环境科学技术

Fe2+ 激活过硫酸氢钾法降解扑热息痛

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  • 同济大学 污染控制与资源化研究国家重点实验室,上海 200092
关小红(1977-),女,教授,博士生导师,主要从事水污染控制研究. E-mail: guanxh@ tongji. edu. cn

收稿日期: 2014-05-14

  修回日期: 2014-07-14

  网络出版日期: 2015-02-10

基金资助

国家科技重大专项(2012ZX07403-001);住房和城乡建设部研究开发项目(2009-K7-4);国家自然科学基金资助项目(51178321)

Degradation of Acetaminophen by Fe2+ -Activated Peroxymonosulfate Oxidation

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  • State Key Laboratory of Pollution Control and Resource Reuse,Tongji University,Shanghai 200092,China
关小红(1977-),女,教授,博士生导师,主要从事水污染控制研究. E-mail: guanxh@ tongji. edu. cn

Received date: 2014-05-14

  Revised date: 2014-07-14

  Online published: 2015-02-10

Supported by

Supported by the National Science and Technology Major Project (2012ZX07403-001),the Research and Development Project of Ministry of Housing and Urban-Rural Construction of China(2009-K7-4)and the National Natural Science Foundation of China(51178321)

摘要

研究了Fe2+激活过硫酸氢钾(PMS)降解扑热息痛(APAP)的反应.通过考察反应的影响因子、动力学、矿化率及自由基(SO-·4及OH·)确认情况,发现反应分为快速反应阶段和慢速反应阶段,降解反应中PMS与Fe2+浓度比值为1.5∶1时APAP的降解速率最大,最适宜p H值为5.0,反应在较高的PMS及Fe2+投量下可获得55%以上的矿化率.通过电子自旋共振(ESR)检测直接证实:PMS-Fe2+系统降解APAP的反应过程中有SO-·4及OH·的出现,并且对APAP降解起主要作用;反应开始3min左右SO-·4及OH·均出现,随后OH·减少直至消失,SO-·4是慢速反应阶段的主要自由基.

本文引用格式

关小红 辛晓岩 高乃云 谈超群 庄珍珍 . Fe2+ 激活过硫酸氢钾法降解扑热息痛[J]. 华南理工大学学报(自然科学版), 2015 , 43(3) : 137 -142 . DOI: 10.3969/j.issn.1000-565X.2015.03.020

Abstract

This paper deals with the degradation of acetaminophen by Fe2+-activated peroxymonosulfate( PMS) in aqueous solution. By investigating the effect factors,reaction kinetics,mineralization and radical( SO-·4or OH·)identification,two degradation stages,one is fast and the other is slow,are discovered,and an optimal concentration ratio of PMS to Fe2+,namely 1. 5∶1,is determined for achieving the highest degradation rate. Moreover,it is found that the optimal pH value is 5. 0,and that relatively high PMS and Fe2+dosages help achieve a mineralization rate more than 55%. ESR test indicates that SO-·4 and OH·appear in the degradation process and play their important roles; and that SO-·4 and OH·appear after 3 min from the reaction initiation,then the quantity of OH·decreases and then vanishes,so that SO-·4 is the main radical for the slow degradation stage.
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