聚甲亚胺酰胺树脂对水中Cu2+的吸附

李青彬, 冯云晓, 程永华. 聚甲亚胺酰胺树脂对水中Cu2+的吸附[J]. 环境工程学报, 2014, 8(5): 1906-1910.
引用本文: 李青彬, 冯云晓, 程永华. 聚甲亚胺酰胺树脂对水中Cu2+的吸附[J]. 环境工程学报, 2014, 8(5): 1906-1910.
Li Qingbin, Feng Yunxiao, Cheng Yonghua. Adsorption of copper(Ⅱ) from aqueous by polyazomethineamides[J]. Chinese Journal of Environmental Engineering, 2014, 8(5): 1906-1910.
Citation: Li Qingbin, Feng Yunxiao, Cheng Yonghua. Adsorption of copper(Ⅱ) from aqueous by polyazomethineamides[J]. Chinese Journal of Environmental Engineering, 2014, 8(5): 1906-1910.

聚甲亚胺酰胺树脂对水中Cu2+的吸附

  • 基金项目:

    河南省基础与前沿技术研究项目(122300410178)

    平顶山市科技攻关计划项目(2012C037)

    平顶山学院青年科研基金资助项目(20120014)

  • 中图分类号: X703.1

Adsorption of copper(Ⅱ) from aqueous by polyazomethineamides

  • Fund Project:
  • 摘要: 制备了聚甲亚胺酰胺树脂,对其进行傅里叶变换红外光谱分析。采用批处理方法实验了pH、铜离子初始浓度、吸附时间、吸附剂用量对吸附量的影响,研究了等温吸附模型和吸附动力学模型。优化后的吸附条件为:在铜离子溶液体积50 mL、初始浓度为300 mg/L、pH为6.0时,吸附剂投放量50 mg、吸附时间60 min,此时吸附量达到269.1 mg/g,去除率达89.7%。25℃时在研究浓度范围内,铜离子吸附过程用Langmuir等温线模型和Freundlich等温线模型描述均可;与准一级动力学方程、Elovich方程及内扩散方程相比,准二级动力学方程能更好地描述其吸附动力学过程。
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  • [1] Tang Wang Wang, Zeng Guang Ming, Gong Ji Lai, et al. Impact of humic/fulvic acid on the removal of heavy metals from aqueous solutions using nanomaterials: A review. Science of the Total Environment. 2014, 468-469: 1014-1027
    [2] 李青彬,韩永军,刘雪平,等. 土壤分离菌株去除水溶液中铅离子研究. 环境工程学报, 2007, 1(3): 70-74
    [3] Li Qingbin, Han Yongjun, Liu Xueping, et al. Removal of Pb(Ⅱ) from aqueous solution by bacterial strain isolated from soil. Chinese Journal of Environmental Engineering, 2007, 1(3): 70-74 (in Chinese)
    [4] Khattab I. A., Shaffei M. F., Shaaban N. A., et al. Electrochemical removal of copper ions from dilute solutions using packed bed electrode. Part Ⅰ. Egyptian Journal of Petroleum, 2013, 22(1): 199-203
    [5] Ochoa-Herrera Valeria, León Glendy, Banihani Qais, et al. Toxicity of copper(Ⅱ) ions to microorganisms in biological wastewater treatment systems. Science of the Total Environment, 2011, 412-413: 380-385
    [6] 杨阳,谢翼飞,李红,等. 水泥在铜污染事故应急处理中的应用. 环境科学与技术, 2013, 36(1): 125-130
    [7] Yang Yang, Xie Yifei, Li Hong, et al. Application of cement in the emergence treatment of sudden copper pollution. Environmental Science & Technology, 2013, 36(1): 125-130 (in Chinese)
    [8] Alonso-González O., Nava-Alonso F., Jimenez-Velasco C., et al. Copper cyanide removal by precipitation with quaternary ammonium salts. Minerals Engineering, 2013, 42: 43-49
    [9] Wen Junjie, Zhang Qixiu, Zhang Guiqing, et al. Deep removal of copper from cobalt sulfate electrolyte by ion-exchange. Transactions of Nonferrous Metals Society of China, 2010, 20(8): 1534-1540
    [10] Zhang Gaosheng, Ren Zongming, Zhang Xiwang, et al. Nanostructured iron(Ⅲ)-copper(Ⅱ) binary oxide: A novel adsorbent for enhanced arsenic removal from aqueous solutions. Water Research Nanotechnology for Water and Wastewater Treatment, 2013, 47(12): 4022-4031
    [11] Lan Shanhong, Ju Feng, Wu Xiuwen. Treatment of wastewater containing EDTA-Cu(Ⅱ) using the combined process of interior microelectrolysis and Fenton oxidation-coagulation. Separation and Purification Technology, 2012, 89: 117-124
    [12] 彭人勇,程宝珍. Fe/C微电解-絮凝沉淀法处理电镀废水中铜的研究. 环境工程学报, 2012, 6(2): 501-504
    [13] Peng Renyong, Cheng Baozhen. Treatment of copper from electroplating wastewater by Fe/C micro-electrolysis-flocculation-deposition process. Chinese Journal of Environmental Engineering, 2012, 6(2): 501-504 (in Chinese)
    [14] Escoda Aurélie, Euvrard Myriam, Lakard Sophie, et al. Ultrafiltration-assisted retention of Cu(Ⅱ) ions by adsorption on chitosan-functionalized colloidal silica particles. Separation and Purification Technology, 2013, 118: 25-32
    [15] Tomaszewska Barbara, Bodzek Michał. Desalination of geothermal waters using a hybrid UF-RO process. Part II: Membrane scaling after pilot-scale tests. Desalination, 2013, 319: 107-114
    [16] Bruckard W. J., Davey K. J., Jorgensen F. R. A., et al. Development and evaluation of an early removal process for the beneficiation of arsenic-bearing copper ores. Minerals Engineering, 2010, 23(15): 1167-1173
    [17] 王哲,李鑫钢,丁辉,等. 悬浮电解法回收废旧电子印刷线路板中的铜. 环境工程学报, 2010, 4(1): 195-198
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    [22] 朱明. 作为空穴传输材料的聚甲亚胺的制备及性能研究. 长春:吉林大学博士学位论文, 2011
    [23] Zhu Ming. Preparation and properities of polyazomethines as hole transport materials. Changchun: Doctor Dissertation of Jilin University, 2011 (in Chinese)
    [24] Girgis Badie S., El-Sherif Iman Y., Attia Amina A., et al. Textural and adsorption characteristics of carbon xerogel adsorbents for removal of Cu (Ⅱ) ions from aqueous solution. Journal of Non-Crystalline Solids, 2012, 358(4): 741-747
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出版历程
  • 收稿日期:  2013-12-29
  • 刊出日期:  2014-05-06
李青彬, 冯云晓, 程永华. 聚甲亚胺酰胺树脂对水中Cu2+的吸附[J]. 环境工程学报, 2014, 8(5): 1906-1910.
引用本文: 李青彬, 冯云晓, 程永华. 聚甲亚胺酰胺树脂对水中Cu2+的吸附[J]. 环境工程学报, 2014, 8(5): 1906-1910.
Li Qingbin, Feng Yunxiao, Cheng Yonghua. Adsorption of copper(Ⅱ) from aqueous by polyazomethineamides[J]. Chinese Journal of Environmental Engineering, 2014, 8(5): 1906-1910.
Citation: Li Qingbin, Feng Yunxiao, Cheng Yonghua. Adsorption of copper(Ⅱ) from aqueous by polyazomethineamides[J]. Chinese Journal of Environmental Engineering, 2014, 8(5): 1906-1910.

聚甲亚胺酰胺树脂对水中Cu2+的吸附

  • 1. 平顶山学院化学化工学院, 平顶山 467000
基金项目:

河南省基础与前沿技术研究项目(122300410178)

平顶山市科技攻关计划项目(2012C037)

平顶山学院青年科研基金资助项目(20120014)

摘要: 制备了聚甲亚胺酰胺树脂,对其进行傅里叶变换红外光谱分析。采用批处理方法实验了pH、铜离子初始浓度、吸附时间、吸附剂用量对吸附量的影响,研究了等温吸附模型和吸附动力学模型。优化后的吸附条件为:在铜离子溶液体积50 mL、初始浓度为300 mg/L、pH为6.0时,吸附剂投放量50 mg、吸附时间60 min,此时吸附量达到269.1 mg/g,去除率达89.7%。25℃时在研究浓度范围内,铜离子吸附过程用Langmuir等温线模型和Freundlich等温线模型描述均可;与准一级动力学方程、Elovich方程及内扩散方程相比,准二级动力学方程能更好地描述其吸附动力学过程。

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