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首页> 外文期刊>Environmental Pollution >Bioaccumulation and biomagnification of perfluoroalkyl acids and precursors in East Greenland polar bears and their ringed seal prey
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Bioaccumulation and biomagnification of perfluoroalkyl acids and precursors in East Greenland polar bears and their ringed seal prey

机译:东格陵兰北极熊及其环状海豹捕食者中全氟烷基酸和前体的生物富集和生物放大

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The bioaccumulation and biomagnification of 22 major perfluoroalkyl substances (PFAS) were investigated in tissues of polar bears (Ursus maritimus) and their major prey species, the ringed seal (Pula hispida), from the Scoresby Sound region of East Greenland. In polar bear liver the mean Sigma(13)PFSA (per-fluoroalkyl sulfonic acid) concentration (C-4, C-6, C-8 and C-10) was 2611 +/- 202 ng/g wet weight (ww; 99% perfluorooctane sulfonate (PFOS)) and two orders of magnitude higher than the 20 +/- 3 ng/g ww (89% PFOS) concentration in fat. The mean ERFSAs in seal liver was 111 +/- 5 ng/g ww (98% PFOS) and three orders of magnitude higher relative to the 0.05 +/- 0.01 ng/g ww concentration in blubber (100% perfluorohexane sulfonate). Perfluoro-l-octane sulfonamide (FOSA) was quantifiable in bear (mean 10 +/- 1.4 ng/g ww) and seal (mean 0.6 +/- 0.1 ng/g ww) liver but not in fat or blubber. The mean Sigma 13PFCAs (C4-C 1 9; perfluoroalkyl carboxylic acids) in bear liver (924 +/- 71 ng/g ww) was much greater than in seal liver (74 +/- 6 ng/g ww). In bear fat and seal blubber, the mean Sigma 13PFCAs were 15 +/- 1.9 and 0.9 +/- 0.1 ng/g ww, respectively. Longer chain C(11 )to C-14 PFCAs dominated in bear fat and seal blubber (60-80% of Sigma(13)PFCA), whereas shorter-chain C-9 to C-11 PFCAs dominated in the liver (85-90% of Sigma(13)PFCA). Biomagnification factors (BMFs) were orders of magnitude greater for PFHxS and C-9 to C-13 PFCAs when based on bear liver to seal blubber rather than bear liver to seal liver, and PFCA (C-9 to C-13) BMFs decreased with increasing chain length. Seal blubber to bear liver BMFs better reflects the dietary exposure relationship of PFAS between bears and seals. (C) 2019 Elsevier Ltd. All rights reserved.
机译:在东格陵兰岛的斯科斯比桑德地区,对北极熊(海象)及其主要猎物(环斑海豹)的组织中的22种主要全氟烷基物质(PFAS)进行了生物富集和生物放大。在北极熊肝脏中,平均Sigma(13)PFSA(全氟烷基磺酸)浓度(C-4,C-6,C-8和C-10)为2611 +/- 202 ng / g湿重(ww; 99%的全氟辛烷磺酸盐(PFOS))和脂肪中20 +/- 3 ng / g ww(89%PFOS)的浓度高两个数量级。海豹肝脏中的平均ERFSAs为111 +/- 5 ng / g ww(98%PFOS),相对于润滑脂(100%全氟己烷磺酸盐)中的0.05 +/- 0.01 ng / g ww浓度高三个数量级。在熊(平均10 +/- 1.4 ng / g重量)和密封(平均0.6 +/- 0.1 ng / g重量)的肝脏中,全氟-1-辛烷磺酰胺(FOSA)可定量,但在脂肪或脂肪中则无法定量。熊肝中的平均Sigma 13PFCA(C4-C 1 9;全氟烷基羧酸)(924 +/- 71 ng / g重量)比海豹肝中的平均值(74 +/- 6 ng / g重量)大得多。在熊油脂和海豹油中,西格玛13PFCA的平均值分别为15 +/- 1.9和0.9 +/- 0.1 ng / g ww。较长的C(11)至C-14 PFCA在熊油脂和密封脂中占主导地位(Sigma(13)PFCA的60-80%),而较短的C-9至C-11 PFCA在肝脏中占主导(85- 90%的Sigma(13)PFCA)。当基于熊肝来密封脂肪而不是熊肝来密封肝脏时,PFHxS和C-9至C-13 PFCA的生物放大因子(BMF)会大几个数量级,而PFCA(C-9至C-13)BMF则降低随着链长的增加。海豹脂肪对熊肝的BMFs更好地反映了熊和海豹之间PFAS的饮食接触关系。 (C)2019 Elsevier Ltd.保留所有权利。

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