4.7 Article

Combination of hydrodynamic cavitation and SR-AOPs for simultaneous degradation of BTEX in water

Journal

CHEMICAL ENGINEERING JOURNAL
Volume 417, Issue -, Pages -

Publisher

ELSEVIER SCIENCE SA
DOI: 10.1016/j.cej.2020.128081

Keywords

Hydrodynamic cavitation; BTEX; Persulfate; Peroxymonosulfate; Sulfate radical; Hydroxyl radical

Funding

  1. National Science Centre, Warsaw, Poland within the project OPUS [UMO-2017/25/B/ST8/01364]
  2. National Natural Science Foundation of China [51906125]

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Hydrodynamic cavitation technology is gaining interest in water treatment for eliminating organic pollutants, with hybrid techniques like HC-PS and HC-PMS showing promising results in degrading BTEX. The molar ratio of oxidant to BTEX equal to 5 is favorable for both cases, allowing for efficient degradation of contaminants.
Hydrodynamic cavitation (HC) is an emerging technology gaining interest in water treatment for use in elimination of a wide range of organic pollutants. The energy released during cavitation phenomenon has number of applications and, particularly, it can be utilized for activation of persulfate (PS) and peroxymonosulfate (PMS). In the present study, hybrid techniques: HC combined with persulfates - HC-PS and HC-PMS were tested for the degradation of BTEX in water. Studies on the effect of initial PS and PMS concentration showed that a molar ratio of the oxidant to BTEX equal to 5 is favorable for both cases. Thus, in 240 min HC-PS-5 process allowed to degrade 91.51%, 95.50%, 94.65%, 94.95% of benzene, toluene, ethylbenzene and o-xylene, respectively, while 90.85%, 94.50%, 94.36%, 93.07% of those compounds were degraded by HC-PMS-5. BTEX degradation pathway was proposed for HC-PS-5 and HC-PMS-5 processes relying on the identification of the main reaction intermediates using liquid chromatography coupled with UV diode array detector (HPLC-UV-DAD). Benzyl alcohol, phenol, benzoic acid, benzaldehyde and o-cresol were the main intermediates of BTEX degradation, which multistep pathway involved H-abstraction, OH addition and dealkylation in route to mineralization. At final time of treatment primary and secondary pollutants were effectively degraded. In terms of kinetics, BTEX degradation followed the pseudo-first-order reaction model and the degradation kinetics were faster in HC-PMS-5 system than in HC-PS-5. Surprisingly, the presence of chloride ions (Cl) in HC-PMS-5 improved the degradation efficiency of alkylated benzene derivatives indicating a synergistic effect of Cl with SO4 center dot- radicals.

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