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富含金属的贫液在酸性矿山废水被动处理中的环境行为。

Environmental behavior of metal-rich residues from the passive treatment of acid mine drainage.

机构信息

Research Institute on Mines and Environment (RIME), University of Québec in Abitibi-Témiscamingue (UQAT), Canada.

Research Institute on Mines and Environment (RIME), University of Québec in Abitibi-Témiscamingue (UQAT), Canada.

出版信息

Sci Total Environ. 2020 Apr 10;712:136541. doi: 10.1016/j.scitotenv.2020.136541. Epub 2020 Jan 7.

Abstract

In closed or abandoned mine sites, passive systems are often used for acid mine drainage (AMD) treatment. They generate metal-rich residues with variable chemical stability, which is rarely reported. The objective of the present study was to evaluate the potential mobility of contaminants (metals and sulfates) from AMD post-treatment residues to better anticipate their fate and enable their proper management. Sampling of a field tri-step passive system, consisting of two passive biochemical reactors (PBR1 and PBR2), separated by a wood ash reactor (WA), implemented in the reclaimed Lorraine mine site, QC, Canada, was carried out. Samples were collected from the inlet (In) and the outlet (Out) of each treatment unit. Physicochemical and mineralogical characterization was performed. The potential mobility of the metals was then assessed via static and kinetic leaching tests. Results showed that all residues had high metal contents (e.g. Fe content >29 g/kg in PBR1-In, > 76 g/kg in WA-In and > 80 g/kg in PBR2-Out). A high residual neutralizing potential was also found in the WA residues (inorganic carbon 6.5%). Native and organic sulfur were found in the PBR2 residues, while Fe-oxyhydroxide (hematite, goethite and magnetite), carbonate and sulfate minerals were present in all residues. According to USEPA regulations, all residues were considered non-hazardous, but Quebec's provincial regulation relative on mining effluents classifies these residues as leachable for some metals, such as Fe, Al, Ni, Zn and Mn. A potential generation of contaminated neutral mine drainage (Al, Ni, Mn and Zn concentrations exceeding criteria) could occur from PBR1 (In & Out) and WA (In & Out) residues. Moreover, the PBR2 residues (In & Out) regenerated AMD rich in Fe and sulfates, especially for PBR2-Out (1 g/L Fe and 6 g/L sulfates). Therefore, all residues were proven to require stabilization prior to their landfill (co-)disposal with municipal waste.

摘要

在封闭或废弃的矿山场地中,通常使用被动系统来处理酸性矿山排水(AMD)。它们生成具有不同化学稳定性的富含金属的残渣,但很少有报道。本研究的目的是评估 AMD 后处理残渣中污染物(金属和硫酸盐)的潜在迁移性,以便更好地预测它们的命运,并对其进行适当的管理。在加拿大魁北克省朗维耶矿区,对由两个被动生化反应器(PBR1 和 PBR2)和一个木灰反应器(WA)组成的现场三步被动系统进行了采样。从每个处理单元的入口(In)和出口(Out)处采集样品。对样品进行了物理化学和矿物学特征分析。然后通过静态和动力学浸出试验评估了金属的潜在迁移性。结果表明,所有残渣都含有高金属含量(例如,PBR1-In 中 Fe 含量>29 g/kg,WA-In 中 Fe 含量>76 g/kg,PBR2-Out 中 Fe 含量>80 g/kg)。WA 残渣中还发现了高残余中和潜力(无机碳 6.5%)。PBR2 残渣中发现了天然和有机硫,而所有残渣中都存在 Fe-氢氧化物(赤铁矿、针铁矿和磁铁矿)、碳酸盐和硫酸盐矿物。根据美国环保署的规定,所有残渣均被认为无危险,但魁北克省关于采矿废水的省级法规将这些残渣归类为某些金属(如 Fe、Al、Ni、Zn 和 Mn)可浸出。PBR1(In 和 Out)和 WA(In 和 Out)残渣可能会产生受污染的中性矿山排水(Al、Ni、Mn 和 Zn 浓度超过标准)。此外,PBR2 残渣(In 和 Out)再生了富含 Fe 和硫酸盐的 AMD,尤其是 PBR2-Out(Fe 含量 1 g/L,硫酸盐含量 6 g/L)。因此,所有残渣在与城市废物一起填埋(共同)处置之前都需要进行稳定化处理。

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