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成型表面改性生物质环境材料制备及其吸附水中多环芳烃的研究 被引量:2

Research on Preparation of the Surface Modified-shaped Environmental Biomaterials and Adsorption on Aqueous PAHs
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摘要 700℃热解炭化大豆秸秆8h,经H3PO4溶液表面改性处理后,采用成型工艺技术制得成型表面改性生物质环境材料。测定了所制备的表面改性秸秆生物质环境材料的比表面积、表面形态及其对亚甲基蓝的吸附性能;以单一多环芳烃(PAHs)菲和复合PAHs萘、菲、苊为目标污染物,研究了生物质环境材料对水中有机污染物的吸附性能。结果表明,成型工艺制备的生物质活性炭的比表面积为320~359m2/g,孔隙高度发达。SEM结果显示,成型压力、热处理温度和热处理时间明显影响所制得材料的表面形态。成型工艺对亚甲基蓝吸附值影响顺序为热处理温度>成型压力>胶粘剂比例>热处理时间;成型生物质环境材料的最佳制备条件为:粘结剂比例15%、成型压力65MPa、热处理温度260℃、热处理时间90min。按此条件制得的生物质环境材料对亚甲基蓝的吸附值达135mg/g。成型工艺制备的秸秆生物质环境材料对水中菲的去除率均超过98%,与商品活性炭对菲的去除率相当;其对复合污染下3种PAHs的去除率为菲>萘>苊,对于同一PAHs,不同生物质环境材料的吸附能力存在差异。 The soybean stalk were pyrolyzed at 700℃ in muffle, and then surface modified by H3PO4 the obtained biomass carbons were pressed to obtain the columns of stalk biomass environmental biomaterials by molding technics. The BET specific surface, surface form, and the adsorption capacity of columns of shaped environmental biornaterials on methylene blue were determined, respectively. In order to prepare the economical and highly effective adsorption materials and evaluate their adsorption capacity, the absorption efficiencies of environmental biornaterials on single phenanthrene and mixed naphthalene, phenanthrene with acenaphthene were further studied. The results show that the BET specific surfaces obtained by shaped environmental biomaterials is 320-359m2/g, with good pore space structures; molding pressure, heat treatment temperature and heat treatment time have a clear affect on the surface forms of the shaped environmental biomaterials. The factors that influences adsorption of the methylene blue follows an descending order: heat treatment temperature 〉 molding pressure 〉 ratio of binder 〉 heat treatment time. The optimum condition obtained the shaped environmental biomaterials is binder: 15 %, molding pressure: 65 MPa, heat treatment temperature: 260℃, and heat treatment time: 90rnin, respectively. The adsorption values of the methylene blue on shaped activated carbon prepared by these conditions arrived at 135rng/g. The environmental biomaterials from soybean stalk can effectively remove the PAHs from water, and removal efficiencies on phenanthrene arrive at 98%, which is close to commercial activated carbons(CAC). For the shaped activated carbons based on different treatments, there is an obvious discrepancy in PAHs absorption.
出处 《材料导报》 EI CAS CSCD 北大核心 2011年第20期32-36,共5页 Materials Reports
基金 国家自然科学基金(20777036 40701073 40971137) 江苏省自然科学基金(BK2009315) 霍英东教育基金(122045)
关键词 秸秆生 物质环境材料 成型工艺 多环芳烃 吸附 adsorption stalk, environmental biomaterials, molding technics, polycyclic aromatic hydrocarbon (PAHs),
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参考文献22

  • 1Gao L J, Yang H Y. Rice straw fermentation using lactic acid bacteria [J]. Bioresour Techn, 2008,99 :2742.
  • 2李瑞,陈华,夏秋瑜,赵松林,李枚秋.椰壳活性炭脱色蔗糖溶液的研究[J].现代食品科技,2007,23(12):54-55. 被引量:8
  • 3Bernardo E C, Egashira R, Kawaski J. Ecolorization of molasses wastewater using carbon prepared from cane bagassecarbon [J]. Carbon, 1997,35 (9) : 1217.
  • 4Manol I E, Samara C. Polycyclic aromatic hydrocarbons in natural waters: Sources occurrence and analysis[J]. Trends Anal Chem, 1999,18(6) : 417.
  • 5Luo X J, Mai B X,Yang Q S,et al. Polycyclic aromatic hydrocarbons(PAHs) and organochlorine pesticides in water columns from the pearl river and the macao harbor in the pearl river delta in south China [J].Mar Pollut Bull,2004, 48(11-12) : 1102.
  • 6霍金仙,刘会娟,曲久辉,茹加,刘海宁,李国亭.三油酸甘油酯复合吸附剂去除狄氏剂和异狄氏剂研究[J].科学通报,2005,50(18):1957-1961. 被引量:4
  • 7Walter J, Weber J R. A distributed reactivity model for sorption by soils and sediments. 4. intraparticle heterogeneity and phase-distribution relationships under nonequilibrium conditions[J]. Environ Sci Techn, 1996,30(3) :881.
  • 8王重庆,刘晓勤,姚虎卿.表面改性活性炭对CO_2的吸附性能[J].南京化工大学学报,2000,22(2):63-65. 被引量:26
  • 9GB/T19587-2004气体吸附BET法测定固态物质比表面积[S].北京:中国标准出版社,2004.
  • 10GB/T12496.10-1999.木质活性炭亚甲基蓝的测定[S].北京:中国标准出版社,1999.

二级参考文献160

共引文献371

同被引文献65

  • 1杨娇萍,田艳红.化学-物理混合活化法改性活性炭电化学性能[J].电源技术,2005,29(6):372-375. 被引量:13
  • 2崔静,赵乃勤,李家俊.活性炭制备及不同品种活性炭的研究进展[J].气体净化,2005,5(3):7-11. 被引量:6
  • 3谢志刚,刘成伦.活性炭的制备及其应用进展[J].工业水处理,2005,25(7):10-12. 被引量:52
  • 4Zhu B,Fan T X,Zhang D. Adsorption of copper ions from aqueous solution by citric acid modified soybean straw [ J ]. Journal of Hazardous Materials, 2008,153 ( 1 ) : 300- 308.
  • 5Qian Q R, Maehida M, Tatsumoto H. Preparation of acti- vated carbons from cattle-manure compost by zinc chloride activation [ J ]. Bioresource Technology,2007,98 (2) :353- 360.
  • 6Hayashi J, Kazehaya A, Muroyama K, et al. Preparation of activated carbon from lignin by chemical activation [ J ]. Carbon ,2000,38 ( 13 ) : 1873-1878.
  • 7Duan X H, Srinivasakannan C, Peng J H, et al. Compari- son of activated carbon prepared from Jatropha hull by conventional heating and microwave heating [ J ]. Biomass and Bioenergy, 2011,35 ( 9 ) : 3920-3926.
  • 8Fierro V, Mufiiz G, Basta A, et al. Rice straw as precursor of activated carbons : Activation with ortho-phosphoric acid [ J]. Journal of Hazardous Materials, 2010, 181 ( 1 ) :27- 34.
  • 9Nabais J, Comes J, Carrott P, et al. Phenol removal onto novel activated carbons made from lignoceUulosic precur- sors : Influence of surface properties [ J ]. Journal of Haz- ardous Materials ,2009,167 ( 1 ) :904-910.
  • 10Laine J, Yunes S. Effect of the preparation method on the pore size distribution of activated carbon from coconut shell[J]. Carbon,1992,30(4) :601-604.

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