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Persistent organic pollutants in bird, fish and invertebrate samples from King George Island, Antarctica

机译:南极乔治王岛鸟类,鱼类和无脊椎动物样本中的持久性有机污染物

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AbstractDespite small direct anthropic/anthropogenic influence, Antarctica cannot be considered out of the reach of pollutants. The present study evaluated the distribution and transfer of the following organic pollutants: PCBs (polychlorinated biphenyls), organochlorine pesticides and PBDEs (polybrominated diphenyl ethers) in invertebrates, fish, bird eggs and liver samples from Admiralty Bay, King George Island, South Shetland Islands. The prevailing compounds were (in ng g-1 wet weight for species averages): PCBs up to 1821 for birds, 6.82 for fish and 41.3 for invertebrates, HCB (hexachlorobenzene) up to 69.8 for birds, 0.66 for fish and 0.56 for invertebrates and DDTs (dichlorodiphenyltrichloroethane) up to 524 for birds, 3.04 for fish and 0.74 for invertebrates. PBDEs (detected only in bird eggs and liver, up to 39.1 and 7.95, respectively) occurred in levels one or two orders of magnitude lower than organochlorines, probably due to the lower and more recent usage of PBDEs. The qualitative profiles of PCBs agree with trophic level and diet data. PBDEs showed small difference in composition when compared to the technical product available in the Americas, especially in endemic species, which could indicate that fractionation does not have a major role for this contaminant group. Trophic level, but also and more importantly, diet, range, ecological niche and “growth dilution” effect explain the variation of pollutants concentrations found in this study.
机译:摘要尽管人类活动/人为活动受到的直接影响很小,但不能将南极洲视为污染物无法触及的地方。本研究评估了南设得兰群岛金钟湾金钟湾无脊椎动物,鱼类,禽蛋和肝脏样本中以下有机污染物的分布和转移:多氯联苯(多氯联苯),有机氯农药和多溴二苯醚(多溴联苯醚) 。占主导地位的化合物是(以物种均值的ng g-1湿重计):鸟类的PCBs最高为1821,鱼类为6.82,无脊椎动物为41.3,HCB(六氯苯)为鸟类,最高为69.8,鱼类为0.66,无脊椎动物为0.56,鸟类的滴滴涕(二氯二苯基三氯乙烷)最高为524,鱼类为3.04,无脊椎动物为0.74。 PBDEs(仅在禽蛋和肝脏中检出,分别高达39.1和7.95)的水平比有机氯低一到两个数量级,这可能是由于PBDEs的使用量减少和更新。多氯联苯的定性概况与营养水平和饮食数据一致。与美洲可用的技术产品相比,多溴二苯醚的成分差异不大,尤其是在地方性物种中,这可能表明分馏对这一污染物类别没有主要作用。营养水平,但更重要的是饮食,范围,生态位和“生长稀释”效应解释了本研究中发现的污染物浓度的变化。

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