{"title":"核壳ZnO@ZIF-8-derived氮掺杂碳纳米管用于甲基橙的有效去除","authors":"Karthikeyan Chandrasekaran , Deepak Verma , Hiroshi Uyama , Manunya Okhawilai","doi":"10.1016/j.watcyc.2025.04.004","DOIUrl":null,"url":null,"abstract":"<div><div>The nitrogen-doped carbon nanotubes (NC) are synthesized via pyrolysis of zeolitic imidazolate framework-8 (ZIF-8) coated on ZnO nanorods, followed by acid etching. Morphological studies reveal that the NC shows a porous, tube-like structure with a diameter of 194 nm. The ZIF-8 template on the ZnO nanorods forms thin, shell-like layers surrounding the core ZnO. X-ray diffraction (XRD) analysis reveals the amorphous structure of NC, while FTIR/XPS spectra affirm nitrogen doping, Zn-N interaction in ZnO@ZIF-8, and the N-C environment in NC. The BET surface areas for ZnO@ZIF-8, ZnO@NC, and NC are 724.81 ± 12.77, 638.92 ± 1.29, and 787.11 ± 4.26 m<sup>2</sup> g<sup>−1</sup>, respectively. ZnO@NC and NC successfully removed MO at concentrations of 10 and 20 mg L<sup>−1</sup>, achieving equilibrium adsorption capacities of 50.23 and 100.50 mg g<sup>−1</sup>, respectively. The optimum conditions for ZnO@NC and NC were a pH of 6, a contact time of 60 min, and an adsorbent dosage of 0.2 g L<sup>−1</sup>, respectively. The high correlation coefficient R<sup>2</sup> (0.9983) from the Langmuir isotherm indicated monolayer adsorption on NC with the maximum adsorption capacity (q<sub>max</sub> = 126.58 mg g<sup>−1</sup>). NC followed pseudo-second-order kinetics with a high R<sup>2</sup> (0.999), substantiating the chemical interaction between the NC surface and MO. ZnO@NC showed chemical adsorption, while NC underwent physical and chemical adsorption, as identified through the isotherm (D-R) and kinetic (Elovich) models. The results show that NC proves a large BET surface area, a tubular structure, heterogeneous nitrogen-doped carbon, and abundant mesoporous channels that beneficially facilitate effective MO adsorption.</div></div>","PeriodicalId":34143,"journal":{"name":"Water Cycle","volume":"6 ","pages":"Pages 412-427"},"PeriodicalIF":8.7000,"publicationDate":"2025-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Core–shell ZnO@ZIF-8-derived nitrogen-doped carbon nanotubes for the effective removal of methyl orange\",\"authors\":\"Karthikeyan Chandrasekaran , Deepak Verma , Hiroshi Uyama , Manunya Okhawilai\",\"doi\":\"10.1016/j.watcyc.2025.04.004\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>The nitrogen-doped carbon nanotubes (NC) are synthesized via pyrolysis of zeolitic imidazolate framework-8 (ZIF-8) coated on ZnO nanorods, followed by acid etching. Morphological studies reveal that the NC shows a porous, tube-like structure with a diameter of 194 nm. The ZIF-8 template on the ZnO nanorods forms thin, shell-like layers surrounding the core ZnO. X-ray diffraction (XRD) analysis reveals the amorphous structure of NC, while FTIR/XPS spectra affirm nitrogen doping, Zn-N interaction in ZnO@ZIF-8, and the N-C environment in NC. The BET surface areas for ZnO@ZIF-8, ZnO@NC, and NC are 724.81 ± 12.77, 638.92 ± 1.29, and 787.11 ± 4.26 m<sup>2</sup> g<sup>−1</sup>, respectively. ZnO@NC and NC successfully removed MO at concentrations of 10 and 20 mg L<sup>−1</sup>, achieving equilibrium adsorption capacities of 50.23 and 100.50 mg g<sup>−1</sup>, respectively. The optimum conditions for ZnO@NC and NC were a pH of 6, a contact time of 60 min, and an adsorbent dosage of 0.2 g L<sup>−1</sup>, respectively. The high correlation coefficient R<sup>2</sup> (0.9983) from the Langmuir isotherm indicated monolayer adsorption on NC with the maximum adsorption capacity (q<sub>max</sub> = 126.58 mg g<sup>−1</sup>). NC followed pseudo-second-order kinetics with a high R<sup>2</sup> (0.999), substantiating the chemical interaction between the NC surface and MO. ZnO@NC showed chemical adsorption, while NC underwent physical and chemical adsorption, as identified through the isotherm (D-R) and kinetic (Elovich) models. The results show that NC proves a large BET surface area, a tubular structure, heterogeneous nitrogen-doped carbon, and abundant mesoporous channels that beneficially facilitate effective MO adsorption.</div></div>\",\"PeriodicalId\":34143,\"journal\":{\"name\":\"Water Cycle\",\"volume\":\"6 \",\"pages\":\"Pages 412-427\"},\"PeriodicalIF\":8.7000,\"publicationDate\":\"2025-01-01\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Water Cycle\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://www.sciencedirect.com/science/article/pii/S2666445325000182\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"Environmental Science\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Water Cycle","FirstCategoryId":"1085","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S2666445325000182","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"Environmental Science","Score":null,"Total":0}
Core–shell ZnO@ZIF-8-derived nitrogen-doped carbon nanotubes for the effective removal of methyl orange
The nitrogen-doped carbon nanotubes (NC) are synthesized via pyrolysis of zeolitic imidazolate framework-8 (ZIF-8) coated on ZnO nanorods, followed by acid etching. Morphological studies reveal that the NC shows a porous, tube-like structure with a diameter of 194 nm. The ZIF-8 template on the ZnO nanorods forms thin, shell-like layers surrounding the core ZnO. X-ray diffraction (XRD) analysis reveals the amorphous structure of NC, while FTIR/XPS spectra affirm nitrogen doping, Zn-N interaction in ZnO@ZIF-8, and the N-C environment in NC. The BET surface areas for ZnO@ZIF-8, ZnO@NC, and NC are 724.81 ± 12.77, 638.92 ± 1.29, and 787.11 ± 4.26 m2 g−1, respectively. ZnO@NC and NC successfully removed MO at concentrations of 10 and 20 mg L−1, achieving equilibrium adsorption capacities of 50.23 and 100.50 mg g−1, respectively. The optimum conditions for ZnO@NC and NC were a pH of 6, a contact time of 60 min, and an adsorbent dosage of 0.2 g L−1, respectively. The high correlation coefficient R2 (0.9983) from the Langmuir isotherm indicated monolayer adsorption on NC with the maximum adsorption capacity (qmax = 126.58 mg g−1). NC followed pseudo-second-order kinetics with a high R2 (0.999), substantiating the chemical interaction between the NC surface and MO. ZnO@NC showed chemical adsorption, while NC underwent physical and chemical adsorption, as identified through the isotherm (D-R) and kinetic (Elovich) models. The results show that NC proves a large BET surface area, a tubular structure, heterogeneous nitrogen-doped carbon, and abundant mesoporous channels that beneficially facilitate effective MO adsorption.