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铁在碳酸氢盐存在下与过一硫酸盐和过二硫酸盐的反应:铁和碳酸盐自由基阴离子的形成。

Reaction of Fe with Peroxymonosulfate and Peroxydisulfate in the Presence of Bicarbonate: Formation of Fe and Carbonate Radical Anions.

机构信息

Department of Chemical Sciences and The Radical Research Center, Ariel University, Ariel 40700, Israel.

Chemistry Department, Ben-Gurion University, Beer-Sheva 8410501, Israel.

出版信息

Environ Sci Technol. 2023 Apr 25;57(16):6743-6753. doi: 10.1021/acs.est.3c00182. Epub 2023 Apr 12.

DOI:10.1021/acs.est.3c00182
PMID:37050889
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10134498/
Abstract

Many advanced oxidation processes (AOPs) use Fenton-like reactions to degrade organic pollutants by activating peroxymonosulfate (HSO, PMS) or peroxydisulfate (SO, PDS) with Fe(HO) (Fe). This paper presents results on the kinetics and mechanisms of reactions between Fe and PMS or PDS in the absence and presence of bicarbonate (HCO) at different pH. In the absence of HCO, Fe, rather than the commonly assumed SO, is the dominant oxidizing species. Multianalytical methods verified the selective conversion of dimethyl sulfoxide (DMSO) and phenyl methyl sulfoxide (PMSO) to dimethyl sulfone (DMSO) and phenyl methyl sulfone (PMSO), respectively, confirming the generation of Fe by the Fe-PMS/PDS systems without HCO. Significantly, in the presence of environmentally relevant concentrations of HCO, a carbonate radical anion (CO) becomes the dominant reactive species as confirmed by the electron paramagnetic resonance (EPR) analysis. The new findings suggest that the mechanisms of the persulfate-based Fenton-like reactions in natural environments might differ remarkably from those obtained in ideal conditions. Using sulfonamide antibiotics (sulfamethoxazole (SMX) and sulfadimethoxine (SDM)) as model contaminants, our study further demonstrated the different reactivities of Fe and CO in the Fe-PMS/PDS systems. The results shed significant light on advancing the persulfate-based AOPs to oxidize pollutants in natural water.

摘要

许多高级氧化工艺(AOPs)利用芬顿类反应通过激活过一硫酸盐(HSO₅⁻,PMS)或过二硫酸盐(SO₄²⁻,PDS)与 Fe(HO)(Fe)来降解有机污染物。本文介绍了在不同 pH 值下,在不存在和存在碳酸氢盐(HCO₃⁻)的情况下,Fe 与 PMS 或 PDS 之间反应的动力学和机制的结果。在不存在 HCO₃⁻的情况下,Fe 而不是通常假定的 SO₄²⁻是主要的氧化物种。多种分析方法验证了二甲基亚砜(DMSO)和苯甲基亚砜(PMSO)分别选择性转化为二甲基砜(DMSO)和苯甲基砜(PMSO),证实了 Fe-PMS/PDS 体系在没有 HCO₃⁻的情况下生成了 Fe。重要的是,在存在环境相关浓度的 HCO₃⁻的情况下,如电子顺磁共振(EPR)分析所证实的,碳酸根自由基阴离子(CO)成为主要的反应性物质。新发现表明,在自然环境中基于过硫酸盐的类芬顿反应的机制可能与在理想条件下获得的机制有很大的不同。本研究使用磺胺类抗生素(磺胺甲恶唑(SMX)和磺胺二甲氧嘧啶(SDM))作为模型污染物,进一步证明了 Fe 和 CO 在 Fe-PMS/PDS 体系中的不同反应活性。这些结果为推进基于过硫酸盐的 AOPs 以氧化天然水中的污染物提供了重要的启示。

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