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模拟环境条件下δ-MnO_2氧化As(Ⅲ)的搅拌流动动力学特征 被引量:2

Kinetic characteristics of As(Ⅲ) oxidation by δ-MnO_2 in the simulated environment: A stirred flow study
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摘要 采用搅拌流动法研究了酸性水钠锰矿及水羟锰矿2种δ-MnO2矿物氧化As(Ⅲ)的动力学过程,构建了可用于多相体系的搅拌-流动氧化还原反应动力学模型.经过As吸附量的校正后,该模型对酸性水钠锰矿及水羟锰矿氧化As(Ⅲ)动力学数据拟合度分别为0.980和0.951,模型拟合得到pH 7时2种矿物单位比表面上氧化As(Ⅲ)的初始反应速率常数k分别为0.131,0.014min-1·m-2.相比而言,该速率常数明显高于批量法得到的表观速率常数kobs,0.021,0.001min-1?m-2更接近真实的化学动力学参数.搅拌流动法与批量法得到的不同矿物的速率常数大小趋势一致,即尽管酸性水钠锰矿对As(Ⅲ)的氧化率低于水羟锰矿,单位比表面上酸性水钠锰矿氧化As(Ⅲ)初始反应速率却远高于水羟锰矿.反应过程分析表明,反应初始阶段,As(Ⅲ)的吸附为主要限速步骤;而随着反应的进行,矿物表面反应位点逐渐钝化或减少,反应位点数量成为限速步骤. In this study, As (III) oxidation at the surfaces of two δ-MnO2 minerals, birnessite and vernadite, was investigated using stirred-flow technique, and the corresponding model was established to describe the kinetics of the redox reactions in the stirred-flow heterogeneous system. Following correction of As adsorption, the degree of fitting of the stirred-flow kinetic data of As (III) oxidation by birnessite and vernadite using the established model was 0.980and 0.951, respectively. The obtained initial rate constants (k) per unit specific area at pH 7were 0.131 and 0.014min-1m-2, respectively, which were much greater than apparent initial rate constant (kobs), 0.021min-1m-2 and 0.001min-1m-2, derived from the batch experiments. This indicated that rate constant (k) is much closer to the real chemical kintics that could be obtained using the stirred-flow technique. Both stirred-flow and the batch experiments showed that birnessite exhibited the greater reaction rate on a per surface area basis in As (III) oxidation than on vernadite, although birnessite had a relatively lower suface area and As (III) oxidation capacity. Analysis of the reaction process suggested that As (III) absorption was the rate determining step in the initial stage, and then the number of suface Mn reactive sites gradually became the rate determining step with the passivation and decrease of the sites.
出处 《中国环境科学》 EI CAS CSCD 北大核心 2014年第4期966-975,共10页 China Environmental Science
基金 国家自然科学基金项目(41171197和40971142) 中央高校基本科研业务费专项资金资助(2013JQ004,2010PY006)
关键词 AS(III) Δ-MNO2 搅拌流动法 动力学 速率常数 反应位点 As (III) δ-MnO2 stirred-flow technique kinetics rate constant reactive site
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  • 1FENG Xionghan1, TAN Wenfeng1, LIU Fan1, HUANG Qiaoyun1 & LIU Xiangwen2 1. College of Resources and Environment, Huazhong Agricultural University, Wuhan 430070, China,2. Testing Center, China University of Geosciences, Wuhan 430074, China.Pathways of birnessite formation in alkali medium[J].Science China Earth Sciences,2005,48(9):1438-1451. 被引量:7
  • 2王敬华,张效年,于天仁.华南红壤对酸雨敏感性的研究[J].土壤学报,1994,31(4):348-355. 被引量:84
  • 3董长勋,潘根兴,兰叶青.溶液pH和吸附离子对水相中δ-MnO_2氧化Cr(Ⅲ)的影响研究[J].生态环境,2006,15(1):27-31. 被引量:7
  • 4张瑞华,孙红文.电动力和铁PRB技术联合修复铬(Ⅵ)污染土壤[J].环境科学,2007,28(5):1131-1136. 被引量:37
  • 5林玉锁 薛家骅.锌在石灰性土壤中的吸附动力学初步研究[J].环境科学学报,1989,9(4):114-148.
  • 6章钢娅 张效年 于天仁.可变电荷土壤对SO4^2-吸附[J].土壤学报,1987,24(1):14-17.
  • 7鲁如坤.土壤农化分析方法[M].北京:中国农业科技出版社,1999.13-14,24-26,60-69,107-108,278-282.
  • 8Murry K J, Tebo B M. Cr(m) is Indirectly Oxidized by the Mn(Ⅱ)-Oxidizing Bacterium bacillus sp. Strain SG-1 [J]. Environ Sci Technol, 2007, 41: 528-533.
  • 9Tan W F, Liu F, Feng X H, et al. Adsorption and redox reactions of heavy metals on Fe-Mn nodules from Chinese soils [J]. J Colloid Interf Sci, 2005, 284: 600-605.
  • 10Weaver R M, Hochella M F, Ihon E S. Dynamic processes occurring at the Craq^Ⅲ-mangamte (τ-MnOOH ) interface: simultaneous adsorption, microprecipitation, oxidation/reductlon, and dissolution [J]. Geochim Cosmochim Acta, 2002, 66: 4119-4132.

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  • 1陈集,尹忠,冯英,樊松林.油气田高Cl^-废水的COD测定[J].西南石油大学学报(自然科学版),1992,26(4):94-101. 被引量:14
  • 2杨春维,王栋.Fenton试剂对亚甲基蓝氧化褪色的反应动力学实验研究[J].环境技术,2004,22(6):24-29. 被引量:17
  • 3周抗寒,周定.复极性固定床电解槽内电极电位的分布[J].环境化学,1994,13(4):318-322. 被引量:30
  • 4马承愚,彭英利.高浓度难降解有机废水的治理与控制[M].北京:化学工业出版社,2007.
  • 5CAN W,YAO K H,QING Z,et al.Treatment of secondary effluent using a three-dimensional electrodesystem:COD removal,biotoxicity assessment,and disinfection effects[J].Chemical Engineering Journal,2014,243(1):1-6.
  • 6MO G,ZHANG Y,ZHANG W,et al.Design and synthesis of hierarchical porous electrode with nanocomposites of Mn O2thin layer encapsulated carbon nanotubes and its superb charge storage characteristics[J].Electrochim Acta,2013,113(15):373-381.
  • 7WANG Y,ZHAO G,CHAI S,et al.Three-Dimensional Homogeneous Ferrite-Carbon Aerogel:One Pot Fabrication and Enhanced Electro-Fenton Reactivity[J].ACS Applied Materials&Interfaces,2013,5(3):842-852.
  • 8GARCIA-SEGURA S,KELLER J,BRILLAS E,et al.Removal of organic contaminants from secondary effluent by anodic oxidation with a boron-doped diamond anode as tertiary treatment[J].J Hazard Mater,2015,283(11):551-557.
  • 9BRILLASE,MARTíNEZHUITLE C A.Decontaminationofwastewaters containing syntheticorganicdyesby electrochemical methods.An updated review[J].Applied Catalysis B:Environmental,2015,166-167(5):603-643.
  • 10NANAYAKKARA K G,ALAM A K,ZHENG Y M,et al.A low-energy intensive electrochemical system for the eradication of Escherichia coli from ballast water:Process development,disinfection chemistry,and kinetics modeling[J].Marine Pollution Bulletin,2012,64(6):1238-1245.

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