Temperature is an important factor controlling CH 4 production in anoxic rice soils. Soil slurries, prepared from Italian rice field soil, were incubated anaerobically in the dark at six temperatures of between 10 to 37°C or in a temperature gradient block covering the same temperature range at intervals of 1°C. Methane production reached quasi-steady state after 60 to 90 days. Steady-state CH 4 production rates increased with temperature, with an apparent activation energy of 61 kJ mol ؊1 . Steady-state partial pressures of the methanogenic precursor H 2 also increased with increasing temperature from <0.5 to 3.5 Pa, so that the Gibbs free energy change of H 2 plus CO 2 -dependent methanogenesis was kept at ؊20 to ؊25 kJ mol of CH 4 ؊1 over the whole temperature range. Steady-state concentrations of the methanogenic precursor acetate, on the other hand, increased with decreasing temperature from <5 to 50 M. Simultaneously, the relative contribution of H 2 as methanogenic precursor decreased, as determined by the conversion of radioactive bicarbonate to 14 CH 4 , so that the carbon and electron flow to CH 4 was increasingly dominated by acetate, indicating that psychrotolerant homoacetogenesis was important. The relative composition of the archaeal community was determined by terminal restriction fragment length polymorphism (T-RFLP) analysis of the 16S rRNA genes (16S rDNA). T-RFLP analysis differentiated the archaeal Methanobacteriaceae, Methanomicrobiaceae, Methanosaetaceae, Methanosarcinaceae, and Rice clusters I, III, IV, V, and VI, which were all present in the rice field soil incubated at different temperatures. The 16S rRNA genes of Rice cluster I and Methanosaetaceae were the most frequent methanogenic groups. The relative abundance of Rice cluster I decreased with temperature. The substrates used by this microbial cluster, and thus its function in the microbial community, are unknown. The relative abundance of acetoclastic methanogens, on the other hand, was consistent with their physiology and the acetate concentrations observed at the different temperatures, i.e., the high-acetate-requiring Methanosarcinaceae decreased and the more modest Methanosaetaceae increased with increasing temperature. Our results demonstrate that temperature not only affected the activity but also changed the structure and the function (carbon and electron flow) of a complex methanogenic system.Methane is one of the most important greenhouse gases (7,20,49). With a contribution of about 15 to 20% to the anthropogenic CH 4 emissions, rice fields are one of the major sources for CH 4 (8, 26, 44). In addition, rice fields may be considered as a rather simple model system for vegetated wetland ecosystems. Methane is the final product of anaerobic degradation of organic matter, which is accomplished by a complex microbial community involving hydrolytic, fermenting, homoacetogenic, syntrophic, and methanogenic microorganisms (54,60,75,76).Temperature, salinity, redox potential, pH, availability of organic substrates, and nutrient ...