Many methane-oxidizing bacteria (MOB) have been shown to aerobically oxidize ammonia and hydroxylamine (NH(2)OH) to produce nitrite and nitrous oxide (N(2)O). Genome sequences of alphaproteobacterial, gammaproteobacterial, and verrucomicrobial methanotrophs revealed the presence of haoAB, cytL, cytS, nirS or nirK, and norCB genes that may be responsible for N(2)O production, and additional haoAB genes were sequenced from two strains of Methylomicrobium album. The haoAB genes of M. album ATCC 33003 were inducible by ammonia and NH(2)OH, similar to haoAB induction by ammonia in Methylococcus capsulatus Bath. Increased expression of genes encoding nitric oxide reductase (cNOR; norCB) was measured upon exposure of M. capsulatus Bath to NaNO(2) and NO-releasing sodium nitroprusside. Only incubations of M. capsulatus Bath with methane, ammonia, and nitrite produced N(2)O. The data suggest a possible pathway of nitrite reduction to NO by reversely operating NH(2)OH oxidoreductase and NO reduction to N(2)O by cNOR independently or in conjunction with ammonia-induced enzymes (i.e. HAO or cytochrome c'-β). Results of this study show that MOB likely have diverse mechanisms for nitrogen oxide metabolism and detoxification of NH(2)OH that involve conventional and unconventional enzymes.

The effects of nitrite and ammonium on cultivated methanotrophic bacteria were investigated. Methylomicrobium album ATCC 33003 outcompeted Methylocystis sp. strain ATCC 49242 in cultures with high nitrite levels, whereas cultures with high ammonium levels allowed Methylocystis sp. to compete more easily. M. album pure cultures and cocultures consumed nitrite and produced nitrous oxide, suggesting a connection between denitrification and nitrite tolerance.The application of ammonium-based fertilizers has been shown to immediately reduce the uptake of methane in a number of diverse ecological systems (3, 5, 7, 8, 11-13, 16, 27, 28), due likely to competitive inhibition of methane monooxygenase enzymes by ammonia and production of nitrite (1). Longer-term inhibition of methane uptake by ammonium has been attributed to changes in methanotrophic community composition, often favoring activity and/or growth of type I Gammaproteobacteria methanotrophs (i.e., Gammaproteobacteria methane-oxidizing bacteria [gamma-MOB]) over type II Alphaproteobacteria methanotrophs (alpha-MOB) (19-23, 25, 26, 30). It has been argued previously that gamma-MOB likely thrive in the presence of high N loads because they rapidly assimilate N and synthesize ribosomes whereas alpha-MOB thrive best under conditions of N limitation and low oxygen levels (10,21,23).Findings from studies with rice paddies indicate that N fertilization stimulates methane oxidation through ammonium acting as a nutrient, not as an inhibitor (2). Therefore, the actual effect of ammonium on growth and activity of methanotrophs depends largely on how much ammonia-N is used for assimilation versus cometabolism. Many methanotrophs can also oxidize ammonia into nitrite via hydroxylamine (24,29). Nitrite was shown previously to inhibit methane consumption by cultivated methanotrophs and by organisms in soils through an uncharacterized mechanism (9, 17, 24), although nitrite inhibits purified formate dehydrogenase from Methylosinus trichosporium OB3b (15). Together, the data from these studies show that ammonium and nitrite have significant effects on methanotroph activity and community composition and reveal the complexity of ammonia as both a nutrient and a competitive inhibitor. The present study demonstrates the differential influences of high ammonium or nitrite loads on the competitive fitness of a gamma-MOB versus an alpha-MOB strain.Growth and activity of pure cultures. Methylomicrobium album ATCC 33003 (a gamma-MOB strain) and Methylocystis sp. strain ATCC 49242 (an alpha-MOB strain) were grown in batch cultures (consisting of 100 ml of medium in 250-ml Wheaton bottles sealed with septated screw-top lids) with nitrate mineral salts medium (NMS; ATCC medium 1306) or ammonium mineral salts medium (AMS; ATCC medium 784) containing 10 M copper at pH 6.8 under a 50% air-50% methane atmosphere. Cultures were initiated with 1 ϫ 10 6 to 3 ϫ 10 6 cells ml Ϫ1 and grown in the dark at 30°C with shaking (200 rpm). Although a range of NH 4 Cl (25 to 100 mM) and NaNO 2 (0.5 to 5 ...

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