亚铁铝类水滑石吸附铀的性能与吸附机制

刘星群; 谢水波; 曾凡勇; 钟宇; 曾涛涛; 刘迎九

doi:10.13801/j.cnki.fhclxb.20160308.001

亚铁铝类水滑石吸附铀的性能与吸附机制

doi: 10.13801/j.cnki.fhclxb.20160308.001

刘星群¹,
谢水波^1,2,,
曾凡勇¹,
钟宇³,
曾涛涛^1,2,
刘迎九^1,2

1.
南华大学城市建设学院, 湖南衡阳 421001;
2.
污染控制与资源化技术湖南省重点实验室, 湖南衡阳 421001;
3.
湖南大学环境科学与工程学院, 湖南长沙 410012

基金项目: 国家自然科学基金项目（11175081）；高等学校博士点基金项目（20134324110003）；湖南省高校重点实验室创新基金项目（13K085）；湖南省教育厅优秀青年项目（14B154）

详细信息

通讯作者:
谢水波,博士,教授,博士生导师,研究方向为水处理理论与技术,E-mail:xiesbmr@263.net

中图分类号: TB332
计量
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- 被引次数: 0
出版历程
- 收稿日期: 2016-01-04
- 修回日期: 2016-02-22
- 刊出日期: 2017-01-15

Characteristics and mechanism of uranium (Ⅵ) adsorption by Fe(Ⅱ)-Al LDH

1.
Insitute of Urban Construction University of South China Hengyang 421001, China;
2.
Hunan Province Key Laboratory of Pollution Control and Resources Reuse Technology Hunan Hengyang 421001, China;
3.
College of Environmental Science and Engineering, Hunan University, Changsha 410082, China

摘要

摘要: 运用超声共沉淀制备了亚铁铝类水滑石（Fe（Ⅱ）-Al LDH），用于处理含U（Ⅵ）废水。实验考察了初始pH、吸附剂投加量、温度、吸附时间以及U（Ⅵ）初始浓度对Fe（Ⅱ）-Al LDH吸附U（Ⅵ）的影响。采用SEM、FTIR、XRD与XPS等手段分析了相关机制。试验表明，Fe（Ⅱ）-Al LDH吸附U（Ⅵ）的最佳pH为6，当温度为25℃，投加量为1.0 g/L，U（Ⅵ）初始质量浓度为10 mg/L时，对U（Ⅵ）的去除率达到99.98%，反应在120 min达到平衡，饱和吸附量为117.13 mg/g。Langmuir等温吸附模型和准二级动力学模型（R²≈1）较好地拟合了吸附过程，Fe（Ⅱ）-Al LDH对U（Ⅵ）的吸附是自发的吸热反应。SEM、FTIR、XPS分析结果表明，吸附前后的Fe（Ⅱ）-Al LDH结构没有发生改变，Fe（Ⅱ）-Al LDH对U（Ⅵ）的吸附是化学吸附为主，氧化还原作用为辅。
- 亚铁铝类水滑石 /
- U(Ⅵ) /
- 机制 /
- 吸附 /
- 化学吸附
Abstract: Fe(Ⅱ)-Al layered double hydroxides (Fe-Al LDHs) were prepared by the ultrasound-assisted co-precipitation method and used for the adsorption of uranium (Ⅵ) from aqueous solution. The effects of initial pH, adsorbent dosage, temperature, adsorption time and initial U(Ⅵ) ions concentration on adsorption of U(Ⅵ) were investigated. The prepared composites were characterized by SEM, FTIR, XRD and X-ray photoelectron spectroscopy (XPS). The experiment results indicate that the maximum adsorption occur at pH of 6 and the adsorption reach equilibrium within 120 min. Meanwhile the removal rate is up to 99.98% for initial U(Ⅵ) concentration of 10 mg/L and adsorbent dosage of 1.0 g/L at 25℃, and the maximum adsorption capacity for U(Ⅵ) ions is 117.13 mg/g. The experimental data fit well with the Langmuir isotherm model and pseudo-second-order kinetic model(R²≈1), Adsorption of U(Ⅵ) on Fe(Ⅱ)-Al LDH is primarily due to spontaneous endothermic reaction. The results of SEM、FTIR and XPS show that the structure of Fe(Ⅱ)-Al LDH has no change, chemisorption plays a major role and redox take subsidiary function.
- layered double hydroxides /
- uranium (Ⅵ) /
- mechanism /
- adsorption /
- chemisorption