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氧化锰改性的茶叶渣吸附水体中Pb(Ⅱ) 被引量:12

Study on sorption characteristic of tea waste modified by hydrated manganese oxide toward Pb( Ⅱ) in water
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摘要 将水合氧化锰(HMO)采用原位沉积技术负载于废弃茶叶渣表面,合成了复合材料氧化锰改性的茶叶渣(HMO-TW),研究了HMO-TW对水溶液中常见重金属离子Pb(Ⅱ)的吸附特性,探讨了溶液p H值、共存碱土离子、温度、接触时间、Pb(Ⅱ)初始浓度等因素对Pb(Ⅱ)的吸附效果的影响.结果表明:酸性范围内,Pb(Ⅱ)的去除率随p H升高而增大;在竞争离子Ca(Ⅱ)、Mg(Ⅱ)、Na(Ⅰ)的浓度高于Pb(Ⅱ)20倍时,Pb(Ⅱ)的吸附去除率仅分别下降11%、7%和1%;Pb(Ⅱ)的吸附过程较好的符合Freundlich等温模型,计算的理论最大吸附容量为188.25 mg·g-1.远远高于未经改性茶叶渣的Pb(Ⅱ)吸附量(33.49 mg·g-1);Pb(Ⅱ)的吸附速度较快,250 min内便基本达吸附平衡.所有结果均证实HMO-TW在净化实际铅污染水体中有着较为广阔的应用前景. Hydrated manganese oxide was impregnated successfully onto tea waste by precipitation to obtain a new sorbent named HMO-TW,and the sorption behaviors of it toward Pb( Ⅱ) from aqueous solution was evaluated by investigating the influences of pH value, coexisting ion,temperature,contact time and initial concentration of Pb( Ⅱ). The experiment results demonstrated that Pb( Ⅱ) sorption onto HMO-TW was p H-dependent,and the higher pH value was much helpful for Pb( Ⅱ) removal onto HMO-TW at investigated pH range. The removal efficiency of Pb( Ⅱ)onto HMO-TW declined only 11%,7% and 1% with the addition of Ca( Ⅱ),Mg( Ⅱ) or Na( Ⅰ)at 20 times higher than lead concentration. In addition, Pb( Ⅱ) sorption onto HMO-TW could be described well by Freundlich model,and the calculated maximum sorption capacity by Langmuir equation was 188. 25 mg·g^-1,which was much higher than the unmodified tea waste( 33. 49 mg·g^-1),sorption speed of lead was quick and could nearly reach equilibrium within 250 min. All the listed results validated that HMO-TW is a promising sorbent for removal of lead from waters.
出处 《环境化学》 CAS CSCD 北大核心 2014年第12期2198-2205,共8页 Environmental Chemistry
基金 大学生创新创业训练计划项目(201310375007 201310375009) 安徽省教育厅高校优秀青年重点基金(2013SQRL091ZD) 国家自然科学基金(21207112)资助
关键词 水合氧化锰 茶叶渣 吸附 应用 hydrated manganese oxide lead tea waste adsorption application
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  • 1李海英,张书廷,赵新华.城市污水污泥热解温度对产物分布的影响[J].太阳能学报,2006,27(8):835-840. 被引量:41
  • 2夏畅斌,刘春华,曾经,张玲,周艺,何湘柱.污泥制备活性炭对Pb(II)和Ni(II)的吸附和回收利用[J].材料保护,2006,39(12):58-60. 被引量:20
  • 3吴成,张晓丽,李关宾.黑碳吸附汞砷铅镉离子的研究[J].农业环境科学学报,2007,26(2):770-774. 被引量:61
  • 4吴成,张晓丽,李关宾.热解温度对黑碳阳离子交换量和铅镉吸附量的影响[J].农业环境科学学报,2007,26(3):1169-1172. 被引量:23
  • 5Rulkens W. Sewage sludge as a hiomass resource for the production of energy: overview and assessment of the various options[ J]. Energy & Fuels, 2008, 22(1) : 9-15.
  • 6Anderson M, Skerratt R G. Variability study of incinerated sewage sludge ash in relation to future use in ceramic brick manufacture [ J ]. British Ceramic Transactions, 2003,102 (3) : 109-113.
  • 7Rozada F, Otero M, Moran A, et al. Adsorption of heavy metals onto sewage sludge-derived materials [ J ]. Bioresource Technology, 2008, 99(14) :6332-6338.
  • 8Heiazmann B. Phosphorus recycling in sewage treatment plants with biological phosphorus removal [J].Water Science & Technology, 2005,52( 10/11 ) : 543-548.
  • 9Daniel D. Warnock,Johannes Lehmann,Thomas W. Kuyper,Matthias C. Rillig.Mycorrhizal responses to biochar in soil – concepts and mechanisms[J]. Plant and Soil . 2007 (1-2)
  • 10E. Hiller,A. Farga?ová,L. Zemanová,M. Bartal.Influence of Wheat Ash on the MCPA Immobilization in Agricultural Soils[J]. Bulletin of Environmental Contamination and Toxicology . 2007 (4)

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