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用密度泛函和XANES计算研究Zn2+在水锰矿表面的吸附和沉淀
引用本文:朱孟强,潘纲,刘涛,李贤良,杨玉环,李薇,李晋,胡天斗,吴自玉,谢亚宁.用密度泛函和XANES计算研究Zn2+在水锰矿表面的吸附和沉淀[J].物理化学学报,2005,21(12):1378-1383.
作者姓名:朱孟强  潘纲  刘涛  李贤良  杨玉环  李薇  李晋  胡天斗  吴自玉  谢亚宁
作者单位:State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085;1.Beijing Synchrotron Radiation Facility, Institute of High Energy Physics, Chinese Academy of Sciences, Beijing 100039
基金项目:国家自然科学基金(20777050)、中科院"优秀百人计划"资助项目
摘    要:用密度泛函理论(density function theory, DFT)和X射线近边结构(X-ray absorption near edge structure, XANES)模拟计算了不同酸度(pH = 7.0, 7.5 和 8.0)下Zn(II)在水锰矿表面的吸附. 优化的几何结构表明, 只有双边吸附方式的水解簇既能解释H+ 释放机制, 又能与扩展X射线吸收精细结构(extended X-ray absorption fine structure, EXAFS)实验键长值相吻合. 吸附能计算表明, 各种吸附方式的稳定性双边(DE)>双角(DC)>B型单边(SE-B)>A型单边(SE-A);水解能计算表明各种吸附态Zn2+ 均比溶液中水合锌离子易水解. 各种吸附簇模型的XANES计算谱未能与实验谱吻合, 即, 表面发生的并不是简单的吸附. pH=7.5和pH=8.0吸附样品的XANES实验谱与Zn5(OH)6(CO3)2的实验谱非常接近, 因此认为pH=7.5和pH=8.0下Zn(II)在水锰矿表面发生沉淀, Zn(II)是Zn—O八面体和Zn—O四面体的混合, 它们按类似Zn5(OH)6(CO3)2结构中的八面体和四面体排列方式排列. pH=7.0时, Zn(II)在水锰矿表面发生的主要是边连接方式的吸附.

关 键 词:密度泛函理论  XANES  表面吸附  沉淀  Zn(II)  γ-MnOOH  
收稿时间:2005-05-13
修稿时间:2005-07-14

Zn(Ⅱ) Adsorption and Precipitation on γ-MnOOH-Water Interfaces DFT and XANES Calculation
ZHU,Meng-Qiang,PAN,Gang,LIU,Tao,LI,Xian-Liang,YANG,Yu-Huan,LI,Wei,LI,Jin,HU,Tian-Dou,WU,Zi-Yu,XIE,Ya-Ning.Zn(Ⅱ) Adsorption and Precipitation on γ-MnOOH-Water Interfaces DFT and XANES Calculation[J].Acta Physico-Chimica Sinica,2005,21(12):1378-1383.
Authors:ZHU  Meng-Qiang  PAN  Gang  LIU  Tao  LI  Xian-Liang  YANG  Yu-Huan  LI  Wei  LI  Jin  HU  Tian-Dou  WU  Zi-Yu  XIE  Ya-Ning
Institution:State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085;1.Beijing Synchrotron Radiation Facility, Institute of High Energy Physics, Chinese Academy of Sciences, Beijing 100039
Abstract:Mechanisms of adsorption and precipitation of Zn(II) on γ-MnOOH-water interfaces were studied using DFT (density functional theory) and XANES (X-ray absorption near edge structure) simulation at different pH conditions. Optimal adsorption structures showed that only hydrolyzed clusters of double-edge-link mode could explain the H+ release mechanism and experimental bond-length values. Adsorption energy calculations indicated that the stability sequence of adsorption modes was in the order of double-edge (DE)>double-corner (DC)>single-edge-B (SE-B)> single-edge-A (SE-A). Hydrolysis energy calculations showed that the adsorbed Zn2+ of all the linkage modes hydrolyzed easier than Zn2+ in solution. XANES simulations of optimal adsorption clusters did not accord well with experimental results, indicating that mechanisms other than surface adsorption were involved in the adsorption samples. Surface precipitation species were formed in adsorption samples of pH > 7.5, where mixtures of Zn—O tetrahedron and Zn—O octahedron were arranged in the way similar to that of Zn5(OH)6(CO3)2. Simulated and experimental XANES spectrums of Zn5(OH)6(CO3)2 were very close to that of adsorption samples of pH > 7.5. At pH < 7.0, Zn(II) was mainly adsorbed in edge link mode on the surface of γ-MnOOH.
Keywords:DFT  XANES  Surface adsorption  Precipitation  Zn(II)  γ-MnOOH
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