化学
硝基苯
亚硫酸盐
电子顺磁共振
激进的
甲醇
核化学
降级(电信)
六亚甲基四胺
反应机理
氧化还原
无机化学
药物化学
催化作用
有机化学
物理
电信
核磁共振
计算机科学
作者
Hongyu Dong,Guangfeng Wei,Wenjuan Fan,Shangchen Ma,Hongying Zhao,Wei‐xian Zhang,Xiaohong Guan,Timothy J. Strathmann
出处
期刊:Chemosphere
[Elsevier BV]
日期:2017-12-30
卷期号:196: 593-597
被引量:40
标识
DOI:10.1016/j.chemosphere.2017.12.194
摘要
Experimental work was undertaken in this study to re-investigate the mechanisms and active species responsible for oxidation of co-contaminants in the Cr(VI)/HSO3- reaction system. Batch experiments showed that the degradation rates of 4-chlorophenol (4-CP) correlated well with the rates of Cr(VI) reduction by sulfite in the same solutions, and that O2(aq) was necessary for the oxidation of 4-CP. Multiple lines of evidences indicate that Cr(VI)/HSO3- reaction is a SO4--based oxidation process. SO3- was generated in Cr(VI)/HSO3- system based on the electron spin resonance spectra, which could be transformed to secondary radicals (SO4-, SO5-, and HO). The contribution of SO5- was ruled out through almost complete inhibition of methanol (MeOH) on 4-CP degradation. Considering the negligible inhibition of tert-butanol (TBA) on 4-CP degradation, SO4- was identified to be reactive species in Cr(VI)/HSO3- process. This result was further verified by almost no degradation of nitrobenzene and the inhibiting effect of Cl- in Cr(VI)/HSO3- process. This mechanism is beneficial to application of Cr(VI)/HSO3- system in wastewater treatment.
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