Department of Earth & Environmental Sciences, Wright State University, 3640 Colonel Glenn Hwy., Dayton, OH 45435, United States.
Department of Biological Sciences, Kent State University, Kent, OH 44242, United States.
Sci Total Environ. 2015 Nov 1;532:467-73. doi: 10.1016/j.scitotenv.2015.06.025. Epub 2015 Jun 19.
Terrestrial biomass and soils are a primary global reservoir of mercury (Hg) derived from natural and anthropogenic sources; however, relatively little is known about the fate and stability of Hg in the surface soil reservoir and its susceptibility to change as a result of deforestation and cultivation. In southwest Ohio, we measured Hg concentrations in soils of deciduous old- and new-growth forests, as well as fallow grassland and agricultural soils that had once been forested to examine how, over decadal to century time scales, man-made deforestation and cultivation influence Hg mobility from temperate surface soils. Mercury concentrations in surficial soils were significantly greater in the old-growth than new-growth forest, and both forest soils had greater Hg concentrations than cultivated and fallow fields. Differences in Hg:lead ratios between old-growth forest and agricultural topsoils suggest that about half of the Hg lost from deforested and cultivated Ohio soils may have been volatilized and the other half eroded. The estimated mobilization potential of Hg as a result of deforestation was 4.1 mg m(-2), which was proportional to mobilization potentials measured at multiple locations in the Amazon relative to concentrations in forested surface soils. Based on this relationship and an estimate of the global average of Hg concentrations in forested soils, we approximate that about 550 M mol of Hg has been mobilized globally from soil as a result of deforestation during the past two centuries. This estimate is comparable to, if not greater than, the amount of anthropogenic Hg hypothesized by others to have been sequestered by the soil reservoir since Industrialization. Our results suggest that deforestation and soil cultivation are significant anthropogenic processes that exacerbate Hg mobilization from soil and its cycling in the environment.
陆地生物量和土壤是汞(Hg)的主要全球储存库,这些汞来自自然和人为来源;然而,对于 Hg 在表层土壤储层中的命运和稳定性以及由于森林砍伐和耕作而导致其变化的敏感性,人们知之甚少。在俄亥俄州西南部,我们测量了落叶林老林和新林、休耕地和曾经为森林的农业土壤中的 Hg 浓度,以研究在数十年到一个世纪的时间尺度内,人为的森林砍伐和耕作如何影响温带地表土壤中 Hg 的迁移性。与新生长林相比,老生长林的表层土壤中 Hg 浓度显著更高,而森林土壤中的 Hg 浓度均高于耕作和休耕地。老生长林土壤与农业表土之间的 Hg:铅比值差异表明,俄亥俄州森林砍伐和耕作土壤中损失的 Hg 可能有一半已挥发,另一半已侵蚀。由于森林砍伐导致的 Hg 可迁移性的估计值为 4.1mg m(-2),与亚马逊地区多个地点相对于森林地表土壤浓度测量的迁移潜力成正比。基于这种关系以及对森林土壤中 Hg 浓度的全球平均值的估计,我们估计,在过去两个世纪中,由于森林砍伐,全球约有 5500 兆摩尔的 Hg 从土壤中被迁移出来。这一估计与其他人假设的自工业化以来土壤库中封存的人为 Hg 量相当,如果不比其大的话。我们的研究结果表明,森林砍伐和土壤耕作是加剧土壤中 Hg 迁移及其在环境中循环的重要人为过程。