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采用 O-羧甲基壳聚糖席夫碱-甘蔗渣微球吸附法从废水中去除 Pb(II)离子。

Adsorptive removal of Pb(II) ions from aqueous effluents using O-carboxymethyl chitosan Schiff base-sugarcane bagasse microbeads.

机构信息

University of Jeddah, College of Science, Department of Chemistry, Jeddah, Saudi Arabia.

Chemistry Department, Faculty of Science, Suez University, Suez, Egypt; Institut für Anorganische Chemie und Strukturchemie, Heinrich-Heine Universität Düsseldorf, Düsseldorf, Germany.

出版信息

Int J Biol Macromol. 2024 Oct;277(Pt 2):134350. doi: 10.1016/j.ijbiomac.2024.134350. Epub 2024 Jul 31.

DOI:10.1016/j.ijbiomac.2024.134350
PMID:39094877
Abstract

In this study, a novel and cost-effective approach was employed to prepare an effective Pb(II) adsorbent. We synthesized highly porous CMCSB-SCB microbeads with multiple active binding sites by combining carboxymethylated chitosan Schiff base (CMCSB) and sugarcane bagasse (SCB). These microbeads were structurally and morphologically characterized using various physical, analytical, and microscopic techniques. The SEM image and N2-adsorption analysis of CMCSB-SCB revealed a highly porous structure with irregularly shaped voids and interconnected pores. The CMCSB-SCB microbeads demonstrated an impressive aqueous Pb(II) adsorption capacity, reaching a maximum of 318.21 mg/g, under identified optimal conditions: pH 4.5, 15 mg microbeads dosage, 30 min contact time, and Pb(II) initial concentration (350 mg/L). The successful adsorption of Pb(II) onto CMCSB-SCB beads was validated using FTIR, EDX, and XPS techniques. Furthermore, the experimental data fitting indicated a good agreement with the Langmuir model (R = 0.99633), whereas the adsorption kinetics aligned well with the pseudo-second-order model (R = 0.99978). The study also identified the Pb(II) adsorption mechanism by CMCSB-SCB microbeads as monolayer chemisorption.

摘要

在这项研究中,我们采用了一种新颖且经济高效的方法来制备有效的 Pb(II) 吸附剂。我们通过结合羧甲基化壳聚糖席夫碱 (CMCSB) 和甘蔗渣 (SCB) 合成了具有多个活性结合位点的高多孔性 CMCSB-SCB 微球。我们使用各种物理、分析和显微镜技术对这些微球进行了结构和形态表征。CMCSB-SCB 的 SEM 图像和 N2 吸附分析显示出具有不规则形状的空隙和互联孔的高度多孔结构。在确定的最佳条件下,CMCSB-SCB 微球在水溶液中对 Pb(II) 的吸附容量达到了 318.21 mg/g 的最大值:pH 值为 4.5,15 mg 微球剂量,30 min 接触时间和 Pb(II) 初始浓度(350 mg/L)。使用 FTIR、EDX 和 XPS 技术验证了 Pb(II) 成功吸附到 CMCSB-SCB 珠上。此外,实验数据拟合表明与 Langmuir 模型(R = 0.99633)吻合较好,而吸附动力学与准二级模型(R = 0.99978)吻合较好。该研究还通过 CMCSB-SCB 微球确定了 Pb(II) 吸附机制为单层化学吸附。

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