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Environmental impacts of unmanaged solid waste at a former base metal mining and ore processing site (Kirkip Greece)

机译:以前的贱金属开采和矿石加工场所未经管理的固体废物对环境的影响(希腊基尔基普)

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The Kirki project aimed to identify, among the mining waste abandoned at a mine and processing plant, the most critical potential pollution sources, the exposed milieus and the main pathways for contamination of a littoral area. This was accompanied by the definition of a monitoring network and remedial options. For this purpose, field analytical methods were extensively used to allow a more precise identification of the source, to draw relevant conceptual models and outline a monitoring network. Data interpretation was based on temporal series and on a geographical model. A classification method for mining waste was established, based on data on pollutant contents and emissions, and their long-term pollution potential. Mining waste present at the Kirki mine and plant sites comprises (A) extraction waste, mainly metal sulfide-rich rocks; (B) processing waste, mainly tailings, with iron and sulfides, sulfates or other species, plus residues of processing reagents; and (C) other waste, comprising leftover processing reagents and Pb-Zn concentrates. Critical toxic species include cadmium and cyanide. The stormy rainfall regime and hilly topography favour the flush release of large amounts of pollutants. The potential impacts and remedial options vary greatly. Type C waste may generate immediate and severe chemical hazards, and should be dealt with urgently by careful removal, as it is localised in a few spots. Type B waste has significant acid mine drainage potential and contains significant amounts of bioavailable heavy metals and metalloids, but they may also be released in solid form into the surface water through dam failure. The most urgent action is thus dams consolidation. Type A waste is by far the most bulky, and it cannot be economically removed. Unfortunately, it is also the most prone to acid mine drainage (seepage pH 1 to 2). This requires neutralisation to prevent acid water accelerating heavy metals and metalloids transfer. All waste management options require the implementation of a monitoring network for the design of a remediation plan, efficiency control, and later, community alert in case of accidental failure of mitigation/remediation measures. A network design strategy based on field measurements, laboratory validation and conceptual models is proposed.
机译:Kirki项目旨在在矿山和加工厂遗弃的采矿废料中找出最关键的潜在污染源,暴露的环境以及污染沿海地区的主要途径。随之而来的是监测网络的定义和补救方案。为此,广泛使用了现场分析方法,以更精确地识别来源,绘制相关的概念模型并概述监测网络。数据解释基于时间序列和地理模型。基于污染物含量和排放量及其长期污染潜力的数据,建立了采矿废物分类方法。 Kirki矿山和工厂现场的采矿废物包括:(A)提取废物,主要是富含金属硫化物的岩石; (二)加工废料,主要是尾矿,含铁,硫化物,硫酸盐或其他物质,加上加工试剂的残留物; (C)其他废物,包括剩余的处理试剂和铅锌精矿。关键有毒物质包括镉和氰化物。暴雨的降雨状况和丘陵地形有利于大量污染物的冲洗释放。潜在的影响和补救方案差异很大。 C型废料可能会造成立即和严重的化学危害,由于其分布在几个地点,因此应通过认真清除进行紧急处理。 B型废物具有巨大的酸性矿山排水潜力,并且含有大量可生物利用的重金属和准金属,但它们也可能通过大坝破坏而以固体形式释放到地表水中。因此,最紧急的行动是大坝加固。迄今为止,A类废物体积最大,无法从经济上清除。不幸的是,它也是最容易发生酸性矿山排水的地方(渗透pH值1至2)。这需要中和,以防止酸性水加速重金属和准金属的转移。所有废物管理选项都需要实施监控网络,以设计补救计划,效率控制,以及在缓解/补救措施意外失败的情况下向社区发出警报。提出了一种基于现场测量,实验室验证和概念模型的网络设计策略。

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