.titleBioaccumulation of Per and Polyfluoroalkyl Substances in Antarctic Breeding South Polar Skuas (Catharacta maccormicki) and Their Preyen_US
dc.title.alternativeBioaccumulation of Per and Polyfluoroalkyl Substances in Antarctic Breeding South Polar Skuas (Catharacta maccormicki) and Their Preyen_US
dc.typePeer revieweden_US
dc.typeJournal articleen_US
dc.description.versionpublishedVersion
dc.description.versionpublishedVersion
dc.subject.nsiVDP::Økotoksikologi: 489
dc.subject.nsiVDP::Eco-toxicology: 489
dc.source.pagenumber14en_US
dc.source.volume9en_US
dc.source.journalFrontiers in Marine Scienceen_US
dc.identifier.doi10.3389/fmars.2022.819525
dc.identifier.cristin2019262
dc.relation.projectNorges forskningsråd: 243763
dc.relation.projectNILU - Norsk institutt for luftforskning: 114029
dc.relation.projectNorges forskningsråd: 247698
dc.relation.projectKlima- og miljødepartementet: QZA-15/0137
cristin.ispublishedtrue
cristin.fulltextoriginal
cristin.fulltextoriginal
cristin.qualitycode1


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