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Cd(II)在我国黄土土壤上的吸附行为及机理。

Adsorption behavior and mechanism of Cd(II) on loess soil from China.

机构信息

MOE Key Laboratory of Soft Soils and Geoenvironmental Engineering, Department of Civil Engineering, Zhejiang University, Yuhangtang Road 388, Hangzhou 310058, PR China.

出版信息

J Hazard Mater. 2009 Dec 15;172(1):30-7. doi: 10.1016/j.jhazmat.2009.06.121. Epub 2009 Jun 30.

Abstract

Cadmium is a toxic heavy metal that has caused serious public health problems. It is necessary to find a cost effective method to deal with wastewater containing Cd(II). Loess soils in China have proven to be a potential adsorbent for Cd(II) removal from wastewater. The adsorption capacity of loess towards Cd(II) has been determined to be about 9.37 mg g(-1). Slurry concentration, initial solution pH, reaction time and temperature have also been found to significantly influence the efficiency of Cd(II) removal. The adsorption isotherms and kinetics of loess soil from China can be best-fit with the Langmuir model and pseudo-second order kinetics model, respectively. The thermodynamic analysis revealed that the adsorption process was spontaneous, endothermic and the system disorder increased with duration. The natural organic matter in loess soil is mainly responsible for Cd(II) removal at pH < 4.2, while clay minerals contribute to a further gradual adsorption process. Chemical precipitation dominates the adsorption stage at pH > 8.97. Further studies using X-ray diffraction, Fourier transform infrared spectra of Cd(II) laden loess soil and Cd(II) species distribution have confirmed the adsorption mechanism.

摘要

镉是一种有毒重金属,已对公共健康造成严重问题。有必要寻找一种经济有效的方法来处理含 Cd(II)的废水。中国黄土已被证明是一种从废水中去除 Cd(II)的潜在吸附剂。黄土对 Cd(II)的吸附能力约为 9.37mg/g。泥浆浓度、初始溶液 pH 值、反应时间和温度也被发现对 Cd(II)去除效率有显著影响。中国黄土的吸附等温线和动力学最好分别符合朗缪尔模型和拟二级动力学模型。热力学分析表明,吸附过程是自发的、吸热的,系统无序度随时间增加而增加。黄土中的天然有机质主要负责 pH<4.2 时的 Cd(II)去除,而粘土矿物则有助于进一步的逐渐吸附过程。在 pH>8.97 时,化学沉淀主导吸附阶段。使用 X 射线衍射、Cd(II)负载黄土的傅里叶变换红外光谱和 Cd(II)物种分布的进一步研究证实了吸附机制。

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