Fe3O4/MoS2活化过硫酸氢盐降解水中双酚A研究

李章良1,2,3, 韩婷婷1, 蔡伊婷1

化工新型材料 ›› 2024, Vol. 52 ›› Issue (4) : 190 -196.

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化工新型材料 ›› 2024, Vol. 52 ›› Issue (4) : 190-196. DOI: 10.19817/j.cnki.issn1006-3536.2024.04.036
科学研究

Fe3O4/MoS2活化过硫酸氢盐降解水中双酚A研究

    李章良1,2,3, 韩婷婷1, 蔡伊婷1
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Degradation of bisphenol A in water by Fe3O4/MoS2 activated PMS

  • Li Zhangliang1,2,3, Han Tingting1, Cai Yiting1
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摘要

以MoS2为载体,通过共沉淀法合成了一种新型的Fe3O4/MoS2催化剂,并将其用于活化过硫酸氢盐(PMS)降解双酚A(BPA)。利用X射线衍射仪(XRD)、场发射扫描电子显微镜(SEM)、比表面积分析仪(BET)、傅里叶变换红外光谱(FT-IR)等手段对催化剂的形貌、微观结构进行了表征。研究了不同反应体系对BPA降解效果的影响,探讨了不同影响因素对BPA降解效果的影响。结果表明:Fe3O4/MoS2/PMS反应体系可提高对BPA降解率;当BPA浓度为20mg/L、Fe3O4/MoS2催化剂投加量为1.0g/L、PMS浓度为1mmol/L、pH为6.8、温度为60℃条件下,反应120min时Fe3O4/MoS2对BPA降解率达78.20%。Cl-、HCO-3、H2PO-4对反应体系降解BPA有一定影响,NO-3对BPA的降解影响较小。自由基淬灭实验表明,·OH、1O2、和·O-2均发挥了作用,其中 1O2和·O-2起主要作用。

Abstract

A novel Fe3O4/MoS2 catalyst was successfully synthesized by coprecipitation method using MoS2 as a carrier,and was used for the degradation of bisphenol A (BPA) by activated persulfate (PMS).The morphology and microstructure of the catalyst were characterized by X-ray diffraction instrument (XRD),field emission scanning electron microscope (SEM),specific surface area analyzer (BET) and Fourier transform infrared spectroscopy (FT-IR).The effects of different reaction systems on the effect of BPA degradation were investigated,and the influence of different factors on the degradation effect of BPA was explored.The results showed that the Fe3O4/MoS2/PMS reaction system could improve the degradation rate of BPA.When the concentration of BPA was 20mg/L,the catalyst Fe3O4/MoS2 dosage was 1.0g/L,the PMS concentration was 1.0mmol/L,the pH was 6.8,and the temperature was 60℃,the degradation rate of BPA by Fe3O4/MoS2 could reach up to 78.20% after 120min.The presence of Cl-,HCO-3 and H2PO-4 had certain effects on the degradation of BPA in the reaction system,while NO-3 had less effect on the degradation of BPA.Free radical quenching experiments indicated that ·OH,1O2,and ·O-2 all played roles,of which 1O2 and ·O-2 played major roles.

关键词

四氧化三铁 / 二硫化钼 / 过硫酸氢盐 / 双酚A / 降解

Key words

Fe3O4 / molybdenum disulfide / PMS / bisphenol A / degradation

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引用格式 ▾
Fe3O4/MoS2活化过硫酸氢盐降解水中双酚A研究[J]. 化工新型材料, 2024, 52(4): 190-196 DOI:10.19817/j.cnki.issn1006-3536.2024.04.036

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参考文献

[1] 马婷婷.高级催化氧化技术处理工业废水研究[D].兰州:兰州大学,2015.
[2] 孙芳.过硫酸盐高级氧化技术的研究进展[J].辽宁化工,2023,52(1):141-143.
[3] 敖韩,何辉超,田浩,等.高级氧化技术处理难降解有机废水研究进展[J].云南化工,2022,49(12):9-12.
[4] 王肖磊.过渡金属化合物活化单过硫酸盐降解有机污染物的机制研究[D].安庆:安庆师范大学,2020.
[5] 郑琴琴,闵中芳,李吉平,等.活化过硫酸盐高级氧化技术降解水中抗生素的研究进展[J].化工环保,2021,41(6):678-687.
[6] Ding Y B,Pan C,Peng X Q,et al.Deep mineralization of bisphenol A by catalytic peroxymonosulfate activation with nano CuO/Fe3O4 with strong Cu-Fe interaction[J].Chemical Engineering Journal,2020,384:123378.
[7] 付明翔,张丽,刘东方,等.CoMgFe-LDO活化过一硫酸盐降解双酚A的性能研究[J].水处理技术,2023,49(3):53-58.
[8] 林尤强.过硫酸盐活化高级氧化技术在废水处理中的应用[D].长春:长春理工大学,2020.
[9] Li J,Wan Y J,Li Y J,et al.Surface Fe(Ⅲ)/Fe(Ⅱ) cycle promoted the degradation of atrazine by peroxymonosulfate activation in the presence of hydroxylamine[J].Applied Catalysis B:Environmental,2019,256:117782.
[10] Tan C Q,Gao N Y,Deng Y,et al.Radical induced degradation of acetaminophen with Fe3O4 magnetic nanoparticles as heterogeneous activator of peroxymonosulfate[J].Journal of Hazardous Materials,2014,276:452-460.
[11] 郭玉拓.二硫化钼的表面和界面的研究与应用[D].北京:中国科学院大学(中国科学院物理研究所),2022.
[12] 李怡芳.双酚A催化剂新技术研究及进展[J].炼油与化工,2022,33(4):4-6.
[13] 王颖,徐定华.双酚A的检测方法研究进展概述[J].计量科学与技术,2022,66(6):49-53,44.
[14] 徐浩,汤荣华.环境中双酚A检测和降解处理[C].天津:中国环境科学学会2021年科学技术年会,2021.
[15] Cheng J S,Han L,Wei Y,et al.Enhancement of photocatalytic property on ZnS/MoS2 composite under visible light irradiation[J].MATEC Web of Conferences,2017,108:1008.
[16] 范顶,王黎明,徐丽慧,等.ZnFe2O4/TiO2复合材料的表征及其光催化性能研究[J].化工新型材料,2023,51(7):298-302.
[17] Wang Y,Li S K,Xing X R,et al.Self-assembled 3D flowerlike hierarchical Fe3O4@Bi2O3 core-shell architectures and their enhanced photocatalytic activity under visible light[J].Chemisitry-A European Journal,2011,17:4802-4808.
[18] 刘赛.几类基于Fe3O4@SiO2核壳结构复合材料固载钯催化剂的制备、表征及性能研究[D].郑州:郑州大学,2020.
[19] 邢孟孟.g-C3N4复合材料的制备、表征及应用研究[D].合肥:合肥工业大学,2021.
[20] 陈文凯,曹宇,赵焕新,等.MnOOH@g-C3N4的制备及其活化PMS降解苯酚的研究[J].化学试剂,2022,44(10):1491-1499.
[21] 李曾志强.双金属MOF及其复合材料活化过硫酸盐去除有机污染物的研究[D].南宁:广西大学,2022.
[22] 张政煜.Co基非均相催化剂活化PMS去除有机污染物的进展[J].广州化学,2022,47(5):9-17.
[23] Wang Y J,Dong X.PMS activation by natural pyrite for APAP degradation:Underlying mechanism and long-term removal of APAP[J].Catalysis Communications,2023,177:106661.
[24] 刘玲玲.金属有机框架衍生铁钴氧化物活化过硫酸盐降解水中环丙沙星研究[D].重庆:重庆交通大学,2022.
[25] Liu J,Zhao Z W,Shao P H,et al.Activation of peroxymonosulfate with magnetic Fe3O4-MnO2 core-shell nanocomposites for 4-chlorophenol degradation[J].Chemical Engineering Journal,2015,262:854-861.
[26] 马红芳,杨浩宇,陈思颖,等.NTA强化Fe(Ⅱ)/PMS体系降解橙黄G的效能与机制[J].华侨大学学报(自然科学版),2023,44(2):222-232.
[27] Ung-Jin K,Satoshi K,Masahisa W.Highly enhanced adsorption of Congo red onto dialdehyde cellulose-crosslinked cellulose-chitosan foam[J].Carbohydrate Polymers,2019,214:294-302.
[28] 王盟,李硕,郑禾山,等.Ag掺杂Co3O4催化活化过硫酸盐降解双酚A研究[J].齐齐哈尔大学学报(自然科学版),2023,39(2):83-94.
[29] 王雪如,丁耀彬,唐和清.CuO/Fe3O4活化过一硫酸盐降解RhB[J].武汉工程大学学报,2018,40(3):273-278.
[30] Feng Y,Liu J H,Wu D L,et al.Efficient degradation of sulfamethazine with CuCo2O4 spinel nanocatalysts for peroxymonosulfate activation[J].Chemical Engineering Journal,2015,280:514-524.

基金资助

福建省自然科学基金项目(2020J01912);福建省大学生创新创业训练计划(S202211498025)

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