Photo-Fenton and oxygen vacancies' synergy for enhancing catalytic activity with S-scheme FeS/BiWO heterostructure

Using calcination and solvothermal methods, a series of FeS 2 /Bi 2 WO 6 heterojunctions were prepared by coupling FeS 2 into the surface oxygen vacancy enriched Bi 2 WO 6 . The prepared catalysts were used as photo-Fenton catalysts to degrade tetracycline hydrochloride (TC-HCl) and rhodamine B (RhB...

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Veröffentlicht in:Catalysis science & technology 2022-07, Vol.12 (13), p.4228-4242
Hauptverfasser: Ye, Jin, Zhang, Yuanyuan, Wang, Juan, Liu, Shuang, Chang, Yuanhang, Xu, Xiuping, Feng, Chunte, Xu, Jian, Guo, Li, Xu, Jiating, Fu, Yujie
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container_issue 13
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container_title Catalysis science & technology
container_volume 12
creator Ye, Jin
Zhang, Yuanyuan
Wang, Juan
Liu, Shuang
Chang, Yuanhang
Xu, Xiuping
Feng, Chunte
Xu, Jian
Guo, Li
Xu, Jiating
Fu, Yujie
description Using calcination and solvothermal methods, a series of FeS 2 /Bi 2 WO 6 heterojunctions were prepared by coupling FeS 2 into the surface oxygen vacancy enriched Bi 2 WO 6 . The prepared catalysts were used as photo-Fenton catalysts to degrade tetracycline hydrochloride (TC-HCl) and rhodamine B (RhB). Then, a rational catalytic mechanism where an S-scheme catalyst was constructed between FeS 2 and Bi 2 WO 6 -OVs was put forward. Furthermore, electron spin resonance (ESR) was employed to confirm that the main active substances in the photo-Fenton degradation process are hydroxyl radicals (&z.rad;OH) and superoxide radicals (&z.rad;O 2 − ). The enhancement of catalytic activity is mainly due to the synergistic effect between photocatalytic oxidation and Fenton oxidation. And the introduction of oxygen vacancies can not only broaden the light absorption range of the catalyst because of the rise of the valence band but also promote the efficient separation of photogenerated carriers. Besides, the O-O bond of H 2 O 2 could be elongated and weakened due to the presence of surface oxygen vacancies, which can promote the decomposition of H 2 O 2 . Meanwhile, the photogenerated electrons in the conduction band (CB) of Bi 2 WO 6 -OVs can rapidly transfer to FeS 2 near the oxygen vacancies on the catalyst surface, which can achieve a cyclic process from Fe 3+ to Fe 2+ and boost the degradation efficiency of traditional Fenton catalysis and photocatalysis. The experimental results showed the photo-Fenton rate constants for TC-HCl and RhB over 1%FeS 2 /Bi 2 WO 6 which were evaluated to be about 0.04430 and 0.02007 min 1 within 50 and 150 min, which was 1.74 and 1.41 times that of the optimum Fenton process, respectively. This strategy showed that the FeS 2 /Bi 2 WO 6 heterostructure has great advantages in photo-Fenton treatment of multiple organic pollutants due to the synergy of photocatalysis and Fenton catalysis. A series of FeS 2 /Bi 2 WO 6 S-scheme photo-Fenton catalysts with efficient catalytic performances were successfully prepared by coupling FeS 2 into the surface oxygen vacancy enriched Bi 2 WO 6 using calcination and solvothermal methods.
doi_str_mv 10.1039/d2cy00610c
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The prepared catalysts were used as photo-Fenton catalysts to degrade tetracycline hydrochloride (TC-HCl) and rhodamine B (RhB). Then, a rational catalytic mechanism where an S-scheme catalyst was constructed between FeS 2 and Bi 2 WO 6 -OVs was put forward. Furthermore, electron spin resonance (ESR) was employed to confirm that the main active substances in the photo-Fenton degradation process are hydroxyl radicals (&amp;z.rad;OH) and superoxide radicals (&amp;z.rad;O 2 − ). The enhancement of catalytic activity is mainly due to the synergistic effect between photocatalytic oxidation and Fenton oxidation. And the introduction of oxygen vacancies can not only broaden the light absorption range of the catalyst because of the rise of the valence band but also promote the efficient separation of photogenerated carriers. Besides, the O-O bond of H 2 O 2 could be elongated and weakened due to the presence of surface oxygen vacancies, which can promote the decomposition of H 2 O 2 . Meanwhile, the photogenerated electrons in the conduction band (CB) of Bi 2 WO 6 -OVs can rapidly transfer to FeS 2 near the oxygen vacancies on the catalyst surface, which can achieve a cyclic process from Fe 3+ to Fe 2+ and boost the degradation efficiency of traditional Fenton catalysis and photocatalysis. The experimental results showed the photo-Fenton rate constants for TC-HCl and RhB over 1%FeS 2 /Bi 2 WO 6 which were evaluated to be about 0.04430 and 0.02007 min 1 within 50 and 150 min, which was 1.74 and 1.41 times that of the optimum Fenton process, respectively. This strategy showed that the FeS 2 /Bi 2 WO 6 heterostructure has great advantages in photo-Fenton treatment of multiple organic pollutants due to the synergy of photocatalysis and Fenton catalysis. A series of FeS 2 /Bi 2 WO 6 S-scheme photo-Fenton catalysts with efficient catalytic performances were successfully prepared by coupling FeS 2 into the surface oxygen vacancy enriched Bi 2 WO 6 using calcination and solvothermal methods.</description><identifier>ISSN: 2044-4753</identifier><identifier>EISSN: 2044-4761</identifier><identifier>DOI: 10.1039/d2cy00610c</identifier><ispartof>Catalysis science &amp; technology, 2022-07, Vol.12 (13), p.4228-4242</ispartof><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,778,782,27907,27908</link.rule.ids></links><search><creatorcontrib>Ye, Jin</creatorcontrib><creatorcontrib>Zhang, Yuanyuan</creatorcontrib><creatorcontrib>Wang, Juan</creatorcontrib><creatorcontrib>Liu, Shuang</creatorcontrib><creatorcontrib>Chang, Yuanhang</creatorcontrib><creatorcontrib>Xu, Xiuping</creatorcontrib><creatorcontrib>Feng, Chunte</creatorcontrib><creatorcontrib>Xu, Jian</creatorcontrib><creatorcontrib>Guo, Li</creatorcontrib><creatorcontrib>Xu, Jiating</creatorcontrib><creatorcontrib>Fu, Yujie</creatorcontrib><title>Photo-Fenton and oxygen vacancies' synergy for enhancing catalytic activity with S-scheme FeS/BiWO heterostructure</title><title>Catalysis science &amp; technology</title><description>Using calcination and solvothermal methods, a series of FeS 2 /Bi 2 WO 6 heterojunctions were prepared by coupling FeS 2 into the surface oxygen vacancy enriched Bi 2 WO 6 . The prepared catalysts were used as photo-Fenton catalysts to degrade tetracycline hydrochloride (TC-HCl) and rhodamine B (RhB). Then, a rational catalytic mechanism where an S-scheme catalyst was constructed between FeS 2 and Bi 2 WO 6 -OVs was put forward. Furthermore, electron spin resonance (ESR) was employed to confirm that the main active substances in the photo-Fenton degradation process are hydroxyl radicals (&amp;z.rad;OH) and superoxide radicals (&amp;z.rad;O 2 − ). The enhancement of catalytic activity is mainly due to the synergistic effect between photocatalytic oxidation and Fenton oxidation. And the introduction of oxygen vacancies can not only broaden the light absorption range of the catalyst because of the rise of the valence band but also promote the efficient separation of photogenerated carriers. Besides, the O-O bond of H 2 O 2 could be elongated and weakened due to the presence of surface oxygen vacancies, which can promote the decomposition of H 2 O 2 . Meanwhile, the photogenerated electrons in the conduction band (CB) of Bi 2 WO 6 -OVs can rapidly transfer to FeS 2 near the oxygen vacancies on the catalyst surface, which can achieve a cyclic process from Fe 3+ to Fe 2+ and boost the degradation efficiency of traditional Fenton catalysis and photocatalysis. The experimental results showed the photo-Fenton rate constants for TC-HCl and RhB over 1%FeS 2 /Bi 2 WO 6 which were evaluated to be about 0.04430 and 0.02007 min 1 within 50 and 150 min, which was 1.74 and 1.41 times that of the optimum Fenton process, respectively. This strategy showed that the FeS 2 /Bi 2 WO 6 heterostructure has great advantages in photo-Fenton treatment of multiple organic pollutants due to the synergy of photocatalysis and Fenton catalysis. 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The prepared catalysts were used as photo-Fenton catalysts to degrade tetracycline hydrochloride (TC-HCl) and rhodamine B (RhB). Then, a rational catalytic mechanism where an S-scheme catalyst was constructed between FeS 2 and Bi 2 WO 6 -OVs was put forward. Furthermore, electron spin resonance (ESR) was employed to confirm that the main active substances in the photo-Fenton degradation process are hydroxyl radicals (&amp;z.rad;OH) and superoxide radicals (&amp;z.rad;O 2 − ). The enhancement of catalytic activity is mainly due to the synergistic effect between photocatalytic oxidation and Fenton oxidation. And the introduction of oxygen vacancies can not only broaden the light absorption range of the catalyst because of the rise of the valence band but also promote the efficient separation of photogenerated carriers. Besides, the O-O bond of H 2 O 2 could be elongated and weakened due to the presence of surface oxygen vacancies, which can promote the decomposition of H 2 O 2 . Meanwhile, the photogenerated electrons in the conduction band (CB) of Bi 2 WO 6 -OVs can rapidly transfer to FeS 2 near the oxygen vacancies on the catalyst surface, which can achieve a cyclic process from Fe 3+ to Fe 2+ and boost the degradation efficiency of traditional Fenton catalysis and photocatalysis. The experimental results showed the photo-Fenton rate constants for TC-HCl and RhB over 1%FeS 2 /Bi 2 WO 6 which were evaluated to be about 0.04430 and 0.02007 min 1 within 50 and 150 min, which was 1.74 and 1.41 times that of the optimum Fenton process, respectively. This strategy showed that the FeS 2 /Bi 2 WO 6 heterostructure has great advantages in photo-Fenton treatment of multiple organic pollutants due to the synergy of photocatalysis and Fenton catalysis. A series of FeS 2 /Bi 2 WO 6 S-scheme photo-Fenton catalysts with efficient catalytic performances were successfully prepared by coupling FeS 2 into the surface oxygen vacancy enriched Bi 2 WO 6 using calcination and solvothermal methods.</abstract><doi>10.1039/d2cy00610c</doi><tpages>15</tpages></addata></record>
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