Pathways for methane transport and atmospheric exchange in a coastal floodplain system

Nicholas D Ward, Pacific Northwest National Laboratory, Richland, United States
Abstract:
Methane (CH4) emissions from wetland soils to the atmosphere commonly decrease from net positive in freshwater environments to net negative in coastal environments, where sulfate reduction suppresses methanogenesis. However, belowground transport of water and dissolved CH4 from one watershed compartment to another (e.g., soils-to-river, soils-to-vegetation, or river-to-landscape during floods) allows CH4 produced in one compartment (e.g., anaerobic soils) to bypass oxidation in other compartments (e.g., shallow aerobic soils). These “short-circuits” can result in perceived hot spots/moments that have not been incorporated into watershed-scale conceptual models or budgets.

This study examines CH4 fluxes along each watershed component and landscape position—soils, tree stems, and surface water at upland, freshwater wetland, floodplain, and river channel sites—across a first-order coastal watershed in the US Pacific Northwest, Beaver Creek (BC). Likewise, CH4 concentrations and stable isotopic composition were measured in soil porewater, tree stems, and river water to evaluate physical exchange of gas/water between each watershed sub-unit and the extent of CH4 oxidation in transit. We determined that spatially-scaled CH4 uptake by the upland forest soils and trees was nearly balanced by positive emissions from the freshwater wetland and river channel. Minimal CH4 was transported from the watershed’s headwaters (i.e., the wetland) to the river. River CH4 emissions were fueled by sediment production and lateral transport from the floodplain. Coastal floodplain soils had near zero CH4 fluxes. However, flood events and floodplain trees (which bypass soil oxidation) contributed positive emissions that resulted in the watershed being a net CH4 source to the atmosphere in 2018. Tidal inundation of the previously freshwater floodplain was restored in 2014, thus, continued research will reveal how the CH4 balance shifts as floodplain salt-exposure continues to increase.