The global methane reservoir in the form of gas hydrate is estimated at 500–10,000 Gt (KVENVOLDEN, 1995; MILKOV, 2004). This pool of carbon resides in permafrost/sub-permafrost and sub-seafloor settings. Neither the rates of methane generation/loss from the reservoir are known, nor if the reservoir is currently growing, shrinking, or at steady state. Evidence suggests that the hydrate reservoir has been unstable in the geologic past (JAHREN et al., 2001; THOMAS et al., 2002), and the reservoir is now considered as a capacitor on geologic time-scales (DICKENS, 2003). Given the magnitude and potential instability of at least some portion of this reservoir, combined with the potency of methane as a greenhouse gas, it is critical to understand the natural processes that act to control the release of subsurface methane to the ocean and atmosphere.
One fundamental knowledge gap standing between methane hydrates and the carbon cycle at earth’s surface is an understanding of the physical, chemical, geological, and biological controls on methane release from the subsurface to the ocean and atmosphere. Physical, chemical, and geological controls tend to trap or otherwise hinder methane transport from the subsurface, and are of primary importance in determining the magnitude, distribution, and phase of subsurface methane reservoirs, as well as the flux of methane departing the subsurface to the ocean and atmosphere (ETIOPE and KLUSMAN, 2002; ETIOPE and MILKOV, 2004). However, only methanotrophy (biological methane consumption) is known to destroy methane in the ocean and shallow subsurface, and the efficiency of this “methanotrophic biofilter” through space and time is a critical factor controlling how much subsurface methane ultimately reaches the atmosphere.
The potential impacts of methanotrophy in marine waters extend beyond the issue of methane transport to the atmosphere. The biological consumption of methane in the ocean is potentially an important process in the global carbon cycle in its own right, particularly at times of enhanced subsurface methane flux, as might be associated with broad hydrate destabilization. Methanotrophy not only removes methane, but also consumes O2 and produces both CO2 and abundant biomass (HANSON and HANSON, 1996). These processes have potentially far reaching consequences, including contributions to ocean anoxia (SLUIJS et al., 2007), ocean acidification (ZACHOS et al., 2005), and direct inputs of organic carbon to the deep ocean. In order to understand the linkage between methanotrophy and these factors, and how they might feed into the carbon cycle and broader earth system, it is critical to first understand the nature of the process and the associated controls.
A) Methanotroph-containing mat from Coal Oil Point, CA (COP), B) In-situ incubation of a methanotrophic mat at COP, C) Ongoing in-situ incubation of mats at Santa Monica Basin (SMB), D) Vein filling orange mats at the SMB methane seep, E) Mosaic of orange and white mats at SMB site, F) Methane hydrate was formed from an active seep at the SMB site-released here.