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Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia

In this study, an (A-R)TiO(2) catalyst (ART) was prepared via the sol–gel method, and g-C(3)N(4) (CN) was used as an amendment to prepare the g-C(3)N(4)/(A-R)TiO(2) composite catalyst (ARTCN). X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), Raman...

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Autores principales: Zhu, Jiaming, Liu, Zuohua, Wang, Hao, Jian, Yue, Long, Dingbiao, Pu, Shihua
Formato: Online Artículo Texto
Lenguaje:English
Publicado: MDPI 2022
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9657263/
https://www.ncbi.nlm.nih.gov/pubmed/36361920
http://dx.doi.org/10.3390/ijms232113131
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author Zhu, Jiaming
Liu, Zuohua
Wang, Hao
Jian, Yue
Long, Dingbiao
Pu, Shihua
author_facet Zhu, Jiaming
Liu, Zuohua
Wang, Hao
Jian, Yue
Long, Dingbiao
Pu, Shihua
author_sort Zhu, Jiaming
collection PubMed
description In this study, an (A-R)TiO(2) catalyst (ART) was prepared via the sol–gel method, and g-C(3)N(4) (CN) was used as an amendment to prepare the g-C(3)N(4)/(A-R)TiO(2) composite catalyst (ARTCN). X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), Raman spectroscopy, N(2) adsorption–desorption curves (BET), UV–Vis diffuse absorption spectroscopy (UV–Vis DRS), and fluorescence spectroscopy (PL) were used to evaluate the structure, morphology, specific surface area, optical properties, and photocarrier separation ability of the catalysts. The results showed that when the modifier CN content was 0.5 g, the dispersion of the ARTCN composite catalyst was better, with stronger light absorption performance, and the forbidden band width was smaller. Moreover, the photogenerated electrons in the conduction band of ART transferred to the valence band of CN and combined with the holes in the valence band of CN, forming Z-type heterostructures that significantly improved the efficiency of the photogenerated electron-hole migration and separation, thus increasing the reaction rate. Gaseous and liquid ammonia were used as the target pollutants to investigate the activity of the prepared catalysts, and the results showed that the air wetness and initial concentration of ammonia had a great influence on the degradation of gaseous ammonia. When the initial concentration of ammonia was 50 mg/m(3) and the flow rate of the moist air was 0.9 mL/min, the degradation rate of gaseous ammonia by ARTCN-0.5 reached 88.86%, and it had good repeatability. When the catalytic dose was 50 mg and the initial concentration of NH(4)(+) was 100 mg/L, the degradation rate of liquid ammonia by ARTCN-0.5 was 71.60% after 3 h of reaction, and small amounts of NO(3)(−) and NO(2)(−) were generated. The superoxide anion radical (·O(2)(−)) and hydroxyl radical (·OH) were the main active components in the photocatalytic reaction process.
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spelling pubmed-96572632022-11-15 Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia Zhu, Jiaming Liu, Zuohua Wang, Hao Jian, Yue Long, Dingbiao Pu, Shihua Int J Mol Sci Article In this study, an (A-R)TiO(2) catalyst (ART) was prepared via the sol–gel method, and g-C(3)N(4) (CN) was used as an amendment to prepare the g-C(3)N(4)/(A-R)TiO(2) composite catalyst (ARTCN). X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), Raman spectroscopy, N(2) adsorption–desorption curves (BET), UV–Vis diffuse absorption spectroscopy (UV–Vis DRS), and fluorescence spectroscopy (PL) were used to evaluate the structure, morphology, specific surface area, optical properties, and photocarrier separation ability of the catalysts. The results showed that when the modifier CN content was 0.5 g, the dispersion of the ARTCN composite catalyst was better, with stronger light absorption performance, and the forbidden band width was smaller. Moreover, the photogenerated electrons in the conduction band of ART transferred to the valence band of CN and combined with the holes in the valence band of CN, forming Z-type heterostructures that significantly improved the efficiency of the photogenerated electron-hole migration and separation, thus increasing the reaction rate. Gaseous and liquid ammonia were used as the target pollutants to investigate the activity of the prepared catalysts, and the results showed that the air wetness and initial concentration of ammonia had a great influence on the degradation of gaseous ammonia. When the initial concentration of ammonia was 50 mg/m(3) and the flow rate of the moist air was 0.9 mL/min, the degradation rate of gaseous ammonia by ARTCN-0.5 reached 88.86%, and it had good repeatability. When the catalytic dose was 50 mg and the initial concentration of NH(4)(+) was 100 mg/L, the degradation rate of liquid ammonia by ARTCN-0.5 was 71.60% after 3 h of reaction, and small amounts of NO(3)(−) and NO(2)(−) were generated. The superoxide anion radical (·O(2)(−)) and hydroxyl radical (·OH) were the main active components in the photocatalytic reaction process. MDPI 2022-10-28 /pmc/articles/PMC9657263/ /pubmed/36361920 http://dx.doi.org/10.3390/ijms232113131 Text en © 2022 by the authors. https://creativecommons.org/licenses/by/4.0/Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
spellingShingle Article
Zhu, Jiaming
Liu, Zuohua
Wang, Hao
Jian, Yue
Long, Dingbiao
Pu, Shihua
Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia
title Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia
title_full Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia
title_fullStr Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia
title_full_unstemmed Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia
title_short Preparation of a Z-Type g-C(3)N(4)/(A-R)TiO(2) Composite Catalyst and Its Mechanism for Degradation of Gaseous and Liquid Ammonia
title_sort preparation of a z-type g-c(3)n(4)/(a-r)tio(2) composite catalyst and its mechanism for degradation of gaseous and liquid ammonia
topic Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9657263/
https://www.ncbi.nlm.nih.gov/pubmed/36361920
http://dx.doi.org/10.3390/ijms232113131
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