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Activation of peroxymonosulfate by molybdenum disulfide-mediated traces of Fe(III) for sulfadiazine degradation.
Li, Yu; Feng, Yong; Yang, Bin; Yang, Zequn; Shih, Kaimin.
Affiliation
  • Li Y; SCNU Environmental Research Institute, Guangdong Provincial Key Laboratory of Chemical Pollution and Environmental Safety & MOE Key Laboratory of Theoretical Chemistry of Environment, South China Normal University, Guangzhou, 510006, China; School of Environment, South China Normal University, U
  • Feng Y; SCNU Environmental Research Institute, Guangdong Provincial Key Laboratory of Chemical Pollution and Environmental Safety & MOE Key Laboratory of Theoretical Chemistry of Environment, South China Normal University, Guangzhou, 510006, China; School of Environment, South China Normal University, U
  • Yang B; SCNU Environmental Research Institute, Guangdong Provincial Key Laboratory of Chemical Pollution and Environmental Safety & MOE Key Laboratory of Theoretical Chemistry of Environment, South China Normal University, Guangzhou, 510006, China; School of Environment, South China Normal University, U
  • Yang Z; Department of Civil Engineering, The University of Hong Kong, Pok Fu Lam, Hong Kong, China. Electronic address: Zequn_Yang@hotmail.com.
  • Shih K; Department of Civil Engineering, The University of Hong Kong, Pok Fu Lam, Hong Kong, China. Electronic address: kshih@hku.hk.
Chemosphere ; 283: 131212, 2021 Nov.
Article in En | MEDLINE | ID: mdl-34146879
The activation of persulfate by ferrous iron (Fe(II)) is of great interest to the environmental remediation community, but the reduction of ferric iron (Fe(III)) to Fe(II) is slow and the accumulation of iron sludge resulted from the precipitation of Fe(III) is a great concern. Here, molybdenum disulfide (MoS2) was studied as a co-catalyst to improve the activation of peroxymonosulfate (PMS) by Fe(III) for sulfadiazine (SDZ) degradation and different characterization technologies were used to reveal the reactive species. The results showed that a strong synergy existed between MoS2 and Fe(III); approximately 94.3% of the SDZ was removed by MoS2-Fe(III)-PMS after reaction for 30 min, while only 8.5% and 56.4% of the SDZ was removed by Fe(III)-PMS and MoS2-PMS, respectively. Both hydroxyl radicals and sulfate radicals were generated and the latter was the primary species. In addition to the radicals, singlet oxygen was found to be generated and contributed to the degradation of SDZ. The chemical probe reaction with methyl phenyl sulfoxide showed that the generation of high-valent iron-oxo species was not obvious by MoS2-Fe(III)-PMS under both acidic and neutral conditions. MoS2 had good stability. No noticeable deactivation was observed during the 1st to 5th run and no obvious oxidation of surface Mo(IV) occurred. Based on the characterization of catalyst and oxidizing species, a mechanism for the activation of PMS by MoS2-Fe(III) was proposed. The results from this study are expected to clarify the reactive species and deepen the understanding of MoS2-promoted persulfate activation by Fe(II)/Fe(III).
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Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Sulfadiazine / Molybdenum Language: En Journal: Chemosphere Year: 2021 Document type: Article Country of publication: Reino Unido

Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Sulfadiazine / Molybdenum Language: En Journal: Chemosphere Year: 2021 Document type: Article Country of publication: Reino Unido