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钾长石和海泡石作为土壤成分对Cd(II)的吸附及鼠李糖脂生物表面活性剂对Cd(II)的回收的对比研究

A comparative study for the sorption of Cd(II) by K-feldspar and sepiolite as soil components, and the recovery of Cd(II) using rhamnolipid biosurfactant.

作者信息

Aşçi Y, Nurbaş M, Açikel Y Sağ

机构信息

Department of Chemical Engineering, Eskişehir Osmangazi University, 26480 Bati Meşelik, Eskişehir, Turkey.

出版信息

J Environ Manage. 2008 Aug;88(3):383-92. doi: 10.1016/j.jenvman.2007.03.006. Epub 2007 Apr 25.

Abstract

This study investigated the sorption characteristics and recovery of selected heavy metal Cd(II) from K-feldspar and sepiolite, representative soil components, using rhamnolipid biosurfactant. Although the proposed technique was classified as a soil bioremediation process, it can also be applied to treatment of waste waters containing Cd(II) ions with minor modifications. The effect of initial Cd(II) concentration on sorption capacity was characterized by determining the sorption isotherms. Of the four models examined, the Freundlich model showed the best fit for the sorption of Cd(II) on K-feldspar, whereas the Langmuir-model was used successfully to characterize the sorption of Cd(II) on sepiolite. Although a high Cd(II) uptake of 7.49 mmol/kg by K-feldspar was obtained, sepiolite was a superior Cd(II) accumulater, with a maximum Cd(II) uptake of 24.66 mmol Cd(II)/kg. The presence of Cd(II) in the sepiolite or K-feldspar prior to addition of the rhamnolipid generally resulted in less rhamnolipid sorption to sepiolite or K-feldspar. The maximum Cd(II) desorption efficiency by rhamnolipid from K-feldspar was substantially higher than that of sepiolite and determined to be 96% of the sorbed Cd(II), whereas only 10.1% of the sorbed Cd(II) from sepiolite was recovered by rhamnolipid solution.

摘要

本研究使用鼠李糖脂生物表面活性剂,研究了从代表性土壤成分钾长石和海泡石中吸附特定重金属Cd(II)的特性及回收情况。尽管所提出的技术被归类为土壤生物修复过程,但只需稍作修改,它也可应用于处理含Cd(II)离子的废水。通过测定吸附等温线来表征初始Cd(II)浓度对吸附容量的影响。在所研究的四个模型中,Freundlich模型对Cd(II)在钾长石上的吸附拟合效果最佳,而Langmuir模型成功地用于表征Cd(II)在海泡石上的吸附。尽管钾长石对Cd(II)的高吸附量达到7.49 mmol/kg,但海泡石是一种更优的Cd(II)累积剂,其最大Cd(II)吸附量为24.66 mmol Cd(II)/kg。在添加鼠李糖脂之前,海泡石或钾长石中Cd(II)的存在通常会导致鼠李糖脂对海泡石或钾长石的吸附减少。鼠李糖脂从钾长石中对Cd(II)的最大解吸效率显著高于海泡石,测定为吸附的Cd(II)的96%,而鼠李糖脂溶液从海泡石中仅回收了10.1%吸附的Cd(II)。

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