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Preparation of poly(vinyl alcohol)(PVA)/peat/clay composite beads as adsorbents for the removal of Pb (II) and Zn(II) ions from aqueous solutions

机译:聚(乙烯醇)(PVA)/泥炭/粘土复合珠作为吸附剂,用于从水溶液中除去Pb(II)和Zn(II)离子的吸附剂

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A new type of poly(vinyl alcohol)(PVA)/peat/clay composite bead was prepared and shown to be suitable for use as an adsorbent. The mass transport process for the adsorption of metal ions onto the composite beads in an aqueous system was investigated. In the external mass transport process, the rate of ion diffusion decreased and increased with increasing initial metal ion concentrations for Pb~(2+) and Zn~(2+) ions, respectively. In the intraparticle diffusion process, the diffusion coefficient decreased with increasing initial metal ion concentrations in the range of 1×10~(-3) to 4×10~(-3) M, and the diffusion coefficient maintained an almost constant value in the range of 6×10~(-3) to 22×10~(-3) M. The rate of ion diffusion within the adsorbent for the Pb~(2+) ions was faster than that for the Zn~(2+) ions. The adsorption mechanism was controlled by the intraparticle diffusion process. The maximum amount of adsorbed metal ions at adsorption equilibrium for Pb~(2+) and Zn~(2+) ions in this study was 134.57 and 13.28 mg/g composite bead, respectively.
机译:制备了一种新型聚(乙烯醇)(PVA)/泥炭/粘土复合珠,并显示适合用作吸附剂。研究了对金属离子吸附到水性体系中的复合珠上的质量传递方法。在外部传质过程中,离子扩散的速率分别随着PB〜(2+)和Zn〜(2+)离子的初始金属离子浓度增加而增加。在椎间内部扩散过程中,扩散系数随着1×10〜(-3)至4×10〜(3)m的范围内的初始金属离子浓度的增加而降低,并且扩散系数保持了几乎恒定的值6×10〜(-3)的范围至22×10〜(-3)m。Pb〜(2+)离子的吸附剂内的离子扩散速率比Zn〜(2+)的吸附剂离子。吸附机制由粒前扩散过程控制。本研究中PB〜(2+)和Zn〜(2+)离子的吸附平衡的最大吸附金属离子的最大量分别为134.57和13.28mg / g复合珠粒。

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