Research Institute on Mines and Environment (RIME), University of Quebec in Abitibi-Temiscamingue (UQAT), 445 Boul. de l'Université, Rouyn-Noranda, QC, J9X 5E4, Canada.
Environ Sci Pollut Res Int. 2019 Dec;26(35):35588-35601. doi: 10.1007/s11356-019-04608-1. Epub 2019 Mar 22.
Passive systems are often used for the treatment of acid mine drainage (AMD) on closed and abandoned mine sites. Metal-rich residues (solid precipitates) with variable chemical composition and physical properties can be generated. Their characterization is required to better anticipate the potential fate, including stability for disposal, potential recovery, or reuse. The present study evaluated the leaching potential of solids from a laboratory passive multi-step treatment for Fe-rich AMD (2350 ± 330 mg/L Fe, 0.7 ± 0.4 mg/L Ni, 0.2 ± 3.0 mg/L Zn, and 5073 ± 407 mg/L SO, at pH 3.04 ± 0.45). To do so, post-treatment solids from three units (Fe-pretreatment reactor (50% wood chips and 50% wood ash, WA50), passive biochemical reactor, PBR for SO treatment (30% inorganic materials, 70% organic substrate), and polishing reactor (50% calcite and 50% wood chips, C50)) of a pilot laboratory treatment system were sampled. Physicochemical and mineralogical characterization, as well as static leaching tests were then performed. Results showed that all solids had high neutralizing potential, while high inorganic carbon was found in C50. Moreover, high metal concentrations were found in WA50. Metals and sulfates in all solids precipitated in the form of oxyhydroxides, oxy-hydroxy-sulfates, carbonates, sulfides, sulfate, and native sulfur. The Fe was not found as problematic contaminant in solids, but it was in AMD. However, a probable generation of contaminated neutral drainage by Ni and Zn could occur from WA50. The C50 had the highest acid neutralizing capacity and could better resist to acid aggression relative to solids from PBR and WA50. The PBR and C50 solids were considered as non-hazardous towards regulation's limits and a potential co-disposal with municipal wastes could be a storage option. Further studies should be undertaken by testing other leaching and kinetic tests to assess long-term metal stability.
被动系统常用于处理已关闭和废弃矿山场地的酸性矿山排水 (AMD)。会生成具有不同化学成分和物理性质的富金属残渣(固体沉淀物)。需要对其进行特征描述,以更好地预测其潜在命运,包括处置稳定性、潜在回收或再利用。本研究评估了实验室中用于处理富铁 AMD 的多步被动处理后的固体的浸出潜力(2350±330mg/L Fe、0.7±0.4mg/L Ni、0.2±3.0mg/L Zn 和 5073±407mg/L SO,pH 值为 3.04±0.45)。为此,从一个中试实验室处理系统的三个单元(Fe 预处理反应器(50%木屑和 50%木灰,WA50)、被动生化反应器、用于 SO 处理的 PBR(30%无机材料,70%有机基质)和抛光反应器(50%方解石和 50%木屑,C50))中采集了处理后的固体。然后进行了物理化学和矿物学特性分析以及静态浸出试验。结果表明,所有固体都具有很高的中和潜力,而 C50 中则含有高无机碳。此外,WA50 中的金属浓度很高。所有固体中的金属和硫酸盐均以氢氧化物、羟氢硫酸盐、碳酸盐、硫化物、硫酸盐和自然硫的形式沉淀。Fe 不是固体中的问题污染物,但在 AMD 中是。然而,WA50 可能会产生含 Ni 和 Zn 的污染中性排水。C50 的酸中和能力最高,相对于 PBR 和 WA50 的固体,其耐酸侵蚀性更好。PBR 和 C50 固体被认为对法规限制没有危害,与城市废物一起共同处置可能是一种储存选择。应进一步开展其他浸出和动力学试验研究,以评估长期金属稳定性。