Acid Mine Drainage: Sources and Treatment in the United States

J. Skousen, P. Ziemkiewicz, L. McDonald
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Abstract

Acid mine drainage (AMD) occurs when metal sulfides are exposed to oxidizing conditions. Leaching of reaction products into surface waters pollute over 20,000 km of streams in the United States alone. Mining companies must predict the potential of creating AMD by using overburden analyses. Where a potential exists, special handling of overburden materials and quick coverage of acid-producing materials in the backfill should be practiced. The addition of acid-neutralizing materials can reduce or eliminate AMD problems. Placing acid-producing materials under dry barriers can isolate these materials from air and water. Other AMD control technologies being researched include injection of alkaline materials (ashes and limestone) into abandoned underground mines and into buried acid material in mine backfills, remining of abandoned areas, and installation of alkaline recharge trenches. Chemicals used for treating AMD are Ca(OH)2, CaO, NaOH, Na2CO3, and NH3, with each having advantages under certain conditions. Under low-flow situations, all chemicals except Ca(OH)2 are cost effective, whereas at high flow, Ca(OH)2 and CaO are clearly the most cost effective. Floc, the metal hydroxide material collected after treatment, is disposed of in abandoned deep mines, refuse piles, or left in collection ponds. Wetlands remove metals from AMD through formation of oxyhydroxides and sulfides, exchange and organic complexation reactions, and direct plant uptake. Aerobic wetlands are used when water contains enough alkalinity to promote metal precipitation, and anaerobic wetlands are used when alkalinity must be generated by microbial sulfate reduction and limestone dissolution. Anoxic limestone drains are buried trenches of limestone that intercept AMD underground to generate alkalinity. Under anoxia, limestone should not be coated with Fe+3 hydroxides in the drain, which decreases the likelihood of clogging. Vertical flow wetlands pretreat oxygenated AMD with organic matter to remove oxygen and Fe+3, and then the water is introduced into limestone underneath the organic matter. Open limestone channels use limestone in aerobic environments to treat AMD. Coating of limestone occurs, and the reduced limestone dissolution is designed into the treatment system. Alkaline leach beds, containing either limestone or slag, add alkalinity to acid water. At present, most passive systems offer short-term treatment and are more practical for installation on abandoned sites or watershed restoration projects where effluent limits do not apply and where some removal of acid and metals will benefit a stream. Keywords: acid-base accounting; acid-producing material; acid-neutralizing material; alkalinity-producing systems; anoxic limestone drains; chemical treatment; open limestone channels; passive treatment; wetlands
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酸性矿井排水:美国的来源和处理
酸性矿井排水(AMD)发生时,金属硫化物暴露在氧化条件。仅在美国,反应产物渗入地表水就污染了2万多公里的河流。矿业公司必须通过覆盖层分析来预测产生AMD的可能性。如果存在潜在风险,应对覆盖层材料进行特殊处理,并对充填体中的产酸材料进行快速覆盖。加入酸中和材料可以减少或消除AMD问题。将产酸物质置于干燥的屏障下可以使这些物质与空气和水隔绝。正在研究的其他AMD控制技术包括将碱性物质(灰烬和石灰石)注入废弃的地下矿山和矿山回填区的埋藏酸性物质,开采废弃区域,以及安装碱性补给壕。用于治疗AMD的化学物质有Ca(OH)2、CaO、NaOH、Na2CO3和NH3,每种化学物质在一定条件下都具有优势。在低流量情况下,除Ca(OH)2外的所有化学品都具有成本效益,而在高流量情况下,Ca(OH)2和CaO显然是最具成本效益的。絮凝体,即处理后收集的金属氢氧化物材料,被弃置在废弃的深矿、垃圾堆或留在收集池中。湿地通过形成氢氧化物和硫化物、交换和有机络合反应以及直接植物吸收来去除AMD中的金属。当水含有足够的碱度以促进金属沉淀时使用好氧湿地,当必须通过微生物硫酸盐还原和石灰石溶解产生碱度时使用厌氧湿地。缺氧石灰石排水沟是埋在地下的石灰石沟槽,它拦截AMD以产生碱度。在缺氧情况下,石灰石不应在排水管中涂上铁+3氢氧化物,这样可以减少堵塞的可能性。垂直流湿地用有机物对含氧AMD进行预处理,去除氧和铁+3,然后将水引入有机物下面的石灰岩中。开放的石灰石通道在有氧环境中使用石灰石来治疗AMD。发生石灰石涂层,并将石灰石还原溶解设计到处理系统中。含有石灰石或矿渣的碱性浸出床向酸性水中添加碱度。目前,大多数被动系统提供短期处理,更实用的是安装在废弃场地或流域恢复项目上,因为这些地方不适用排放限制,而且一些酸和金属的去除将有利于河流。关键词:酸碱核算;制造酸性物质材料;acid-neutralizing材料;alkalinity-producing系统;缺氧石灰石排水;化学处理;开阔的石灰岩河道;被动治疗;湿地
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