School of Chemistry and Chemical Engineering, Shanghai University of Engineering Science, Shanghai, 201620, PR China.
Beijing Key Laboratory of Aqueous Typical Pollutants Control and Water Quality Safeguard, School of Environment, Beijing Jiaotong University, Beijing, 10044, China.
Chemosphere. 2023 Oct;338:139388. doi: 10.1016/j.chemosphere.2023.139388. Epub 2023 Jul 7.
Zero-valent iron (ZVI) and modified ZVI have been investigated extensively for groundwater remediation. However, ZVI based powder was difficult to be applied directly as permeable reactive barrier (PRB) materials due to their low water permeability and usage rate. In this study, sulfide iron-copper bimetal was prepared by ball milling, which is environment-friendly without second contamination. The optimal preparation parameters of sulfide iron-copper bimetal for Cr(VI) removal were determined (Cu/Fe ratio (w/w), 0.018; FeS/Fe ratio (w/w), 0.1213; ball milling speed, 450 rpm; ball milling time, 5 h). A composite permeable material was prepared by sintering a mixture of sulfide iron-copper bimetal, sludge, and kaolin. The parameters for composite permeable material preparation including sludge content and particle size, and sintering time were optimized, which were 60%, 60-75 mesh, and 4 h, respectively. The optimal composite permeable material was characterized by SEM-EDS, XRD, and FTIR. The results demonstrated preparation parameters can affect the hydraulic conductivity and hardness of composite permeable material. High sludge content, small particles size, and moderate sintering time resulted in high permeability of composite permeable material and were beneficial for Cr(VI) removal. The dominant Cr(VI) removal mechanism was reduction, and the reaction followed pseudo-first order kinetics. Conversely, low sludge content and large particle size, and long sintering time lead to low permeability of composite permeable material. Chromate removal was mainly by chemisorption following pseudo-second order kinetics. The hydraulic conductivity and hardness of the optimal composite permeable material achieved 1.732 cm/s and 50, respectively. The results of column experiments indicated that its Cr(VI) removal capacity was 0.54 mg/g, 0.39 mg/g and 0.29 mg/g at pH 5, 7 and 9, respectively. The ratio of Cr(VI) to Cr(III) on composite permeable material surface was similar under acidic and alkaline conditions. This study will provide an effective reactive material of PRB for field application.
零价铁(ZVI)和改性 ZVI 已被广泛研究用于地下水修复。然而,由于其低水渗透性和使用率,ZVI 基粉末难以直接用作可渗透反应屏障(PRB)材料。在本研究中,通过球磨制备了环境友好的无二次污染的硫化铁-铜双金属。确定了用于去除 Cr(VI) 的硫化铁-铜双金属的最佳制备参数(Cu/Fe 比(w/w),0.018;FeS/Fe 比(w/w),0.1213;球磨速度,450 rpm;球磨时间,5 h)。通过烧结硫化铁-铜双金属、污泥和高岭土的混合物制备了复合渗透材料。优化了复合渗透材料制备的参数,包括污泥含量和粒径以及烧结时间,分别为 60%、60-75 目和 4 h。最佳复合渗透材料通过 SEM-EDS、XRD 和 FTIR 进行了表征。结果表明,制备参数会影响复合渗透材料的水力传导率和硬度。高污泥含量、小粒径和适度的烧结时间会导致复合渗透材料具有较高的渗透性,有利于 Cr(VI) 的去除。主要的 Cr(VI)去除机制是还原,反应遵循准一级动力学。相反,低污泥含量、大粒径和长烧结时间会导致复合渗透材料的渗透性降低。铬酸盐的去除主要是通过化学吸附遵循准二级动力学。最佳复合渗透材料的水力传导率和硬度分别达到 1.732 cm/s 和 50。柱实验结果表明,其在 pH 5、7 和 9 下的 Cr(VI)去除容量分别为 0.54、0.39 和 0.29 mg/g。在酸性和碱性条件下,复合渗透材料表面的 Cr(VI)与 Cr(III)的比例相似。本研究将为现场应用提供一种有效的 PRB 反应材料。