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十六烷基三甲基溴化铵改性磁性纳米粒子去除砷酸盐。

Removal of arsenate by cetyltrimethylammonium bromide modified magnetic nanoparticles.

机构信息

The Key Laboratory of Water and Sediment Sciences, Ministry of Education, College of Environmental Sciences and Engineering, Peking University, Beijing, PR China.

出版信息

J Hazard Mater. 2012 Aug 15;227-228:461-8. doi: 10.1016/j.jhazmat.2012.05.004. Epub 2012 May 9.

DOI:10.1016/j.jhazmat.2012.05.004
PMID:22703733
Abstract

Cetyltrimethylammonium bromide (CTAB) modified magnetic nanoparticles (Fe(3)O(4)@CTAB) were synthesized and used to remove arsenate from water. Fe(3)O(4)@CTAB was prepared by a modified simple co-precipitation process with cheap and environmental friendly iron salts and cationic surfactant CTAB. Powder X-ray diffraction, X-ray photoelectron spectroscopy, and Fourier transform infra-red spectroscopy were utilized to characterize the prepared adsorbent (Fe(3)O(4)@CTAB). Transmission electron microscopy (TEM) image showed that Fe(3)O(4)@CTAB particles were approximately spherical with the core size of 10 nm. With a saturation magnetization of 67.2 emu g(-1), the Fe(3)O(4)@CTAB nanoparticles could be easily separated from solutions with a simple magnetic process in very short time (within 5 min). Adsorption of arsenate on Fe(3)O(4)@CTAB reached equilibrium within 2 min at pH 6. Arsenate adsorption agreed well with pseudo-second order kinetic model and two-site Langmuir isotherm model with the arsenate adsorption capacity of 23.07 mg g(-l), which was twice greater than that of pure Fe(3)O(4). Arsenate removal rate was over 90% at a wide pH range from 3 to 9 and the removal of arsenate was not obviously affected by the presence of dissolved natural organic matter (up to 10 mg L(-1) as TOC) and competitive anions (sulfate, bicarbonate, and silicate up to 20 mg L(-1), and phosphate up to 5 mg L(-1)) in solutions. Fe(3)O(4)@CTAB could be regenerated in alkali solutions and more than 85% As(V) was removed even in fifth regeneration/reuse cycle.

摘要

十六烷基三甲基溴化铵(CTAB)修饰的磁性纳米粒子(Fe(3)O(4)@CTAB)被合成并用于从水中去除砷酸盐。Fe(3)O(4)@CTAB 通过一种改良的简单共沉淀工艺,使用廉价且环保的铁盐和阳离子表面活性剂 CTAB 制备。粉末 X 射线衍射、X 射线光电子能谱和傅里叶变换红外光谱用于对制备的吸附剂(Fe(3)O(4)@CTAB)进行表征。透射电子显微镜(TEM)图像表明,Fe(3)O(4)@CTAB 颗粒近似为球形,核心尺寸为 10nm。Fe(3)O(4)@CTAB 纳米粒子的饱和磁化强度为 67.2 emu g(-1),可以通过简单的磁处理在很短的时间(5 分钟内)内从溶液中轻松分离。在 pH 值为 6 时,砷酸盐在 Fe(3)O(4)@CTAB 上的吸附在 2 分钟内达到平衡。砷酸盐的吸附符合准二级动力学模型和双位 Langmuir 等温线模型,砷酸盐的吸附容量为 23.07mg g(-1),是纯 Fe(3)O(4)的两倍。砷酸盐的去除率在 3 至 9 的宽 pH 范围内超过 90%,并且砷酸盐的去除不受溶液中存在的溶解天然有机物(高达 10mg L(-1)作为 TOC)和竞争阴离子(硫酸盐、碳酸氢盐和硅酸盐高达 20mg L(-1),磷酸盐高达 5mg L(-1))的明显影响。Fe(3)O(4)@CTAB 可以在碱溶液中再生,即使在第五次再生/再利用循环中,也可以去除超过 85%的 As(V)。

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