HR: 1330h
AN: B42A-0937    [PDF]
TI: Modeling the CO$_{2}$ and N$_{2}$O Emissions From Stover Removal for Biofuel Production From Continuous Corn Production in Iowa
AU: Paustian, K
EM: keithp@nrel.colostate.edu
AF: Colorado State University, Natural Resource Ecology Laboratory, NESB, B248, Fort Collins, CO 80523-1499 United States
AU: * Killian, K
EM: kendrick@nrel.colostate.edu
AF: Colorado State University, Natural Resource Ecology Laboratory, NESB, B248, Fort Collins, CO 80523-1499 United States
AU: Brenner, J
EM: jbrenner@nrel.colostate.edu
AF: USDA-Natural Resources Conservation Service, Natural Resource Ecology Laboratory, NESB, A217, Fort Collins, CO 80523-1499 United States
AB: Corn stover, an agricultural residue, can be used as feedstock for near term bioethanol production and is available today at levels that can significantly impact energy supply. We evaluated the environmental impact of such a large-scale change in agricultural practices on green house gas production, soil erosion and soil carbon using the Century model. Estimates of soil C changes and GHG emissions were performed for the 99 counties in Iowa where previous environmental, management and erosion data was available. We employed climate, soil and historical management databases from a separate USDA-funded project as input to Century. RUSLE estimates of the residue requirements for acceptable soil loss rates under continuous corn agriculture were available from a previous study done Dr. Richard Nelson (Enersol Resources). Two mulch tillage and a no-till systems, where erosion estimates were available, were used as the basis for the simulations. Century simulations of these systems were run under a variety of stover removal rates. For each soil type within each county the model was run for 15 years (1980-1995) under continuous corn with convention tillage, and full residue return. Model simulation of crop yields and residue production were then calibrated to match those used by the Polysys model team at Oak Ridge and the simulation was repeated with the addition of the three corn tillage regimes, and several residue removal rates. County-average soil C changes (and net CO$_{2}$ emissions) were calculated as area-weighted averages of the individual soil types in each county. For this study, we have utilized the IPCC approach to estimate annual N$_{2}$O emissions. At low or zero residue removal rates, county-averaged soil C stocks were predicted to increase (i.e. net CO$_{2}$ emissions are negative). Where the allowable residue removal rates (based on erosion tolerance) for mulch-tillage are on the order of 40-50% or more, the reduced input of C is such that the soils no longer sequester C and become a net source of CO$_{2}$. Estimates of N$_{2}$O emissions from soil ranged from 1.4 to 2.8 kg N$_{2}$O-N ha$^{-1}$ yr$^{-1}$ across all counties, tillage systems and residue removal rates. The magnitude of these values is consistent with direct measurements of N$_{2}$O flux.
DE: 0400 Biogeosciences
SC: Biogeosciences [B]
MN: 2003 Fall Meeting