Modulating oxone-MnOx/silica catalytic systems towards ibuprofen degradation: Insights into system effects, reaction kinetics and mechanisms

过硫酸盐 化学 催化作用 降级(电信) 激进的 水溶液 动力学 电子转移 腐植酸 环境修复 人体净化 无机化学 有机化学 污染 废物管理 工程类 物理 生物 电信 量子力学 计算机科学 肥料 生态学
作者
Jia‐Cheng E. Yang,Baoling Yuan,Haojie Cui,Shaobin Wang,Ming‐Lai Fu
出处
期刊:Applied Catalysis B-environmental [Elsevier BV]
卷期号:205: 327-339 被引量:108
标识
DOI:10.1016/j.apcatb.2016.12.046
摘要

Heterogeneous processes activated persulfate for organic degradation is increasingly recognized as an environmentally important remediation technology. However, manipulating persulfate oxidation processes with desirable decontamination effectiveness is still underdeveloped. Towards this goal, we systematically investigated the catalytic behaviors of Oxone-MnOx/silica systems towards aqueous ibuprofen (IBU) degradation in terms of system effects, reaction kinetics and mechanisms. MnOx/SBA-15 (MS) demonstrated variable catalytic Oxone efficacies towards IBU removal at different solution pHs. Meanwhile, the catalyst supports and FeOx co-doping within MS also produced significant impacts on catalytic Oxone efficacy. Moreover, the catalytic Oxone efficacies of MS for IBU degradation were generally inhibited by humic acid, NO3−, HCO3−, SO42− and PO43− to different extents at low/high levels. Interestingly, Cl− at low concentrations (2 mM) obviously inhibited IBU removal by Oxone-MS, while Cl− at high concentrations (20 mM) greatly enhanced IBU removal. Kinetic studies implied that IBU removal by Oxone-MnOx/silica systems using two first-order kinetic models was closely related to the extents of the interferences of synthetic conditions and water chemistry components. The surface electron transfer between MnOx(OH)y species of MS and HSO5− of Oxone was responsible for the formation of reactive oxygen radicals, thus contributing to IBU degradation. Liquid chromatography–mass spectrometry was employed to identify oxidation products of IBU, and reaction pathways of IBU oxidation were accordingly proposed.

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