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与酸性矿山排水污染溪流中重金属衰减相关的水文地球化学和矿物学特征:以中国大宝山矿为例。

Hydrogeochemical and mineralogical characteristics related to heavy metal attenuation in a stream polluted by acid mine drainage: a case study in Dabaoshan Mine, China.

机构信息

School of Environmental Science and Engineering, Sun Yat-Sen University, Guangzhou 510275, China.

出版信息

J Environ Sci (China). 2012;24(6):979-89. doi: 10.1016/s1001-0742(11)60868-1.

Abstract

Dabaoshan Mine, the largest mine in south China, has been developed since the 1970s. Acid mine drainage (AMD) discharged from the mine has caused severe environmental pollution and human health problems. In this article, chemical characteristics, mineralogy of ocher precipitations and heavy metal attenuation in the AMD are discussed based on physicochemical analysis, mineral analysis, sequential extraction experiments and hydrogeochemistry. The AMD chemical characteristics were determined from the initialwater composition, water-rock interactions and dissolved sulfide minerals in the mine tailings. The waters, affected and unaffected by AMD, were Ca-SO4 and Ca-HCO3 types, respectively. The affected water had a low pH, high SO4(2-) and high heavy metal content and oxidation as determined by the Fe2+/Fe3+ couple. Heavy metal and SO4(2-) contents of Hengshi River water decreased, while pH increased, downstream. Schwertmannite was the major mineral at the waste dump, while goethite and quartz were dominant at the tailings dam and streambed. Schwertmannite was transformed into goethite at the tailings dam and streambed. The sulfate ions of the secondary minerals changed from bidentate- to monodentate-complexes downstream. Fe-Mn oxide phases of Zn, Cd and Pb in sediments increased downstream. However, organic matter complexes of Cu in sediments increased further away from the tailings. Fe3+ mineral precipitates and transformations controlled the AMD water chemistry.

摘要

大宝山矿是华南最大的矿山,自 20 世纪 70 年代开始开发。矿山排放的酸性矿山排水(AMD)造成了严重的环境污染和人类健康问题。本文通过理化分析、矿物分析、连续提取实验和水文地球化学,讨论了 AMD 中的化学特征、赭石沉淀的矿物学和重金属衰减。AMD 的化学特征取决于初始水成分、水岩相互作用和矿渣中溶解的硫化物矿物。受 AMD 影响和不受 AMD 影响的水分别为 Ca-SO4 和 Ca-HCO3 型。受影响的水具有低 pH 值、高 SO4(2-) 和高重金属含量以及 Fe2+/Fe3+ 对确定的氧化作用。恒石河水中的重金属和 SO4(2-)含量下降,而 pH 值则升高。尾矿堆中的主要矿物为水铁矿,尾矿坝和河床中的主要矿物为针铁矿和石英。尾矿坝和河床中的水铁矿发生了向针铁矿的转化。次生矿物中的硫酸根离子从双齿配合物向单齿配合物转化。沉积物中 Zn、Cd 和 Pb 的 Fe-Mn 氧化物相增加。然而,沉积物中 Cu 的有机络合物在远离尾矿的地方进一步增加。Fe3+ 矿物沉淀和转化控制了 AMD 水化学。

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