The hydrolysis and photolysis of clomazone in aqueous solutions and natural water were assessed under natural and controlled conditions in this work. The kinetics of hydrolysis and photolysis of clomazone was determined using HPLC-DAD and the identification of photoproducts was carried out with HPLC-MS. Hydrolysis experimental results showed that no noticeable hydrolysis occurred in aqueous buffer solutions (25 ± 2℃, pH 4.5 ± 0.1, pH 7.4 ± 0.1, pH 9.0 ± 0.1; 50 ± 2℃, pH 4.5 ± 0.1, pH 7.4 ± 0.1) or in natural water up to 90 d, and the half-life of clomazone in pH 9.0 ± 0.1 buffer solutions at 50 ± 2 ℃ was 50.2 d. The rate of photodecomposition of clomazone in aqueous solutions followed first-order kinetics both in UV radiation and natural sunlight. The degradation rates were faster under UV light than sunlight, with the half-lives of 51.4-58.8 min and 86.7-135.9 d, respectively. Under UV light, four major photoproducts were detected and tentatively identified according to HPLC-MS spectral information as 2-Chlorobenzamide, N-hydroxy-(2-benzyl)-2-methylpropan-amide, 2-[2-phenol]-4,4-dimethyl-3-isoxazolidinone and 2-[(4,6-dihydroxyl-2-chlorine phenol)]-4,4-dimethyl-3-isoxazolidinone. These results suggested that the photodegradation of clomazone proceeds via a number of reaction pathways: (1) dehalogenation, (2) substitution of chlorine group by hydroxyl, (3) cleavage of the side chain. Photosensitizers, such as H2O2 and riboflavin, could enhance photolysis of clomazone in natural sunlight. The results obtained indicated that photoreaction was an important dissipation pathway of clomazone in natural water systems.