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Photolytic degradation of methylmercury enhanced by binding to natural organic ligands

机译:与天然有机配体的结合促进了甲基汞的光解降解

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Methylmercury is a neurotoxin that accumulates in food webs and poses a significant risk to human health. In natural water bodies, methylmercury concentrations remain low due to the degradation of methylmercury into inorganic mercury by sunlight, a process known as photodecomposition. Rates of photodecomposition are relatively rapid in freshwater lakes, and slow in marine waters, but the cause of this difference is not clear. Here, we carry out incubation experiments with artificial freshwater and seawater samples to examine the mechanisms regulating methylmercury photodecomposition. We show that singlet oxygen-a highly reactive form of dissolved oxygen generated by sunlight falling on dissolved organic matterdrives photodecomposition. However, in our experiments the rate of methylmercury degradation depends on the type of methylmercury-binding ligand present in the water. Relatively fast degradation rates (similar to observations in freshwater lakes) were detected when methylmercury species were bound to sulphur-containing ligands such as glutathione and mercaptoacetate. In contrast, methylmercury-chloride complexes, which are the dominant form of methylmercury in marine systems, did not degrade as easily. Our results could help to explain why methylmercury photodecomposition rates are relatively rapid in freshwater lakes and slow in marine waters.
机译:甲基汞是一种神经毒素,会积聚在食物网中,对人体健康构成重大风险。在天然水体中,由于阳光将甲基汞降解为无机汞,因此甲基汞浓度仍然很低,这一过程称为光分解。在淡水湖中,光分解速率相对较快,而在海水中,则较慢,但这种差异的原因尚不清楚。在这里,我们进行人工淡水和海水样品的孵育实验,以研究调节甲基汞光分解的机理。我们表明,单重态氧-一种由溶解在有机物上的日光所产生的溶解氧的高反应性形式会驱动光分解。但是,在我们的实验中,甲基汞的降解速率取决于水中存在的甲基汞结合配体的类型。当甲基汞物种与含硫的配体(如谷胱甘肽和巯基乙酸酯)结合时,检测到相对较快的降解速度(类似于在淡水湖中的观察结果)。相反,甲基汞-氯化物络合物是海洋系统中甲基汞的主要形式,其降解不那么容易。我们的结果可以帮助解释为什么甲基汞的光分解速率在淡水湖泊中相对较快而在海水中相对较慢。

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