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施氏矿物的化学合成及其对含Cr(Ⅵ)地下水吸附修复
摘要点击 2164  全文点击 803  投稿时间:2016-08-01  修订日期:2016-09-21
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中文关键词  化学合成  施氏矿物  地下水  Cr(Ⅵ)/六价铬  吸附  环境条件
英文关键词  chemical synthesis  Schwertmannite  groundwater  Cr(Ⅵ)/hexavalent chromium  adsorption  environmental factors
作者单位E-mail
朱立超 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044 952033972@qq.com 
刘元元 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044 liuyuanyuan@cqu.edu.cn 
李伟民 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044 332678495@qq.com 
牟海燕 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044
四川大学建筑与环境学院, 成都 610065 
 
王婉玉 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044  
石德智 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044  
王涛 重庆大学三峡库区生态环境教育部重点实验室, 重庆 400044  
中文摘要
      采用简单快速的化学合成方法在实验室人工合成施氏矿物,研究了合成的施氏矿物对地下水中Cr(Ⅵ)的吸附动力学、吸附能力以及环境条件对施氏矿物吸附Cr(Ⅵ)的影响.结果表明,合成的施氏矿物对水溶液中Cr(Ⅵ)具有较强的吸附作用,24 h后反应达到平衡,吸附动力学过程符合Lagergren二级速率方程;而吸附等温方程符合Langmiur方程,pH值在4.5~6之间时Cr(Ⅵ)的去除效果最佳,最大吸附能力达到40.4 mg·g-1.溶液中Cr(Ⅵ)的去除率随施氏矿物投加量的增大而升高.Cl-对施氏矿物吸附地下水中Cr(Ⅵ)无明显影响,而HCO3-、SO42-会对施氏矿物吸附Cr(Ⅵ)产生较为显著的抑制作用;有机物和Ca2+、Mg2+等无机阳离子对施氏矿物吸附Cr(Ⅵ)的影响受pH值的影响:pH=6时,有机物和无机阳离子基本对施氏矿物吸附Cr(Ⅵ)无影响;pH=8时有机物以及无机阳离子均会对施氏矿物吸附Cr(Ⅵ)产生明显的抑制作用.
英文摘要
      Schwertmannite is usually naturally found in acidic mining wastewater and frequently used in the adsorption of heavy metal anions from water and wastewater. Schwertmannite was synthesized through a facile chemical method and utilized to remove Cr(Ⅵ) from contaminated groundwater. The kinetics, thermodynamics and isotherms, as well as the effects of environmental factors on the Schwertmannite adsorption processes were investigated. The experimental results showed that the synthesized Schwertmannite had a strong adsorption capability of Cr(Ⅵ) from aqueous solution. At the pre-set initial concentrations of Cr(Ⅵ), the Schwertmannite adsorption of Cr(Ⅵ) achieved equilibrium within 24 h, and the Lagergren's second-order model fitted the adsorption process better compared to Lagergren's first-order model and intraparticle diffusion model. Langmiur equation fitted the adsorption isotherms better than Freundlich equation. The Cr(Ⅵ) adsorption on Schwertmannite mainly involved ion exchange reaction between Cr(Ⅵ) and anions such as OH- and SO42- and surface complexation reactions. The ΔHθ and ΔGθ were 6.368 kJ·mol-1 and -1.215 kJ·mol-1, respectively, therefore the adsorption of Cr(Ⅵ) was a spontaneous and endothermic process. The removal of Cr(Ⅵ) from aqueous solution increased with increasing Schwertmannite dosage at pH=4.5. Acidic pH in the range of 4.5-6 favored Cr(Ⅵ) removal with Schwertmannite compared to that under basic conditions. Under the conditions of 5 mg·L-1of initial Cr(Ⅵ) concentration, 0.5 g·L-1 of Schwertmannite dosage, pH=6, maximum Cr(Ⅵ) removal of 93.1% was achieved and the adsorption capacity of Cr(Ⅵ) with Schwertmannite reached up to 40.4 mg·g-1. Batch tests showed that the presence of HCO3- and SO42- inhibited the adsorption of Cr(Ⅵ) while Cl- had no significant impact. Cations and natural organic matter had a pH-dependent impact on Cr(Ⅵ) removal:at pH=8 natural organic matter and cations would significantly inhibit the Cr(Ⅵ) sorption, while the impact could be neglected at weak acidic conditions (pH=6).

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