4.7 Article

A comparative study of activation of peroxymonosulfate and peroxydisulfate by greigite (Fe3S4) for the degradation of sulfamethazine in water

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ELSEVIER
DOI: 10.1016/j.seppur.2022.120873

关键词

Advanced oxidation; Greigite; Peroxymonosulfate; Peroxydisulfate; Sulfamethoazine

资金

  1. National Natural Science Foun-dation of China [52122011, 51879100]
  2. Science and Technol-ogy Innovation Program of Hunan Province [2021RC3050]

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In this study, greigite (Fe3S4) was used as a catalyst to degrade sulfamethoazine (SMT) in water using peroxymonosulfate (PMS) and peroxydisulfate (PDS) as activators. Factors such as oxidant concentration, sulfur sources, iron sources, and pH were investigated. The results showed that SMT could be completely removed in the Fe3S4/PMS system at a concentration of 0.1 mM within 15 minutes, and 96.7% of SMT could be removed in the Fe3S4/PDS system at a concentration of 1.0 mM within 60 minutes. The study also evaluated the degradation intermediates of SMT and their practical application in both systems.
In this study, greigite (Fe3S4) was used to activate peroxymonosulfate (PMS) and peroxydisulfate (PDS) for sulfamethoazine (SMT) degradation in water. The possible influencing factors such as oxidant concentration, sulfur sources, iron sources and initial pH were investigated. Experimental results showed that SMT could be completely removed at 0.1 mM PMS in 15 min in Fe3S4/PMS system. 96.7% of SMT was removed at 1.0 mM PDS in 60 min in Fe3S4/PDS system. Both systems had good performance over a wide pH range of 3-9. In addition, different sulfur sources could affect the crystal structure, morphology and composition of the synthesized catalysts, while different iron sources had little influence. Quenching experiments and electron paramagnetic resonance (EPR) test evidenced that the activation of PMS and PDS by Fe3S4 was a multi-reactive oxygen species process with the coexistence of center dot OH, SO4 center dot-, O-2(center dot-) and O-1(2). SO4 center dot- was the main active species in the Fe3S4/PMS system, while SO4 center dot- and center dot OH were the main free radicals in the Fe3S4/PDS system. X-ray photoelectron spectroscopy (XPS) experiments showed that Fe(II) on Fe3S4 surface effectively activated PMS and PDS, and S2- species were key factors controlling Fe(II) regeneration and subsequent activation of PMS and PDS. However, the consumption of Fe(II) and S2- in Fe3S4/PDS system was higher than that in Fe3S4/PMS system. In addition, in the two systems, the degradation intermediates of SMT and their practical application were also evaluated. This study provided a systematic evaluation of the performance of Fe3S4/PMS and Fe3S4/PDS systems for treatment of antibiotic contaminated water.

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