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Poly(ethylene glycol dimethacrylate-n-vinyl imidazole) beads for heavy metal removal

机译:用于重金属去除的聚乙二醇二甲基丙烯酸酯-正乙烯基咪唑

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Poly(ethylene glycol dimethacrylate-n-vinyl imidazole) [poly(EGDMA-VIM)] hydrogel (average diameter 150-200 pun) was prepared by copolymerizing ethylene glycol dimethacrylate (EGDMA) with n-vinyl imidazole (VIM). The copolymer hydrogel bead composition was characterized by elemental analysis and found to contain 5 EGDMA monomer units each VIM monomer unit. Poly(EGDMA-VIM) beads had a specific surface area of 59.8 m~2/g. Poly(EGDMA-VIM) beads were characterized by swelling studies and scanning electron microscopy (SEM). These poly(EGDMA-VIM) beads with a swelling ratio of 78% were used for the heavy metal removal studies. Chelation capacity of the beads for the selected metal ions, i.e., Cd(II), Hg(II) and Pb(II) were investigated in aqueous media containing different amounts of these ions (10-750 mg/l) and at different pH values (3.0-7.0). Chelation rate was very fast. The maximum chelation capacities of the poly(EGDMA-VIM) beads were 69.4 mg/g for Cd(II), 114.8 mg/g for Pb(II) and 163.5 mg/g for Hg(II). The affinity order on molar basis was observed as follows: Hg(II) > Cd(II) > Pb(II). Chelation behavior of heavy metal ions could be modelled using both the Langmuir and Freundlich isotherms. pH significantly affected the chelation capacity of VIM incorporated beads. Chelation of heavy metal ions from synthetic wastewater was also studied. The chelation capacities are 45.6 mg/g for Cd(II), 74.2 mg/g for Hg(II) and 92.5 mg/g for Pb(II) at 0.5 mmol/l initial metal concentration. Regeneration of the chelating-beads was easily performed with 0.1 M HNO_3. These features make poly(EGDMA-VIM) beads potential candidate adsorbent for heavy metal removal.
机译:聚乙二醇二甲基丙烯酸酯-正乙烯基咪唑[聚(EGDMA-VIM)]水凝胶(平均直径150-200 pun)是通过将乙二醇二甲基丙烯酸酯(EGDMA)与正乙烯基咪唑(VIM)共聚制备的。通过元素分析表征共聚物水凝胶珠粒组合物,发现每个VIM单体单元包含5个EGDMA单体单元。聚(EGDMA-VIM)珠的比表面积为59.8m 2 / g。通过溶胀研究和扫描电子显微镜(SEM)表征聚(EGDMA-VIM)珠。这些具有78%溶胀率的聚(EGDMA-VIM)珠用于重金属去除研究。在含有不同量(10-750 mg / l)这些离子的水性介质中,研究了珠粒对选定的金属离子(Cd(II),Hg(II)和Pb(II))的螯合能力值(3.0-7.0)。螯合速度非常快。聚(EGDMA-VIM)珠的最大螯合能力对Cd(II)为69.4 mg / g,对Pb(II)为114.8 mg / g,对于Hg(II)为163.5 mg / g。观察到基于摩尔的亲和力顺序如下:Hg(II)> Cd(II)> Pb(II)。重金属离子的螯合行为可以使用Langmuir和Freundlich等温线进行建模。 pH值显着影响并入VIM的珠的螯合能力。还研究了合成废水中重金属离子的螯合。在初始金属浓度为0.5 mmol / l时,Cd(II)的螯合容量为45.6 mg / g,Hg(II)的螯合容量为74.2 mg / g,Pb(II)的螯合容量为92.5 mg / g。用0.1 M HNO_3容易进行螯合珠的再生。这些特征使聚(EGDMA-VIM)珠成为去除重金属的潜在候选吸附剂。

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