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Metallic Active Sites on MoO(2)(110) Surface to Catalyze Advanced Oxidation Processes for Efficient Pollutant Removal

Advanced oxidation processes (AOPs) based on sulfate radicals (SO(4)(⋅−)) suffer from low conversion rate of Fe(III) to Fe(II) and produce a large amount of iron sludge as waste. Herein, we show that by using MoO(2) as a cocatalyst, the rate of Fe(III)/Fe(II) cycling in PMS system accelerated signif...

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Detalles Bibliográficos
Autores principales: Ji, Jiahui, Aleisa, Rashed M., Duan, Huan, Zhang, Jinlong, Yin, Yadong, Xing, Mingyang
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Elsevier 2020
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7011042/
https://www.ncbi.nlm.nih.gov/pubmed/32058972
http://dx.doi.org/10.1016/j.isci.2020.100861
Descripción
Sumario:Advanced oxidation processes (AOPs) based on sulfate radicals (SO(4)(⋅−)) suffer from low conversion rate of Fe(III) to Fe(II) and produce a large amount of iron sludge as waste. Herein, we show that by using MoO(2) as a cocatalyst, the rate of Fe(III)/Fe(II) cycling in PMS system accelerated significantly, with a reaction rate constant 50 times that of PMS/Fe(II) system. Our results showed outstanding removal efficiency (96%) of L-RhB in 10 min with extremely low concentration of Fe(II) (0.036 mM), outperforming most reported SO(4)(⋅−)-based AOPs systems. Surface chemical analysis combined with density functional theory (DFT) calculation demonstrated that both Fe(III)/Fe(II) cycling and PMS activation occurred on the (110) crystal plane of MoO(2), whereas the exposed active sites of Mo(IV) on MoO(2) surface were responsible for accelerating PMS activation. Considering its performance, and non-toxicity, using MoO(2) as a cocatalyst is a promising technique for large-scale practical environmental remediation.