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- 2015
羟乙基纤维素/海藻酸钠复合膜对六价铀的吸附性能及吸附机制
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Abstract:
将羟乙基纤维素(HEC)与海藻酸钠(SA)进行混合,利用戊二醛交联处理后制备了HEC/SA高分子复合多孔薄膜,并探讨了其对模拟含铀废水中的六价铀(U(Ⅵ))的吸附特性。通过静态实验,探讨了初始pH值、U(Ⅵ)初始浓度、温度和吸附时间等对HEC/SA复合膜吸附U(Ⅵ)效果的影响;对吸附过程进行了热力学与动力学分析,利用FTIR、SEM和X射线能谱等手段分析了其吸附机制。实验结果表明,U(Ⅵ)的吸附量与温度正相关,吸附平衡时间约为90 min,最佳吸附效果的初始pH值为5.0;吸附过程符合准二级动力学模型,主要表现为颗粒内部扩散;等温吸附过程符合Langmuir等温吸附线模型,在45 ℃时,HEC/SA复合膜对U(Ⅵ)的最大吸附容量达357.1 mg·g-1,HEC/SA复合膜对U(Ⅵ)的吸附存在离子交换作用,与U(Ⅵ)的相互作用基团为羧基。 Hydroxyethyl cellulose/sodium alginate (HEC/SA) polymer composite porous films were made by blending HEC and SA together and crosslinked by glutaraldehyde, and its adsorption properties for uranium(Ⅵ) (U(Ⅵ)) in simulated wastewater containing uranium were studied. The effects of initial pH value, initial U(Ⅵ) ions concentration, temperature and adsorption time et al on the adsorption of HEC/SA blend films for U(Ⅵ) were investigated by static experiment. The process of adsorption was investigated by thermodynamic and kinetic analysis. The adsorption mechanism was investigated by FTIR, SEM, energy dispersive X-ray spectrum and so on. The experimental results show that there is a positive correlation between temperature and the U(Ⅵ) adsorption quantity, adsorption equilibrium time is about 90 min, and the optimal initial pH value is 5.0. The adsorption process conforms to the pseudo-second-order kinetics model, and mainly preforms particle internal diffusion. The isothermal adsorption process conforms to the Langmuir isothermal adsorption model, when the temperature is 45 ℃, the maximum adsorption capacity of HEC/SA blend films for U(Ⅵ) ions reaches 357.1 mg·g-1. The adsorption of HEC/SA blend films for U(Ⅵ) presents ion-exchange process, and the interaction groups with U(Ⅵ) is carboxyl. 国家自然科学基金(11175081, 21177053); 高等学校博士学科点专项科研基金(20134324110003); 湖南省科技计划重点项目(2011sk2015); 湖南省高校创新平台开放基金(13K085, 13K086)
[1] | Guo Z X, Qiu S, Lu X L. Study on preparation and properties of calcium alginate/nanocrystalline cellulose composite films[J]. Science and Technology of Food Industry, 2012, 33(24): 174-179 (in Chinese). 郭正旭, 邱思, 卢晓黎. 海藻酸钙/纳米晶纤维素复合膜的制备及性能研究[J]. 食品工业科技, 2012, 33(24): 174-179. |
[2] | Wang B, Qin S, Yang Y, et al. Study on structure and properties of sodium alginate-chondroitin sulfate blend films[J]. Chemical Research and Application, 2007, 19(7): 740-744 (in Chinese). 王碧, 覃松, 杨意, 等. 海藻酸钠-硫酸软骨素共混膜的结构及性能研究[J]. 化学研究与应用, 2007, 19(7): 740-744. |
[3] | Chen J H, Liu Q L, Hu S R, et al. Adsorption mechanism of Cu(Ⅱ) ions from aqueous solution by glutaraldehyde crosslinked humic acid-immobilized sodium alginate porous membrane adsorbent[J]. Chemical Engineering Journal, 2011, 173(2): 511-519. |
[4] | Chen J H, Ni J C, Liu Q L, et al. Adsorption behavior of Cd(Ⅱ) ions on humic acid-immobilized sodium alginate and hydroxyl ethyl cellulose blending porous composite membrane adsorbent[J]. Desalination, 2012, 285: 54-61. |
[5] | Akhtar K, Khalid A M, Akhtar M W, et al. Removal and recovery of uranium from aqueous solutions by Ca-alginate immobilized trichoderma harzianum[J]. Bioresource Technology, 2009, 100(20): 4551-4558. |
[6] | Zhu G H. Application of sodium carboxymethyl cellulose and hydroxyethyl cellulose for daily chemicals[J]. Detergent and Cosmetics, 2005, 28(4): 16-20 (in Chinese). 朱刚卉. 羧甲基纤维素钠和羟乙基纤维素在日化产品中的应用[J]. 日用化学品科学, 2005, 28(4): 16-20. |
[7] | Zhang F A. Cellulose ethers and its application[J]. New Chemical Materials, 2001, 29(11): 21-23 (in Chinese). 张发爱. 纤维素醚及其应用[J]. 化学新型材料, 2001, 29(11): 21-23. |
[8] | Kilincarslan A, Akyil S. Uranium adsorption characteristic and thermodynamic behavior of clinoptilolite zeolite[J]. Journal of Radioanalytical and Nuclear Chemistry, 2005, 263(3): 541-548. |
[9] | Donat R. Adsorption and thermodynamics studies of U(Ⅵ) by composite adsorbent in a batch system[J]. Original Paper, 2010, 16(8): 741-749. |
[10] | Anirudhan T S, Jalajamony S. Ethyl thiosemicarbazide intercalated organophilic calcined hydrotalcite as a potential sorbent for the removal of uranium(Ⅵ) and thorium(Ⅳ) ions from aqueous solutions[J]. Journal of Environmental Sciences, 2013, 25(4): 717-725. |
[11] | Mishra S, Maity S, Bhalke S, et al. Thermodynamic and kinetic investigations of uranium adsorption on soil[J]. Journal of Radioanalytical and Nuclear Chemistry, 2012, 294(1): 97-102. |
[12] | Wang X L, Peng G W, Yang Y, et al. Uranium adsorption by dry and wet immobilized Saccharomyces cerevisiae[J]. Journal of Radioanalytical and Nuclear Chemistry, 2012, 291(3): 825-830. |
[13] | Weng S P. Fourier transform infrared spectroscopy[M]. 2nd edition. Beijing: Chemical Industry Press, 2010: 291-323, 325-328, 306 (in Chinese). 翁诗甫. 傅里叶变换红外光谱分析[M]. 第2版. 北京: 化学工业出版社, 2010: 291-323, 325-328, 306. |
[14] | Liu X M, Dong F Q, Li Q F, et al. Research on the yeast biosorption of uranium under culture conditions[J]. Environmental Science and Technology, 2009, 32(5): 31-34 (in Chinese). 刘学明, 董发勤, 李琼芳, 等. 培养条件下酵母菌吸附铀的研究[J]. 环境科学与技术, 2009, 32(5): 31-34. |
[15] | Chen J H, Liu G P, Liu Q L, et al. Cr(Ⅲ) ionic imprinted polyvinyl alcohol/sodium alginate (PVA/SA) porous composite membranes for selective adsorption of Cr(Ⅲ) ions[J]. Chemical Engineering Journal, 2010, 165(2): 465-473. |
[16] | Xia L S, Tan K X, Wang X, et al. Behavior of uranium and mechanism analysis on banyan leaves[J]. Atomic Science and Energy Technology, 2010, 44(3): 278-284 (in Chinese). 夏良树, 谭凯旋, 王晓, 等. 铀在榕树叶上的吸附行为及其机理分析[J]. 原子能科学技术, 2010, 44(3): 278-284. |
[17] | Zhang L X, Sun Y Z, Luo M B, et al. Adsorption of uranium by chemically modified titanate nanowhiskers[J]. Acta Materiae Compositae Sinica, 2011, 28(3): 96-102 (in Chinese). 张麟熹, 孙玉珍, 罗明标, 等. 磷酸三丁酯Ti纳米晶须应用于吸附铀酰离子[J]. 复合材料学报, 2011, 28(3): 96-102. |
[18] | Yang Z G. Membrane processes and principles of science and technology[M]. Shanghai: Donghua University Press, 2008: 1 (in Chinese). 杨座国. 膜科学技术过程与原理[M]. 上海: 东华理工大学出版社, 2008: 1. |
[19] | Liu K, Wang B, Qiu Y. Study on structure and properties of sodium alginate/carboxylmethyl cellulose blend films[J]. Chemical World, 2010(11): 660-664 (in Chinese). 刘凯, 王碧, 邱艳. 海藻酸/羧甲基纤维素共混膜的结构与性能研究[J]. 化学世界, 2010(11): 660-664. |