U.S. Geological Survey, Forest and Rangeland Ecosystem Science Center, 3200 SW Jefferson Way, Corvallis, OR 97331, USA.
University of Wisconsin La Crosse, River Studies Center, 1725 State Street, La Crosse, WI 54601, USA.
Sci Total Environ. 2016 Oct 15;568:1213-1226. doi: 10.1016/j.scitotenv.2016.05.094. Epub 2016 Jun 16.
Western North America is a region defined by extreme gradients in geomorphology and climate, which support a diverse array of ecological communities and natural resources. The region also has extreme gradients in mercury (Hg) contamination due to a broad distribution of inorganic Hg sources. These diverse Hg sources and a varied landscape create a unique and complex mosaic of ecological risk from Hg impairment associated with differential methylmercury (MeHg) production and bioaccumulation. Understanding the landscape-scale variation in the magnitude and relative importance of processes associated with Hg transport, methylation, and MeHg bioaccumulation requires a multidisciplinary synthesis that transcends small-scale variability. The Western North America Mercury Synthesis compiled, analyzed, and interpreted spatial and temporal patterns and drivers of Hg and MeHg in air, soil, vegetation, sediments, fish, and wildlife across western North America. This collaboration evaluated the potential risk from Hg to fish, and wildlife health, human exposure, and examined resource management activities that influenced the risk of Hg contamination. This paper integrates the key information presented across the individual papers that comprise the synthesis. The compiled information indicates that Hg contamination is widespread, but heterogeneous, across western North America. The storage and transport of inorganic Hg across landscape gradients are largely regulated by climate and land-cover factors such as plant productivity and precipitation. Importantly, there was a striking lack of concordance between pools and sources of inorganic Hg, and MeHg in aquatic food webs. Additionally, water management had a widespread influence on MeHg bioaccumulation in aquatic ecosystems, whereas mining impacts where relatively localized. These results highlight the decoupling of inorganic Hg sources with MeHg production and bioaccumulation. Together the findings indicate that developing efforts to control MeHg production in the West may be particularly beneficial for reducing food web exposure instead of efforts to simply control inorganic Hg sources.
北美西部是一个地貌和气候梯度变化极大的地区,支持着多种多样的生态群落和自然资源。由于无机汞源广泛分布,该地区的汞(Hg)污染也存在极大的梯度变化。这些多样化的汞源和多样化的景观,使得与差异甲基汞(MeHg)产生和生物累积相关的汞损伤的生态风险呈现出独特而复杂的镶嵌模式。要了解与 Hg 输运、甲基化和 MeHg 生物累积相关的过程在规模和相对重要性方面的景观尺度变化,需要超越小尺度变异性的多学科综合。《北美西部汞综合研究》对汞和 MeHg 在空气、土壤、植被、沉积物、鱼类和野生动物中的时空分布模式和驱动因素进行了汇编、分析和解释。该合作评估了汞对鱼类和野生动物健康、人类暴露的潜在风险,并考察了影响 Hg 污染风险的资源管理活动。本文综合了该综合研究中包含的各个论文中提出的关键信息。汇编的信息表明,Hg 污染在北美西部广泛存在,但存在异质性。无机 Hg 在景观梯度上的储存和输运主要受气候和土地覆盖因素(如植物生产力和降水)的调节。重要的是,在水生食物网中,无机 Hg 库和来源与 MeHg 之间存在明显的不一致。此外,水管理对水生生态系统中 MeHg 的生物累积有广泛的影响,而矿业影响相对局限。这些结果突出了无机 Hg 源与 MeHg 产生和生物累积的解耦。这些发现表明,在西部开发控制 MeHg 产生的努力可能特别有利于减少食物网暴露,而不是简单地控制无机 Hg 源。