. 1997. Kinetic formulation of oxygen consumption and denitrification processes in soil. Can. J. Soil Sci. 77: 253-260. A kinetic expression for oxygen, nitrate, nitrite and nitrous oxide reduction in soil was developed. The formulation was based on competitive Michaelis-Menten kinetics for a steady microbial population whose respiratory activity was assumed to be constant so that the number of electrons produced per unit of time was constant. Competition among the electron acceptors was characterized by their affinity toward the electron and by their concentration. Several different values for the affinity coefficients were used to simulate the concentration of O 2 , NO 3 -, NO 2 -, N 2 O and N 2 at various times. When relative magnitudes of affinity coefficients were chosen to be 100 000, 1, 100 and 0.1, for O 2 , NO 3 -, NO 2 -and N 2 O, respectively, the temporal plot of concentration showed that the disappearance of O 2 and NO 3 -was zero order. The accumulation of NO 2 -was very small and it was rapidly reduced to N 2 O. The production rate of N 2 O was nearly zero order but the magnitude of the rate was rather small as opposed to the rate of disappearance of NO 3 -. The reduction of N 2 O to N 2 took place only after NO 3 -had almost disappeared. With these competition parameters NO 3 -was stable in the presence of O 2 . The reduction of N 2 O was also very much retarded in the presence of NO 3 -. NO 2 -was relatively unstable, even in the presence of O 2 , and it was further reduced to N 2 O. With the relative magnitude of the chosen affinity coefficients, the kinetic formulation effectively simulated the "inhibitory" effect of O 2 upon the denitrification process, and the "inhibitory" effect of NO 3 -and NO 2 -upon the reduction of N 2 O to N 2 . Nitrogen has oxidation states ranging from -3 to +5. The most reduced form, ammonium, is stable under reduced conditions and the oxidized form, nitrate, is stable under oxidized conditions. The oxidation-reduction status of the environment determines whether the oxidation of ammonium to nitrate (nitrification) or the reduction of NO 3 -to gaseous forms, such as N 2 or N 2 O (denitrification) will occur. Even though the denitrification process has been extensively investigated (Kohl et al. 1976;Betlach and Tiedje 1981;Cho 1982;Leffelaar and Wessel 1988;Dendooven et al. 1994), the mechanisms and kinetic expressions for denitrification are not fully understood. Cho and Mills (1979) proposed a competitive kinetic expression for denitrification based on steady state Michaelis-Menten kinetics. Their expression was based on a constant denitrification intensity, defined to be the sum of production rates of NO 2 -, N 2 O and N 2 from their immediate precursors. The model of Cho and Mills (1979) explains several important observations made by many workers (Blackmer and Bremner 1978;Cho and Sakdinan 1978;Gaskell et al. 1981). These include i) the apparent inhibition of N 2 O reduction by high concentrations of NO 3 -and NO 2 -, ii) the lag in the reduction of N 2 O prior ...