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Soils and Climate Change: Greenhouse gas emissions
  implications and research requirements

Jeff Baldock, Ichansi Wheeler, Neil
McKenzie and Alex McBratney
CCRSPI Conference, Melbourne
15-17 February, 2011
Outline

• Introduction

• Summary of the processes that generate and consume
  greenhouse gases in soil

• Climate change projections

• For each greenhouse gas (CO2, N2O, and CH4) examine:
   • Potential impacts of climate change
   • Mitigation options and and mitigation options

• Future research requirements

• Summary
Introduction

• Soils contain significant stores of carbon and nitrogen (1500 Pg
  organic C and 190 Pg total N)

• These stores are continuously exposed to decomposition and
  other biochemical processes that generate or consume CO2,
  N2O and CH4.

• Using soil and atmospheric carbon stocks of 1500 and 720 Pg
  and an atmospheric CO2 concentration of 390 ppm, a 1%
  change in soil carbon = 8 ppm change in CO2 concentration
  (assuming no feedbacks)

• Concern exists over the potential positive feedback that
  increased temperature may have on soil carbon loss and CO2
  concentration
Generation of greenhouse gases by soil
                          CO2    N fertiliser &           N2O                     CH4
                                 Animal waste
       Soil surface
                                                                Denitrification

                       Respiration           NH4             NO3      Methanogenic
                                               Nitrification           organisms
                                         Mineralisation


Assimilation          Decomposition
and mineral
 protection
               Organic        Organic
               carbon         nitrogen        Aerobic                Anaerobic
                                                soil                    soil
                 Soil organic matter         conditions              conditions
               including decomposer
                      organisms
Consumption of greenhouse gases in soil
                       CO2
Photosynthesis

                                                    N2O            CH4
   Shoot dry     Plant dry
    matter        matter
                                                                         Soil surface
   Root dry
    matter                           Biological
                                  transformations             Methanotrophic
                                  associated with               organisms
      Residue                        N cycling
     deposition              Uptake
                                                    Inorganic N
                                                    NH4 & NO3

Organic        Organic                                                    Aerobic
carbon         nitrogen                                                     soil
                                          Immobilisation                 conditions
  Soil organic matter
including decomposer
       organisms
Projected changes to Australia’s climate
         2030                    2050                    2070

                                                                            Australian agricultural regions
                                                                               • warmer and drier
                                                                               • altered seasonality
                                                                               • greater extremes
              0.3 0.6 1.0 1.5 2.0 2.5 3.0 4.0 5.0
         Change in average annual temperature ( C)
                                                                            Such changes will undoubtedly
                                                                            influence rates of net
                                                                            greenhouse gas emissions

                                                                            Magnitude of change will be
              -40 -20 -10 -5     -2   2   5   10 20 40
                                                                            defined by the sum of the
                     Change in annual rainfall (%)                          climate change influence on all
                                                                            processes




                -4      -2   2    4       8   12   16
     Change in annual potential evapotranspiration (%)
Source: http://climatechangeinaustralia.com.au - 50th percentile of projected changes under the medium
future emissions profile relative to 1980-1999
CO2 / Soil carbon: inputs of carbon

                                 Controls on potential carbon input
  Photosynthetically              1) The amount of PAR
  active radiation (PAR)          2) Fraction of PAR used
                                  3) Efficiency of carbon capture,
                                  4) Proportion lost to respiration
                      CO2         5) Proportion removed in products.

                                  Factors 1-4 define potential net
                                  primary productivity
Product
harvest
                                  Other constraints
                                  (water, fertility, disease) may reduce
                                  efficiencies and lead to Actual NPP <
                                  Potential NPP
                                  Product removal – harvest index
                                  issue
CO2 / Soil carbon: inputs of carbon

                                     Where can carbon inputs be
                                            increased?
  Photosynthetically
  active radiation (PAR)          Identify systems that are not achieving
                                  100% resource use efficiency (water
                                  and nutrients)
                      CO2
                                  Identify constraints and define
                                  whether or not they can be managed
                                        Yes                 No
Product
harvest
                                    Implement               Consider
                                   management              alternative
                                   changes and             production
                                      capture          systems that may
                                     additional         be better suited
                                      carbon             to constraints
CO2 / Soil carbon: fate of carbon inputs


  Photosynthetically                 What happens to the carbon
  active radiation (PAR)                      inputs?
                                   The majority is decomposed and
                      CO2          returned to the atmosphere as CO2

                                   The remainder resists decomposition
                                   and replaces the soil organic carbon
Product                            that is being decomposed
harvest

                                   Issues
                                   - residue placement – surface
                                      residues vs roots
                   Soil organic    - reduced incorporation
                     carbon
CO2 / Soil carbon: controls on stability of SOC




• Most of these factors vary
  spatially

• Different soils have different
  capacities to stabilise SOC

• Practical implication –
  management outcomes on
  SOC will vary with soil type
CO2 / Soil carbon: climate change impacts

• Dryland agriculture
   • Inputs
       • Reduced potential plant growth and the inputs of carbon to soil is
         likely where water is the main constraint.
   • Losses
       • Drier conditions are likely to reduce decomposition
       • Evidence is mounting to suggest enhanced decomposition with
         increasing temperature (larger relative impact on stable forms)
       • Extension of cropping systems into current cold/wet environments
         may occur – possible threat to existing carbon stocks

• Irrigated agriculture
   • Increases inputs and rates of decomposition are likely.
   • Net effect will depend on extent of alterations of inputs and losses
CO2 / Soil carbon: mitigation/sequestration

• The guiding principal - maximising the capture carbon given the
  resources available at any particular location will maximise
  SOC
   • Enhanced water use efficiency (kg dm/mm water)
   • Greater tolerance to subsoil constraints where possible
   • Greater root: shoot ratios

• Altered composition of plant residues – increased lignin

• CO2 fertilisation may help offset reductions

• Positive impacts of building SOC on soil productivity – water
  holding capacity, nutrient cycling, etc.
Nitrous oxide: climate change impacts

  • Strong influence of temperature and water availability




                                                      Relative N2O emission
                                  Temperature                                             Soil water content
  Total N2O emission




                                                                              0.6
      (µg N kg-1)




                                                                              0.4


                                                                              0.2


                                                                              0.0
                                                                                    40         60          80           100

                       Incubation Temperature (°C)                                  Water filled pore space (%)
                         Chen et al 2010 SBB 42 660                                      Dalal et al 2003 AJSR 41 165



  • Net change will depend on the relative responses
                Dryland                                                                     Irrigated
Increased in tropics and subtropics                                                  Increased in all regions
Decreased in cooler temperate regions
Nitrous oxide: mitigation strategies

Key requirement – minimise the concentration of inorganic N

   • Better matching of fertiliser N application to crop demand as
     dictated by the season – develop flexible N strategies

   • Increased reliance on biological N fixation to enhance soil N
     status – processes controlling N mineralisation also control
     plant growth

   • Alteration of animal diets to avoid an intake of excess N and
     excretion of high N content urine and faeces

   • Application of inhibitors to reduce rates of formation and
     transformation of soil ammonium – urease and nitrification
     inhibitors
Methane: climate change impacts

• Soils can be a source or a sink for methane depending on their
  oxidative condition

• Significant methane production occurs at redox potentials more
  negative than -100 mV (rates increase

• Dependence on redox potential means that properties controlling
  rates of oxygen diffusion and consumption exert strong control

• Where methane production conditions are met a strong response to
  temperature exists (Q10 = 4 with an optimum near 35°C)


Flood irrigation         Drip/sprinkler irrigation           Dryland

              Potential for methane emission will increase
           Potential for methane consumption will increase
Methane: mitigation strategies

Key requirement – maintain soil in an oxidative state

 • Adequate water management strategies:
    • Flood irrigation - create temporary oxic conditions
      (oxidises reduced species – e.g. Fe2+ to Fe3+)
    • Sprinkler/drip irrigation – avoid prolonged saturation to
      reduce emission, judicious control of soil water content can
      optimise methane consumption

 • Avoid incorporation of large amounts of degradable residues
   just prior to or when soils are saturated

 • Addition of SO42- - gypsum
Future research directions

• All gases
   • Quantification of uncertainties associated with estimates
   • Should build systems to define the cumulative probability of
      outcomes

• N2O and CH4 from soils
   • National evaluation of N2O and CH4 emissions reductions
     will rely on modelling and/or emission factors
   • Continued measurement of fluxes (e.g. NORP) will be
     essential
      • How do we best to deal with the diversity of agricultural
         practice, soil type and climatic condition?
      • How do we deal with climate change? Will calibration
         against current conditions be good enough?
   • Definition of the relative responses to temperature and soil
     water content and potential interactions.
Future research directions

• Soil carbon
   • A combination of measurement and modelling will be required
       • Measurement – establish initial conditions, verify model
         predictions, and allow recalibration
       • Models – predict the likely outcomes of alterations to
         management to help guide management


   • Derivation of an appropriate statistical approach to assess the
     potential of innovative practices
   • Rapid and cost effective soil sampling -
   • Smarter sampling of soils at different scales – use of available
     spatial datasets to help direct sampling.
Regional soil carbon estimation (Wheeler et al.2011a)

                       Regional soil carbon prediction



                       • 3 biogeographic regions
                                  – Brigalow (NSW portion)
                                  – NSW South Western
                                    Slopes
                                  – South Eastern Highlands
                       • ~170 000 km2
                                  – 65% grazing
                                  – 18% cropping
                                  – 11% forestry
                                  – 6% other
Regional soil carbon estimation (Wheeler et al.2011a)

     On training data                                        On training data
Average absolute error    0.1                           Average absolute error   0.09
                   R2    0.59                                              R2    0.55
         On test data                                            On test data
Average absolute error   0. 14                          Average absolute error   0. 11
                    R2   0.45                                               R2   0.38




   0 – 10 cm                                            0 – 30 cm
Summary

• Development of a robust modelling capability will be required to
   • construct regional and national emission assessments and
   • define the potential outcomes of on farm management decisions
     and policy decisions.

• This model development will require comprehensive field data
  sets to calibrate models and validate outputs.

• Improved spatial layers of model input variables collected on a
  regular basis will be required to optimise accounting at regional
  through to national scales.

• A diversity of agricultural practices exist in Australia. A
  continual matching of practice to soil and climate and economic
  assessment to optimise outcomes.
Jeff Baldock
Sustainable Agriculture Flagship

Phone: (08) 8303 8537
Email: jeff.baldock@csiro.au




Thank you
Contact Us
Phone: 1300 363 400 or +61 3 9545 2176
Email: Enquiries@csiro.au Web: www.csiro.au
CO2 / Soil carbon: composition


Particulate organic carbon (2 mm – 0.05 mm) (POC)           Resistance to
                                                            decomposition
Humus (<0.05 mm) (HumC)                                       increases

Resistant organic carbon (ROC): dominated by charcoal


     Particulate carbon      Humus carbon               Resistant
     (2mm – 0.05 mm)          (<0.05mm)             (charcoal <2mm)




           400 m                  10 m                   20 m

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Soils - Jeff Baldock

  • 1. Soils and Climate Change: Greenhouse gas emissions implications and research requirements Jeff Baldock, Ichansi Wheeler, Neil McKenzie and Alex McBratney CCRSPI Conference, Melbourne 15-17 February, 2011
  • 2. Outline • Introduction • Summary of the processes that generate and consume greenhouse gases in soil • Climate change projections • For each greenhouse gas (CO2, N2O, and CH4) examine: • Potential impacts of climate change • Mitigation options and and mitigation options • Future research requirements • Summary
  • 3. Introduction • Soils contain significant stores of carbon and nitrogen (1500 Pg organic C and 190 Pg total N) • These stores are continuously exposed to decomposition and other biochemical processes that generate or consume CO2, N2O and CH4. • Using soil and atmospheric carbon stocks of 1500 and 720 Pg and an atmospheric CO2 concentration of 390 ppm, a 1% change in soil carbon = 8 ppm change in CO2 concentration (assuming no feedbacks) • Concern exists over the potential positive feedback that increased temperature may have on soil carbon loss and CO2 concentration
  • 4. Generation of greenhouse gases by soil CO2 N fertiliser & N2O CH4 Animal waste Soil surface Denitrification Respiration NH4 NO3 Methanogenic Nitrification organisms Mineralisation Assimilation Decomposition and mineral protection Organic Organic carbon nitrogen Aerobic Anaerobic soil soil Soil organic matter conditions conditions including decomposer organisms
  • 5. Consumption of greenhouse gases in soil CO2 Photosynthesis N2O CH4 Shoot dry Plant dry matter matter Soil surface Root dry matter Biological transformations Methanotrophic associated with organisms Residue N cycling deposition Uptake Inorganic N NH4 & NO3 Organic Organic Aerobic carbon nitrogen soil Immobilisation conditions Soil organic matter including decomposer organisms
  • 6. Projected changes to Australia’s climate 2030 2050 2070 Australian agricultural regions • warmer and drier • altered seasonality • greater extremes 0.3 0.6 1.0 1.5 2.0 2.5 3.0 4.0 5.0 Change in average annual temperature ( C) Such changes will undoubtedly influence rates of net greenhouse gas emissions Magnitude of change will be -40 -20 -10 -5 -2 2 5 10 20 40 defined by the sum of the Change in annual rainfall (%) climate change influence on all processes -4 -2 2 4 8 12 16 Change in annual potential evapotranspiration (%) Source: http://climatechangeinaustralia.com.au - 50th percentile of projected changes under the medium future emissions profile relative to 1980-1999
  • 7. CO2 / Soil carbon: inputs of carbon Controls on potential carbon input Photosynthetically 1) The amount of PAR active radiation (PAR) 2) Fraction of PAR used 3) Efficiency of carbon capture, 4) Proportion lost to respiration CO2 5) Proportion removed in products. Factors 1-4 define potential net primary productivity Product harvest Other constraints (water, fertility, disease) may reduce efficiencies and lead to Actual NPP < Potential NPP Product removal – harvest index issue
  • 8. CO2 / Soil carbon: inputs of carbon Where can carbon inputs be increased? Photosynthetically active radiation (PAR) Identify systems that are not achieving 100% resource use efficiency (water and nutrients) CO2 Identify constraints and define whether or not they can be managed Yes No Product harvest Implement Consider management alternative changes and production capture systems that may additional be better suited carbon to constraints
  • 9. CO2 / Soil carbon: fate of carbon inputs Photosynthetically What happens to the carbon active radiation (PAR) inputs? The majority is decomposed and CO2 returned to the atmosphere as CO2 The remainder resists decomposition and replaces the soil organic carbon Product that is being decomposed harvest Issues - residue placement – surface residues vs roots Soil organic - reduced incorporation carbon
  • 10. CO2 / Soil carbon: controls on stability of SOC • Most of these factors vary spatially • Different soils have different capacities to stabilise SOC • Practical implication – management outcomes on SOC will vary with soil type
  • 11. CO2 / Soil carbon: climate change impacts • Dryland agriculture • Inputs • Reduced potential plant growth and the inputs of carbon to soil is likely where water is the main constraint. • Losses • Drier conditions are likely to reduce decomposition • Evidence is mounting to suggest enhanced decomposition with increasing temperature (larger relative impact on stable forms) • Extension of cropping systems into current cold/wet environments may occur – possible threat to existing carbon stocks • Irrigated agriculture • Increases inputs and rates of decomposition are likely. • Net effect will depend on extent of alterations of inputs and losses
  • 12. CO2 / Soil carbon: mitigation/sequestration • The guiding principal - maximising the capture carbon given the resources available at any particular location will maximise SOC • Enhanced water use efficiency (kg dm/mm water) • Greater tolerance to subsoil constraints where possible • Greater root: shoot ratios • Altered composition of plant residues – increased lignin • CO2 fertilisation may help offset reductions • Positive impacts of building SOC on soil productivity – water holding capacity, nutrient cycling, etc.
  • 13. Nitrous oxide: climate change impacts • Strong influence of temperature and water availability Relative N2O emission Temperature Soil water content Total N2O emission 0.6 (µg N kg-1) 0.4 0.2 0.0 40 60 80 100 Incubation Temperature (°C) Water filled pore space (%) Chen et al 2010 SBB 42 660 Dalal et al 2003 AJSR 41 165 • Net change will depend on the relative responses Dryland Irrigated Increased in tropics and subtropics Increased in all regions Decreased in cooler temperate regions
  • 14. Nitrous oxide: mitigation strategies Key requirement – minimise the concentration of inorganic N • Better matching of fertiliser N application to crop demand as dictated by the season – develop flexible N strategies • Increased reliance on biological N fixation to enhance soil N status – processes controlling N mineralisation also control plant growth • Alteration of animal diets to avoid an intake of excess N and excretion of high N content urine and faeces • Application of inhibitors to reduce rates of formation and transformation of soil ammonium – urease and nitrification inhibitors
  • 15. Methane: climate change impacts • Soils can be a source or a sink for methane depending on their oxidative condition • Significant methane production occurs at redox potentials more negative than -100 mV (rates increase • Dependence on redox potential means that properties controlling rates of oxygen diffusion and consumption exert strong control • Where methane production conditions are met a strong response to temperature exists (Q10 = 4 with an optimum near 35°C) Flood irrigation Drip/sprinkler irrigation Dryland Potential for methane emission will increase Potential for methane consumption will increase
  • 16. Methane: mitigation strategies Key requirement – maintain soil in an oxidative state • Adequate water management strategies: • Flood irrigation - create temporary oxic conditions (oxidises reduced species – e.g. Fe2+ to Fe3+) • Sprinkler/drip irrigation – avoid prolonged saturation to reduce emission, judicious control of soil water content can optimise methane consumption • Avoid incorporation of large amounts of degradable residues just prior to or when soils are saturated • Addition of SO42- - gypsum
  • 17. Future research directions • All gases • Quantification of uncertainties associated with estimates • Should build systems to define the cumulative probability of outcomes • N2O and CH4 from soils • National evaluation of N2O and CH4 emissions reductions will rely on modelling and/or emission factors • Continued measurement of fluxes (e.g. NORP) will be essential • How do we best to deal with the diversity of agricultural practice, soil type and climatic condition? • How do we deal with climate change? Will calibration against current conditions be good enough? • Definition of the relative responses to temperature and soil water content and potential interactions.
  • 18. Future research directions • Soil carbon • A combination of measurement and modelling will be required • Measurement – establish initial conditions, verify model predictions, and allow recalibration • Models – predict the likely outcomes of alterations to management to help guide management • Derivation of an appropriate statistical approach to assess the potential of innovative practices • Rapid and cost effective soil sampling - • Smarter sampling of soils at different scales – use of available spatial datasets to help direct sampling.
  • 19. Regional soil carbon estimation (Wheeler et al.2011a) Regional soil carbon prediction • 3 biogeographic regions – Brigalow (NSW portion) – NSW South Western Slopes – South Eastern Highlands • ~170 000 km2 – 65% grazing – 18% cropping – 11% forestry – 6% other
  • 20. Regional soil carbon estimation (Wheeler et al.2011a) On training data On training data Average absolute error 0.1 Average absolute error 0.09 R2 0.59 R2 0.55 On test data On test data Average absolute error 0. 14 Average absolute error 0. 11 R2 0.45 R2 0.38 0 – 10 cm 0 – 30 cm
  • 21. Summary • Development of a robust modelling capability will be required to • construct regional and national emission assessments and • define the potential outcomes of on farm management decisions and policy decisions. • This model development will require comprehensive field data sets to calibrate models and validate outputs. • Improved spatial layers of model input variables collected on a regular basis will be required to optimise accounting at regional through to national scales. • A diversity of agricultural practices exist in Australia. A continual matching of practice to soil and climate and economic assessment to optimise outcomes.
  • 22. Jeff Baldock Sustainable Agriculture Flagship Phone: (08) 8303 8537 Email: jeff.baldock@csiro.au Thank you Contact Us Phone: 1300 363 400 or +61 3 9545 2176 Email: Enquiries@csiro.au Web: www.csiro.au
  • 23. CO2 / Soil carbon: composition Particulate organic carbon (2 mm – 0.05 mm) (POC) Resistance to decomposition Humus (<0.05 mm) (HumC) increases Resistant organic carbon (ROC): dominated by charcoal Particulate carbon Humus carbon Resistant (2mm – 0.05 mm) (<0.05mm) (charcoal <2mm) 400 m 10 m 20 m