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Effects of Copper, Lead, and Cadmium on the Sorption of 2,4,6-Trichlorophenol Onto and Desorption from Wheat Ash and Two Commercial Humic Acids

机译:铜,铅和镉对2,4,6-三氯苯酚在小麦灰和两种市售腐殖酸上的吸附和解吸的影响

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摘要

The effects of copper (Cu~(2+)), lead (Pb~(2+)), and cadmium (Cd~(2+)) on the sorption of 2,4,6-trichlorophenol (TCP) to and desorption from wheat ash and two commercial humic acids were studied. Copper and Pb~(2+) diminished the sorption of TCP onto all adsorbents, and made desorption of TCP less hysteretic from ash and German humic acids (GeHA), but more hysteretic from Tianjin humic acids (TJHA). Cadmium had little effect on TCP sorption and desorption. Fourier-transform infra red (FTIR) and X-ray absorption spectroscopy (XAS) in conjunction with fluorescence quenching studies provided insights into the mechanisms of TCP sorption and desorption as affected by Cu~(2+) and Pb~(2+), indicating that complexation of Cu~(2+) and Pb~(2+) was likely via carboxylic, hydroxylic and phenolic groups of ash, TJHA and GeHA, and that theses same functional groups also reacted with TCP during sorption. In contrast, Cd, a "soft acid", had no effect on the adsorption of TCP. Hydration shells of dense water around adsorbed Cu~(2+) and Pb~(2+) ions may also compete with TCP for available surface area. Fluorescence quenching of pyrene verified that for TJHA, Cu~(2+) and Pb~(2+) promoted the formation of supramolecular associations with interior hydrophobic regions separated from aqueous surroundings by exterior hydrophilic layers.
机译:铜(Cu〜(2+)),铅(Pb〜(2+))和镉(Cd〜(2+))对2,4,6-三氯苯酚(TCP)的吸附和解吸的影响对小麦灰和两种商业腐殖酸进行了研究。铜和Pb〜(2+)减少了TCP在所有吸附剂上的吸附,并使得TCP的脱附相对于灰分和德国腐植酸(GeHA)的滞后性较小,但较天津除腐殖酸(TJHA)的滞后性更大。镉对TCP的吸附和解吸几乎没有影响。傅里叶变换红外(FTIR)和X射线吸收光谱(XAS)结合荧光猝灭研究提供了对受Cu〜(2+)和Pb〜(2+)影响的TCP吸附和解吸机理的见解,表明Cu〜(2+)和Pb〜(2+)可能通过灰分,TJHA和GeHA的羧基,羟基和酚基络合,并且这些相同的官能团在吸附过程中也与TCP反应。相反,Cd(一种“软酸”)对TCP的吸附没有影响。吸附的Cu〜(2+)和Pb〜(2+)离子周围的浓水水合壳也可能与TCP竞争可用的表面积。的荧光猝灭证明,对于TJHA,Cu〜(2+)和Pb〜(2+)促进了超分子缔合的形成,其内部疏水区域与外部水性亲水层隔开了水性环境。

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  • 来源
    《Environmental Science & Technology》 |2009年第15期|5726-5731|共6页
  • 作者单位

    State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, PO Box 2871, Beijing 100085, China;

    State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, PO Box 2871, Beijing 100085, China;

    State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, PO Box 2871, Beijing 100085, China State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, 73 East Beijing Road, Nanjing 210008, China;

    State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, PO Box 2871, Beijing 100085, China Research Institute of Subtropical Forestry, Chinese Academy of Forestry, Fuyang, Zhejiang 311400, China;

    State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, PO Box 2871, Beijing 100085, China;

    State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, PO Box 2871, Beijing 100085, China;

    Beijing Synchrotron Radiation Laboratory, Institute of High Energy Physics, Chinese Academy of Sciences, Beijing 100049, China;

    Beijing Synchrotron Radiation Laboratory, Institute of High Energy Physics, Chinese Academy of Sciences, Beijing 100049, China;

    Centre for Environmental Risk Assessment and Remediation, University of South Australia, Mawson Lakes, SA 5095, Australia;

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