dThe objective of this study was to characterize metabolically active, aerobic methanotrophs in an ombrotrophic peatland in the Marcell Experimental Forest, in Minnesota. Methanotrophs were investigated in the field and in laboratory incubations using DNA-stable isotope probing (SIP), expression studies on particulate methane monooxygenase (pmoA) genes, and amplicon sequencing of 16S rRNA genes. Potential rates of oxidation ranged from 14 to 17 mol of CH 4 g dry weight soil ؊1 day ؊1 . Within DNA-SIP incubations, the relative abundance of methanotrophs increased from 4% in situ to 25 to 36% after 8 to 14 days. Phylogenetic analysis of the 13 C-enriched DNA fractions revealed that the active methanotrophs were dominated by the genera Methylocystis (type II; Alphaproteobacteria), Methylomonas, and Methylovulum (both, type I; Gammaproteobacteria). In field samples, a transcript-to-gene ratio of 1 to 2 was observed for pmoA in surface peat layers, which attenuated rapidly with depth, indicating that the highest methane consumption was associated with a depth of 0 to 10 cm. Metagenomes and sequencing of cDNA pmoA amplicons from field samples confirmed that the dominant active methanotrophs were Methylocystis and Methylomonas. Although type II methanotrophs have long been shown to mediate methane consumption in peatlands, our results indicate that members of the genera Methylomonas and Methylovulum (type I) can significantly contribute to aerobic methane oxidation in these ecosystems.
Methane is the third most important greenhouse gas and has 28 times the potential of carbon dioxide to trap heat radiation on a molecular basis over a 100-year time scale (1, 2, 3). Wetlands, such as peatlands, represent the largest natural source of methane to the atmosphere (4). Aerobic methanotrophic bacteria live at the oxic-anoxic interface of wetland soils, and it has been shown that they consume as much as 90% of the methane produced belowground before it reaches the atmosphere, thus serving as a biofilter regulating emissions (3, 5, 6, 7). The response of methane dynamics in wetlands to global climate change is uncertain, and climate models would be improved through quantification of the response of microbially mediated mechanisms of methanotrophy to temperature and moisture variation.Aerobic methanotrophs are phylogenetically located in two phyla: the Proteobacteria and Verrucomicrobia (8). The majority of characterized methane-oxidizing organisms have been separated into type I methanotrophs of the Gammaproteobacteria and type II methanotrophs of the Alphaproteobacteria (9, 10, 11). The prevailing view has been that most methanotrophs grow only on methane or methanol as a source of carbon and energy (4). However, more recently, a number of type II methanotrophs (Methylocella, Methylocapsa, and Methylocystis) have been characterized as facultative methanotrophs capable of conserving energy for growth on multicarbon compounds such as acetate, pyruvate, succinate, malate, and ethanol (12). Although members of the phylum Verrucomic...