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Decomposition of ozone in water in the presence of organic solutes acting as promoters and inhibitors of radical chain reactions

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1985

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Abstract

The decomposition of aqueous ozone is generally due to a chain reaction involving <B>·</B>OH radicals. Many organic solutes (impurities) can react with <B>·</B>OH to yield <B>·</B>O<sub>2</sub><sup>-</sup> upon addition of O<sub>2</sub>. <B>·</B>O<sub>2</sub><sup>-</sup>transfers its electron to a further ozone molecule in a rather selective reaction. The ozonide anion (<B>·</B>O<sub>3</sub><sup>-</sup>) formed immediately decomposes into a further <B>·</B>OH radical. Compounds that convert <B>·</B>OH radicals into ozone-selective <B>·</B>O<sub>2</sub><sup>-</sup>, therefore, act as promoters of the chain reaction. The efficiencies of different <B>·</B>OH to <B>·</B>O<sub>2</sub><sup>-</sup> converters (e.g., formic acid, primary and secondary alcohols (including sugars), glyoxylic acid, and humic acids) are tested in the presence of other <B>·</B>OH radical scavengers that do not primarily produce <B>·</B>O<sub>2</sub><sup>-</sup> (carbonate, aliphatic alkyl compounds, and <I>tert</I>-butyl alcohol). The derived reaction kinetics allows one to qualitatively interpret the variation of the lifetime of O<sub>3</sub> found in model solutions and even in natural waters and during drinking water treatment.