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影响河口食物网中持久性有机污染物生物积累的因素。

Factors influencing the bioaccumulation of persistent organic pollutants in food webs of the scheldt estuary.

机构信息

Laboratory of Systemic Physiological and Ecotoxicological Research, Department of Biology, University of Antwerp , Groenenborgerlaan 171, 2020 Antwerp, Belgium.

出版信息

Environ Sci Technol. 2013 Oct 1;47(19):11221-31. doi: 10.1021/es400307s. Epub 2013 Sep 19.

Abstract

Concentrations of several persistent organic pollutants (POPs: PCBs, PBDEs, OCPs) in aquatic species from the Scheldt estuary were related with factors (body size, lipids, trophic position) possibly influencing their bioaccumulation. Stable nitrogen isotope ratios (δ(15)N) were used as a measure for trophic position. A decreasing trend in POP levels toward the sea was observed. For POP concentrations in sediments, this trend could be attributed to a dilution effect from mixing with seawater. However, concentrations in biota more downstream were higher than expected after taking into account the dilution effect, possibly due to differences in bioavailability. Tissue concentrations were correlated with the lipid content in biota, but not with body size. Biomagnification was only significant for some PCB congeners and p,p'-DDE at the most marine sampling location (Terneuzen, L1) and for p,p'-DDD and BDE 100 at the second sampling location (Bath, L2). A significant decreasing relationship was found for γ-HCH concentrations with increasing δ(15)N at Terneuzen. For Antwerpen (L3), no significant relationships were detected. TMFs ranged from 0.64 for γ-HCH up to 1.60 for PCB 194. These results suggest that biomagnification was more important in the marine part of the estuary, although the presence of multiple carbon sources at the freshwater side might have led to an underestimation of the influence of trophic position.

摘要

在斯海尔德河口的水生生物中,几种持久性有机污染物(POPs:多氯联苯、多溴联苯醚、有机氯农药)的浓度与可能影响其生物积累的因素(体型、脂质、营养级)有关。稳定的氮同位素比值(δ(15)N)被用作营养级的衡量标准。从河口到海的方向,POP 水平呈下降趋势。对于沉积物中的 POP 浓度,这种趋势可以归因于与海水混合的稀释效应。然而,在考虑到稀释效应后,下游生物群中的浓度却高于预期,这可能是由于生物利用度的差异。组织浓度与生物体内的脂质含量相关,但与体型无关。生物放大作用仅在最靠海的采样点(特内泽恩,L1)对某些 PCB 同系物和 p,p'-DDE 以及在第二个采样点(巴思,L2)对 p,p'-DDD 和 BDE 100 具有显著影响。在特内泽恩,γ-HCH 浓度与 δ(15)N 的增加呈显著负相关关系。在安特卫普(L3),未检测到显著相关性。总甲基汞(TMF)范围从γ-HCH 的 0.64 到 PCB 194 的 1.60。这些结果表明,生物放大作用在河口的海洋部分更为重要,尽管在淡水侧存在多种碳源可能导致对营养级影响的低估。

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