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Abstract: The photodegradation kinetics and the break down pathway of fenhexamid were studied in aqueous systems using [phenyl-UL-14C]- and [carbonyl-14C]-labelled compounds. The photolysis of fenhexamid followed first-order kinetics. The degradation rate of fenhexamid was significantly influenced by the solution pH with rate constants (k) of 2.11×10−2, 4.47×10−2, 6.11×10−1 and 1.69h−1 at pH 5.0, 6.6, 7.3 and 9.0, respectively. Fenhexamid exhibited no significant change in degradation rate in the presence of acetone and hydrogen peroxide, while humic and fulvic acids retarded the degradation rate, because they shielded the active molecules from light. However, in phosphate medium, the photolysis rate was significantly enhanced as a function of concentration. About 3–8% and 10–25% photo mineralization were observed, using [carbonyl-14C]- and [phenyl-UL-14C]-labelled fenhexamid in aqueous solutions at different pH, respectively. In addition to four known metabolites, one major and five minor photoproducts out of which one is reported for the first time, were identified using high resolution LC–MS/MS and NMR. The toxicity of the new metabolite was tested against the fish Oncorhynchus mykiss with no lethal effect at 100mgL−1. [ABSTRACT FROM AUTHOR]

Abstract: Photolysis of 14C-sulfadiazine in aqueous solution under simulated sunlight followed first-order kinetics. The impact of H2O2, humic acid, fulvic acid and acetone to enhance the photodegradation of sulfadiazine (SDZ) was studied. Six photoproducts, 4-OH-SDZ, 5-OH-SDZ, N-formyl-SDZ, 4-[2-iminopyrimidine-1(2H)-yl] aniline, 2-aminopyrimidine, and aniline were identified. Extrusion of SO2 was found to be the main degradation process during irradiation. These photoproducts can occur in water and soil upon sunlight exposure, when soil is treated with SDZ contained in manure. Due to photodegradation the experimental half-life of the SDZ in water was 32h and in the presence of photosensitizers the half-life values were 19.3–31.4h, 17.2–31.4h, 12.6–29.8h, and 3.8–30.7h for H2O2, humic acid, fulvic acid, and acetone, respectively depending on the concentration of the photosensitizers. The presence of photosensitizers markedly reduced SDZ persistence, indicating that indirect photolytic processes are important factors governing the photodegradation of SDZ in aqueous environments. Investigation revealed further persistence behavior of SDZ in manure. The half-life value of SDZ in manure was 158h. [Copyright &y& Elsevier]