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地下水零价铁(Fe°)活化过二硫酸盐(PDS)体系中 PPCPs 降解的动力学和机制。

Kinetics and mechanisms of the degradation of PPCPs by zero-valent iron (Fe°) activated peroxydisulfate (PDS) system in groundwater.

机构信息

Guangdong Provincial Key Laboratory of Environmental Pollution Control and Remediation Technology, School of Environmental Science and Engineering, Sun Yat-Sen University, Guangzhou 510275, PR China.

School of Environmental Science and Engineering, Zhejiang Gongshang University, Hangzhou, 310018, PR China.

出版信息

J Hazard Mater. 2018 Sep 5;357:207-216. doi: 10.1016/j.jhazmat.2018.06.008. Epub 2018 Jun 3.

DOI:10.1016/j.jhazmat.2018.06.008
PMID:29890417
Abstract

The abatement of pharmaceuticals and personal care products (PPCPs), including carbamazepine (CBZ), acetaminophen (ACP) and sulfamethoxazole (SMX), by zero-valent iron (Fe°) activated peroxydisulfate (PDS) system (Fe°/PDS) in pure water and groundwater was investigated. The removal rates of CBZ, ACP and SMX were 85.4%, 100% and 73.1%, respectively, within 10 min by Fe°/PDS in pure water. SO, OH and O were identified in the Fe°/PDS system, and O was indicated to play an important role in the ACP degradation. The degradation of PPCPs increased with increasing dosages of Fe° and PDS or with decreasing pH and initial PPCP concentrations. Interestingly, the degradation of PPCPs by Fe°/PDS was significantly enhanced in groundwater compared with that in pure water, which was partially attributed to SO and Cl. The first-order constants of CBZ, ACP and SMX increased from 0.021, 0.242 and 0.013 min- to 0.239, 2.536 and 0.259 min, and to 0.172, 1.516 and 0.197 min, respectively, with increasing the concentrations of SO and Cl to 100 mg/L and 10 mg/L, respectively. This study firstly reports the unexpected enhancement of groundwater matrix on the degradation of micropollutants by Fe°/PDS, demonstrating that Fe°/PDS can be an efficient technology for groundwater remediation.

摘要

零价铁(Fe°)活化过二硫酸盐(PDS)体系(Fe°/PDS)去除水中及地下水中药物和个人护理产品(PPCPs),包括卡马西平(CBZ)、对乙酰氨基酚(ACP)和磺胺甲恶唑(SMX)的效能研究。在纯水中,Fe°/PDS 在 10 分钟内分别对 CBZ、ACP 和 SMX 的去除率达到 85.4%、100%和 73.1%。在 Fe°/PDS 体系中鉴定出 SO、OH 和 O,表明 O 在 ACP 降解中起重要作用。随着 Fe°和 PDS 剂量的增加、pH 值的降低和初始 PPCP 浓度的降低,PPCP 的降解率增加。有趣的是,与在纯水中相比,Fe°/PDS 在地下水中对 PPCP 的降解有明显增强,这部分归因于 SO 和 Cl 的存在。CBZ、ACP 和 SMX 的一级反应常数从 0.021、0.242 和 0.013 min-1分别增加到 0.239、2.536 和 0.259 min-1,以及增加到 0.172、1.516 和 0.197 min-1,当 SO 和 Cl 的浓度分别增加到 100 mg/L 和 10 mg/L 时。本研究首次报道了地下水中基质对 Fe°/PDS 降解微量污染物的意外增强作用,证明 Fe°/PDS 可作为地下水修复的有效技术。

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