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利用花生壳水热炭/β-环糊精/FeO 磁性复合材料从水溶液中去除铅离子。

Utilization of peanut hull hydrochar /beta cyclodextrin/FeO magnetic composite for lead ion removal from water solution.

机构信息

Chongqing Vocational Institute of Engineering, Chongqing, 402660, PR China.

出版信息

Environ Res. 2024 Oct 15;259:119525. doi: 10.1016/j.envres.2024.119525. Epub 2024 Jul 2.

Abstract

This study involves synthesizing peanut hull hydrochar (PHH) and a PHH/β-CD/FeO magnetic composite through hydrothermal and chemical precipitation methods, respectively, to use as effective adsorbents for Pb removal. Vibrating-sample magnetometry (VSM) and Brunauer-Emmett-Teller (BET) analyses revealed that the magnetic saturation value and specific active surface area of PHH/β-CD/FeO are 31.543 emu/g and 32.123 m/g, respectively. The impact of key variables on adsorption efficiency was evaluated using the response surface method - central composite design. ANOVA results (F-value: 166.22 and p-value: <0.05) demonstrated that the model effectively assesses the interaction of variables in the adsorption process. Additionally, R, Adjusted R, and Predicted R values were 0.999, 0.986, and 0.975, respectively, indicating the model's high adequacy in describing response changes. The maximum efficiency for Pb adsorption was found to be 95.35% using PHH and 99.73% with the PHH/β-CD/FeO magnetic composite. These measurements were taken at a temperature of 25 °C, an adsorbent dose of 1 g/L, a pH of 6, and a Pb concentration of 5 mg/L, with respective contact times of 130 min and 50 min. Thermodynamic analysis revealed negative enthalpy and Gibbs free energy values, indicating that the adsorption process is exothermic and spontaneous. The negative entropy parameter suggests a reduction in random interactions during the process. The Pb adsorption data for both PHH (R: 0.982) and PHH/β-CD/FeO (R: 0.985) were best described by the Pseudo 2nd order kinetic model. Equilibrium data followed the Freundlich model, with R values of 0.981 for PHH and 0.990 for PHH/β-CD/FeO, highlighting the importance of heterogeneous surfaces in the removal process. The maximum adsorption capacities for Pb were 26.72 mg/g for PHH and 33.88 mg/g for PHH/β-CD/FeO. Reuse and stability tests confirmed the structural stability and reusability of the adsorbents. Therefore, the PHH/β-CD/FeO magnetic composite is a promising option for removing Pb from aqueous solutions.

摘要

本研究通过水热法和化学沉淀法分别合成了花生壳水凝胶(PHH)和 PHH/β-CD/FeO 磁性复合材料,将其用作去除 Pb 的有效吸附剂。振动样品磁强计(VSM)和 Brunauer-Emmett-Teller(BET)分析表明,PHH/β-CD/FeO 的磁饱和值和比表面积分别为 31.543 emu/g 和 32.123 m/g。利用响应面法-中心复合设计评估了关键变量对吸附效率的影响。方差分析(F 值:166.22 和 p 值:<0.05)结果表明,该模型能够有效地评估吸附过程中变量的相互作用。此外,R、调整 R 和预测 R 值分别为 0.999、0.986 和 0.975,表明该模型在描述响应变化方面具有很高的充分性。在 25°C、吸附剂剂量 1 g/L、pH 值为 6 和 Pb 浓度为 5mg/L 的条件下,使用 PHH 和 PHH/β-CD/FeO 磁性复合材料的最大 Pb 吸附效率分别为 95.35%和 99.73%。在分别为 130min 和 50min 的接触时间下进行了这些测量。热力学分析表明焓和吉布斯自由能值为负值,表明吸附过程是放热和自发的。负熵参数表明过程中随机相互作用减少。PHH(R:0.982)和 PHH/β-CD/FeO(R:0.985)的 Pb 吸附数据均通过拟二阶动力学模型得到最佳描述。平衡数据遵循 Freundlich 模型,PHH 的 R 值为 0.981,PHH/β-CD/FeO 的 R 值为 0.990,这突出了去除过程中异质表面的重要性。PHH 的最大 Pb 吸附容量为 26.72mg/g,PHH/β-CD/FeO 的最大 Pb 吸附容量为 33.88mg/g。重复使用和稳定性测试证实了吸附剂的结构稳定性和可重复使用性。因此,PHH/β-CD/FeO 磁性复合材料是从水溶液中去除 Pb 的一种很有前途的选择。

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