Butyrate-degrading bacteria in four methanogenic sludges were studied by RNA-based stable isotope probing. Bacterial populations in the 13 C-labeled rRNA fractions were distinct from unlabeled fractions, and Syntrophaceae species, Tepidanaerobacter sp., and Clostridium spp. dominated. These results suggest that diverse microbes were active in butyrate degradation under methanogenic conditions.Butyrate is one of the important intermediates in the degradation of organic matter under methanogenic conditions (14,16). Under these conditions, butyrate degradation is carried out by a syntrophic association of butyrate-oxidizing bacteria and hydrogenotrophic methanogens, because of thermodynamic constraints (17). Due to the fastidious nature of this syntrophic metabolism, isolation of butyrate-degrading syntrophs has been difficult and thus information on butyratedegrading bacteria is based on some isolates belonging to the family Syntrophomonadaceae. Due to this lack of knowledge and the lack of appropriate molecular markers, culture-independent studies have focused only on species of the family Syntrophomonadaceae (5, 15, 25). Consequently, the natural diversity of syntrophic butyrate-degrading bacteria has not been studied in any detail.The recent development of stable isotope probing (SIP) enables metabolic function and taxonomic identity to be examined concurrently (3). Only one study on methanogenic butyrate degradation has been reported with this technique (1), but not within waste/wastewater-treated methanogenic sludges. SIP provides a potentially fruitful tool for identifying potential butyrate-degraders in a methanogenic environment. In this study, therefore we used RNA-based SIP (RNA-SIP) with [ 13 C 4 ]butyrate as a substrate to explore the microorganisms involved in butyrate degradation in four methanogenic sludges.Four methanogenic sludges were used in this study. Mesophilic granular sludge MP and thermophilic granular sludge TP were taken from two lab-scale multistage upflow anaerobic sludge blanket reactors treating palm oil mill effluent. Mesophilic anaerobic digester sludge treating palm oil mill effluent (sludge MBF) and thermophilic digester sludge treating municipal solid waste (sludge JET) were taken from commercial plants. Detailed properties of these sludges were described in our previous report (7). Incubation was carried out anaerobically at 37°C (for mesophilic sludges) or 55°C (for thermophilic sludges). The granular sludges TP and MP were preincubated with 5 mM butyrate because of prolonged storage at 4°C for over 2 years. Degradation of butyrate was monitored by measuring methane production using gas chromatography as described previously (6). Preincubation was conducted for 14 days, added butyrate was completely converted to methane, and then the sludge was sampled as an unlabeled control microbial consortium. Digester sludges MBF and JET were used immediately after sampling, and RNA extracted from unincubated sludges was used as an unlabeled control RNA. Incubation of stable isotope-label...