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Ozonation of water: kinetics of oxidation of ammonia by ozone and hydroxyl radicals

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1978

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Abstract

Ozone initiated oxidation of ammonia in water can result from the direct reaction of O<sub>3</sub> with NH<sub>3</sub> as well as from the reactions of OH<sup><B>·</B></sup> radicals formed upon O<sub>3</sub> decomposition. The direct reaction of O<sub>3</sub> predominates at pH <9. In the presence of low concentrations of free NH<sub>3</sub>, it is a slow reaction; the rate constant for O<sub>3</sub> depletion by reaction of O<sub>3</sub> with NH<sub>3</sub> is 20 ± 1 M<sup>-1</sup> s<sup>-1</sup>. At pH values >9, OH<sup><B>·</B></sup> and radical-catalyzed decomposition of O<sub>3</sub> to the very reactive intermediate, OH<sup><B>·</B></sup>, determines the kinetics of the NH<sub>3</sub> oxidation. The reaction rate constant of OH<sup><B>·</B></sup> with NH<sub>3</sub> is relatively small. Whenever the OH<sup><B>·</B></sup> mechanism is involved, NH<sub>3</sub> is easily protected by other solutes which also consume OH<sup><B>·</B></sup> radicals. Even carbonate and bicarbonate ions may act as efficient OH<sup><B>·</B></sup> scavengers. Because carbonate and organic solutes affect the lifetime of O<sub>3</sub> in water, they consequently shift the pH range in which either the direct O<sub>3</sub> or the OH<sup><B>·</B></sup> mechanism predominates. A comparison with reactions initiated by gamma irradiation proves helpful in elucidating the reaction mechanisms.