Halides and natural organic matter (NOM) are inevitable in aquatic environment and influence the degradation of contaminants in sulfate radical (SO 4 •– )-based advanced oxidation processes. This study investigated the formation of chlorate in the coexposure of SO 4 •–, chloride (Cl – ), bromide (Br – ) and/or NOM in UV/persulfate (UV/PDS) and cobalt(II)/peroxymonosulfate (Co/PMS) systems. The formation of chlorate increased with increasing Cl – concentration in the UV/PDS system, however, in the Co/PMS system, it initially increased and then decreased. The chlorate formation involved the formation of hypochlorous acid/hypochlorite (HOCl/OCl – ) as an intermediate in both systems. The formation was primarily attributable to SO 4 •– in the UV/PDS system, whereas Co(III) played a significant role in the oxidation of Cl – to HOCl/OCl – and SO 4 •– was important for the oxidation of HOCl/OCl – to chlorate in the Co/PMS system. The pseudo-first-order rate constants ( k′ ) of the transformation from Cl – to HOCl/OCl – were 3.32 × 10 –6 s –1 and 9.23 × 10 –3 s –1 in UV/PDS and Co/PMS, respectively. Meanwhile, k′ of HOCl/OCl – to chlorate in UV/PDS and Co/PMS were 2.43 × 10 –3 s –1 and 2.70 × 10 –4 s –1, respectively. Br – completely inhibited the chlorate formation in UV/PDS, but inhibited it by 45.2% in Co/PMS. The k′ of SO 4 •– reacting with Br – to form hypobromous acid/hypobromite (HOBr/OBr – ) was calculated to be 378 times higher than that of Cl – to HOCl/OCl –, but the k′ of Co(III) reacting with Br – to form HOBr/OBr – was comparable to that of Cl – to HOCl/OCl – . NOM also significantly inhibited the chlorate formation, due to the consumption of SO 4 •– and reactive chlorine species (RCS, such as Cl ·, ClO · and HOCl/OCl – ). This study demonstrated the formation of chlorate in SO 4 •– -based AOPs, which should to be considered in their application in water treatment.
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Hou et al. (2018) studied this question.
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