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摘要
以焙烧、酸浸改性后的高岭土作为非均相芬顿(Fenton)催化剂的载体,采用共沉淀法制得高岭土-三氧化二铁(Fe2O3)/二氧化锰(MnO2)非均相Fenton催化剂,并于高岭土-Fe2O3/MnO2、紫外光、过氧化氢(H2O2)的反应体系中高效降解罗丹明B(RhB)染料废水。利用X射线荧光光谱分析(XRF)、X射线衍射(XRD)、扫描电子显微镜(SEM)、能谱分析仪(EDS)以及X射线光电子能谱(XPS)对催化剂的结构和化学组成进行了表征。研究结果表明:在高岭土-Fe2O3/MnO2用量为0.1g/L,反应温度25℃,H2O2用量为10.0mmol/L,溶液初始pH=3.0,RhB初始浓度为90.0mg/L,反应30min条件下,RhB的脱色率达到99.12%,运用一级动力学方程对反应过程进行拟合,R2=0.99,速率常数为0.159min-1。
Abstract
Kaolin was modified by roasting and acid leaching,and the modified kaolin was used as a supporter of heterogeneous Fenton catalyst.The kaolin-Fe2O3/MnO2 heterogeneous Fenton catalyst was prepared by coprecipitation method,and rhodamine B(RhB) dye in wastewater was degraded efficiently in the reaction system of kaolin-Fe2O3/MnO2,UV and H2O2.The chemical composition and structural characterization of catalyst was analyzed by X-ray fluorescence spectrometry(XRF),X-ray powder diffraction(XRD),scanning electron microscopy(SEM),energy dispersive spectrometry(EDS) and X-ray photoelectron spectroscopy(XPS).The results showed that the decolorization rate of RhB was 99.12% under agitation after 30min treatment with dosage of kaolin-Fe2O3/MnO2 0.1g/L,reaction temperature 25℃,dosage of H2O2 10.0mmol/L,pH of 3.0 and initial concentration of RhB 90.0mg/L.The first-order kinetic equation was used to fit the reaction process and the rate constant was 0.159min-1,R2=0.99.
关键词
高岭土
/
降解
/
非均相Fenton
/
催化剂
/
废水
Key words
kaolin
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degradation
/
heterogeneous Fenton
/
catalyst
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wastewater
改性高岭土基非均相Fenton催化剂降解罗丹明B染料废水的研究[J].
化工新型材料, 2018, 46(11): 208-211 DOI:
[1] 李双菊,毕彩丰,范玉华,等.宽pH范围的类Fenton纤维催化剂降解罗丹明B的研究[J].化工新型材料,2017,45(2):168-170.
[2] Pilli S,More T T,Yan S,et al.Fenton pre-treatment of secondary sludge to enhance anaerobic digestion:energy balance and greenhouse gas emissions[J].Chemical Engineering Journal,2016,283(1):285-292.
[3] Liu Y,Zhang G,Fang S,et al.Degradation of aniline by heterogeneous Fenton's reaction using a Ni-Fe oxalate complex catalyst[J].Journal of Environmental Management,2016,182(1):367-373.
[4] Liu Y,Yu Z,Hou Y,et al.Highly efficient Pd-Fe/Ni foam as heterogeneous Fenton catalysts for the three-dimensional electrode system[J].Catalysis Communications,2016,86(5):63-66.
[5] 袁建军,杨柳,郑经堂,等.新型非均相炭基Fenton催化剂可见光降解甲基橙的研究[J].化工新型材料,2014,42(7):163-165.
[6] Guo S,Zhang G,Wang J.Photo-Fenton degradation of rhodamine B using Fe2O3-kaolin as heterogeneous catalyst:characterization,process optimization and mechanism[J].Journal of Colloid & Interface Science,2014,433(11):1-8.
[7] Wang N,Zheng T,Zhang G,et al.A review on Fenton-like processes for organic wastewater treatment[J].Journal of Environmental Chemical Engineering,2015,4(1):762-787.
[8] 陆银平,邢学玲,刘钦甫.不同产地煤系高岭土的矿物学特征及插层复合物的制备[J].岩石矿物学杂志,2014,33(3):561-566.
[9] 陆银平,刘钦甫,张玉德,等.改性纳米高岭土的制备及特性研究[J].矿物岩石,2008,28(4):43-46.
[10] 梁欢.硅藻土基非均相Fenton催化材料的制备及其降解染料废水的研究[D].武汉:中国地质大学,2015.
[11] 王继全.Fe2O3/高岭土复合催化剂的制备及其在异相可见光Fenton体系中的应用[D].武汉:武汉理工大学,2013.
[12] Herney-Ramirez J,Vicente M A,Madeira L M.Heterogeneous photo-Fenton oxidation with pillared clay-based catalysts for wastewater treatment:a review[J].Applied Catalysis B Environmental,2010,98(1/2):10-26.
基金资助
国家自然科学基金(51604097);河南理工大学博士基金(B2013-011)