Pseudomonas mendocina KR-1 grew well on toluene, n-alkanes (C 5 to C 8 ), and 1°alcohols (C 2 to C 8 ) but not on other aromatics, gaseous n-alkanes (C 1 to C 4 ), isoalkanes (C 4 to C 6 ), 2°alcohols (C 3 to C 8 ), methyl tertiary butyl ether (MTBE), or tertiary butyl alcohol (TBA). Cells grown under carbon-limited conditions on n-alkanes in the presence of MTBE (42 mol) oxidized up to 94% of the added MTBE to TBA. Less than 3% of the added MTBE was oxidized to TBA when cells were grown on either 1°alcohols, toluene, or dextrose in the presence of MTBE. Concentrated n-pentane-grown cells oxidized MTBE to TBA without a lag phase and without generating tertiary butyl formate (TBF) as an intermediate. Neither TBF nor TBA was consumed by n-pentanegrown cells, while formaldehyde, the expected C 1 product of MTBE dealkylation, was rapidly consumed. Similar K s values for MTBE were observed for cells grown on C 5 to C 8 n-alkanes (12.95 ؎ 2.04 mM), suggesting that the same enzyme oxidizes MTBE in cells grown on each n-alkane. All growth-supporting n-alkanes (C 5 to C 8 ) inhibited MTBE oxidation by resting n-pentane-grown cells. Propane (K i ؍ 53 M) and n-butane (K i ؍ 16 M) also inhibited MTBE oxidation, and both gases were also consumed by cells during growth on n-pentane. Cultures grown on C 5 to C 8 n-alkanes also exhibited up to twofold-higher levels of growth in the presence of propane or n-butane, whereas no growth stimulation was observed with methane, ethane, MTBE, TBA, or formaldehyde. The results are discussed in terms of their impacts on our understanding of MTBE biodegradation and cometabolism.