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Impact of Sea Surface Temperatures, Climate and Management on Plant Production and GHG fluxes in Asia and the Great Plains

  1. Impact of Sea Surface Temperatures, Climate and Management on Plant Production and GHG fluxes in Asia and the Great Plains William Parton Maosi Chen Melannie Hartman Steve Del Grosso Dennis Ojima
  2. Outline • Linking DayCent soil C and nutrient cycling model to UCLA land surface model • Predicting the impact of land use practices on greenhouse gas fluxes in Asia • Impact of sea surface temperatures on spring AET and grassland plant production in the Great Plains • Global patterns in plant production and soil decomposition from 1900 to 2015 • Conclusions
  3. Progress Linking SSiB and DayCent  Completed: Point version of DayCent SOM cycling model with SSiB I/O • Reads daily SSiB drivers (plant litter inputs, potential NPP, plant N demand, soil moisture, soil temperature, precipitation, radiation, AET, snow cover) from a text file • Updates SOM pools, inorganic N pools • Returns fraction of plant N demand that can be met, soil respiration, NOx, CH4, N2O • This fraction is used by SSiB to downscale daily NPP • Tested for all 7 SSiB Land Cover Types  In progress: Interface for SSiB and DayCent • Enables DayCent to be run on a grid across space before time • For each day, for each grid cell 1. DayCent retrieves SSiB drivers and the state of the grid cell from the previous day 2. DayCent completes the simulation for the day and sends its results to the interface 3. DayCent saves the state of the grid cell to the interface
  4. SSiB DayCent Retrieve grid cell state from previous time step for each grid cell If time=0, initialize grid cell from spinup Receive inputs from SSiB Save grid cell state to global data structure Send results to SSiB SSiB/DayCent Interface
  5. Use of Agricultural Best Management Practices in China 30% reduction in inorganic fertilizer Use of no-tillage cultivation practices Addition of straw and manure Drainage of flooded rice fields
  6. Cheng, K. S.M. Ogle, W.J. Parton, and G. Pan. 2014. Simulating greenhouse gas mitigation potentials for Chinese Croplands using the DAYCENT ecosystem model. Global Change Biology 20: 948-962.
  7. Cheng, K. S.M. Ogle, W.J. Parton, and G. Pan. 2014. Simulating greenhouse gas mitigation potentials for Chinese Croplands using the DAYCENT ecosystem model. Global Change Biology 20: 948-962.
  8. Cheng, K. S.M. Ogle, W.J. Parton, and G. Pan. 2014. Simulating greenhouse gas mitigation potentials for Chinese Croplands using the DAYCENT ecosystem model. Global Change Biology 20: 948-962. BMP1: 30% N Fertilizer Reduction and Flooding BMP2: Reduced Tillage with Straw Return BMP3: 30% N Fertilizer Reduction and Manure Application BMP4: 30% N Fertilizer Reduction, Flooding, Straw Return and Manure Application Zhangye Xigaze
  9. N2O Emissions for Maize (2015- 2020) g N2O-N m-2 yr-1 Business As Usual Auto-fertilization of N
  10. AET ratio 0.63 - 0.75 0.76 - 0.80 0.81 - 0.85 0.86 - 0.90 0.91 - 0.95 0.96 - 1.00 1.01 - 1.05 1.06 - 1.10 1.11 - 1.15 1.16 - 1.43 DayCent Model Satellite Derived (NDVI) Mean Spring Evapotranspiration Cool PDO (1998-2014)/ Warm PDO (1978-1997) Mean Annual Plant Production Cool PDO (1998-2014)/ Warm PDO (1982-1997) Mean Values
  11. DayCent Model Satellite Derived (NDVI) Annual Spring Evapotranspiration Variability Cool PDO (1998-2014)/ Warm PDO (1978-1997) Annual Plant Production Variability Cool PDO (1998-2014)/ Warm PDO (1982-1997) AET variability 0.43 - 0.70 0.71 - 0.80 0.81 - 0.90 0.91 - 1.10 1.11 - 1.20 1.21 - 1.30 1.31 - 1.40 1.41 - 1.50 1.51 - 1.60 1.61 - 2.86 Variability
  12. Shortgrass Steppe
  13. Shortgrass Steppe COLD PDO Nino 3 Average AET % < 14 < -.75 14.89 44.44% -.25 to -.75 18.39 14.29% .25 to -.25 18.69 27.27% > .25 20.39 0.00% WARM PDO Nino 3 Average AET % < 14 < -.25 16.56 26.67% .25 to -.25 20.05 7.14% > .25 21.42 0.00%
  14. Conclusions • Making progress in linking DayCent to UCLA GCM • Using best land use practice in agriculture can greatly reduce GHG fluxes • PDO, AMO, and ENSO SST’s are correlated to drought frequency and plant production in the Great Plains • Plant production and soil decomposition rates have been increasing rapidly from 1980 to 2015 for the tundra and boreal systems • Soil decomposition is increasing more rapidly
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