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Rehabilitation of Mine Tailings by Simultaneous Prevention of Oxidation and Treatment of Acid Effluents Using a Wood-Waste Cover

机译:用木材废物覆盖立即防止氧化和治疗酸污水的康复

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At the East Sullivan site, wood wastes covering the abandoned mine tailings impoundment prevent sulfide oxidation by creating an anoxic environment. The addition of coarse ligneous wastes and their high permeability favour infiltration, resulting in a water table rise that maintains most tailings under water saturation and thus provides an additional protection against sulfide oxidation. Moreover, high infiltration allows a more rapid flushing of acid prone groundwater generated prior to the cover placement, which could cause acid mine drainage over a long period of time. Finally, the pore-waters under the cover are characterised by a strong reducing potential, high alkalinity, and near neutral pHs. These conditions favour sulfate reduction and base metal precipitation as sulfides and as carbonates. Pore-water composition monitored from 1992 to 1998 showed a significant Fe~(2+) decrease, following cover placement. Thereafter, the restoration strategy capitalised on the alkaline and reductive properties of the waters underlying the wood-waste cover. An original treatment of acid effluents, based on the recirculation of water discharging around the impoundment through the organic cover, was implemented. In 2002, the recirculated water from May to October had a mean pumping rate of 240 m~3/h, for a total volume of 800 000 m~3. Data gathered near the dispersal zone from 2000 to 2002 show that despite the recirculation of acid water (pH approx = 3), the pH decreases by only one unit from 7 to 6, during the recirculation period, ie from May to November. However, alkalinity decreases from 800 to 100 mg/L-CaCO_3. Despite this decrease, the alkalinity is back up to 800 mg/L-CaCO_3 the following May, thanks to sulfate reduction. From 2000 to 2002, Fe~(2+) concentration in the pore waters near the dispersal zone is maintained below 2 mg/L. Evolution of surface water quality suggests that the contaminated groundwater flush is completed in the north and north-west area of the impoundment; the east sector is under recovery, while the south sector remains the most problematic. A wood-waste cover, besides limiting sulfide oxidation, can fill the role of alkaline reducing barrier for the treatment of these acidogenic waters, until a balance between acidity and alkalinity in the effluent is reached.
机译:在东部沙利文网站上,木废弃物覆盖废弃的矿山尾矿蓄积,防止硫化物氧化通过产生缺氧环境。添加粗胶质废物及其高渗透性渗透,导致水位上升,在水饱和度下保持大多数尾矿,从而提供额外的硫化物氧化保护。此外,高渗透允许在盖子放置之前产生的酸易发的地下水更快冲洗,这可能在很长一段时间内引起酸性矿井排水。最后,覆盖下的孔隙的特征在于强的还原势,高碱度和近中性pH。这些条件利用硫酸盐还原和碱金属沉淀作为硫化物和碳酸盐。 1992年至1998年监测的孔水组成显示出显着的Fe〜(2+)减少,后续封面。此后,恢复策略大写了木材废盖下面水域的碱性和还原性能。实施了基于通过有机覆盖的蓄水围绕蓄水的排水的再循环的原始处理。 2002年,从5月至10月的再循环水的平均泵率为240m〜3 / h,总体积为800 000 m〜3。从2000〜2002年聚集在分散区附近的数据表明,尽管酸性水(pH约= 3)的再循环,但在再循环期间,即在从5月至11月起,PH将仅在7比6中减少。然而,碱度从800-100mg / l-caco_3降低。尽管如此,由于硫酸盐还原,碱度较高可恢复到下面的800mg / l-caco_3。从2000〜2002,分散区附近的孔隙水中的Fe〜(2+)浓度保持在2mg / L以下。地表水质的演变表明,污染的地区污染的地下水冲洗造成的蓄水区;东部门正在恢复,而南部部门仍然是最有问题的。除了限制硫化物氧化之外,木制废盖可以填充碱性还原屏障的作用,用于治疗这些酸性水域,直到达到流出物中酸度和碱度之间的平衡。

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