首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Influence of hardpan layers on arsenic mobility in historical gold mine tailings
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Influence of hardpan layers on arsenic mobility in historical gold mine tailings

机译:硬壳层对历史金矿尾矿中砷迁移率的影响

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Hardpans, or cemented layers, form by precipitation and cementation of secondary minerals in mine tailings and may act as both physical and chemical barriers. Precipitation of secondary minerals during weathering of tailings can sequester metal(loid)s, thereby limiting their release to the environment. At Montague Gold Mines in Nova Scotia, tailings are partially cemented by the Fe arsenate mineral scorodite (FeAsO_4·2H_2O). Previous studies have shown that the formation of scorodite can effectively limit aqueous As concentrations due to its relatively low solubility (<1mg/L at pH 3-4) and high As content (43-52wt.% As_2O_5, this study). Co-existing waters and solids were sampled at Montague Gold Mines to identify present-day field conditions influencing scorodite precipitation and dissolution, and to better understand the mineralogical and chemical relationship between hardpan and tailings. In addition to scorodite, hardpan cements were found to include amorphous Fe arsenate and Fe oxyhydroxide. Nearly all hardpan is associated with historical arsenopyrite-bearing concentrate which provides a source of acidity, As~(5+) and Fe~(3+) for secondary mineral precipitation. Pore waters sampled from the hardpan have pH values ranging from 2.43 to 7.06. Waters with the lowest pH values also have the highest As concentrations (up to 35.8mg/L) and are associated with the most extensive hardpan and greatest amount of weathered sulfide. Samples from areas with discontinuous hardpan and less sulfide have near-neutral pH and lower As concentrations. Detailed petrographic observations indicate that the identity and stability of As-bearing secondary minerals depends on the continued availability of sulfide concentrate. The results of this study are being used to develop remediation strategies for highly weathered, hardpan-bearing tailings that consider the stability of both primary and secondary minerals under various cover scenarios.
机译:硬顶或胶结层是由矿山尾矿中次生矿物质的沉淀和胶结作用形成的,可作为物理和化学屏障。尾矿风化过程中次生矿物质的沉淀会螯合金属(胶体),从而限制其向环境的释放。在新斯科舍省的蒙塔格金矿,尾矿被砷酸铁矿物臭葱石(FeAsO_4·2H_2O)部分胶结。先前的研究表明,臭葱石的形成由于其相对较低的溶解度(在pH 3-4下<1mg / L)和较高的As含量(43-52wt。%As_2O_5,可以有效地限制As的浓度)。在蒙塔古金矿中对共存的水和固体进行了采样,以发现影响田间臭葱石沉淀和溶解的当今野外条件,并更好地了解硬壳和尾矿之间的矿物学和化学关系。除臭葱石外,发现硬盘水泥还包含无定形砷酸铁和羟基氧化铁。几乎所有的硬地层都与历史悠久的含砷黄铁矿的精矿有关,该精矿为二次矿物沉淀提供了酸性来源As〜(5+)和Fe〜(3+)。从硬盘采样的孔隙水的pH值范围为2.43至7.06。 pH值最低的水也具有最高的As浓度(高达35.8mg / L),并且与最广泛的硬质合金和最多的风化硫化物有关。硬盘不连续且硫化物较少的区域的样品具有接近中性的pH和较低的As浓度。详细的岩石学观察表明,含砷次生矿物的身份和稳定性取决于硫化物精矿的持续供应。这项研究的结果被用于开发针对高风化,含铁锅尾矿的尾矿的治理策略,该尾矿考虑了在各种掩盖情况下主要和次要矿物的稳定性。

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