Abstract

Sulfate radical-based advanced oxidation processes (SR-AOPs) show a good prospect for effective elimination of organic contaminants in water due to the powerful oxidation capability and good adaptability of sulfate radical (SO4•−). However, great concerns have been raised on occurrence of the carcinogenic byproduct bromate (BrO3−) in SR-AOPs. The present article aims to provide a critical review on BrO3− formation during bromine (Br)-containing water oxidation by various SR-AOPs. Potential reaction mechanisms are elaborated, mainly involving the sequential oxidation of bromide (Br−) by SO4•− to Br-containing radicals (e.g., bromine atom (Br•)) and then to hypobromous acid/hypobromite (HOBr/OBr−), which acts as the requisite intermediate for BrO3− formation. Some key influencing factors on BrO3− formation are discussed. Particularly, dissolved organic matter (DOM) as a component ubiquitously present in aquatic environments shows a significant suppression effect on BrO3− formation, primarily attributed to the reduction of Br• by DOM to Br−. The reaction of Br• with DOM can hardly produce organic brominated byproducts, while their formation is mainly due to the bromination of HOBr/OBr− generated through nonradical pathways such as the direct reaction of Br− with oxidants (e.g., peroxymonosulfate (PMS)) or other reactive species derived from catalytic activators (e.g., Co(III) in the Co(II)/PMS process). The debromination of brominated pollutants during their oxidation by SO4•− results in the release of Br−, which, however, is not further transformed to BrO3− until coexisting organic matters are mineralized nearly completely. Furthermore, possible strategies for control of BrO3− formation in SR-AOPs as well as the future research needs are proposed.

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