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Biological manganese removal from acid mine drainage in constructed wetlands and prototype bioreactors

机译:人工湿地和原型生物反应器中酸性矿山排水中的生物锰去除

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Mine drainage waters vary considerably in the range and concentration of heavy metals they contain. Besides iron, manganese is frequently present at elevated concentrations in waters draining both coal and metal mines. Passive treatment systems (aerobic wetlands and compost bioreactors) are designed to remove iron by biologically induced oxidation/ precipitation. Manganese, however, is problematic as it does not readily form sulfidic minerals and requires elevated pH (>8) for abiotic oxidation of Mn (II) to insoluble Mn (IV). As a result, manganese removal in passive remediation systems is often less effective than removal of iron. This was found to be the case at the pilot passive treatment plant (PPTP) constructed to treat water draining the former Wheal Jane tin mine in Cornwall, UK, where effective removal of manganese occurred only in one of the three rock filter components of the composite systems over a 1-year period of monitoring. Water in the two rock filter systems where manganese removal was relatively poor was generally H 5, whereas it was significantly higher (similar topH 7) in the third (effective) system. These differences in water chemistry and manganese removal were due to variable performances in the compost bioreactors that feed the rock filter units in the composite passive systems at Wheal Jane. An alternative approach for removing soluble manganese from mine waters, using fixed bed bioreactors, was developed. Ferromanganese nodules (about 2 cm diameter), collected from an abandoned mine adit in north Wales, were used to inoculate the bioreactors (working volume ca. 700 ml). Following colonization by manganese-oxidizing microbes, the aerated bioreactor catalysed the removal of soluble manganese, via oxidation of Mn (II) and precipitation of the resultant Mn (IV) in the bioreactor, in synthetic media and mine water from the Wheal Jane PPTP. Such an approach has potential application for removing soluble Mn from mine streams and other Mc-contaminated water courses. (C) 2004 Elsevier B.V All rights reserved.
机译:矿井排水中所含重金属的范围和浓度差异很大。除铁外,排干煤炭和金属矿山的水中锰含量也经常升高。被动处理系统(需氧湿地和堆肥生物反应器)旨在通过生物诱导的氧化/沉淀去除铁。然而,锰是有问题的,因为它不易形成硫化矿物,并且需要较高的pH(> 8)才能将Mn(II)非生物氧化为不溶的Mn(IV)。结果,被动修复系统中的锰去除通常不如铁去除。在试验性被动处理厂(PPTP)中发现了这种情况,该厂用于处理英国康沃尔郡前Wheal Jane锡矿的排水问题,该厂仅在复合材料的三个岩石过滤器组件之一中有效去除了锰。系统进行为期1年的监控。在两个除锰能力相对较差的岩石过滤系统中,水的一般pH值小于5,而在第三个(有效)系统中的水含量明显更高(类似于pH值7)。水化学和除锰方面的这些差异是由于堆肥生物反应器性能的变化所致,该堆肥生物反应器向Wheal Jane复合被动系统中的岩石过滤器单元供料。开发了一种使用固定床生物反应器从矿井水中去除可溶性锰的替代方法。从北威尔士的一个废弃矿山收集到的锰铁结核(直径约2厘米)用于接种生物反应器(工作量约700毫升)。在锰氧化微生物定居之后,充气生物反应器通过在生物培养基中的Mn(II)氧化和沉淀的Mn(IV)在合成介质和矿井水中从Wheal Jane PPTP催化去除可溶性锰。这种方法具有潜在的应用潜力,可从矿山溪流和其他受Mc污染的水道中去除可溶性Mn。 (C)2004 Elsevier B.V保留所有权利。

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