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GEOCHEMISTRY OF LABORATORY ANOXIC LIMESTONE DRAINS

机译:实验室缺氧石灰石漏斗的地球化学

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An anoxic limestone drain (ALD) is a passive treatment system for treating acid mine drainage (AMD). Historically it has been thought that AMD containing Fe~(3+) and Al~(3+) severely inhibits or stops limestone dissolution due to coating of limestone surfaces by precipitates generated during the neutralization process. Limestone dissolution in field ALDs is difficult to quantify because sampling of the water in ALDs at various locations is not possible, and fluctuations in flow and water chemistry affect limestone dissolution rates. Laboratory experiments were developed to determine the effects of Fe~(3+) and Al~(3+) precipitation on limestone dissolution and the controlling precipitation reactions. Synthetic AMD containing Fe~(3+) or Al~(3+) with and without sulfate was pumped through limestone-packed columns constructed with three sampling ports at equidistant intervals along the column. Water and sediments were periodically extracted for analysis at all sampling ports over a 12-hr period. Results show the majority of milestone dissolution occurred within the first 1.2 hrs of water-limestone contact. Limestone dissolution rate decreased with time and distance along the flow path. Higher concentrations of Fe~(3+) and Al~(3+) (increases in mineral acidity and ionic strength) enhanced limestone dissolution. Geochemical modeling predicted that solutions were nearest equilibrium with respect to the amorphic metal hydroxide phases. Although solutions were periodically oversaturated with respect to sulfate containing minerals, but no x-ray identifiable sulfate minerals were found in the solid phase. The data suggest that smaller anoxic limestone drains may be used when the goal is to neutralize mineral acidity, thus reducing spatial requirements. However, if the goal is to treat AMD to NPDES limits, ALDs may not be a viable long term treatment alternative.
机译:缺氧石灰石排水管(ALD)是用于治疗酸性矿渗流(AMD)的被动处理系统。从历史上看,已经认为含有Fe〜(3+)和Al〜(3+)严重抑制或阻止由于在中和过程中产生的沉淀物的石灰石表面涂覆而抑制或停止石灰石溶解。田间ALD中的石灰石溶解难以量化,因为不可能对各个位置的ALD中的水进行采样,并且流动和水化学的波动影响石灰石溶解率。开发了实验室实验以确定Fe〜(3+)和Al〜(3+)降水对石灰石溶解的影响和控制沉淀反应。含有Fe〜(3+)或Al〜(3+)的合成AMD通过具有在柱等距间隔的三个采样端口构造的石灰石填充柱中泵送。在12小时内,定期提取水和沉积物以分析所有采样端口。结果表明,大部分里程碑溶解发生在水石灰石接触的前1.2小时内。石灰石溶出速率随着时间和沿着流动路径的距离而降低。较高浓度的Fe〜(3+)和Al〜(3+)(矿物酸度和离子强度的增加)增强了石灰石溶解。地球化学建模预测,溶液相对于无形态金属氢氧化物相位最近的均衡。虽然含有含硫酸盐的硫酸盐周期性过饱和溶液,但在固相中没有发现X射线可识别的硫酸盐矿物。数据表明,当目标是中和矿酸性时,可以使用较小的缺氧石灰石排水管,从而降低空间要求。但是,如果目标是将AMD视为NPDES限制,ALD可能不是可行的长期治疗替代方案。

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