Department of Civil and Resource Engineering, Dalhousie University, 1360 Barrington Street, Halifax, Nova Scotia B3H 4R2, Canada.
Department of Civil and Resource Engineering, Dalhousie University, 1360 Barrington Street, Halifax, Nova Scotia B3H 4R2, Canada.
Water Res. 2015 Nov 15;85:443-50. doi: 10.1016/j.watres.2015.08.056. Epub 2015 Sep 4.
The purpose of this study was to investigate the potential to replace lime with cement kiln dust (CKD) in high density sludge (HDS) treatment of acid mine drainage (AMD). The bench-scale study used two water samples: AMD sampled from a lead-zinc mine with high concentrations of iron (Fe), zinc (Zn), and arsenic (As) (Fe/Zn-AMD) and a synthetic AMD solution (Syn-AMD) spiked with ferric sulfate (Fe2(SO4)3). Arsenic was found to be significantly reduced with CKD-HDS treatment of Fe/Zn-AMD compared to lime-HDS treatment, to concentrations below the stringent mine effluent discharge regulation of 0.10 mg As/L (i.e., 0.04 ± 0.02 mg/L). Both CKD- and lime-HDS treatment of the two AMD samples resulted in settled water Fe concentrations above the stringent discharge guideline of 0.3 mg Fe/L. CKD addition in the HDS process also resulted in high settled water turbidity, above typical discharge guidelines of 15 mg TSS/L. CKD-HDS treatment was found to result in significantly improved settled solids (i.e., sludge) quality compared to that generated in the lime-HDS process. HDS treatment with CKD resulted in 25-88% lower sludge volume indices, 2 to 9 times higher % wet solids, and 10 to 20 times higher % dry solids compared to lime addition. XRD and XPS testing indicated that CKD-HDS sludge consisted of mainly CaCO3 and SiO2 with Fe(3+) precipitates attached at particle surfaces. XRD and XPS testing of the lime-HDS generated sludge showed that it consisted of non-crystalline Fe oxides typical of sludge formed from precipitates with a high water concentration. Increased sedimentation rates were also found for CKD (1.3 cm/s) compared to lime (0.3 cm/s). The increased solids loading with CKD addition compared to lime addition in the HDS process was suggested to both promote surface complexation of metal precipitates with insoluble CKD particles and increase compression effects during Type IV sedimentation. These mechanisms collectively contributed to the reduced water content of CKD-HDS sludge. The results of this study suggest that solids loading is a significant factor in increased sludge density found with the HDS process compared to conventional lime precipitation-sedimentation.
本研究旨在探讨在高浓度污泥(HDS)处理酸性矿山排水(AMD)中用水泥窑灰(CKD)替代石灰的潜力。该台架研究使用了两个水样:一个是来自高铁(Fe)、锌(Zn)和砷(As)浓度的铅锌矿的 AMD(Fe/Zn-AMD),另一个是用硫酸铁(Fe2(SO4)3)掺杂的合成 AMD 溶液(Syn-AMD)。与石灰-HDS 处理相比,CKD-HDS 处理 Fe/Zn-AMD 可显著降低砷浓度,使其低于严格的矿山废水排放规定 0.10mg/L(即 0.04±0.02mg/L)。CKD 和石灰-HDS 处理两种 AMD 样品均导致沉淀水 Fe 浓度高于严格的排放指南 0.3mg/Fe/L。在 HDS 过程中添加 CKD 还会导致沉淀水浊度升高,超过典型的 15mgTSS/L 排放指南。研究发现,与石灰-HDS 工艺相比,CKD-HDS 处理可显著改善沉淀固体(即污泥)的质量。与石灰添加相比,CKD-HDS 处理导致污泥体积指数降低 25-88%,湿固体百分比提高 2-9 倍,干固体百分比提高 10-20 倍。XRD 和 XPS 测试表明,CKD-HDS 污泥主要由 CaCO3 和 SiO2 组成,Fe(3+) 沉淀物附着在颗粒表面。石灰-HDS 生成的污泥的 XRD 和 XPS 测试表明,它由非晶态 Fe 氧化物组成,这是高水浓度沉淀形成的污泥的典型特征。与石灰(0.3cm/s)相比,CKD(1.3cm/s)的沉降速率也有所提高。与石灰相比,在 HDS 过程中添加 CKD 会增加固体负荷,这被认为是促进金属沉淀物与不溶性 CKD 颗粒表面的络合以及增加 IV 型沉降过程中的压缩效应的原因。这些机制共同导致 CKD-HDS 污泥的含水量降低。本研究结果表明,与传统的石灰沉淀-沉降相比,在 HDS 过程中增加固体负荷是导致污泥密度增加的一个重要因素。