Degradation Fate of Perfluorooctansulfonate (PFOS) and Perfluorooctanoic Acid (PFOA) by UV irradiation

  • Yamada Shingo
    Department of Chemical Engineering, Graduate School of Engineering, Tokyo University of Agriculture & Technology
  • Naito Yuta
    Department of Chemical Engineering, Graduate School of Engineering, Tokyo University of Agriculture & Technology
  • Yamamoto Takashi
    Research Center for Material Cycles and Waste Management, National Institute for Environmental Studies
  • Noma Yukio
    Research Center for Material Cycles and Waste Management, National Institute for Environmental Studies
  • Hosomi Masaaki
    Department of Chemical Engineering, Graduate School of Engineering, Tokyo University of Agriculture & Technology

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Other Title
  • ペルフルオロオクタンスルホン酸(PFOS)およびペルフルオロオクタン酸(PFOA)の紫外線分解処理挙動
  • ペルフルオロオクタンスルホンサン PFOS オヨビ ペルフルオロオクタンサン PFOA ノ シガイセン ブンカイ ショリ キョドウ

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Abstract

Perfluorooctanesulfonate (PFOS) and perfluorooctanoic acid (PFOA), persistent organic pollutants, were photodegraded by ultra-violet light irradiation in water, alkaline 2-propanol (IPA), water including H2O2 and water including both H2O2 and Fe2+, and the photodegradability in each condition was compared. F and SO42− were generated with the PFOS decomposition and F was generated with the PFOA decomposition. The degradation ratio of PFOS was lower than that of PFOA in each condition. The photodegradability of PFOS and PFOA depended on the sample condition. Effective degradation was observed in alkaline IPA for PFOS, and in water for PFOA. Added H2O2 increased the photodegradability of PFOS. With the photo-Fenton reaction, although the degradation ratio of PFOA reached to 100%, that of PFOS was only 28.6%.The C–F bond dissociation in PFOA molecular progressed slowly in water, however the process was accelerated under photo-Fenton condition. In PFOS, on the other hand, C–F bond dissociation was suppressed to progress under photo-Fenton condition.

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