Telmer Kevin, Costa Maycira, Simões Angélica Rômulo, Araujo Eric S, Maurice Yvon
School of Earth and Ocean Sciences, University of Victoria, Victoria, BC, Canada; Instituto de Geociências, University of Campinas, São Paulo, Brazil.
J Environ Manage. 2006 Oct;81(2):101-13. doi: 10.1016/j.jenvman.2005.09.027. Epub 2006 Jul 7.
We present results of mercury (Hg) in surface waters and soils and an analysis of satellite imagery from the Tapajós River basin, Brazilian Amazon, and the Reserva Garimpeira do Tapajós, the legal gold mining district of the basin. Hg bound to suspended sediment was roughly 600 and 200 times the concentration of dissolved Hg per litre of water, in impacted and pristine areas, respectively. Suspended sediments thus represent the major pathway of river-borne Hg. Median concentrations of Hg in suspended load from both impacted and pristine waters were 134 ppb, and 80% of samples were below 300ppb-in the range of naturally occurring surficial materials in the tropics. Regionally, riverine Hg fluxes were proportional to the concentration of total suspended solids. This shows that the dominant source of Hg is the sediment itself rather than anthropogenic mercury discharge from the small-scale mines. To independently test this conclusion, a mass balance was performed. A conservative calculation of the annual export of mercury (Hg) from the Creporí River (a minimum) was 1.6 tonnes for the year 1998-it could be significantly larger. This amount of Hg is difficult to account for by anthropogenic discharge alone, confirming that enhanced physical erosion caused by sluicing and dredging operations is the dominant source of Hg. We therefore conclude that gold mining operations are primarily responsible for elevated Hg concentrations. The dominant source of contamination is not, however, the loss of Hg in the gold amalgamation process. Rather, the disturbance and mobilization of large quantities of Hg-rich sediment and floodplain soil into the water column during mining operations is the source of contamination. These findings shift the focus of remediation and prevention efforts away from Hg control toward soil and sediment erosion control. The minimization or elimination of Hg losses in the mining process remains important for the health of local peoples and environments, but keeping basin soils and sediments in place would be a much more effective means of minimizing Hg fluxes to the region's rivers. To gain a spatial and historical perspective on the source and extent of emissions, satellite imagery was used. We were able to reconstruct historical mining activity, locate impacted areas, and estimate historical Hg fluxes with the imagery. To do so, the spectral characteristics of satellite images were calibrated to the concentration of suspended sediment in the rivers, which, in turn, is proportional to the Hg concentration. This analysis shows that mining-induced sediment plumes have been a dominant source of sediment to the Tapajós River system for decades. As well, the intensity and location of these emissions has varied through time. For example, sediment discharge from the Creporí River was greater in 1985 than in 1998; and the tributaries on the west bank of the Tapajós were actively being mined in 1985 but had been abandoned in 1998. This type of information should greatly assist in understanding original and ongoing sources of emissions, and in managing prevention and remediation efforts.
我们展示了巴西亚马逊州塔帕若斯河流域以及该流域法定黄金开采区塔帕若斯淘金者保护区地表水和土壤中的汞(Hg)含量结果,并对卫星图像进行了分析。在受影响区域和原始区域,与悬浮沉积物结合的汞含量分别约为每升水中溶解汞浓度的600倍和200倍。因此,悬浮沉积物是河流中汞的主要传输途径。受影响水域和原始水域悬浮负荷中的汞中位浓度均为134 ppb,80%的样本低于300 ppb,处于热带地区天然表层物质的范围内。从区域来看,河流汞通量与总悬浮固体浓度成正比。这表明汞的主要来源是沉积物本身,而非小规模矿场的人为汞排放。为独立验证这一结论,我们进行了质量平衡计算。1998年,对克雷波里河(最低值)汞年输出量的保守计算为1.6吨,实际可能更大。仅靠人为排放很难解释这一汞含量,这证实了淘金和疏浚作业造成的物理侵蚀加剧是汞的主要来源。因此,我们得出结论,黄金开采作业是汞浓度升高的主要原因。然而,污染的主要来源并非汞在混汞过程中的损失。相反,采矿作业期间大量富含汞的沉积物和河漫滩土壤被扰动并进入水柱才是污染源。这些发现将修复和预防工作的重点从控制汞转向控制土壤和沉积物侵蚀。在采矿过程中尽量减少或消除汞的损失对于当地居民的健康和环境仍然很重要,但保持流域土壤和沉积物原位不动将是减少汞向该地区河流通量的更有效手段。为了从空间和历史角度了解排放源及排放范围,我们使用了卫星图像。我们能够通过这些图像重建历史采矿活动、定位受影响区域并估算历史汞通量。为此,我们将卫星图像的光谱特征校准为河流中悬浮沉积物的浓度,而悬浮沉积物浓度又与汞浓度成正比。分析表明,数十年来,采矿引发的沉积物羽流一直是塔帕若斯河水系沉积物的主要来源。此外,这些排放的强度和位置随时间而变化。例如,1985年克雷波里河的沉积物排放量比1998年更大;1985年塔帕若斯河西岸的支流在积极开采,但1998年已被废弃。这类信息应能极大地帮助我们理解汞排放的原始和持续来源,并有助于管理预防和修复工作。