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使用合成的碱激发泡沫沸石吸附剂从水溶液中吸附铜(II)和镍(II):等温线、动力学及再生研究

Adsorption of Cu(II) and Ni(II) from Aqueous Solutions Using Synthesized Alkali-Activated Foamed Zeolite Adsorbent: Isotherm, Kinetic, and Regeneration Study.

作者信息

Svobodová Eliška, Tišler Zdeněk, Peroutková Kateřina, Strejcová Kateřina, Abrham Jan, Šimek Josef, Gholami Zahra, Vakili Mohammadtaghi

机构信息

ORLEN UniCRE, a.s., Revoluční 1521/84, 400 01 Ústí nad Labem, Czech Republic.

Faculty of Science, Jan Evangelista Purkyně University in Ústí nad Labem, Pasteurova 3632/15, 400 96 Ústí nad Labem, Czech Republic.

出版信息

Molecules. 2024 May 16;29(10):2357. doi: 10.3390/molecules29102357.

DOI:10.3390/molecules29102357
PMID:38792218
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11124001/
Abstract

Water pollution, particularly from heavy metals, poses a significant threat to global health, necessitating efficient and environmentally friendly removal methods. This study introduces novel zeolite-based adsorbents, specifically alkali-activated foamed zeolite (AAFZ), for the effective adsorption of Cu(II) and Ni(II) ions from aqueous solutions. The adsorbents' capabilities were comprehensively characterized through kinetic and isotherm analyses. Alkaline activation induced changes in chemical composition and crystalline structure, as observed via XRF and XRD analyses. AAFZ exhibited a significantly larger pore volume (1.29 times), higher Si/Al ratio (1.15 times), and lower crystallinity compared to ZZ50, thus demonstrating substantially higher adsorption capacity for Cu(II) and Ni(II) compared to ZZ50. The maximum monolayer adsorption capacities of ZZ50 and AAFZ for Cu(II) were determined to be 69.28 mg/g and 99.54 mg/g, respectively. In the case of Ni(II), the maximum monolayer adsorption capacities for ZZ50 and AAFZ were observed at 48.53 mg/g and 88.99 mg/g, respectively. For both adsorbents, the optimum pH for adsorption of Cu(II) and Ni(II) was found to be 5 and 6, respectively. Equilibrium was reached around 120 min, and the pseudo-second-order kinetics accurately depicted the chemisorption process. The Langmuir isotherm model effectively described monolayer adsorption for both adsorbents. Furthermore, the regeneration experiment demonstrated that AAFZ could be regenerated for a minimum of two cycles using hydrochloric acid (HCl). These findings highlight the potential of the developed adsorbents as promising tools for effective and practical adsorption applications.

摘要

水污染,尤其是重金属造成的水污染,对全球健康构成重大威胁,因此需要高效且环保的去除方法。本研究引入了新型的基于沸石的吸附剂,即碱活化泡沫沸石(AAFZ),用于从水溶液中有效吸附铜(II)和镍(II)离子。通过动力学和等温线分析全面表征了吸附剂的性能。如XRF和XRD分析所示,碱性活化导致化学成分和晶体结构发生变化。与ZZ50相比,AAFZ的孔体积显著更大(1.29倍),硅铝比更高(1.15倍),结晶度更低,因此与ZZ50相比,对铜(II)和镍(II)的吸附能力显著更高。ZZ50和AAFZ对铜(II)的最大单层吸附容量分别确定为69.28 mg/g和99.54 mg/g。对于镍(II),ZZ50和AAFZ的最大单层吸附容量分别为48.53 mg/g和88.99 mg/g。对于这两种吸附剂,吸附铜(II)和镍(II)的最佳pH值分别为5和6。约120分钟达到平衡,准二级动力学准确描述了化学吸附过程。Langmuir等温线模型有效地描述了两种吸附剂的单层吸附。此外,再生实验表明,AAFZ使用盐酸(HCl)至少可以再生两个循环。这些发现突出了所开发的吸附剂作为有效且实用的吸附应用的有前途工具的潜力。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/b289ab377b80/molecules-29-02357-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/f0703b1ec38f/molecules-29-02357-g001a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/0bc7b995229e/molecules-29-02357-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/d288d09feb96/molecules-29-02357-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/0471f1dcbefd/molecules-29-02357-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/e509dc70cf63/molecules-29-02357-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/a5c18dbc9407/molecules-29-02357-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/b289ab377b80/molecules-29-02357-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/f0703b1ec38f/molecules-29-02357-g001a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/0bc7b995229e/molecules-29-02357-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/d288d09feb96/molecules-29-02357-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/0471f1dcbefd/molecules-29-02357-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/e509dc70cf63/molecules-29-02357-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/a5c18dbc9407/molecules-29-02357-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e272/11124001/b289ab377b80/molecules-29-02357-g007.jpg

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