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Net methylmercury production as a basis for improved risk assessment of mercury-contaminated sediments

机译:甲基汞净产量作为改进对汞污染沉积物风险评估的基础

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Sediments contaminated by various sources of mercury (Hg) were studied at 8 sites in Sweden covering wide ranges of climate, salinity, and sediment types. At all sites, biota (plankton, sediment living organisms, and fish) showed enhanced concentrations of Hg relative to corresponding organisms at nearby reference sites. The key process determining the risk at these sites is the net transformation of inorganic Hg to the highly toxic and bioavailable methylmercury (MeHg). Accordingly, Hg concentrations in Perca fluviatilis were more strongly correlated to MeHg (p < 0.05) than to inorganic Hg concentrations in the sediments. At all sites, except one, concentrations of inorganic Hg (2-55 mu g g(-1)) in sediments were significantly, positively correlated to the concentration of MeHg (4-90 ng g(-1)). The MeHg/Hg ratio (which is assumed to reflect the net production of MeHg normalized to the Hg concentration) varied widely among sites. The highest MeHg/Hg ratios were encountered in loose-fiber sediments situated in southern freshwaters, and the lowest ratios were found in brackish-water sediments and firm, minerogenic sediments at the northernmost freshwater site. This pattern may be explained by an increased MeHg production by methylating bacteria with increasing temperature, availability of energy-rich organic matter (which is correlated with primary production), and availability of neutral Hg sulfides in the sediment pore waters. These factors therefore need to be considered when the risk associated with Hg-contaminated sediments is assessed.
机译:在瑞典的8个地点对被各种汞(Hg)污染的沉积物进行了研究,涵盖了广泛的气候,盐度和沉积物类型。在所有地点,生物区系(浮游生物,沉积生物和鱼类)相对于附近参考地点的相应生物均显示出较高的Hg浓度。确定这些地点风险的关键过程是无机汞净转化为剧毒和可生物利用的甲基汞(MeHg)。因此,Perca fluviatilis中的Hg浓度与MeHg(p <0.05)的相关性比与沉积物中无机Hg浓度的相关性更强。在除一个站点外的所有站点上,沉积物中无机汞的浓度(2-55μg g(-1))均与MeHg的浓度(4-90 ng g(-1))显着正相关。 MeHg / Hg之比(假定反映了归一化为Hg浓度的MeHg的净产量)在站点之间变化很大。 MeHg / Hg比值最高的位于南部淡水的松散纤维沉积物中,最低的比例出现在淡水最北端的咸淡水沉积物和坚硬的成矿沉积物中。可以通过以下方式解释这种模式:甲基化细菌随着温度的升高而甲基汞的产生增加,富含能量的有机物的可用性(与初级生产相关)以及沉积物孔隙水中的中性Hg硫化物的可用性。因此,在评估与汞污染的沉积物相关的风险时,必须考虑这些因素。

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