Enhancing a novel Al2O3–Chitosan@activated carbon nanocomposite for indoor air quality: Examination of vapor-phase phenanthrene adsorption efficiency of air cleaner material

IF 4.7 2区 化学 Q2 CHEMISTRY, PHYSICAL Journal of Molecular Structure Pub Date : 2025-03-20 DOI:10.1016/j.molstruc.2025.142126
Kaan Isinkaralar , Aydin Turkyilmaz , Hüseyin Güran Ünal , Ahmad Hosseini-Bandegharaei
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Abstract

Herein, we report the chemical activation of Triticum monococcum (einkorn wheat) waste biomass (TRM) with ZnCl2 to obtain a tailored activated carbon (TAC) and modified TAC (MTAC). Chitosan and aluminum oxide nanoparticles (CS–Al2O3@TAC) were incorporated to prepare MTAC. Both TAC and MTAC were exploited for the removal of non-polar phenanthrene (PHE) from the controlled gas steam. The effectiveness of the resulting MTAC was systematically investigated in the gas to solid-phase removal of PHE. Also, the physicochemical properties were evaluated by the Brunauer-Emmett-Teller specific surface area (583 m2g-1 for TAC and 729 m2g-1 for MTAC), Fourier transform infrared spectroscopy, scanning electron microscopy, thermogravimetric analysis, and powder X-ray diffraction. The findings revealed that the MTAC composite is a promising adsorbent for developing cost-effective filters to remove polycyclic aromatic hydrocarbons from indoor environments. The PHE adsorption on MTAC (85 mg g-1) was higher than on TAC (60 mg g-1) during the first 50 min, attributed to the oxygenated functional groups. The adsorption capacity of MTAC increased sharply at concentration of 300 ng m-3 and then slowly increased up to 131 mg g-1 at 500 ng m-3. The adsorption isotherms at different temperatures were determined by thermodynamic parameters such as free energy (ΔG° = −2.59 kJ mol-1 to −5.03 kJ mol-1 for TAC; ΔG° = −5.69 kJ mol-1 to −8.95 kJ mol-1 for MTAC), enthalpy (ΔH° = 30.49 kJ mol-1 for TAC; ΔH° = 36.53 kJ mol-1 for MTAC), entropy (ΔS° = 0.14 kJ mol-1 K for TAC; ΔS° = 0.15 kJ mol-1 K for MTAC) and, overall, PHE adsorption was feasible, spontaneous, and endothermic. This work showed that incorporation of CS–NPs and Al2O3–NPs into TAC brings about better adsorption properties , compared to pristine TAC, which can be attributed to the modification of major functional groups. The desorption efficiency of TAC (73 %) and MTAC (86 %) decreased over five cycles of multiple reuse. Moreover, the adsorption capacity of MTAC remained noticeably higher than that of TAC, suggesting that chemical modification can enhance the removal of gas flow PHE.

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提高新型 Al2O3-Citosan@ 活性炭纳米复合材料的室内空气质量:检验空气净化器材料的气相菲吸附效率
在此,我们报道了用ZnCl2对单粒小麦(小麦)废生物质(TRM)进行化学活化,得到了定制活性炭(TAC)和改性活性炭(MTAC)。壳聚糖和氧化铝纳米颗粒(CS - Al2O3@TAC)掺入制备MTAC。采用TAC和MTAC两种方法对受控燃气蒸汽中的非极性菲进行脱除。系统地研究了所得到的MTAC在气固相脱除PHE中的有效性。此外,通过brunauer - emmet - teller比表面积(TAC为583 m2g-1, MTAC为729 m2g-1)、傅里叶变换红外光谱、扫描电子显微镜、热重分析和粉末x射线衍射来评估其物理化学性质。研究结果表明,MTAC复合材料是一种很有前途的吸附剂,可用于开发具有成本效益的过滤器,以去除室内环境中的多环芳烃。MTAC (85 mg g-1)对PHE的吸附在前50 min高于TAC (60 mg g-1),这是由于含氧官能团的作用。MTAC的吸附量在浓度为300 ng m-3时急剧增加,在浓度为500 ng m-3时缓慢增加至131 mg g-1。通过自由能(ΔG°= - 2.59 kJ mol-1 ~ - 5.03 kJ mol-1)等热力学参数确定了TAC在不同温度下的吸附等温线;ΔG°=−5.69 kJ mol-1至−8.95 kJ mol-1的MTAC),焓(ΔH°= 30.49 kJ mol-1的TAC;ΔH°= 36.53 kJ mol-1 MTAC),熵(ΔS°= 0.14 kJ mol-1 K TAC;ΔS°= 0.15 kJ mol-1 K (MTAC)),总的来说,PHE吸附是可行的,自发的,吸热的。本研究表明,与原始TAC相比,CS-NPs和Al2O3-NPs掺入TAC具有更好的吸附性能,这可归因于主要官能团的修饰。在重复使用5次循环后,TAC(73%)和MTAC(86%)的解吸效率下降。此外,MTAC的吸附能力明显高于TAC,说明化学改性可以增强气流PHE的去除。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Journal of Molecular Structure
Journal of Molecular Structure 化学-物理化学
CiteScore
7.10
自引率
15.80%
发文量
2384
审稿时长
45 days
期刊介绍: The Journal of Molecular Structure is dedicated to the publication of full-length articles and review papers, providing important new structural information on all types of chemical species including: • Stable and unstable molecules in all types of environments (vapour, molecular beam, liquid, solution, liquid crystal, solid state, matrix-isolated, surface-absorbed etc.) • Chemical intermediates • Molecules in excited states • Biological molecules • Polymers. The methods used may include any combination of spectroscopic and non-spectroscopic techniques, for example: • Infrared spectroscopy (mid, far, near) • Raman spectroscopy and non-linear Raman methods (CARS, etc.) • Electronic absorption spectroscopy • Optical rotatory dispersion and circular dichroism • Fluorescence and phosphorescence techniques • Electron spectroscopies (PES, XPS), EXAFS, etc. • Microwave spectroscopy • Electron diffraction • NMR and ESR spectroscopies • Mössbauer spectroscopy • X-ray crystallography • Charge Density Analyses • Computational Studies (supplementing experimental methods) We encourage publications combining theoretical and experimental approaches. The structural insights gained by the studies should be correlated with the properties, activity and/ or reactivity of the molecule under investigation and the relevance of this molecule and its implications should be discussed.
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