用户名: 密码: 验证码:
电催化及光电催化氧化印染废水的研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
染料及印染工业的单位产品耗水量很高,该行业废水具有水量大、色度高、成分复杂、对环境的危害大等特征,因此染料及印染废水的降解脱色处理一直是主要的环境热点之一。电催化氧化和光电催化氧化都是近年发展起来的高级氧化技术,由于具有处理效率高、操作简便、应用灵活、易于自动化、环境友好等优点,因而在染料及印染废水处理的研究中受到广泛的关注。
     本文分别进行了光电催化和电催化降解染料的实验。在光电催化研究中,以TiO_2为阳极,钛网为阴极,研究了活性艳红K-2BP在NaCl和Na_2SO_4电介质中的降解情况,深入探讨了两种电解质在光电催化降解染料中的作用,研究了电解质浓度,溶液pH值的影响,并探讨了在混合盐电解质存在下,活性艳红K-2BP的降解行为。研究表明,以NaCl为电解质时,Cl~-会转化为氧化性很强的活性氯,活性氯及光电的共同作用,加速了染料的降解。以Na_2SO_4为电解质时,SO_4~(2-)在光电的作用下将发生两类反应,一部分SO_4~(2-)捕获光生空穴和HO·,对光电催化降解染料起抑制作用;另一部分SO_4~(2-)将发生反应生成H_2O_2,对染料降解起促进作用。
     在进行电催化降解实验时,我们用自制的钛基RuOx-PdO为电极,以常见的一种染料甲基橙为底物,浓度为100mg/L,以0.1mol/L NaCl为电解质,进行了电催化氧化降解的研究,通过多种分析手段,对甲基橙降解的中间产物进行了检测。研究表明,电解过程中能够产生小分子量物质,氯取代物,苯衍生物,长链烷烃,及无机阴离子等物种。氯代物的产生表明电解过程中生成的活性氯攻击甲基橙分子,使其发生断键,参与降解反应。长链烷烃的出现表明氮与甲基相连的C-N键能够在反应中断裂,生成含有甲基的自由基。含有两个苯环的有机物的出现表明,在反应中生成的一些有机物除了可以被继续降解外,还可以发生聚合反应,生成较复杂的有机物。然后再进一步被降解掉。综合各种数据,我们推测了甲基橙的电降解机理。其降解机理大致如下所述,分三个步骤:首先,电氧化过程中产生的活性氯、羟基等活性物种,进攻甲基橙分子,从而产生断键。活性氯可以进攻偶氮与苯环相连的C-N键,形成氯取代物;磺酸基也受到攻击,而从分子上脱去,形成SO_4~(2-);偶氮基团可能转化为N2,或其他含氮阴离子;氮与甲基相连的C-N键也发生断裂,形成甲基自由基。然后,第一步形成的物质进行聚合或再分解,其中含甲基的自由基发生聚合反应从而生成了饱和长链烷烃,同时也可以相结合而生成小分子化合物;第一步生成的氯取代物及其他可能存在的有机物,进一步被活性物质攻击,发生断键,并可能与生成的羟基,含甲基的自由基等相结合,近而生成其他苯的衍生物,同时这些物质也可能发生聚合而生成含两个苯环的化合物,及其他可能的复杂有机物。最后,以上生成的物质进一步被降解,最终矿化而转化为CO_2,H_2O及无机离子。
The highly coloured waste water of texitile industy contains many complex componds and is harmful to environment. So the discoloration of dye waste water is paid great concern by both governments and reaserchers. Photochemical and photoelectrochemical treatments are two advanced oxidation processes which are widely used because of characters such as high efficiency, simple operation and being benign to environment.
     In this work, Photochemical and photoelectrochemical treatments are investigated to treat the dye waste water. In the photoelectrochemical experiment, The effect of Cl~- and SO_4~(2-) ions on the photoelectrocatalytic degradation of the reactive brilliant K-2BP using TiO_2/Ti as anode is investigated, since Cl~- and SO_4~(2-) are the most common inorganic ions in dye polluted water. It is found that the concentration of the electrolyte, the acidity of the solution and the use of mixed electrolytes alter the degradation process. When NaCl is used as the electrolyte, active chlorine is formed during the process, and is found to be responsible in combination with photo- and electro-effects for the degradation of dye; while Na_2SO_4 is used as electrolyte, two categories of reactions will occur. SO_4~(2-) may trap HO·and h+, thus the efficiency of degradation is reduced. Under the conditions investigated, SO_4~(2-) ion may also catalyze the formation of hydrogen peroxide, which is active for the degradation, and then the degradation is favored.
     In the electrochemical degradation, the mechanism of Methyl Orange degradation with electrochemical method has been studied in 0.1M NaCl solution with RuOx-PdO/Ti as anode. Chemical oxygen demand (COD), ion chromatography(IC), FTIR and GC-MS analyses were employed to obtain the details of electrochemical degradation. During the reaction, inorganic ions (SO_4~(2-), NO_3~–), low molecular weight compounds, chlorinated compound, benzene derives and long chain alkenes could be formed. The formation of chlorinated compound provided strong evidence that during electrochemical process with NaCl as electrolyte, Cl~– was involved in the degradation reaction to form chlorine-substituted byproduct. Formation of long-chain alkenes radicals demonstrated that CH_3·radicals could be formed in the process. The thorough mechanism of the Methyl Orange is proposed in this study.
引文
[1] 杨锦宗.染料分析与剖析.北京:化工出版社,1982.708-709
    [2] Nagarethinam Kannan, Mariappan Meenakshi Sundaram. Kinetics and mechanism of removal of methylene blue by adsorption on various carbons—a comparative study Dyes and Pigments[J], 2001, 51: 25-40
    [3] 陈中颖,余刚,蒋展鹏,张彭义 活性炭纤维对染料的吸附性能研究 环境污染与防治 2001,4:151-154
    [4] 彭继伟 改良厌氧-生物接触氧化纺织印染废水 [J].工业水处理,2002,22(7):46-48
    [5] Marco Panizza, Giacomo Cerisola. Removal of organic pollutants from industrial wastewater by electrogenerated Fenton's reagent. Water Research[J] , 2002 , 35(16):3987-3992
    [6] 张国宇,王鹏,姜思朋等 微波诱导氧化处理雅格素红BF-3B染料废水的研究 [J]. 环境科学,2004,25(2):53-55
    [7]Vlyssides A G, Loizidou M, Karlis P K, et al. Electrochemical oxidation of a textile dye wastewater using a Pt/Ti electrode. Hazardous Materials B. 1997,70: 14-52
    [8] Vlyssides A G, Papaioannou D,Loizidoy M, et al. Testing an electrochemical method for treatment of textile dye wastewater. Waste Management. 2000, 20: 569-574
    [9] Qiquan Wang etc. Kinetic model and optimization of 2,4-degradation by anodic Fenton treatment [J]. Enviromental science & technology. 2001, 35(2): 4509-4514
    [10]梁镇海,许文林,孙彦平 焦化含酚废水在Ti/PbO2电极上的氧化处理 稀有金属材料与工程 1996,25(3): 37-40
    [11]王鹏,刘伟藻,方汉平 电化学氧化与厌氧技术联用处理垃圾渗滤液 环境科学 2001,22(5):70-73
    [12] 贾金平,叶建昌,张舒茶 活性碳纤维电极法处理草浆造纸黑液的应用研究 上海环境科学 2000,19(3):120-123
    [13] 冯玉杰,李晓岩,尤宏等.电化学技术在环境工程中的应用[M].北京:化学工业出版社, 2002.
    [14] Comninellis C. Electrocatalysis in electrochemical conversion/combustion of organic pollutants for waste water treatment. Electrochimica Acta, 1994,39(11/12):1857-1862:
    [15] 吴进,杜琳,李桂英,胡常伟 钛基RuOx-PdO电极电催化氧化降解活性艳红K-2BP研究 贵金属,2006, 27(4):18-25
    [16] 熊蓉春,贾成功,魏刚. 二维和三维电极法催化降解染料废水[J].北京化工大学学报,2002 ,29 (5) :34-37.
    [17] Ya Xiong et al. Teatment of dye wastewater containing acid orangeⅡusing a cell with three-phase three-dimensional electrode [J]. water research, 2001,35(17): 4226-4230
    [18] 苏玉萍,奚旦立. 活性染料印染废水混凝脱色研究,上海环境科学,1999,18(2):88-90
    [19] 卢俊瑞. 溴氨酸活性染料生产废水治理,工业水处理,1999, 19 (3): 20-21
    [20] 李晓娥 祖庸等 纳米TiO2光催化氧化机理研究与应用 J 化工进展 1999,4:35
    [21] K. Vinodgopal, S. Hotchandani, P. V.Kamat. Electrochemically assisted photocatalysis - TiO2 particulate film electrodes for photocatalytic degradation of 4-chlorophenol. J. Phys. Chem.-US. 1993, 97 (35): 9040 – 9044
    [22] K. Vinodgopal, P. V. Kamat. Combine electrochemistry with photocatalysis. Chemtech. 1996, 26(4): 18 – 22.
    [23] 符小荣,张校刚,宋世庚等.TiO2/Pt/glass 纳米薄膜的制备及对可溶性染料的光电催化降解.应用化学, 1997,14(4): 77-79.
    [24] 戴清,郭妍,袁春伟等.二氧化钛多孔薄膜对含氯苯酚的电助光催化降解.催化学报, 1999,20(3): 317-320.
    [25] 姚清照,刘正宝.光电催化降解染料废水.工业水处理, 1999,19(6): 15-26.
    [26] R. Pelegrini, P. Peralta-Zamora, A. R. de Andrade, et al. Electrochemicallly assisted photocatalytic degradation of reactive dyes. Appl. Catal. B-Environ. 1999, 22 (2): 83 – 90.
    [27] 林仲华,叶国宇,黄明东等.电化学中的光学方法.北京:科学出版社,1990
    [28] 卢萍,姚明明,张颖等.过渡金属离子的掺杂对TiO2光催化活性的影响.感光科学与光化学, 2002,20(3): 185-190.
    [29] Litter M I,Navio J A. Photocatalytic properties of iron doped titania semiconductors. J.Photochem.Photobio.A:chem.. 1996,9 8(3): 171一181
    [30] Choi W, Termin A,Hoffmann M R.The role of metal ion dopants in quantum -sizedTi02correlation between photoreactivity and charge carrierrec om bi nationd ynamics. J.Phys.Chem. 1994,9 8: 13669-13679
    [31] 代斌,宫为民,张秀玲,何仁. 等离子体技术在催化剂制备中的应用.现代化工. 2001, 12: 36-41
    [32] 张素香,屈撑囤,王新强.光催化剂改性及固定化技术的研究进展.工业水处理, 2002,22(7): 12-14.
    [33] 李芳柏,古国榜,黎永津.WO3/TiO2复合半导体的光催化性能研究.环境科学,1999,20(4): 75-78.
    [34] Esser P E,H olscherB D, Kerm W.H alogenated oxo-and peroxotitanium porphyrinated as sensitizers for the photooxygenation of ol efi niccom pounds. J.molecularc atalysis A :Chemical. 1999, 140: 13-24
    [35] Chen S M .The photocatalytic auto oxidation of sulfur oxoanions by water-soluble porphyrin complexes.J.of Molecular catalysis A :Chemical. 1999, 138: 1-13
    [36] Hilgendorff M, Sundstrom V.Dynamics of electron injection and recombination of dye-sensitized Ti02 particles. J.Phys.Chem.B. 1998, 102:10505 -10514
    [37] Martini I , Hondaak J H , Hartland G V.Effect of Structure on electront ransfer reaction between anthracene dye and TiO2 nanoparticles. J.Phys.Chem.B. 1998,102: 9508-9517
    [38] Illive V,Alexiev V,Bilyarska L. Effect of phthalocyannine complex aggre gation on the catalytic and photocatalytic oxidation of sulfur containing Compounds,J.Molecular catalysisA :Chemical. 1999 137: 15-22
    [39] 岳林海,徐铸得. 半导体的表面修饰与其光电化学应用.化学通报,1998, 2:28 -31
    [40] F. Y. Oliva, L. B. Avalle, E. Santos, et al. Photoelectrochemical characterization of nanocrystalline TiO2 films on titanium substrates. J. Photoch. Photobio. A. 2002, 146 (3): 175 – 188.
    [41] W. H. Leng, Z. Zhang, J. Q. Zhang. Photoelectrocatalytic degradation of aniline over rutile TiO2/Ti electrode thermally formed at 600 ℃. J. Mol. Catal. A-Chem. 2003, 206(1-2): 239 – 252.
    [42] X. Quan, S. Chen, J. Su, J. W. Chen, et al. Synergetic degradation of 2,4-D by integrated photo- and electrochemical catalysis on a Pt doped TiO2/Ti electrode. Sep. Purif. Technol. 2004, 34 (1): 73 – 79.
    [43] K. Vinodgopal, S. Hotchandani, P. V.Kamat. Electrochemically assisted photocatalysis - TiO2 particulate film electrodes for photocatalytic degradation of 4-chlorophenol. J. Phys. Chem.-US. 1993, 97 (35): 9040 – 9044
    [44] 孔祥晋,潘湛昌,肖楚民,张环华,秦骁强 纳米TiO_2催化剂的固定及其对甲基橙的光电催化降解, 化学与生物工程 2005,6:18-20
    [45] 符小荣,张校刚,宋世庚等. TiO2/Pt/glass 纳米薄膜的制备及对可溶性染料的光电催化降解.应用化学, 1997,14(4): 77-79.
    [46] 李明玉, 熊林, 陈芸芸, 张娜, 张渊明, 尹华 光/电/化学催化降解水中酸性大红3R染料的研究 中国科学 B 辑 2005, 35 (2): 144~150
    [47] 樊彩梅,孙彦平. 苯酚的Ti02薄膜光电催化降解及反应产物的分布. 太原理工大学学报,2000 ,31(5):20-23
    [48] 孙彦平,樊彩梅. 中国专利:ZL99111723.9, 1999.
    [49] 潘湛昌,孔祥晋,肖楚民,张环华 负载型二氧化钛光阳极对碱性紫5BN的光电催化降解 水处理技术 2006, 8:14-17
    [50] M. V. B. Zanoni, J. J. Sene, M. A. Anderson. Photoelectrocatalytic degradation of Remazol Brilliant Orange 3R on titanium dioxide thin-film electrodes. J. Photoch. Photobio. A 2003, 157 (1): 55 – 56.
    [51]吴 进,杜琳,李桂英,梁斌勇,秦松,胡常伟 钛基RuOx-PdO电极光电降解活性艳红K-2BP的研究 物理化学学报 2007(2)268-273
    [52] Szpyrkowicz L., Juzzolino C., Kaul S. N. and Daniele S. Electrochemical oxidation of dyeing baths bearing disperse dyes. Ind. Engng. Chem. Res., 2000, 39(9): 3241-3248.
    [53] 赵国华,胡惠康,李楹等. 氧化物修饰电极降解有机污染物的电催化特性. 中国环境科学,2003, 23(4):385-389.
    [54] P. Montilla, P. A. Michaud, E. Morallon, J. L. Vazquez, Ch. Comninellis. Electrochemical oxidation of benzoic acid at boron-doped diamond electrodes. Electrochim.Acta., 2003, 47(21): 3509-3513.
    [55] Nagarethinam Kannan, Mariappan Meenakshi Sundaram. Kinetics and mechanism of removal of methylene blue by adsorption on various carbons—a comparative study Dyes and Pigments[J], 2001, 51: 25-40
    [56] Chu, W. Dye Removal from Textile Dye Wastewater Using Recycled Alum Sludge Water Res. 2001, 35, 3147-3152
    [57] Brown, D.; Laboureur, P. The degradation of dyestuffs: Part I Primary biodegradation under anaerobic conditions Chemosphere 1983, 12, 397.
    [58] 闫庆松 厌氧+好氧+煤渣吸附处理偶氮染料废水研究工业水处理, 2000, 20,19-22
    [59] Kirk, D. W.; Sharifian, H. F.; Foulkes, R. J. Appl. Electrochem. 1994, 23, 857.
    [60] 安太成,张文兵,朱锡海,熊亚,盛国英,傅家谟 一种新型光电催化反应器的研制及甲酸的光电催化深度氧化 催化学报,2003,24,338-342
    [61] 魏复盛主编. 水和废水监测分析方法(第四版)[M]. 北京: 中国环境科学出版社, 2002. 171-172.
    [62] Zanoni, M. V. B.; Sene, J. J.; Anderson, M. A. Photoelectrocatalytic degradation of Remazol Brilliant Orange 3R on titanium dioxide thin-film electrodes J. Photochem. Photobiol. Sci. 2003, 157, 55.
    [63] 梁斌勇,王波,李桂英等.三种不同阳极上活性艳红 X-3B 的光电降解.催化学报,2005,26(2):557-562
    [64] 梁斌勇,王波,杜 琳等.钌钯氧化物涂层电极光电降解活性红3BS的研究.化学研究与应用,2005,17(5):677-679.
    [65]Hu, C.; Yu, J. C.; Hao, Z.; Wong ,P. K. Appl. Catal. B-Environ. 2003, 40, 35.
    [66]Kim, D. H.; Anderon, M. A. Solution factors affecting the photocatalytic and photoelectrocatalytic degradation of formic acid using supported TiO2 thin films J. Photochem. Photobiol. A-Che. 1996, 94, 221.
    [67] Zhang, W. B.; An, T. C.; Cui, M. C. J. cheml. Technol. Biot. 2005, 80, 233.
    [68] Benifield L D,Judkins JF,Weand B L. Process chemical for water and wastewater treatment [M]. New Jersey: Prentice-Hall. Englewood Cliffs, 1982,102.
    [69] 王鹏等 垃圾渗沥液中氨氮的电化学氧化 中国环境科学 2000.20(4):289-291
    [70] D.Rajkumar, Byung Joo Song, Jong Cuk Kim. Electrochemical degradation of reactive blue 19 in the chloride medium for the treatment of textile dyeing wastewater with identification of intermediate compounds Dyes and Pigments 2004(72): 1-7

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700