4.6 Article

Enhanced Degradation of Paracetamol by the Fe(III)-Sulfite System under UVA Irradiation

Journal

MOLECULES
Volume 27, Issue 7, Pages -

Publisher

MDPI
DOI: 10.3390/molecules27072248

Keywords

paracetamol; photodegradation; Fe(III); sulfite ions; sulfate radical

Funding

  1. National Natural Science Foundation of China (NSFC-CNRS_ PRC) [21711530144]
  2. CNRS [270437]
  3. China Scholarship Council
  4. project I-Site CAP 20-25 through the LIA Laboratory of Environmental Processes Remediation [I-Site CAP 20-25]

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This study investigates the effect of infrared radiation on the degradation efficiency of the Fe(III)/S(IV) system at near-neutral pH, and explores the mechanism of PARA degradation. The results show that radiation can accelerate the decrease of pH, resulting in higher degradation efficiency. Sulfate radical is identified as the main oxidant species responsible for the degradation process.
The Fe(III)-S(IV) system used for advanced oxidation processes (AOPs) at acidic pH has just been proposed and demonstrated valid for very few contaminants in the last several years. In this work, we investigated the effect of ultraviolet A (UVA) radiation on the degradation efficiency of the Fe(III)/S(IV) system at near-neutral pH. Paracetamol (PARA) was selected as a model contaminant. The influencing factors, such as initial pH and Fe(III)/S(IV) molar ratio on chemical kinetics, and the mechanism of PARA degradation are investigated, with an emphasis on the determination of dominant oxidant species. Our results show that irradiation enhances the PARA degradation by accelerating the decrease of pH to acidic levels, and the optimal pH for the degradation of PARA in the Fe(III)/S(IV)/O-2 system was around 4.0. At near-neutral pH, more than 60% of PARA was decomposed within 40 min under irradiation, whereas no significant degradation of PARA was observed using Fe(III)/S(IV) at pH 7.0 without irradiation. Mechanism investigation revealed that sulfate radical (SO4 center dot-) is the main oxidant species generated and responsible for the PARA degradation under these conditions. This finding may have promising implications in developing a new degradation process for dealing with wastewater at near-neutral pH by the Fe(III)/S(IV)/O-2 system under UVA irradiation.

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