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氯氧铁非均相催化过氧化氢降解罗丹明B
摘要点击 2293  全文点击 698  投稿时间:2019-03-21  修订日期:2019-06-09
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中文关键词  氯氧铁(FeOCl)  芬顿(Fenton)  羟基自由基(·OH)  非均相催化  罗丹明B
英文关键词  FeOCl  Fenton  ·OH  heterogeneous catalytic  rhodamine B
作者单位E-mail
张少朋 内蒙古大学生态与环境学院, 呼和浩特 010021
中国科学院生态环境研究中心, 中国科学院饮用水科学与技术重点实验室, 北京 100085 
zsp0921@foxmail.com 
陈瑀 中国科学院生态环境研究中心, 中国科学院饮用水科学与技术重点实验室, 北京 100085
中国科学院大学, 北京 100049 
 
白淑琴 内蒙古大学生态与环境学院, 呼和浩特 010021 baishuqin2000@163.com 
刘锐平 中国科学院生态环境研究中心, 中国科学院饮用水科学与技术重点实验室, 北京 100085
中国科学院大学, 北京 100049 
 
中文摘要
      传统芬顿(Fenton)法因反应pH值低、产生大量铁泥等限制其规模化应用.采用化学气相转变法制备氯氧铁(FeOCl)纳米片,选择罗丹明B为模型污染物,研究FeOCl作为类芬顿催化剂催化过氧化氢(H2O2)降解罗丹明B性能.通过扫描电镜(FE-SEM)和X射线衍射光谱(XRD)等表征结果显示,FeOCl晶型结构完整、呈现纳米片状,可充分暴露催化活性位点.罗丹明B降解实验结果表明,H2O2投量为1.67 mmol·L-1时,投加200mg·L-1FeOCl,可使得罗丹明B去除率由15.5%提高至100%(15 min).FeOCl的催化性能随pH升高而降低,初始pH为3、5和7时,反应15 min后罗丹明B去除率分别为100%、100%和84.0%,初始pH提升至9,去除率则显著降低至57.6%.与传统Fenton法比较,FeOCl催化H2O2的pH值范围明显拓展,在弱酸性和中性条件下表现出优良的催化性能.自由基淬灭实验表明,FeOCl/H2O2体系催化降解罗丹明B起主要作用的是羟基自由基(·OH).电子自旋共振波谱仪测定(EPR)结果表明,单独H2O2体系未检测出明显的自由基信号,而投加FeOCl使得·OH信号显著增强,·OH是降解罗丹明B的主要氧化活性物种.
英文摘要
      The wide application of traditional Fenton reactions was firmly restricted by the requirement for harsh acid conditions, as well as the inevitable generation of iron slurry. The FeOCl nanosheets, prepared by the chemical vapor transformation method, were used to degrade RhB via activation of H2O2. The FeOCl was characterized by a field emission scanning electron microscope (FE-SEM) and X-Ray Diffractometer (XRD), the results showed that FeOCl exhibited a fine crystal structure and nanosheet-like morphology, which was favorable for exposure of active sites. The results of degradation experiments showed that the RhB was totally removed within 15 min under the conditions of[H2O2]=1.67 mmol·L-1 and[FeOCl]=200 mg·L-1. The initial pH plays a negative role in RhB degradation, and the initial pH increased from 3 to 7 as the RhB removal efficiency decreased from 100% to 84%. Typically, when the initial pH was 9, the RhB degradation sharply decreased to 57.6%. Compared with traditional Fenton reactions, the FeOCl/H2O2 system widened the pH range, which resulted in superior organics removal even under a mild-acidic to medium pH condition. The quenching experiments demonstrated that the·OH was the major reactive oxygen species. Additionally, Electron Paramagnetic Resonance (EPR) results showed that intense DMPO-HO·signals were detected in the FeOCl/H2O2 system, which further demonstrated the important role of·OH in RhB degradation.

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