改性膨润土去除水中重金属离子研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
膨润土在自然界储量丰富,其主要成分为蒙脱石。由于蒙脱石自身独特的层状铝硅酸盐结构而具有巨大的吸附潜能。采用适当的方法进行改性,使膨润土中蒙脱石的比表面积得到极大的提高,从而显著地改善其吸附性能。
     本论文以提高膨润土中蒙脱石的吸附性能并用于去除水中重金属离子为主要研究内容,研究蒙脱石的表面性质与吸附性能的相关性。在传统外源柱撑的基础上,重新分析合成过程,提出内源柱撑的合成新方法。并研究了蒙脱石柱撑后的层间距、比表面积和孔径分布等物理参数。本论文主要研究内容及结论如下:
     以市售膨润土为原材料,采用内源柱撑的改性法制备柱撑蒙脱石,采用BET方程分析和计算比表面积、孔容、孔径分布等。研究了浆固含量、反应时间、pH和反应温度等因素对蒙脱石比表面积和孔容孔径的影响。研究结果表明:pH和反应温度是影响柱撑蒙脱石比表面积和孔结构参数的主要因素。通过优化柱撑条件,制备出了比表面积和平均孔容分别高达223.12 m~2/g和0.4981cm~3/g的内源柱撑蒙脱石。
     与膨润土原土和传统方法制得的柱撑土相比,内源柱撑土吸附性能优异。对汞离子和铅离子溶液,内源柱撑土对其的最佳吸附pH分别为7和6,最佳吸附时间分别为90 min和60 min。在相应的最佳吸附条件下,250 mg内源柱撑土对100 mL浓度都为10 mg/L的汞和铅溶液分别能接近百分之百去除,传统方法制得的柱撑土需300 mg、原土需800 mg才能分别对其几乎完全吸附。即内源柱
     撑土的吸附能力分别是传统方法制得的柱撑土和原土的1.2倍和3.2倍。准二级动力学方程和Elovich方程能很好地描述内源柱撑土和外源柱撑土对Hg~(2+)、Pb~(2+)的吸附过程,化学吸附控制了吸附过程的速度。且平衡吸附量qeq与平衡浓度C_(eq)之间的关系符合Freundlich等温方程。
Bentonite is a montmorillonite clay for major compositions and is abundant in nature. Montmorillonite has the huge adsorption potential because of its own unique layered aluminosilicate structure. If we use different methods through the varying modification, the surface area of montmorillonite will be greatly improved, thus its adsorption properties will be significantly improved.
     This topic's goal is to improve the adsorption performance of montmorillonite and it will be applied to the removal of metal ions in waste water. The relevance between the surface properties of montmorillonite and its adsorption performance was studied.Based on the external-intercalation which is the traditional method of intercalation , the synthesis process was analyzed and a new method of inner-intercalation was put forward.The interlayer distance of post-pillared montmorillonite,surface area, distribution of pore size and other physical parameters were studied,too. The paper made the following aspects:
     Bentonite as raw material from commercial, was modified by the inner- intercalation to prepare pillared montmorillonite and according to the nitrogen adsorption - desorption isotherms of pillared samples in 77K , the BET equation was used to analyze and calculate the surface area , pore volume and distribution of pore size. The effect on the surface area and pore size of montmorillonite of slurry solid content, reaction time, pH and reaction temperature during the preparation of pillared montmorillonite, was deeply discussed. The results showed: pH and reaction temperature were the main elements affecting the surface area and pore structure parameters of montmorillonite. Pillared by the optimum conditions, the pillared montmorillonite was prepared with the specific surface area and the average pore volume being as high as 223.12 m~2 / g and 0.4 981 cm~3 /g, respectively.
     Compared with original soil and pillared montmorillonite by the traditional methods,montmorillonite pillared by method of inner-intercalation obtained high adsorption performance. For the solution of mercury and lead, inner-intercalated bentonite get the best adsorption on pH of 7 and 6, respectively, and best adsorption time of 90 min and 60 min, respectively. Under the best adsorption conditions, 100 mL concentration for 10 mg/L mercury and lead solution can be completely adsorbed by 250 mg inner-intercalated bentonite,while traditional external-intercalation bentonite and the original soil were 300 mg and 800 mg respectively, namely the capability of adsorption of montmorillonite pillared by method of inner-intercalation was 1.2 times and 3.2 times,respectively,more than montmorillonite obtained by traditional methods of external-intercalation and original soil.
     The adsorption dynamics follows the laws of pseudo second-order kinetics and Elovich equation,and the chemical adsorption control the speed of the adsorption processes. The relationship between adsorption capacity(q_(eq)) and equilibrium mass concerntration(C_(eq)) is in accord with the isothermal adsorption equation of Langmuir.
引文
[1]季秀玲,魏云林.低温微生物环境污染修复技术研究进展[J].环境污染治理技术与设备,2006,7(10):6-11
    [2]孟祥和,胡国飞.重金属废水处理[M].北京:化学工业出版社,2000,9-12
    [3]奚旦立,孙裕生,刘秀英.环境监测(第三版)[M].北京:高等教育出版社,2004
    [4] Nriagu J.O.,Pacyna J.M..Nature 333 (1988) 134
    [5]戴树桂,岳贵春,王晓蓉,等.环境化学[M].高等教育出版社,1997
    [6]周泽义.中国蔬菜重金属污染及控制[J].资源生态环境网络研究动态,1999,10(3):21-27
    [7]刘文新,汤鸿霄.河流沉积物重金属污染质量控制基准的研究:IC-B-T质量三合一方法[J].环境科学学报,1999,19(2).120-125
    [8] DEACON J R.Distribution of trace elements in streambed sediment associated with mining activities in the upper Colorado river basin,Colorado,USA,1995-1996[J].Arch Environ Contam Toxicol,1999,37(1):7-18
    [9] Wen X H.Mobization of heavy metals from Le An River sediment[J].Sci.total Environ, 1999,227(2):101-108
    [10]傅瑞标,何青.长江南槽重金属的分布特征[J].中国环境科学,2000,20(4):357-360
    [11]刘文新,栾兆坤.河流沉积物重金属污染质量控制基准的研究:Ⅱ相平衡分配方法[J].环境科学学报,1999,19(3):230-235
    [12] Vasudevan P,Padmavathy V,Dhingra S C.Biosorption on monovalent and divalent ions on baker's yeast[J].Bioresource Technology,2002,82:285-289
    [13] Romera E,Gonzalez F,Ballester A,et al.Comparative study on biosorption of heavy metals using different types of algae[J].Biorcsource Technology,2007,98:3344-3353
    [14] Shaik Basha,Murthy Z V P.Kinetic and equilibrinm models for biosorption of Cr(VI) on chemically modified seaweed,cystoseira indica[J].Process Boichemistry,2007,42:1521-1529
    [15]招文锐,杨兵,朱新民,等.人工湿地处理凡口铅锌矿金属废水的稳定性分析[J].生态科学,2001,20(4):16-20
    [16]黄艳,章志昕,韩倩倩,等.国内离子交换树脂生产及应用现状与前景[J].净水技术,2010,29(5):11-16,29
    [17]李有科.膜分离技术的研究现状与进展[J].甘肃冶金,2010,32(6):83-87
    [18]王艳,陈爱民,史志琴.反渗透膜离线清洗技术研究与应用[J].清洗世界,2010,26(1):16
    [19]杨杰.工业废水中重金属离子的处理方法[J].城市给排水,2007,21(5):23-25
    [20]朱又春,林建民.电池厂含汞废水微电解处理[J].环境保护,1999,(3):12-14
    [21]郝鹏飞,梁靖,钟颖.改性沸石对铅废水的处理研究[J].环境科学与管理,2009,34(6):106-108
    [22] Cabriela Huamon Pino,Maria Souza de Mesquits,Mauricio Leonardo Torero ,et al .Biosorption of cadmium by green coconut shell power[J]. Mincrals Engineering, 2006,19(5):380-387
    [23] Gupta V.K..Imran Ali.Removal of lead and chromium from wastewater using bagasse fly ash-a sugar industry waste[J].Colloid and Interface Science,2004,271:321-328
    [24] Madhava Rao M., Kumar Reddy D.H.K.,Padala Venkateswarlu.Removal of mercury from aqueous solutions using activated carbon prepared from agricultural by-product/waste[J].Joural of Evironmental Management,2009,90:634-643
    [25] Kaczala F., Marques M., Hogland W..Lead and vanadium removal from a real industrial wastewater by gravitational setting/sedimengtation and sorption onto Pinus sylvestris sawdust[J].Bioresource Technology,2009,100:235-243
    [26] Vernon Somerset,Leslie Petrik,Emmanuel Iwuoha.The removal of mercury and lead ions from wastewater[J] .Journal of Environmenta Management,2008,87:125-131
    [27]张延安,赵乃仁.用壳聚糖絮凝剂去除水中汞[J].东北大学学报,1997,18(1):68-71
    [28] Boehm H P . Some aspect of the surface chemistry of carbon blacks and other carbons[J].Carbon,1994,32(5):759 -769
    [29] David Harkins D A,Schweitzer G K.Preparetion of site selective ion exchange resins[J].Sep Sci Technl,1991,26:345-354
    [30]于明泉,常青.高分子重金属絮凝剂的性能及作用机理研究[J].环境科学学报,2005,25(2):180-185
    [31]杨蒲仙.新型环保水处理剂一硅藻精土系列在印染废水处理中的应用[J].纺织导报.2007,(3):78-80
    [32]严瑞,胡宇,纪永亮,等.我国水处理剂的理状及发展战略[J].现代化工.1999,19(2):3-7
    [33]朱文喜,余军,魏建华,等.工业水处理剂的研究现状与方向[J].武钢技术.2006.45(2):50-53
    [34]何宏平,郭九皋,朱建喜,等.蒙脱石、高岭石,伊利石对重金属离子吸附容量的实验研究[J].岩石矿物学杂志.2001,20(4):573-578
    [35]姜桂兰,张培萍.膨润土加工与应用[M].北京:化学工业出版杜.2005
    [36] Eren E,Afsin B.An investigation of Cu(Ⅱ) adsorption by raw and acid-activated bentonite:a combined potentiometrie,thermodynamic,XRD,IR,DTA study[J].Journal of Hazardous Materials,2008,15l(2/3):682-691
    [37]胡恭任,于瑞莲.酸改性膨润土处理含铅废水[J].中国矿业,2007,16(2):100-102
    [38] Mercier L,Detellier C.Preparation,characterization,and applications as heavy metals sorbents of covalently grafted thiol functionalities on the interlamellar surface of montmorillonite[J].Environ Sci Technol,1995,29(5):1318-1323
    [39]潘嘉芬.钙基膨润土的钠化改性及其印染废水处理[J].矿产综合利用,2005(3):3-5
    [40] Rao G R,Mishra B G.A comparative UV-vis-diffuso reflectance study on the location and interaction of cerium ions in Al- and Zr-pillared montmorillonite clays[J].Materials Chemistry and Physics,2005,89(1):110-115
    [41] Mishra B G , Rao G R . Physicochemieal and catalytic properties of Zr-piIlared montmorillonite with varying pillar density[J].Microporous and Mesoporous Materials,2004,70(1-3):43—50
    [42]田承圣,马炽丽,曾凡桂.OH-/Al3+的比值变化对铝柱撑蒙脱石的性能影响[J].硅酸盐通报,2005,24(2):32-36
    [43] A.Olaya,S.Moreno,R.Molina.Synthesis of pillared clays with aluminum by means of concentrated suspensions and microwave radiation[J].Catalysis Communications.2009,10: 697–701
    [44]聂锦旭,余鹏钧,刘立凡.微波柱撑膨润土预处理垃圾渗滤液氨氮的研究[J].非金属矿, 2010,33(5:64-66
    [45] Singh S,Wegmann J,Albert K,et al.Variable temperature FT-IR studies of n-alkyl modified silica gels[J].J Phys Chem B,2002,106(4):878-888
    [46]王晋,徐媛嫒,韩颜颜,等.改性蒙脱石对有机污染物的吸附性能研究[J].济南大学学报:自然科学版,2008(1):72-76
    [47]赵斌,王小治,王宜鑫,等.不同表面活性剂改性有机膨润土的稳定性研究[J].环境科学与技术, 2009,32(5):71-74
    [48] Lee J F,Mortland M M,et al.Adsorption of benzene,toluene and xylene by two tetramethylammonium-smectites having different charge densities[J] . Clays and Clay Mineral,1990,38(2):113-120
    [49] Lee J F,Mortland M M.Shape-selective adsorption of aromatic molecules from water by tetramethylammonium-Smectite [J].J Chem Soc Faraday Trans,1989,85:2953-2962
    [50]武占省,张胜琴,胡海纯,等.微波合成有机膨润土对苯、甲苯和二甲苯吸附性能研究[J].非金属矿, 2009,32(4):59-61
    [51] Bentouami M S.Cadmium removal from aqueous solutions by hydroxyl-8 quinoline in tercalated bentonite[J].Journal of Cooloid and Interface Science,2006,29(2):270-277
    [52] Oyanedel-Craver V A,Fuller M and Smith J A.Simultaneous sorption of benzene and heavy metals onto two organoclays[J].Journal of Cooloid and Interface Science,2007,309(2):485-492
    [53]卢杰,潘嘉芬,李梦红.用改性膨润土去除水中四氯化碳的试验研究[J].金属矿山,2008(2):125-127
    [54] Dal Bosco S M,Jimenez R S,Vignado C.Removal of Mn(II) and Cd(II) from wastewaters by natural and modified clays [J].Adsorption,2006,12:133-146
    [55] Zhu L Z,Zhu R L.Simultaneous sorption of organic compounds and phoshate to inorganic-organic bentonitesform water[J].Separation and Purification Technology,2007,54:71-76
    [56]朱一民,王忠安,苏秀娟,等.钙基膨润土对水相中铜离子的吸附[J].东北大学学报(自然科学版),2006.27(1):99-102
    [57]王忠安,朱一民,魏德洲,等.钙基膨润土吸附废水中锌离子的研究[J].有色矿冶,2006,22(2):45-47
    [58] Jyotikusum Acharya,J.N.Sahu, C.R.Mohanty,et al.Removal of lead(II) from wastewater by activated carbon developed from Tamarind wood by zinc chloride activation[J].Chemical Engineering Journal.2009,149:249-262
    [59] Veli S., Alyuz B..Adsorption of copper and zinc from aqueous solutions by using natural clay[J].Journal of Hazardous Materials,2007,149(1):226-233
    [60] Singh C.K., Sahu J.N., Mahalik K.K.,et al.Studies on the removal of Pb(II) from wastewater by activated carbon developed from Tamarind wood activated with sulphuric acid [J].Journal of Hazardous Materials.2008,153:221-228
    [61]田承圣,马炽丽,曾凡桂.OH-/Al3+的比值变化对铝柱撑蒙脱石的性能影响[J].硅酸盐通报,2005,24(2):32-36
    [62]刘云,吴平霄,唐剑文,等.聚羟基铝柱撑蒙脱石吸附重金属离子实验研究[J].矿物岩石,2005,25(3):122-126
    [63]马炽丽,田承圣,曾凡桂.不同制备方法对铝柱撑蒙脱石性能的影响[J].硅酸盐通报, 2007,26(4):661-666
    [64] A.Olaya,S.Moreno,R.Molina.Synthesis of pillared clays with aluminum by means of concentrated suspensions and microwave radiation[J].Catalysis Communications.2009,10: 697–701
    [65]王趁义,唐铭,袁彩君,等.膨润土的原位柱撑改性及其除藻性能研究[J].环境工程学报, 2009,3(6):1019-1022
    [66]陆琦,雷新荣,汤中道,等.柱撑粘土矿物的晶体结构和化学特征[J].地质科技情报,2001,20(1): 91-99
    [67]吴平霄,张惠芬,郭九皋,等.蒙脱石热处理产物的MASNMR研究[J].无机材料学报,1999,14(4):580-586
    [68] Fu-Shen Zhang,Jerome O.Nriagu,Hideaki Itoh.Mercury removal from water using activated carbons derived from organic sewage sludge[J].Water Research,2005,39:389–395
    [69] Anoop Krishnan,K.Anirudhan,T.S..Removal of mercury(II) from aqueous solutions and chlor-alkali industry effluent by steam activated and sulphurised activated carbons prepared from bagasse pith: kinetics and equilibrium studies [J]. Hazard. Mater. 2002,B 92,161-183
    [70] Safa Q A,Erdem B,Ozcan A.Adsorption of Acid Blue 193 from aqueous solution onto Na-bentonite and DTMA-bentonite [J].J Colloid Interface Sci,2004,28?
    [71]黄美荣,王琳,易辉,等.废水中汞离子的去除方法研究[J].化工环保,2007,27(2):135-138

© 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