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CYANIDE RECOVERY AND DETOXIFICATION STUDY ON SEABRIDGE GOLD'S KSM PROJECT

机译:Seabridge Gold KSM项目中的氰化物回收和排毒研究

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This paper presents results from the proposed cyanide detoxification circuit for Seabridge Gold's KSM project. The proposed flowsheet uses a two-stage CCD (counter-current washing/decantation) circuit to transfer the flotation products CIL(carbon-in-leach) barren solution to a SART process (Sulphidization, Acidification, Recycling of precipitate, and Thickening of precipitate) to recover copper and free cyanide from the copper cyanide complex. The SART barren solution is then treated by an AVR process (Acidification, Volatilization of HCN gas, and Reneutralization) to concentrate the cyanide that was liberated in SART for recycling to leach. The washed CIL barren pulp (the CCD underflow) is treated with the SO_2/Air process to oxidize residual cyanide.The goal of this complex flowsheet is to recover and recycle as much cyanide as possible and produce a final effluent containing less than 0.5 mg/L copper and CN_(WAD) at the lowest cost. The SO_2/air process is capable of achieving low residual CN_(WAD) (<1 mg/L) in the final product, but the persistence of aqueous copper above the target level has been detected in the treated solution in some instances. The expected high concentrations of copper and cyanide in the KSM CIL barren ( >200 mg/L each species) and the difficulties this might create for the SO_2/air process was a key factor in the decision to consider including the washing, SART and AVR steps in the project flowsheet.The target concentrations of CN_(WAD) and Cu were readily achieved after aging the SO_2/air treated pulp, as would occur in a tailing or polishing pond. This suggests no additional treatment will be required to sustain low levels of these species in the final plant effluent.
机译:本文展示了海桥黄金的KSM项目所提出的氰化物解毒电路的结果。所提出的流程使用两阶段CCD(逆流洗涤/倾析)电路来传输浮选产品CIL(碳合浸出)贫液的SART处理(Sulphidization,酸化,沉淀物的回收,和沉淀物的增稠),以从所述铜氰化物络合物中回收铜和游离氰化物。该SART贫液然后通过AVR处理(酸化,HCN的挥发气体,和Reneutralization)处理集中这是在SART释放用于再循环到浸出氰化物。经洗涤的CIL贫瘠纸浆(该CCD下溢)与二氧化硫/空气的方法处理,以氧化该复杂流程的残余cyanide.The目标是回收和再循环尽可能多氰化物作为可能的,并且产生最终的流出物含有少于0.5毫克/ L的铜和CN_(WAD)以最低的成本。的二氧化硫/空气工艺能够在最终产品中实现低的残留CN_(WAD)(<1毫克/升),但铜水溶液的目标水平以上的持久性已在一些情况下,处理过的溶液被检测到。预期的高浓度的铜和氰化物的在KSM CIL贫瘠(> 200mg / L的各种),这可能产生用于SO_2 /空气过程的困难是在考虑包括洗涤,SART和AVR的决定的一个关键因素在CN_(WAD)和Cu的项目flowsheet.The目标浓度的步骤老化SO_2 /空气处理后的纸浆后很容易实现,如将发生在一个拖尾或抛光池塘。这表明没有额外的治疗将需要维持在决赛厂出水这些物种的低水平。

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