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中国精品科技期刊2020
王学栋,李娅,戴涛涛,等. 果胶/聚间苯二胺凝胶珠的制备和表征及其对铅(II)吸附性能的研究[J]. 华体会体育,2021,42(15):85−95. doi: 10.13386/j.issn1002-0306.2020120181.
引用本文: 王学栋,李娅,戴涛涛,等. 果胶/聚间苯二胺凝胶珠的制备和表征及其对铅(II)吸附性能的研究[J]. 华体会体育,2021,42(15):85−95. doi: 10.13386/j.issn1002-0306.2020120181.
WANG Xuedong, LI Ya, DAI Taotao, et al. Study on Preparation and Characterization of Pectin/poly-m-phenylenediamine Gel Bead and Its Adsorption Performance on Lead (II)[J]. Science and Technology of Food Industry, 2021, 42(15): 85−95. (in Chinese with English abstract). doi: 10.13386/j.issn1002-0306.2020120181.
Citation: WANG Xuedong, LI Ya, DAI Taotao, et al. Study on Preparation and Characterization of Pectin/poly-m-phenylenediamine Gel Bead and Its Adsorption Performance on Lead (II)[J]. Science and Technology of Food Industry, 2021, 42(15): 85−95. (in Chinese with English abstract). doi: 10.13386/j.issn1002-0306.2020120181.

果胶/聚间苯二胺凝胶珠的制备和表征及其对铅(II)吸附性能的研究

Study on Preparation and Characterization of Pectin/poly-m-phenylenediamine Gel Bead and Its Adsorption Performance on Lead (II)

  • 摘要: 以低酯果胶和CaCl2为原料,采用离子交联法制备果胶凝胶珠,然后在果胶凝胶珠表面组装聚间苯二胺,制备新型果胶/聚间苯二胺凝胶珠并用于铅(II)的吸附。采用傅里叶变换红外光谱(FTIR),扫描电子显微镜(SEM),X射线衍射(XRD),热重分析(TGA),比表面积与孔隙度分析(BET)和能量色散X射线(EDX)对其结构进行了表征,并探究了初始pH、吸附时间、铅(II)初始浓度、吸附剂添加量和共存其它金属离子等条件对铅(II)吸附性能的影响。结果表明,与果胶凝胶珠相比,果胶/聚间苯二胺凝胶珠的比表面积与热稳定性有着显著提高,在相同条件下其对铅(II)的吸附性能更好。吸附过程与朗缪尔等温线模型和准二级动力学模型非常吻合,表明吸附是单分子层并且吸附过程是由化学吸附主导的。果胶/聚间苯二胺凝胶珠对铅(II)的最大吸附容量为352.03 mg/g,远高于果胶凝胶珠(162.99 mg/g)。钠(I)和钙(II)的共存对铅(II)的吸附具有一定程度的抑制作用。在三种重金属离子(铅(II),铁(II),铜(II))体系下,果胶/聚间苯二胺凝胶珠对重金属离子的亲和力为铅(II)>铁(II)>铜(II)。吸附铅(II)的机理可能是钙(II)与铅(II)的离子交换,与含氧官能团和含氮官能团的螯合作用以及静电相互作用。在5个吸附/解吸循环后,果胶/聚间苯二胺凝胶珠显示出良好的再生能力(去除率为90%)。果胶/聚间苯二胺凝胶珠可以作为一种去除铅(II)的吸附剂。

     

    Abstract: The pectin bead was prepared from low-ester pectin and CaCl2 by ion crosslinking method, and then novel pectin/poly-m-phenylenediamine gel bead was prepared by assembling poly-m-phenylenediamine on the surface of pectin gel beads and used for lead (II) adsorption. The structure of pectin/poly-m-phenylenediamine gel bead was characterized by fourier transform infrared spectroscopy (FTIR), scanning electron microscope (SEM), X-ray diffraction (XRD), thermogravimetric analysis (TGA), specific surface area and porosity analysis (BET) and energy dispersive X-ray (EDX), and the effects of initial pH, adsorption time, initial concentration of lead (II), dosage of adsorbent and coexistence of other metal ions on the adsorption of lead (II) were investigated. The results showed that compared with pectin gel beads, the specific surface area and thermal stability of pectin/poly m-phenylenediamine gel beads were significantly improved and it had better adsorption performance on lead (II) under the same conditions. Adsorption process was in good agreement with the Langmuir isotherm model and the Pseudo-second-order kinetic model, indicating that the adsorption was monolayer and the adsorption process was dominated by chemical adsorption. The maximum adsorption capacity of pectin/poly-m-phenylenediamine gel beads for lead (II) was 352.03 mg/g, which was much higher than that of pectin gel beads (162.99 mg/g). The coexistence of sodium (I) and calcium (II) had a certain degree of inhibition on the adsorption of lead (II). Under three heavy metal ion systems (lead (II), iron (II), copper (II)), the affinity of pectin/poly-m-phenylenediamine gel beads for heavy metal ions was lead (II)>iron (II)>copper (II). The adsorption mechanisms of lead (II) were the ion exchange between calcium (II) and lead (II), the chelation with oxygen-containing and nitrogen-containing functional groups and electrostatic interaction. After 5 adsorption/desorption cycles, the pectin/poly-m-phenylenediamine gel bead showed good regeneration ability(removal rate was 90%). Pectin/poly-m-phenylenediamine gel beads can be used as an adsorbent to remove lead (II).

     

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