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废弃前基本金属矿区和矿石加工厂(希腊基尔基)的未管理固体废物的环境影响。

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

机构信息

Institute of Geology and Mineral Exploration (IGME), Acharnai, Greece.

出版信息

Waste Manag Res. 2010 Nov;28(11):996-1009. doi: 10.1177/0734242X10375746. Epub 2010 Jul 21.

Abstract

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.

摘要

基尔基项目旨在确定废弃在矿山和加工厂的采矿废物中最关键的潜在污染源、暴露环境和污染沿海地区的主要途径。同时还确定了一个监测网络和补救方案。为此,广泛使用现场分析方法,以更准确地确定污染源,绘制相关概念模型,并制定监测网络。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及其长期污染潜力,建立了一种采矿废物分类方法。基尔基矿山和工厂场地的采矿废物包括:(A) 开采废物,主要是富含金属硫化物的岩石;(B) 加工废物,主要是尾矿,含有铁和硫化物、硫酸盐或其他物质,以及加工试剂的残留物;(C) 其他废物,包括剩余的加工试剂和铅锌精矿。关键有毒物质包括镉和氰化物。暴风雨的降雨模式和丘陵地形有利于大量污染物的冲洗释放。潜在影响和补救方案差异很大。C 类废物可能会立即产生严重的化学危害,应立即小心清除,因为它只集中在少数几个地方。B 类废物有很大的酸性矿山排水潜力,含有大量可利用的重金属和类金属,但也可能通过大坝失事以固体形式释放到地表水。因此,最紧迫的行动是大坝加固。A 类废物是迄今为止最庞大的,而且无法经济地清除。不幸的是,它也是最容易发生酸性矿山排水(渗漏 pH 值为 1 到 2)的。这需要中和处理,以防止酸性水加速重金属和类金属的转移。所有废物管理选项都需要实施监测网络,以设计补救计划、控制效率,并在缓解/补救措施意外失效时提醒社区。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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