Superfast degradation of refractory organic contaminants by ozone activated with thiosulfate: Efficiency and mechanisms

被引:29
作者
Yang, Jingxin [1 ]
Luo, Cheng [2 ]
Li, Tingting [3 ]
Cao, Jie [3 ]
Dong, Wenyi [3 ]
Li, Ji [3 ]
Ma, Jun [4 ]
机构
[1] Guangzhou Univ, Inst Environm Res Greater Bay, Key Lab Water Qual & Conservat Pearl River Delta, Minist Educ, Guangzhou 510006, Peoples R China
[2] Zhishi Technol Shenzhen Co Ltd, Xinan St, Shenzhen 518101, Guangdong, Peoples R China
[3] Harbin Inst Technol Shenzhen, Sch Civil & Environm Engn, Shenzhen Key Lab Water Resource Applicat & Enviro, Shenzhen 518055, Peoples R China
[4] Harbin Inst Technol, Sch Environm, State Key Lab Urban Water Resource & Environm, Harbin 150090, Peoples R China
基金
中国国家自然科学基金;
关键词
Ozone; Thiosulfate(S2O32-); Ozonation; Sulfur oxides; Degradation; Refractory organic contaminant; ADVANCED OXIDATION PROCESS; RATE CONSTANTS; BROMATE FORMATION; CATALYTIC OZONATION; HYDROXYL RADICALS; DRINKING-WATER; NATURAL-WATER; INITIAL PHASE; WASTE-WATER; KINETICS;
D O I
10.1016/j.watres.2020.115751
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Thiosulfate (S2O32-) is frequently used as an ozone (O-3) quenching agent when investigating the ozonation of organic contaminants and the kinetics thereof. In this study, however, O-3 is activated by S2O32-, resulting in a superfast degradation of O-3-refractory contaminants. Therefore, the focus of this study is the exploration into the enhancing role of S2O32- in the degradation of refractory organic contaminants by O-3, which has been overlooked thus far. Results obtained from scavenging experiments and electron paramagnetic resonance (EPR) spectra verify that (OH)-O-center dot generated from the reaction of S2O32- with O-3 is mainly responsible for the superfast degradation of O-3-refractory contaminants. The (OH)-O-center dot yield from the O-3/S2O32- process is determined to be 0.216. A plausible mechanism for the generation of (OH)-O-center dot from the O-3/S2O32- process is proposed with the implementation of density functional theory (DFT). Initially, ozone reacts with a sulfur of S2O32- to form OOOSSO32-. The adduct then rearranges to OO(O)SSO32- or HOO(O) SSO32- in the presence of H+, which cleaves to give a sulfoxide radical cation and O-2(center dot-)/HO2 center dot. O-2(center dot-)/HO2 center dot is rapidly transformed into (OH)-O-center dot by O-3 through a series of steps. Degradation efficiency of O-3-refractory contaminants of this process highly depends on the molar ratio of S2O32- and O-3 ([S2O32-]:[O-3]). The optimal [S2O32-]:[O-3] is pH dependent in synthetic water (e.g. 0.3 at pH 7). The presence of bicarbonate inhibits the degradation of refractory contaminants by the O-3/S2O32- process. Humic acid exhibits a slight enhancing effect at low concentrations (0.1-0.2 mg-C/L), and an inhibiting effect at higher concentrations (similar to 0.4 mg-C/L). In addition, the efficacy of the O-3/S2O32- process in real water matrices is also confirmed. (C) 2020 Elsevier Ltd. All rights reserved.
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页数:9
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