Leaching of trace metals (Pb, Zn) from contaminated tailings: New insight from a modelling approach

Samuel Mertz, L. Forestier, P. Bataillard, N. Devau
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Abstract

Reclamation measurements are commonly applied to mitigate the leaching of metal pollutants in order to reduce the risk for humans and the environment. Organic and/or inorganic amendments are often recommended to stabilize tailings and to reduce leaching of contaminants. In a recent microcosm percolation experiment (Thouin et al., 2019), the addition of a mining slurry called ochre and manure, either alone or in combination, drastically reduced the leaching of several metal pollutants, notably Pb. Nevertheless, the biogeochemical processes involved in the immobilization of metal pollutants remain unknown, preventing the management of this remediation technique from being optimized and its extension to other sites.  To fill this gap, a multicomponent reactive model was developed to simulate and forecast the impact of amendments on the leaching of metal pollutants. This model accounts for the following biogeochemical processes: kinetically-controlled dissolution and precipitation reactions, sorption reactions (i.e. surface complexation reactions), water-gas interactions and microbially-driven redox reactions with an explicit microbial growth. For all treatments, simulations revealed that Pb reactivity followed dynamic patterns driven by watering steps. The decrease in Pb concentration in the leachates of amended tailings compared to untreated tailings was also accurately reproduced. In untreated tailings, Pb reactivity is mainly controlled by the dissolution of Pb-bearing mineral phases. These reactions were maintained in thermodynamic disequilibrium due to the renewal of pore solution at each watering step. In amended tailings, this pattern was strengthened as the iron oxides contributed by ochre maintained a low Pb concentration in pore solution by sorbing released Pb. Sorption reactions were enhanced by the increase in pH induced by the dissolution of calcium carbonate initially present in ochre. The latter reaction was partially counterbalanced in tailings amended with manure as organic matter provided sufficient energy to fuel microbial aerobic respiration, leading to the release of protons. Pb desorption was promoted by this pH drop. By providing a better understanding of the effect of amendment, this multicomponent reactive model is a powerful tool to optimize the reclamation of tailings, in order to limit contaminant transfer to the environment.

Thouin H. et al. (2019), Appl. Geochem. 111, 104438

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从污染的尾矿中浸出微量金属(铅,锌):从建模方法的新见解
为了减少对人类和环境的风险,通常采用回收措施来减轻金属污染物的浸出。通常建议使用有机和/或无机改良剂来稳定尾矿并减少污染物的浸出。在最近的微观渗滤实验中(Thouin等人,2019),添加一种称为赭石和粪肥的采矿泥浆,无论是单独的还是联合的,都大大减少了几种金属污染物的浸出,尤其是铅。然而,涉及金属污染物固定化的生物地球化学过程仍然未知,这阻碍了这种修复技术的管理得到优化,并将其推广到其他地点。 为了填补这一空白,开发了一个多组分反应模型来模拟和预测修正对金属污染物浸出的影响。该模型考虑了以下生物地球化学过程:动力学控制的溶解和沉淀反应、吸附反应(即表面络合反应)、水气相互作用和微生物驱动的氧化还原反应,并伴有明显的微生物生长。模拟结果显示,在所有处理中,铅的反应性都遵循浇水步骤驱动的动态模式。与未处理的尾矿相比,改性尾矿渗滤液中铅浓度的降低也得到了准确的再现。在未处理的尾矿中,铅的反应性主要受含铅矿物相溶蚀的控制。由于在每个加水步骤中孔隙溶液的更新,这些反应保持在热力学不平衡状态。在修正后的尾矿中,赭石贡献的氧化铁通过吸附释放的铅,使孔隙溶液中的铅浓度保持在较低水平,从而加强了这一规律。最初存在于赭石中的碳酸钙溶解所引起的pH值的增加增强了吸附反应。后一反应在有机肥修饰的尾矿中得到部分平衡,因为有机质为微生物的有氧呼吸提供了足够的能量,导致质子的释放。pH的降低促进了铅的解吸。通过更好地了解修正的效果,这个多组分反应模型是优化尾矿回收以限制污染物向环境转移的有力工具。Thouin H. et al.(2019),苹果。地球化学,2004,23 (4):444 - 444
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