2023
DOI: 10.1016/j.cej.2023.143476
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N-doped biochar mediated peroxydisulfate activation for selective degradation of bisphenol A: The key role of potential difference-driven electron transfer mechanism

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Cited by 30 publications
(7 citation statements)
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“…Three peaks of 284.7 285.3, and 290.3 eV in the C 1s spectrum were defined as CC (49.0%), CN (38.9%), and O–CO (12.1%), respectively (Figure S1g). As presented in Figure S1h, the N 1s spectrum was fitted into three characteristic peaks of pyridinic- N (398.6 eV, 40.8%), pyrrolic- N (400.3 eV, 34.1%), and graphitic- N (401.2 eV, 25.1%), respectively, demonstrating the presence of graphitic N. In addition, the O 1s spectrum had been fitted into four characteristic peaks of CO (532.0 eV, 37.6%), C–O–C (532.7 eV, 27.7%), C–OH (533.6 eV, 23.7%), and O 2 /C (536.9 eV, 11.0%), illustrating the presence of surface oxygenic functional groups (Figure S1i). The morphologies of Co-NCNRs were also investigated by SEM and TEM.…”
Section: Results and Discussionmentioning
confidence: 90%
“…Three peaks of 284.7 285.3, and 290.3 eV in the C 1s spectrum were defined as CC (49.0%), CN (38.9%), and O–CO (12.1%), respectively (Figure S1g). As presented in Figure S1h, the N 1s spectrum was fitted into three characteristic peaks of pyridinic- N (398.6 eV, 40.8%), pyrrolic- N (400.3 eV, 34.1%), and graphitic- N (401.2 eV, 25.1%), respectively, demonstrating the presence of graphitic N. In addition, the O 1s spectrum had been fitted into four characteristic peaks of CO (532.0 eV, 37.6%), C–O–C (532.7 eV, 27.7%), C–OH (533.6 eV, 23.7%), and O 2 /C (536.9 eV, 11.0%), illustrating the presence of surface oxygenic functional groups (Figure S1i). The morphologies of Co-NCNRs were also investigated by SEM and TEM.…”
Section: Results and Discussionmentioning
confidence: 90%
“…The porous structure of TSBC would promote closer contact between the pollutant and the catalyst, thereby enhancing PDS activation and pollutant degradation [37]. Furthermore, N doping would facilitate electron transfer between TSBC and S 2 O 2− 8 , increasing the 1 O 2 generation and thereby boosting the efficiency of the non-radical pathway in SMX degradation [28]. In summary, the TSBC demonstrated exceptional catalytic performance for PDS, significantly enhancing the degradation efficiency of SMX.…”
Section: Theoretical Calculationmentioning
confidence: 97%
“…Further detailed analyses of the catalytic mechanism have revealed a notable influence of N-and O-containing functional groups on the catalytic efficiency of sludge biochar. Tan et al [28] identified graphitic C, pyridine N, and graphitic N as the primary active sites in biochar, which are crucial for facilitating electron transfer and thus promoting PDS activation. Contrarily, Mian et al [29] showed that pyridine N was the predominant active species in their research, facilitating the degradation of pollutants via non-radical pathways.…”
Section: Introductionmentioning
confidence: 99%
“…Therefore, it is necessary to explore efficient technologies for the removal of organic dyes from the wastewater. Advanced oxidation processes based on peroxydisulfate (PDS) have attracted increasing attention for the treatment of aqueous contaminants in recent years. Compared to other radicals (•OH), SO 4 •– radical shows a lot of advantages during the oxidation process, such as high oxidative capacity, high stability, and long half-life. Usually, these excellent radicals are generated by activating PDS via heating, , light irradiation, acoustic cavitation, carbon materials, and transition metals catalyst . Among these activation methods, transition metal catalysts, such as Co, Mn, Fe, Cu, and Ni, are widely studied because of their high activation efficiency, comparatively low toxicity, and abundant in nature. …”
Section: Introductionmentioning
confidence: 99%