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Arsenic mobility and characterization in lakes impacted by gold ore roasting, Yellowknife, NWT, Canada

机译:受金矿石焙烧影响的湖泊中的砷迁移率和特征,加拿大新南威尔士州耶洛奈夫

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The controls on the mobility and fate of arsenic in lakes impacted by historical gold ore roasting in northern Canada have been examined. A detailed characterization of arsenic solid and aqueous phases in lake waters, lake sediments and sediment porewaters as well as surrounding soils was conducted in three small lakes (200ha) downwind and within 5 km of the historic mining and roasting operations of Giant Mine (Northwest Territories). These lakes are marked by differing limnological characteristics such as area, depth and organic content. Radiometric age-dating shows that the occurrence of arsenic trioxide in lake sediments coincides with the regional onset of roasting activities. Quantification by advanced electron microscopy shows that arsenic trioxide accounts for up to 6 wt% of the total arsenic in sediments. The bulk (80 wt%) of arsenic is contained in the form of secondary sulphide precipitates, with iron oxy-hydroxides hosting a minimal amount of arsenic (1 wt%). Soluble arsenic trioxide particles act as the primary source of arsenic into sediment porewaters. Dissolved arsenic in reducing porewaters both precipitates in-situ as secondary sulphides, and diffuses upwards into the overlying lake waters. Geogenic arsenic phases are present in sediments in low concentrations and are not considered a significant source of arsenic to porewaters or lake waters. Sediment-water interface diffusive flux calculations suggest that the diffusion of dissolved arsenic from porewaters, combined with lake water residence time, are the predominant mechanisms controlling arsenic concentrations in lake waters. (C) 2017 Elsevier Ltd. All rights reserved.
机译:已经研究了加拿大北部历史上金矿焙烧对湖泊中砷的迁移率和命运的控制。在顺风的三个小型湖泊(<200公顷)内以及距巨型矿山(西北部)的历史采矿和焙烧作业不到5公里的范围内,对湖泊水,湖泊沉积物和沉积物孔隙水以及周围土壤中的砷固相和水相进行了详细的表征。地区)。这些湖泊具有不同的湖泊学特征,例如面积,深度和有机物含量。放射性年龄测定法表明,湖泊沉积物中三氧化二砷的发生与区域焙烧活动的发生相吻合。通过高级电子显微镜进行的定量显示,三氧化二砷占沉积物中总砷的6 wt%。大量(> 80 wt%)的砷以二次硫化物沉淀的形式包含,氢氧化铁氢氧化物所含砷量最少(<1 wt%)。可溶性三氧化二砷颗粒是沉积物孔隙水中砷的主要来源。还原孔隙水中溶解的砷既作为二次硫化物原位沉淀,又向上扩散到上覆的湖水中。沉积物中低浓度的成因砷相,不被认为是孔隙水或湖泊水中砷的重要来源。沉积物-水界面扩散通量的计算表明,孔隙水中溶解的砷的扩散与湖泊水的停留时间相结合,是控制湖泊水中砷浓度的主要机制。 (C)2017 Elsevier Ltd.保留所有权利。

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