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Reactivity of Performic Acid with Organic and Inorganic Compounds: From Oxidation Kinetics to Reaction Pathways

  • Christelle Nabintu Kajoka
    Christelle Nabintu Kajoka
    LEESU, Ecole des Ponts, Univ Paris Est Creteil, F-94010 Creteil, France
  • Johnny Gasperi
    Johnny Gasperi
    LEE - Laboratoire Eau et Environnement, Université Gustave Eiffel, F-44344 Bouguenais, France
  • Stephan Brosillon
    Stephan Brosillon
    IEM - Institut Européen des Membranes, Université de Montpellier, F-34090 Montpellier, France
  • Emilie Caupos
    Emilie Caupos
    LEESU, Ecole des Ponts, Univ Paris Est Creteil, F-94010 Creteil, France
  • Emmanuelle Mebold
    Emmanuelle Mebold
    Observatoire des Sciences de l’Univers OSU-EFLUVE, plateforme PRAMMICS, Université Paris Est Créteil, CNRS, F-94010 Créteil, France
  • Marcos Oliveira
    Marcos Oliveira
    SIAAP - Service Public de l’assainissement Francilien (SIAAP), Direction Innovation, F-92700 Colombes, France
  • Vincent Rocher
    Vincent Rocher
    SIAAP - Service Public de l’assainissement Francilien (SIAAP), Direction Innovation, F-92700 Colombes, France
  • Ghassan Chebbo
    Ghassan Chebbo
    LEESU, Ecole des Ponts, Univ Paris Est Creteil, F-94010 Creteil, France
  • , and 
  • Julien Le Roux*
    Julien Le Roux
    LEESU, Ecole des Ponts, Univ Paris Est Creteil, F-94010 Creteil, France
    *Email: [email protected]. Tel.: +33(0)182392080.
Cite this: ACS EST Water 2023, 3, 9, 3121–3131
Publication Date (Web):August 29, 2023
https://doi.org/10.1021/acsestwater.3c00279
Copyright © 2023 American Chemical Society

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    Abstract

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    Performic acid (PFA) has gained interest as an alternative chemical disinfectant for wastewater (WW) treatment, but its reactivity with WW constituents remains poorly understood. This study evaluated PFA’s ability to oxidize 45 inorganic and organic compounds commonly found in WW (amino acids, simple organic compounds with specific functional groups, e.g., amines and phenolic compounds, and pharmaceutical micropollutants). PFA does not react with most major ions, except for iodide ions, and reacts with iron(II) in the absence of phosphate buffer. While many organic molecules do not react with PFA, compounds containing reduced-sulfur moieties (e.g., thioether or thiol) are the most reactive (i.e., ranitidine, benzenethiol, and 3-mercaptophenol), followed by compounds with tertiary amine groups (e.g., lidocaine). The reactions follow second-order kinetics with respect to both organic compounds and PFA concentrations. Similar trends were observed in real WW effluents, although removals of pharmaceuticals were lower than expected due to the probable consumption of PFA by WW constituents (dissolved organic carbon, other micropollutants, or transition metals). The results highlight PFA’s selective reactivity with specific functional groups and a low transformation of compounds mostly through oxygen addition (e.g., S-oxide or sulfonyl compounds formed from thiol and thioether moieties and N-oxides from amine groups) with similar mechanisms to peracetic acid.

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    The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acsestwater.3c00279.

    • Additional analytical details, effect of several parameters (phosphate ion, background H2O2 concentration, PFA initial concentration, pH) on PFA autodecomposition and oxidation kinetics, additional kinetics results, species distribution diagrams of PFA and selected micropollutants or inorganic ions, HRMS detailed identifications and the corresponding reaction pathways, and HRMS spectra of micropollutants and their transformation products (PDF)

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