Sonochemical degradation of chlorophenols in water

Sonochemical degradation of dilute aqueous solutions of 2-, 3- and 4-chlorophenol and pentachlorophenol has been investigated under air or argon atmosphere. The degradation follows first-order kinetics in the initial state with rates in the range 4.5–6.6 μM min −1 under air and 6.0–7.2 μM min −1 und...

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Published inUltrasonics sonochemistry Vol. 7; no. 3; pp. 115 - 120
Main Authors Nagata, Yoshio, Nakagawa, Michiyo, Okuno, Hiroshi, Mizukoshi, Yoshiteru, Yim, Bongbeen, Maeda, Yasuaki
Format Journal Article
LanguageEnglish
Published Netherlands Elsevier B.V 01.07.2000
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Abstract Sonochemical degradation of dilute aqueous solutions of 2-, 3- and 4-chlorophenol and pentachlorophenol has been investigated under air or argon atmosphere. The degradation follows first-order kinetics in the initial state with rates in the range 4.5–6.6 μM min −1 under air and 6.0–7.2 μM min −1 under argon at a concentration of 100 μM of chlorophenols. The rate of OH radical formation from water is 19.8 μM min −1 under argon and 14.7 μM min −1 under air in the same sonolysis conditions. The sonolysis of chlorophenols is effectively inhibited, but not completely, by the addition of t-BuOH, which is known to be an efficient OH radical scavenger in aqueous sonolysis. This suggests that the main degradation of chlorophenols proceeds via reaction with OH radicals; a thermal reaction also occurs, although its contribution is small. The addition of appropriate amounts of Fe(II) ions accelerates the degradation. This is probably due to the regeneration of OH radicals from hydrogen peroxide, which would be formed from recombination of OH radicals and which may contribute a little to the degradation. The ability to inhibit bacterial multiplication of pentachlorophenol decreases with ultrasonic irradiation.
AbstractList Sonochemical degradation of dilute aqueous solutions of 2-, 3- and 4-chlorophenol and pentachlorophenol has been investigated under air or argon atmosphere. The degradation follows first-order kinetics in the initial state with rates in the range 4.5–6.6 μM min −1 under air and 6.0–7.2 μM min −1 under argon at a concentration of 100 μM of chlorophenols. The rate of OH radical formation from water is 19.8 μM min −1 under argon and 14.7 μM min −1 under air in the same sonolysis conditions. The sonolysis of chlorophenols is effectively inhibited, but not completely, by the addition of t-BuOH, which is known to be an efficient OH radical scavenger in aqueous sonolysis. This suggests that the main degradation of chlorophenols proceeds via reaction with OH radicals; a thermal reaction also occurs, although its contribution is small. The addition of appropriate amounts of Fe(II) ions accelerates the degradation. This is probably due to the regeneration of OH radicals from hydrogen peroxide, which would be formed from recombination of OH radicals and which may contribute a little to the degradation. The ability to inhibit bacterial multiplication of pentachlorophenol decreases with ultrasonic irradiation.
Sonochemical degradation of dilute aqueous solutions of 2-, 3- and 4-chlorophenol and pentachlorophenol has been investigated under air or argon atmosphere. The degradation follows first-order kinetics in the initial state with rates in the range 4.5-6.6 microM min-1 under air and 6.0-7.2 microM min-1 under argon at a concentration of 100 microM of chlorophenols. The rate of OH radical formation from water is 19.8 microM min-1 under argon and 14.7 microM min-1 under air in the same sonolysis conditions. The sonolysis of chlorophenols is effectively inhibited, but not completely, by the addition of t-BuOH, which is known to be an efficient OH radical scavenger in aqueous sonolysis. This suggests that the main degradation of chlorophenols proceeds via reaction with OH radicals; a thermal reaction also occurs, although its contribution is small. The addition of appropriate amounts of Fe(II) ions accelerates the degradation. This is probably due to the regeneration of OH radicals from hydrogen peroxide, which would be formed from recombination of OH radicals and which may contribute a little to the degradation. The ability to inhibit bacterial multiplication of pentachlorophenol decreases with ultrasonic irradiation.
Author Okuno, Hiroshi
Nagata, Yoshio
Nakagawa, Michiyo
Yim, Bongbeen
Maeda, Yasuaki
Mizukoshi, Yoshiteru
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  givenname: Michiyo
  surname: Nakagawa
  fullname: Nakagawa, Michiyo
  organization: Department of Applied Materials Science, College of Engineering, Osaka Prefecture University, Gakuen-cho 1-1, Sakai, Osaka 599-8530, Japan
– sequence: 3
  givenname: Hiroshi
  surname: Okuno
  fullname: Okuno, Hiroshi
  organization: Department of Applied Materials Science, College of Engineering, Osaka Prefecture University, Gakuen-cho 1-1, Sakai, Osaka 599-8530, Japan
– sequence: 4
  givenname: Yoshiteru
  surname: Mizukoshi
  fullname: Mizukoshi, Yoshiteru
  organization: Department of Applied Materials Science, College of Engineering, Osaka Prefecture University, Gakuen-cho 1-1, Sakai, Osaka 599-8530, Japan
– sequence: 5
  givenname: Bongbeen
  surname: Yim
  fullname: Yim, Bongbeen
  organization: Department of Applied Materials Science, College of Engineering, Osaka Prefecture University, Gakuen-cho 1-1, Sakai, Osaka 599-8530, Japan
– sequence: 6
  givenname: Yasuaki
  surname: Maeda
  fullname: Maeda, Yasuaki
  organization: Department of Applied Materials Science, College of Engineering, Osaka Prefecture University, Gakuen-cho 1-1, Sakai, Osaka 599-8530, Japan
BackLink https://www.ncbi.nlm.nih.gov/pubmed/10909729$$D View this record in MEDLINE/PubMed
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Pentachlorophenol
Sonochemical degradation
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Snippet Sonochemical degradation of dilute aqueous solutions of 2-, 3- and 4-chlorophenol and pentachlorophenol has been investigated under air or argon atmosphere....
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SubjectTerms Chlorophenols
Pentachlorophenol
Sonochemical degradation
Title Sonochemical degradation of chlorophenols in water
URI https://dx.doi.org/10.1016/S1350-4177(99)00039-5
https://www.ncbi.nlm.nih.gov/pubmed/10909729
https://search.proquest.com/docview/1859323431
Volume 7
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