Peroxysulfur species-mediated enhanced oxidation of micropollutants by ferrate(VI): Peroxymonosulfate versus peroxydisulfate

被引:2
|
作者
Pi, Ruobing [1 ]
Yang, Zhe [1 ]
Chai, Jin [1 ]
Qi, Yuan [2 ]
Sun, Xuhui [1 ]
Zhou, Yunlong [1 ]
机构
[1] Northeast Elect Power Univ, Sch Chem Engn, Jilin 132012, Peoples R China
[2] Northeast Elect Power Design Inst Co Ltd, China Power Engn Consulting Grp, Changchun 130021, Jilin, Peoples R China
关键词
PMS/Fe(VI); PDS/Fe(VI); Active oxygen species; Intermediate iron; Free radicals; RADICAL GENERATION; AQUEOUS-SOLUTION; WASTE-WATER; DEGRADATION; KINETICS; ACTIVATION; MECHANISM; IRON; CIPROFLOXACIN; REMOVAL;
D O I
10.1016/j.jhazmat.2024.134871
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Many studies have shown that Peroxymonosulfate (PMS) works synergistically with ferrate (Fe(VI)) to remove refractory organic compounds in a few minutes. However, little has been reported on the combined effects of peroxydisulfate (PDS) and Fe(VI). Since PDS is stable and cost effective, it is of practical significance to study the reaction mechanism and conditions of the PDS/Fe(VI) system. The results of the study indicate that the intermediate Fe(II) is formed during the decomposition of Fe(VI), which is then rapidly oxidized. Due to the asymmetry of the PMS molecular structure, PMS can rapidly trap Fe(II) (k PMS/Fe(II) = 3 x 10 4 M-1 center dot s(-1)), whereas PDS cannot (k PDS/Fe(II) = 26 M-1 center dot s(-1)). Hydroxylamine hydrochloride (HA) can reduce Fe(VI) and Fe(III) to Fe(II) to excite PDS to produce SO4 center dot-. Acetate helps to detect Fe(II), but does not help PDS to trap Fe(II). Active species such as SO4 center dot-, center dot OH, 1 O 2 , and Fe(IV), Fe(V) are present in both systems, but in different amounts. In the PMS/Fe (VI) system, all these active species react with ibuprofen (IBP) and degrade IBP within several minutes. The effects of the initial pH, PMS or Fe(VI) dosage, and different amounts of IBP on the removal rate of IBP were investigated. According to the intermediates detected by the GC-MS, the degradation process of IBP includes hydroxylation, demethylation and single bond breakage. The degradation pathways of IBP were proposed. The degradation of IBP in tap water and Songhua River was also investigated. In actual water treatment, the dosage needs to be increased to achieve the same results. This study provides a basis and theoretical support for the application of PMS/Fe(VI) and PDS/Fe(VI) system in water treatment.
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页数:12
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