用户名: 密码: 验证码:
多孔聚合物—活性炭纳米复合材料的制备及性能研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
活性炭作为一种典型的多孔材料,具有比表面积高、孔结构发达、耐高温、耐腐蚀、导电、传热、抗酸耐碱、化学稳定性好和生物相容性好等一系列优点。活性炭在吸附方面的应用已经成为研究的热点之一,它可用于气相和液相的吸附分离过程,用作防毒面具、分离精制气体、回收有机溶剂、去除重金属离子和净化污水源等。
     目前,关于活性炭的吸附研究主要停留在利用活性炭的多孔特性,以物理吸附为主,但活性炭的吸附特性不仅取决于其孔结构,与表面化学性质也有很大关系,因此,研究者对活性炭表面进行化学改性使其吸附性能增强。本文中研究了将具有特殊基团的功能性聚合物引入到活性炭孔内,制备出多孔聚合物-活性炭纳米复合材料,这种材料既可以发挥活性炭的孔结构优势,还能利用聚合物链段的特殊基团对废水中有机污染物进行吸附。
     多孔聚合物-无机纳米复合材料不仅能将无机材料的光、电、磁等性能与聚合物的力学性能、功能性相结合,更重要的是纳米孔的存在为材料的实际应用提供了通道,比如质子的传送、溶液的运输、气体的扩散、各种生物反应的快速进行等,使这种材料在电学、光学、生物、医药和环保等领域具有广阔的应用前景。
     本文首先采用资源丰富,价格低廉的稻壳作为原料,用NaOH作为活化剂的化学活化法制备活性炭,讨论了浸渍比、活化方式、活化温度和活化时间对活性炭碘吸附值和产率的影响,并对稻壳在450℃氮气保护下炭化4h,浸渍比为3.0,在400℃下预处理30min,再升温到800℃,进行高温活化2h,洗净烘干,制备出的活性炭进行表征,发现其氮气吸附/脱附等温线为Ⅳ型,比表面为1200m~2.g~(-1),平均孔径为3.7nm,孔容积为0.67cm~3.g~(-1)。
     其次,探索了将聚合物合成到活性炭孔内的方法,用冷冻充气法成功地将丙烯酸直接原位聚合在活性炭孔内。发现丙烯酸与活性炭的质量比、聚合温度和聚合时间都会对多孔聚丙烯酸-活性炭纳米复合材料的性能产生影响,当聚合反应温度为80℃,聚合反应时间达到22h,聚丙烯酸含量约为20%时,比表面积下降为349m~2.g~(-1),平均孔径下降为2.7nm,孔容积下降为0.34 cm~3.g~(-1),其红外谱图显出具有活性炭C-C键产生的峰和PAA特征键的偏移峰。并用所制备的复合材料对苯胺和硝基苯进行吸附,发现其对苯胺和硝基苯的吸附以化学吸附为主,聚合物含量越高,吸附容量越大;吸附容量随着时间的延长而增加,直至20h后趋于平衡;吸附剂用量越增加,吸附容量越大,而且吸附过程更加适用Langmuir吸附等温方程和准二级动力学方程。
     最后,用搅拌法以溶液聚合法将丙烯酰胺聚合在活性炭孔内,当聚合反应的温度为90℃,反应时间达到24h,制备的出多孔聚丙烯酰胺-活性炭纳米复合材料的比表面积为611m~2.g~(-1),平均孔径为2.6nm,孔容积为0.42cm~3.g~(-1)。并用所制备的复合材料对苯酚、4-氯苯酚、五氯苯酚钠进行吸附,发现其对酚类化合物以化学吸附为主,吸附容量随着时间的延长而增加,直至20h后趋于平衡;吸附剂用量越增加,吸附容量越大,而且吸附过程更加适用Langmuir吸附等温方程和准二级动力学方程。
Activated carbon materials is a kind of typic porous nanocomposite materials which have many excellent properties such as high surface area and pore volume,a more uniform distribution of the hole diameter,high temperature and corrosion resistance,high electrical conductivity,good chemical resistant and biocompatibility stability.It has been used in gas and liquid adsorption separation process,which has become one of the research hot spots. Now activated carbon is usually used for gas masks,gas separation refuting,organic recycle, inorganic ions and heavy metals remove,sewage purification and so on.
     At present,we research on activated carbon adsorption primarily relying on its porosity which is mainly in physisorption.Activated carbon adsorption characteristic is not only decided by its structure,also has the very big relations with the surface chemistry nature. Therefore,people start to modify its chemic property to improve adsorption selectivity.In this article,we introduced functionality polymer in the activated carbon holes to prepared polymer-activated carbon nanocomposite materials.The material could adsorb organic pollutant in waste water which combines porous activated carbon and polymer with special groups.
     The porous polymer-inorganic nanocomposite materials could unite the light,electricity, magnetism properties of inorganic nanometer crystal and the mechanical properties, functional properties of polymer.Nanometer holes existence have provided chunnel for the material practical application such as the proton transmission,the solution transportation,the gas proliferation,biological response carrying on and so on.The kind of materials have broad application prospect in electricity,optics and biology,medicine,environmental protection field.
     In this paper first we prepared activated carbon using rice husk which is low in price and fruitful and NaOH as chemistry activation.And we discussed activated carbon iodine adsorption value and the activated carbon production rate influence by soaked proportion,the activation way,the activation temperature and the activation time.We prepared activated carbon as follow:the drying rice husk was carbonized at 450℃in nitrogen for 4h,then,the carbonized product was heated in the presence of sodium hydroxide(NaOH:C=3:1) at 400℃for 30 min to dehydrate the mixture,thereafter the temperature was raised to 800℃and this temperature was held for 2 hours to activate the combination,last the activated product were washed with water and dried.Then we found its nitrogen adsorption/desorption isothermal wasⅣ,The specific surface is 1200m~2.g~(-1),the average hole diameter is 3.7nm,and the holes volume is 0.67cm~3.g~(-1).
     Next,we explored the method of synthesizing the polymer in the activated carbon holes, then we successfully made acrylic acid in situ directly polymerizing in activated carbon holes with freezing aeration.We found the properties of polyacrylic acid-activated carbon nanocomposite materials influence by the acrylic acid and the activated carbon mass ratio,the polymerization temperature and the polymerization time.When the polyreaction temperature is 80℃,the reaction time is 22h,and the polypropylene acid content is approximately 20%, the specific surface reduced to 349m~2.g~(-1),the average hole diameter reduced to 2.7nm,the holes volume reduced to 0.34 cm~3.g~(-1).And we found its infrared spectrogram appears the activated carbon C-C peak and displacement peak of PAA characteristic structure.Then we used the compound materials for aniline and nitrobenzene adsorption,and we discovered that it is mainly chemical adsorption;the polymer content is higher,the adsorption effect is better; the adsorption capacity increased with the time prolonging till 20h;the absorbent amount used more,the adsorption effect is better;moreover the adsorption process is more suitable Langmuir equation and the second-level equation dynamic equation.
     Finally,we prepared polyacrylamide-activated carbon nanocomposite materials using mixing solution.When the polyreaction temperature is 90℃,the reaction time is 24h,the specific surface reduced to 611m~2.g~(-1),the average hole diameter reduced to 2.6nm,the holes volume reduced to 0.42 cm~3.g~(-1).Then we used the compound materials for phenol compound, and we discovered that it is mainly chemical adsorption;the adsorption capacity increased with the time prolonging till 20h;the absorbent amount used more,the adsorption effect is better;moreover the adsorption process is more suitable Langmuir equation and the second-level equation dynamic equation.
引文
[1]张立德.纳米材料.化学工业出版社,2000
    [2]Guo Z,Bai S,Sun Y.Preparation and characterization immobilized on magnetic hydrophobic mic-rospheres[J].Enzyme and Microbial Thechonology,2003,32:776-782
    [3]Dave E,Dianna G,et al.Terraced self assembled nano-structures from laminarin[J].International Journal of Biological Macromolecules,2007,40(4):362-366
    [4]Martin C,Rameirez L,Cuellar J.Stainless stell microbeads coated with sulfonated polystyrene-codivinyl benzene[J].Surf.CoatingsTech,2003,165:58-64
    [5]Sing K S W,Everett DH,Haul R A,et al.Reporting physisorption data for gas/solid system[J].Pure Applied Chemistry,1985,57(4):603-619
    [6]Kresge C T,Leonowicz M E,Roth W J,et al.Ordered mesoporous molecular sieves synthesized by a liquid-crystal template mechanism [J].Nature,1992,359:710-712
    [7]Alvaro,M,Corma A,Das D,et al.Single-step Preparation and Catalytic Activity of Mesoporous MCM-41 and SBA-15 Silicas Functionalized with Perfluoroalkylsulfonic Acid Groups Analogous to Nafion [J].Chem.Commun.2004,8:956-957
    [8]Bearzotti A,Bertolo J,Innocenzi P,et al.Humidity sensors based on mesoporous silica thin films synthesized by block copolymers [J].J.Eur.Ceram.Soc.2004,24:1969-1972
    [9]Brnardic I,Huskic M,Zigon M,et al.Montmorillonite modified with liquid crystalline diol hydrochlorides:Preparation and characterization [J].Journal of Non-Crystalline Solids,2008,354(18):1986-1991
    [10]Cole M,Haynes K,et al.Mediates Activation of a Mitochondria Unfolded Protein Response in elegans[J].Developmental Cell,2007,13,(4):467-480
    [11]Kang T,Park Y,Yi J.Highly Selective Adsorption of Pt~(2+)and Pd~(2+)Using Thiol-Functionalized Mesoporous Silica [J].Ind.Eng.Chem.Res,2004,43:1478-1484
    [12]Lee B,Bao L,Im H,et al.Synthesis and Characterization of Organic-Inorganic Hybrid Mesopor-ous Anion-Exchange Resins for Perrhenate (ReO4-)Anion Adsorption [J].Langmuir,2003,19:4246-4252.
    [13]Yiu HH,P.Botting C H,Botting NP,et al.Size selective protein adsorption on thiol-functionalised SBA-15 mesoporous molecular sieve [J].Phys.Chem.Chem.Phys,2001,3,2983-2985.
    [14]Byme JF,Marsh H.Porosity in carbon:characterization and applications[M].Patrick JW,editor.New York:Halsted Press,1995:l-133
    [15]Valix M,Cheung WH,Mackay G Preparation of activated carbon using low temperature carbonization and physical activation of high ash raw bagasses for acid dye adsorption[J].Chemosphere,2004,56(5):493-501
    [16]Lin SH,Wang Chuen S.Recovery of isopropyl alcohol from waste solvent of a semiconductor plant[J].Hazardous Materials.2004,106(2-3):161-168
    [17]Gryglewicz G,Machnikowsk J,Ewa LG,et al.Effect of pore distribution of coal-based activated carbon on double layer capacitance[J].Electronchim Acta,2005,50(5):l 179-1206
    [18]Xing W,Qiao SZ,Ding RG,et al.Superior electric double layer capacitors using ordered mesoporous carbon[J].Carbon,2006,44(2):216-224
    [19]Villegas P,Duran CJ.Pore structure of activated carbons prepared by carbon dioxide and steam activation at different temperatures from extracted rockrose[J].Carbon,2002,40(3):397-402
    [20]陈凤婷,李诗敏,曾汉民.几种植物基活性炭材料的孔结构与吸附性能比较—:孔结构表征[J].离子交换与吸附,2004,20(4):340-347
    [21]Cai Q,Huang Z,Kang,F,et al.Preparation of activated carbon microspheres from phenolic by supercritical water activation[J].Carbon,2004,42:775-783
    [22]郭玉鹏,杨少凤,赵敬哲等.由稻壳制备高比表面积活性炭[J].高等学校化学学报,2000,21(3):335-338
    [23]Suffet H,Michale I,McGuire H.Activated carbon adsorption of organics from the aqueous phase[J].Ann Arbor Science,1980,3,23-29
    [24]凯里泽夫(KellezovHB).吸附技术基础(Fundamental of Adsorption Technology).太原(Taiyuan),1983
    [25]刘成,高乃云,黄廷林.活性炭的表面化学改性研究进展[J].净水技术,2005,24(4):50-52
    [26]Tsutsumi K,Matsushima Y,Matsuoto A.Surface Heterogeneity of Modified Active Carbons[J].Langmuir,1993,9:2665-2669
    [27]Newcombe G,Drikas M,Hayes R.Influence of characterised natural organic matter on activated carbon adsorption:Ⅱ Effect on pore volume distribution and adsorption of 2-methylisoborneol[J].Water Research,1997,31(5):1065-1073
    [28]濑户山得彦,金子克美,Petrotech.材料科学.人民教育出版社,2001
    [29]Sing K S W.Physisorption of nitrogen by porous materials[J].Journal of Porous Materials,1995,2(1):5-8
    [30]姚惠源.谷物加工工艺学[M].中国财经出版社,北京,1997,7
    [31]Armesto L,Bahillo A,Veijonen K,et al.Combustion behaviour of rice husk in a bubbling fluidised bed [J].Biomass and Bioenergy,2002,23(9):171-179
    [32]Gou Y P,Qi JR,Yang SF,et al.Adsorption of Cr(Ⅵ) on micro and mesoporous rice husk-based active carbon[J].Materials Chemistry and Physics,2002,16(78):132-137
    [33]Wei YZ,Fang B,Iwasa S,et al.A novel electrode material for electric double-layer capacitors[J].Power Sources,2005,141(2):386-391
    [34]Maria JH,Katarzyna K.Comparison of molecular sieve properties in microporous chars from low-rank bituminous coal activated by steam and carbon dioxide[J].Carbon,2005,43(5):944-953
    [35]Lozano-Castello D,Lillo-Rodenas MA,Cazoda-Amoros D et al.Preparation of activated carbons from Spanish anthracite activation by KOH[J].Carbon,2001,39(6):741-749
    [36]Lillo-Rodenas MA,Lozano-Castello D,Cazorla-Amoros D et al.Preparation of activated carbons from Spanish anthracite activation by NaOH[J].Carbon,2001,39(5):751-759
    [37]Ismadji S,Sudaryanto Y,Hartono S B,et al.Activated carbons from char obtained from vacuum pyrolysis of tesk sawdust:pore structure development and chahacterization[J].Bioresource Technology.2005,96(12):1364-1369
    [38]卫延安,朱春山,蔡春等.由稻壳灰制备活性炭的工艺及应用研究[J].中国粮油学报.2003,18:29-33.
    [39]Guo YY.Preparation of activated carbons from oil-palm-stone chars by microwave-induced carbon dioxide activation[J].Carbon,2000;38(14):1985-1993
    [40]Lua AC,Yang T.Effect of vacuum pyrolysis conditions on the characteristics of activated carbons derived from pistachio-nut shell[.l].Colloid Inter.Sci,2004,276(2):364-372
    [41]Nevskaia DM,Santianes A,Munoz V,et al.Interaction of aqueous solutions of phenol with commercial activated carbons:an adsorption and kinetic study[J].Carbon,1999(37):1065-1074
    [42]Salame I,Bandosz TJ.Role of surface chemistry in adsorption of phenol on activated carbons[J].Journal of colloid and interface science,2003(264):307-312
    [43]Krisztina L,et al.Adsorption from aqueous phenol and aniline solutions on activated carbons with different surface chemistry[J].Colloids and surfaces A:Physicochem Eng Aspects,2005(256):32-39
    [44]万福成.活性炭富集溶液中Au(Ⅲ)的研究,信阳农业高等专科学校学报[J].2001,9(2):39-43
    [45]Dalfullah A M,Girgis B S.Impact of surface characteristics of activated carbon on adsorption of BTEX[J].Colloids and surfaces A:Physicochem Eng Aspects,2003,2(14):181-193
    [46]Chio M,Ryoo R.Ordered nanoporous polymer-carbon composites[J].Nature Materials,2003,2,473-477
    [47]肖羽堂,张晶晶,等.我国水资源污染与饮用水安全性研究[J].长江流域资源与环境.2001.10(1):51-59
    [48](日)立本英机,(日)安部郁夫主编,高尚愚译编.活性炭的技术应用技术[M].第一版.中国南京:东南大学出版社,2002
    [49]Ania CO,Parra JB,Pis J.Influence of oxygen-containing functional groups on active carbon adsorption of selected organic compounds[J].Fuel Process.Technol,2002,79(3):265-271
    [50]Considine R,Denoyel R,et al.The influence of surface chemistry on activated carbon adsoption of 2-methylisoborneol from aqueous solution Colloid and Surfaces A[J].Physicochemical and Engineering Aspects,2001,179(2):271-280
    [51]Greggs SJ,Sing KSW.Adsorption Surface Area and Porosity[M].Academic Press,New York,1982:41-56
    [52]Rouquerol F,Sing K.Adsorption by powers and porous solids[M].London:Academic Press,1999,165-179
    [53]Terzyk AP,Gauden PA,Kowalczyk P.What kind of pore size distribution is assumed in the Du binin-Astakhov adsorption isotherm equation[J].Carbon,2002.40(15),2879-2886
    [54]Ohkubo T,Iinyama T,Kaneko K.Organized structures of methanol in carbon nanospaces at 303K studies within situ X-ray diffraction[J].Chem.Phys.Letters,1999,312(3):191-195
    [55]Domobrowski RJ,Lastoskie CM,Hyduke DR.The Horvath-Kawazoe method revisited[J].Colloids and Surface,2001,188,23-29
    [56]Guo Y,Yang SF,Wang ZC.The preparation and mechanism studies of rice husk based porous carbon [J].Mater Chem Phys,2002,74(3):320-323
    [57]Faria P C,Orfao,JM,Pereira MFR.Adsorption of anionic and cationic dyes on activated carbons with different surface chemistries[J].Water Res,2004,38:2043-2052
    [58]Akmil B C,Karagunduz A,Keskinler B.Effect of presence of ions on surface characteristics of surfactant modified powdered activated carbon(PAC)[J].Appl.Surf.Sci,2003,218(4):170-175
    [59]Bae J S,Do DD.Surface diffusion of strongly adsorbing vapors in activated carbon by a differential permeation method[J].Chem.Eng.Sci,2003,58(19):4403-4415
    [60]周启星,林海芳.污染土壤及地下水修复的技术及展望.环境污染治理技术与设备,2001,2(5):48-54
    [61]Haigler BE,Spain JC.Biotransmation of nitrobenzene by bacteria containing toluene degradation pathways[J].Appl.Environ.Microbiol,2001,57(11):3156-3166
    [62]Park S.J.,Lim S.T.,Cho M.S.,et al.Electrical properties of multi-walled carbon nanotube/poly(methyl methacrylate) nanocomposite[J].Current Applied Physics,2005,5:302-304.
    [63]Guo Z,Zhu G,Gao B,et al.Adsorption of vitamin B12 on ordered mesoporous carbons coated with PMMA[J].Carbon,2005,43:2344-2351.
    [64]Adam NK.Physics and chemistry of surface.Oxford University Press,Third Edition,London,1941
    [65]Tsutsumi K,Matsushima Y,Matsuoto A.Surface heterogeneity of modified active carbon,Lang muir,1993,9:2665-2669
    [66]Freundlich H.Colloid and zapillary chenmistry.E.P.Dutton.Inc,New York Methuen Co,London,1926
    [67]Feng X,Fryxell GE,Wang LQI.Functionalized monolayers on ordered mesoporous supports[J].Science,1997,276:923-926
    [68]Zhou ML,Martin G.Adsorption ldnetics modeling in batch reactor onto activated carbon by model HSDM[J].Environ.Technol,1995,16:827-838
    [69]Figueiredo JL,Pereira MFR,et al.Modification of the surface chemistry of activated carbon[J].Carbon,1999,37:1379-1389
    [70]Ho YS,Mckay G.The sorption of lead(Ⅱ)ions on peat[J].Water Res,1999,33:578-584
    [71]Ho YS,Mckay G.The kinetic of sorption of divalent metal ions onto sphagnum moss peat[J].Water Res,2002,34:735-742
    [72]Mckay G.Adsorption of dyestuffs from aqueous solution using activated carbon(Ⅲ) Intraparti-cle diffusion processes[J].Chem.Biotechnol,1983,33A:196-204
    [73]Crank G.The mathematics of diffusion[M].london,New York:Clarendon press,1983:106-148
    [74]Aharoni C,Tompkins FC.Kinetics of adsorption and desorption and the Elovich equation[M].New York:Academic Press,1970:1-49
    [75]Daabrowski A,Podkoaccielny P,et al.Adsorption of phenolic compounds by activated carbon-a critical review[J].Chemosphere,2005,58(8):1049-1070
    [76]Agilent T.Solutions to today enviroumental analysis problems-A technical seminar[J].Agilent Corporation,2000:103-106
    [77]Roostaei N,Tezel FH.Removal of phenol from aqueous solutions by adsorption[J].Environmental Management,2004,70(2):157-164
    [78]Alvarez PM,Garcia JF,et al.Effect on Adsorption of selected phenolic compounds from solution[J].Colloid Inter.Sci,2005,283(2):503-512
    [79]国家环境保护总局.水和废水监测分析方法[M].北京:中国环境科学出版社,1989:220-221

© 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