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Geochemical modeling approach to predicting arsenic concentrations in a mine pit lake

机译:地球化学建模方法预测矿坑湖中的砷浓度

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Between 1968 and 1983, the North pit at the Getchell Mine, Humboldt County, NV, filled with water to form a lake. In 1983, water quality data were collected with the following results: As concentrations of 0.29 to 0.59 mg/L, pH of 7.1 to 7.9, SO4- concentrations of 1490 to 1640 mg/L, and TDS of 2394 to 2500 mg/L. Using geochemical modeling techniques presented here, pit lake waters have been theoretically allowed to react for 8.5 a, the approximate time that the North pit had been completely full by 1983. Modeling results predict pH of 7.9 to 8.2, SO4 concentrations of 1503 to 1644 mg/L, TDS of 2054 to 2365 mg/L, and As concentrations ranging from 0.57 in the hypolimnion to 96 mg/L in the epilimnion. In the epilimnion, model results do not match observed As concentrations, suggesting that mechanisms, such as precipitation of arsenate salts or adsorption to mineral surfaces, may control As levels in an actual pit lake system. Adsorption to Fe oxyhydroxide surfaces is questioned by the authors because of the low Fe content in the Getchell system, but adsorption to Al(OH)(3) (gibbsite) and clay mineral surfaces may be important in controlling natural As concentrations. (C) 2000 Elsevier Science Ltd. All rights reserved. [References: 47]
机译:1968年至1983年之间,内华达州洪堡县Getchell矿的北坑充满了水,形成了一个湖泊。 1983年,收集的水质数据得到以下结果:浓度为0.29至0.59 mg / L,pH为7.1至7.9,SO4浓度为1490至1640 mg / L,TDS为2394至2500 mg / L。使用此处介绍的地球化学建模技术,理论上允许矿井湖水反应8.5 a,这是北矿井到1983年完全充满的大致时间。模拟结果预测pH值为7.9至8.2,SO4浓度为1503至1644 mg / L,TDS为2054至2365 mg / L,As浓度范围从次lim烯中的0.57到上lim烯中的96 mg / L。在上等式中,模型结果与观测到的砷浓度不匹配,表明机制(例如砷酸盐的沉淀或对矿物表面的吸附)可能会控制实际坑湖系统中的砷含量。由于Getchell系统中的Fe含量低,作者对羟基氧化铁表面的吸附受到质疑,但是对Al(OH)(3)(菱铁矿)和粘土矿物表面的吸附对于控制天然As的浓度可能很重要。 (C)2000 Elsevier ScienceLtd。保留所有权利。 [参考:47]

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