School of Environment and Energy, Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control, South China University of Technology, Guangzhou, 510006, China.
School of Environment and Energy, Guangdong Provincial Key Laboratory of Atmospheric Environment and Pollution Control, South China University of Technology, Guangzhou, 510006, China; The Key Lab of Pollution Control and Ecosystem Restoration in Industry Clusters, Ministry of Education, Guangzhou, 510006, China; State Key Laboratory of Pulp and Paper Engineering, South China University of Technology, Guangzhou, 510640, China.
Chemosphere. 2019 Oct;233:744-753. doi: 10.1016/j.chemosphere.2019.05.197. Epub 2019 May 25.
In this study, the enhanced effect of pyrite (FeS) on zero-valent iron (Fe) corrosion for arsenic (As) removal was investigated in a combined-Fe/FeS system. The effects of different Fe/FeS composition, dosage and initial pH were evaluated by batch experiments. Results showed that the best combination ratio of Fe:FeS (w/w) was 1:1 and the optimal dosage of mixture was 2.0 g/L. The combination of Fe and FeS in a system significantly enhanced the reactivity of Fe for effective As removal within a broad pH range (3.0-9.0). The effective As removal in the combined-Fe/FeS system was primarily ascribed to being enhanced corrosion of Fe by addition of FeS. SEM and XRD characterizations strongly verified this point. Specifically, the mechanism study (the releases of Fe and total Fe ion, variations of pH values as well as XPS characterization) suggested that FeS in the combined-Fe/FeS system could alleviate the passivation of Fe (pH 3.0-5.0) and accelerate the dissolution of pristine oxide film that coated on Fe surface (pH 6.8-9.0). Besides, FeS in combined-Fe/FeS system could also accelerate the reactions between Fe to O at pH 3.0-9.0. These phenomena were well explained by a galvanic couple between Fe and FeS, where FeS was a cathode and Fe was an anode. Consequently, electrons released from Fe that mediated by FeS to oxide film, passivation layer and O were accelerated in combined-Fe/FeS system and thereby enhanced the corrosion of Fe for efficient As removal. Our findings suggest that utilizing FeS to enhance the corrosion of Fe would be a promising technology for remediation of As-contaminated water.
在这项研究中,研究了在组合-Fe/FeS 系统中黄铁矿 (FeS) 对零价铁 (Fe) 腐蚀去除砷 (As) 的增强作用。通过批量实验评估了不同的 Fe/FeS 组成、用量和初始 pH 的影响。结果表明,Fe:FeS(w/w)的最佳组合比为 1:1,混合物的最佳用量为 2.0g/L。在一个系统中,Fe 和 FeS 的组合在很宽的 pH 范围内(3.0-9.0)显著增强了 Fe 的反应性,从而有效地去除 As。在组合-Fe/FeS 系统中,有效去除 As 的主要原因是添加 FeS 增强了 Fe 的腐蚀。SEM 和 XRD 特性强烈证实了这一点。具体来说,机理研究(Fe 和总 Fe 离子的释放、pH 值的变化以及 XPS 特性)表明,组合-Fe/FeS 系统中的 FeS 可以缓解 Fe 的钝化(pH 3.0-5.0)并加速覆盖在 Fe 表面的原始氧化物膜的溶解(pH 6.8-9.0)。此外,组合-Fe/FeS 系统中的 FeS 还可以加速 pH 为 3.0-9.0 时 Fe 与 O 之间的反应。这些现象很好地解释了 Fe 和 FeS 之间的电偶对,其中 FeS 是阴极,Fe 是阳极。因此,在组合-Fe/FeS 系统中,电子从 Fe 释放出来,通过 FeS 介导到氧化物膜、钝化层和 O 中,从而加速了电子的释放,增强了 Fe 的腐蚀,有效地去除了 As。我们的研究结果表明,利用 FeS 增强 Fe 的腐蚀将是修复受 As 污染水的一种很有前途的技术。