350-3 Seasonal and Landform Influence On Nitrous Oxide Fluxes In Riparian Buffers.

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Sources and Rates of Greenhouse Gas Emissions From Agriculture

Wednesday, November 6, 2013: 8:30 AM
Tampa Convention Center, Room 15

Pierre-Andre Jacinthe, Department of Earth Sciences, Indiana University Purdue University Indianapolis, Indianapolis, IN, Philippe Vidon, SUNY College of Environmental Science and Forestry, Syracuse, NY, Katelin Fisher, National Soil Erosion Laboratory, West Lafayette, IN, Xiaoqiang Liu, Earth Sciences, IUPUI, Indianapolis, IN, Matthew Baker, UMBC, Baltimore, MD and Matthew Panunto, Geography and Environmental Systems, UMBC, Baltimore, MD
Abstract:
Despite the general recognition that riparian buffers are hotspots of nitrogen (N) transformations, their contribution to regional nitrous oxide (N2O) inventory has not been quantified. In riparian ecosystems, N2O fluxes are highly variable owing to the interacting effects of landscape heterogeneity, patchy distribution of nutrients, and hydro-climatic events. Here we present results of a study (bi-weekly sampling for 18 months) conducted at riparian sites representing three of the most common hydro-geomorphic (HGM) settings in Central Indiana: i) HGM-1 – till plain depression near headwater streams/ditches, tile drainage; ii) HGM-2 – incised valley in till plain with thin alluvium deposits above the till layer, no tile drains; and iii) HGM-3, alluvial deposits above thick outwash deposits adjacent to 3rd-4th order stream, no tile drains. Among the soil biochemical properties examined, N mineralization showed the best relationship (r2: 0.61, p<0.001) with the spatial distribution of N2O emission at the study sites. Results showed that N2O emission was on average 4-fold higher (7.02 g N ha-1d-1) at HGM-3 compared to the other units. Short-term validation measurements at other riparian buffers have also shown higher (3-fold) N2O emission in HGM-3 sites than in HGM-1 sites during the wet season. These results are consistent with the higher groundwater NO3- concentration (0.2 - 13.7 mg N L-1), periodic floods, and the more dynamic water table (mean: 42.9 ±86.1 cm) at HGM-3 sites than at other sites. The weak N2O emission at HGM-1 units may be ascribed to tile drainage resulting in deep water table position (mean depth: 122.2 ±33.3 cm), and thus limited interaction between NO3--laden groundwater with the riparian buffer. These observations will be discussed to highlight relevant biogeochemical processes, and to demonstrate the potential of an HGM-based research approach to derive watershed-scale riparian N2O budgets.

See more from this Division: ASA Section: Environmental Quality
See more from this Session: Sources and Rates of Greenhouse Gas Emissions From Agriculture