Harris Reed C, Rudd John W M, Amyot Marc, Babiarz Christopher L, Beaty Ken G, Blanchfield Paul J, Bodaly R A, Branfireun Brian A, Gilmour Cynthia C, Graydon Jennifer A, Heyes Andrew, Hintelmann Holger, Hurley James P, Kelly Carol A, Krabbenhoft David P, Lindberg Steve E, Mason Robert P, Paterson Michael J, Podemski Cheryl L, Robinson Art, Sandilands Ken A, Southworth George R, St Louis Vincent L, Tate Michael T
Tetra Tech Inc., 180 Forestwood Drive, Oakville, ON, Canada L6J 4E6.
Proc Natl Acad Sci U S A. 2007 Oct 16;104(42):16586-91. doi: 10.1073/pnas.0704186104. Epub 2007 Sep 27.
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.
几个世纪以来工业大气排放造成的渔业甲基汞污染对全球人类和野生动物产生了负面影响。由于沉积物/土壤中含有大量历史污染物,而且除了沉降之外,还有许多因素会影响鱼类体内的汞含量,因此很难确定鱼类甲基汞浓度对汞沉降变化的响应情况。为了直接测试鱼类污染对不断变化的汞沉降的响应,我们进行了一项全生态系统实验,通过添加富集稳定汞同位素来增加一个湖泊及其流域的汞负荷。这些同位素使我们能够区分实验添加的汞和生态系统中已有的汞,并研究沉降到流域不同部位的汞的生物累积情况。在研究的头三年里,鱼类甲基汞浓度对汞沉降的变化迅速做出了反应。鱼类甲基汞浓度的增加基本上都来自直接沉降到湖面的汞。相比之下,沉降到流域的汞同位素中不到1%输出到了湖泊。三年之内未达到稳态。湖泊生物群中的汞同位素浓度仍在上升,流域汞同位素向湖泊的输出也在缓慢增加。因此,我们预测汞排放的减少将使鱼类甲基汞浓度迅速(数年)降低,并将同时降低风险。然而,由于流域中储存的汞的逐渐输出,全面的响应将被延迟。响应速度在不同湖泊之间会有所不同,这取决于水域和流域的相对表面积。