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羟基和硫酸盐自由基介导的简单和复杂有机底物降解的对比实验和计算研究。

Comparative Experimental and Computational Studies of Hydroxyl and Sulfate Radical-Mediated Degradation of Simple and Complex Organic Substrates.

机构信息

School of Civil and Environmental Engineering, The University of New South Wales, Sydney, New South Wales 2052, Australia.

Beijing Originwater Technology Co., Ltd, Beijing 102206, China.

出版信息

Environ Sci Technol. 2022 Jun 21;56(12):8819-8832. doi: 10.1021/acs.est.2c00686. Epub 2022 May 13.

DOI:10.1021/acs.est.2c00686
PMID:35549159
Abstract

Persulfate (PS)-based advanced oxidation processes (AOPs) have been promoted as alternatives to HO-based AOPs. To gauge the potential of this technology, the PS/Fe(II) and Fenton (HO/Fe(II)) processes were comparatively evaluated using formate as a simple target compound and nanofiltration concentrate from a municipal wastewater treatment plant as a complex suite of contaminants with the aid of kinetic modeling. In terms of the short-term rate and extent of mineralization of formate and the nanofiltration concentrate, PS/Fe(II) is less effective due to slow Fe(II)/Fe(III) cycling attributable to the scavenging of superoxide by PS. However, in the concentrate treatment, PS/Fe(II) provided a sustained removal of total organic carbon (TOC), with ∼81% removed after 7 days with SO consistently produced via homolysis of the long-life PS. In comparison, HO/Fe(II) exhibited limited TOC removal over ∼57% after 10 h due to the futile consumption of HO by HO. PS/Fe(II) also offers better performance at transforming humic-like moieties to more biodegradable compounds as a result of chlorine radicals formed by the reaction of SO with the matrix constituents present in the concentrate. The application of PS/Fe(II) is, however, subject to the limitations of slow oxidation of organic contaminants, release of sulfate, and formation of chlorinated byproducts.

摘要

过硫酸盐(PS)基高级氧化工艺(AOPs)已被推广为 HO 基 AOPs 的替代品。为了评估该技术的潜力,我们使用甲酸盐作为简单的目标化合物,并借助动力学模型,使用来自城市污水处理厂的纳滤浓缩物作为复杂的污染物套件,对 PS/Fe(II) 和芬顿(HO/Fe(II))工艺进行了比较评估。就甲酸盐和纳滤浓缩物的短期矿化速率和程度而言,由于 PS 对超氧自由基的清除作用导致 Fe(II)/Fe(III) 循环缓慢,PS/Fe(II) 的效果较差。然而,在浓缩物处理中,PS/Fe(II)提供了持续的总有机碳(TOC)去除,经过 7 天处理后,SO 的产生量稳定,TOC 的去除率约为 81%,这是由于 PS 的长寿命均裂产生了 SO。相比之下,由于 HO 的无效消耗,HO/Fe(II)在 10 小时内仅表现出有限的 TOC 去除率,约为 57%。PS/Fe(II)还通过 SO 与浓缩物中存在的基质成分反应形成的氯自由基,将类腐殖质部分转化为更具生物降解性的化合物,从而具有更好的性能。然而,PS/Fe(II)的应用受到有机污染物氧化缓慢、硫酸盐释放和氯化副产物形成的限制。

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