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Whole-ecosystem study shows rapid fish-mercury response to changes in mercury deposition

机译:整个生态系统研究表明鱼汞对汞沉积变化的快速反应

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摘要

Methylmercury contamination of fisheries from centuries of industrial atmospheric emissions negatively impacts humans and wildlife worldwide. The response of fish methylmercury concentrations to changes in mercury deposition has been difficult to establish because sediments/soils contain large pools of historical contamination, and many factors in addition to deposition affect fish mercury. To test directly the response of fish contamination to changing mercury deposition, we conducted a whole-ecosystem experiment, increasing the mercury load to a lake and its watershed by the addition of enriched stable mercury isotopes. The isotopes allowed us to distinguish between experimentally applied mercury and mercury already present in the ecosystem and to examine bioaccumulation of mercury deposited to different parts of the watershed. Fish methylmercury concentrations responded rapidly to changes in mercury deposition over the first 3 years of study. Essentially all of the increase in fish methylmercury concentrations came from mercury deposited directly to the lake surface. In contrast, <1% of the mercury isotope deposited to the watershed was exported to the lake. Steady state was not reached within 3 years. Lake mercury isotope concentrations were still rising in lake biota, and watershed mercury isotope exports to the lake were increasing slowly. Therefore, we predict that mercury emissions reductions will yield rapid (years) reductions in fish methylmercury concentrations and will yield concomitant reductions in risk. However, a full response will be delayed by the gradual export of mercury stored in watersheds. The rate of response will vary among lakes depending on the relative surface areas of water and watershed.
机译:数百年来工业大气排放对渔业造成的甲基汞污染,对全世界的人类和野生生物造成了负面影响。鱼类甲基汞浓度对汞沉积变化的响应难以确定,因为沉积物/土壤含有大量的历史污染,除沉积以外,还有许多因素影响鱼类汞。为了直接测试鱼类污染对汞沉积变化的响应,我们进行了整个生态系统实验,通过添加丰富的稳定汞同位素来增加湖泊及其流域的汞负荷。同位素使我们能够区分实验应用的汞和生态系统中已经存在的汞,并检查沉积在流域不同部分的汞的生物蓄积性。在最初的三年研究中,鱼类甲基汞浓度对汞沉积的变化做出了快速响应。鱼类甲基汞浓度的增加基本上全部来自直接沉积在湖面的汞。相反,沉积到流域的汞同位素中只有不到1%出口到了湖泊。 3年内未达到稳定状态。湖泊生物区中的湖泊汞同位素浓度仍在上升,流域向湖泊的汞同位素出口增长缓慢。因此,我们预测减少汞排放将使鱼类甲基汞浓度快速(年)降低,并随之降低风险。但是,由于分水岭中储存的汞的逐步出口,将无法充分响应。湖泊之间的响应速度会有所不同,具体取决于水域和流域的相对表面积。

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