Assessing the potential for greenhouse gas mitigation in intensively managed annual cropping systems at the regional scale

Abstract We predicted changes in yields and direct net soil greenhouse gas (GHG) fluxes from converting conventional to alternative management practices across one of the world's most productive agricultural regions, the Central Valley of California, using the DAYCENT model. Alternative practices included conservation tillage, winter cover cropping, manure application, a 25% reduction in N fertilizer input and combinations of these. Alternative practices were evaluated for all unique combinations of crop rotation, climate, and soil types for the period 1997–2006. The crops included were alfalfa, corn, cotton, melon, safflower, sunflower, tomato, and wheat. Our predictions indicate that, adopting alternative management practices would decrease yields up to 5%. Changes in modeled SOC and net soil GHG fluxes corresponded to values reported in the literature. Average potential reductions of net soil GHG fluxes with alternative practices ranged from −0.7 to −3.3 Mg CO 2 -eq ha −1  yr −1 in the Sacramento Valley and −0.5 to −2.5 Mg CO 2 -eq ha −1  yr −1 for the San Joaquin Valley. While adopting a single alternative practice led to modest net soil GHG flux reductions (on average −1 Mg CO 2 -eq ha −1  yr −1 ), combining two or more of these practices led to greater decreases in net soil GHG fluxes of up to −3 Mg CO 2 -eq ha −1  yr −1 . At the regional scale, the combination of winter cover cropping with manure application was particularly efficient in reducing GHG emissions. However, GHG mitigation potentials were mostly non-permanent because 60–80% of the decreases in net soil GHG fluxes were attributed to increases in SOC, except for the reduced fertilizer input practice, where reductions were mainly attributed to decreased N 2 O emissions. In conclusion, there are long-term GHG mitigation potentials within agriculture, but spatial and temporal aggregation will be necessary to reduce uncertainties around GHG emission reductions and the delivery risk of the associated C credits.

[1]  Johan Six,et al.  Simulating greenhouse gas budgets of four California cropping systems under conventional and alternative management. , 2010, Ecological applications : a publication of the Ecological Society of America.

[2]  G. Robertson,et al.  Nonlinear response of N2O flux to incremental fertilizer addition in a continuous maize (Zea mays L.) cropping system , 2005 .

[3]  R. Bell,et al.  Organic Wheat Production and Soil Nutrient Status in a Mediterranean Climatic Zone , 2003 .

[4]  W. Parton,et al.  Analysis of factors controlling soil organic matter levels in Great Plains grasslands , 1987 .

[5]  S. Kyamanywa,et al.  Effects of organic versus conventional fertilizers on insect pests, natural enemies and yield of Phaseolus vulgaris , 2006 .

[6]  F. Miguez,et al.  Review of Corn Yield Response under Winter Cover Cropping Systems Using Meta-Analytic Methods , 2005 .

[7]  W. Parton,et al.  DAYCENT and its land surface submodel: description and testing , 1998 .

[8]  B. Kay,et al.  Variability in carbon sequestration potential in no-till soil landscapes of southern Ontario , 2002 .

[9]  J. Six,et al.  Realistic payments could encourage farmers to adopt practices that sequester carbon , 2009 .

[10]  S Pacala,et al.  Stabilization Wedges: Solving the Climate Problem for the Next 50 Years with Current Technologies , 2004, Science.

[11]  N. M. Idaikkadar,et al.  CHAPTER 10 – Census of Agriculture , 1979 .

[12]  Wilfried Winiwarter,et al.  Assessing the uncertainty associated with national greenhouse gas emission inventories:: a case study for Austria , 2001 .

[13]  A. Franzluebbers Soil organic carbon sequestration and agricultural greenhouse gas emissions in the southeastern USA , 2005 .

[14]  A. Dobermann,et al.  Agroecosystems, Nitrogen-use Efficiency, and Nitrogen Management , 2002, Ambio.

[15]  Corinne Le Quéré,et al.  Climate Change 2013: The Physical Science Basis , 2013 .

[16]  G. Pan,et al.  Policy and technological constraints to implementation of greenhouse gas mitigation options in agriculture , 2007 .

[17]  W. Parton,et al.  General model for N2O and N2 gas emissions from soils due to dentrification , 2000 .

[18]  Stephen M. Ogle,et al.  Estimating uncertainty in N2O emissions from U.S. cropland soils , 2010 .

[19]  Johan Six,et al.  The potential to mitigate global warming with no‐tillage management is only realized when practised in the long term , 2004 .

[20]  L. Drinkwater,et al.  Fundamental Differences Between Conventional and Organic Tomato Agroecosystems in California , 1995 .