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Francisco X. Aguilar, Michael Goerndt, Stephen Shifley, Nianfu Song

                     Department of Forestry
                 The School of Natural Resources
                      University of Missouri
   Logging residues
   Removal of excess biomass (fuel treatments)
   Fuelwood from forestlands
   Primary and secondary wood processing mill
    residues and pulping liquors
   Urban wood residues
   Dedicated energy plantations
   Climate change: Reduce CO2 emissions from
    fossil fuels.
   Rules and regulations: E.g. Renewable Portfolio
    Standards.
   Economics: Relatively low cost for conversion to
    co-firing compared to other renewable energy
    (e.g. wind, solar, liquid biofuels)
   Forest stewardship: e.g. Promote forest health
   Estimate potential for co-firing of biomass in
    existing coal-fired power plants for the U.S.
    Northern Region

   Use results to establish a “coarse screen” for
    county-level potential of co-firing biomass for
    electricity based on physical factors
   County-level is smallest practical scale for
    estimation, given restrictions on estimation of
    explanatory factors (e.g. infrastructure,
    waterways, biomass resource availability).

   Potential for co-firing can be indicated by
    estimated presence (probability estimate>0.5).




                                                      5
   Important Issues:

    ◦ Possible spatial interdependence

    ◦ Dependence of county-level co-firing on
      presence of coal-fired power plant(s)
   Theoretical Framework
    ◦ Natural conditionality of co-firing on presence of
      coal-fired power plants.
    ◦ Probability of co-firing y within the ith county is
      conditional on the expected probability of a coal
      power plant in the same county (E[ci]) & other
      location factors captured in an information factor
      matrix X.

    ◦ Prob(yi=1| E[ci], X) = F(E[ci|Lα], Xβ)
   County-level probability for placement of coal-fired
    power plants was analyzed as a first stage (Model A)

   Two models created for final stage (co-firing
    probability (potential))

    1. Model B: Known coal power plant frequency
       included as independent variable

    2. Model C: First stage (Model A) estimates included
       as independent variable
   Standard probit regression
    ◦ Assumes binary response (0,1)
    ◦ Does not account for spatial dependencies

   Bayesian spatial autoregressive probit
    ◦ Assumes binary response (0,1)
    ◦ Accounts for spatial dependencies

   Preliminary Chi-squared tests conducted on
    dependent variables for spatial dependence
    prior to assessing Bayesian spatial
    autoregressive probit
   Dependent
    ◦ Location of coal-fired power plants & co-firing
      status (EPA, DOE)

   Independent
    ◦   Electricity demand (EIA)
    ◦   Infrastructure (EPA, US Census)
    ◦   Coal availability and price
    ◦   Renewable energy policy
    ◦   Resource availability of biomass (TPO, NASS)
    ◦   Sub-regional variation
   Energy demand
    ◦ Population
    ◦ County area
   Infrastructure
    ◦ Rail presence
    ◦ Road presence
    ◦ River & stream presence
   Renewable energy policy
    ◦ Renewable energy portfolio standards (RPS) by 2001
   Resource availability of biomass
    ◦ Wood mill residues
    ◦ Corn yield (stover)
   Spatial autoregressive probit: no significant
    improvement over standard probit

   Energy demand proxies such as county area &
    urban percentage of county area were highly
    significant

   Infrastructural proxies of road presence &
    stream presence (namely road x stream
    interaction) were highly significant.
   Known frequency of coal-fired power plant
    highly significant.
   Significant proxies
    ◦   Electricity Price
    ◦   Rail Presence
    ◦   Road presence x stream presence
    ◦   Wood mill residues
    ◦   RPS implementation
    ◦   One sub-regional indicator
   Component from Model A not significant
   Significant proxies
    ◦   Rail Presence
    ◦   Road presence x stream presence
    ◦   Wood mill residues
    ◦   RPS implementation
    ◦   Two sub-regional indicators
   5 counties with
    high potential
    but no current
    co-firing
    facilities
   Indicated
    counties have
    high values for
    electricity
    demand,
    infrastructure &
    mill residues
   Model success
    rate = 96%
   3 counties with
    high potential
    but no current
    co-firing
    facilities
   Indicated
    counties have
    high values for
    infrastructure &
    mill residues
   Model success
    rate = 96%
   Notable positive relationship between electricity
    price and probability of co-firing biomass

   Adoption of RPS was significant for both final
    models, denoting a strong relationship between
    energy policy and co-firing

   Counties identified by Models B & C had fairly high
    values for relevant infrastructure and biomass
    supply (mill residues)
   Inclusion of known coal-fired power plant
    frequency in Model B did not decrease significance
    of infrastructural proxies

   Infrastructure variables such as road presence are
    vital to co-firing operations with or without current
    presence of coal-fired power plants

   Sub-regional variation has a greater effect on co-
    firing probability in the absence of known coal-
    fired power plant frequency
   Physical potential of co-firing biomass is highly
    influenced by variables indicating
     Supply infrastructure
     Current availability of wood mill residues

   Implementation of RPS has a significant positive
    effect on co-firing

   Valuable county-level preliminary examination of
    co-firing potential across the Northern region.
Dr. Michael Goerndt
goerndtm@missouri.edu
Department of Forestry
 University of Missouri

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Session 27 ic2011 goerndt

  • 1. Francisco X. Aguilar, Michael Goerndt, Stephen Shifley, Nianfu Song Department of Forestry The School of Natural Resources University of Missouri
  • 2. Logging residues  Removal of excess biomass (fuel treatments)  Fuelwood from forestlands  Primary and secondary wood processing mill residues and pulping liquors  Urban wood residues  Dedicated energy plantations
  • 3. Climate change: Reduce CO2 emissions from fossil fuels.  Rules and regulations: E.g. Renewable Portfolio Standards.  Economics: Relatively low cost for conversion to co-firing compared to other renewable energy (e.g. wind, solar, liquid biofuels)  Forest stewardship: e.g. Promote forest health
  • 4. Estimate potential for co-firing of biomass in existing coal-fired power plants for the U.S. Northern Region  Use results to establish a “coarse screen” for county-level potential of co-firing biomass for electricity based on physical factors
  • 5. County-level is smallest practical scale for estimation, given restrictions on estimation of explanatory factors (e.g. infrastructure, waterways, biomass resource availability).  Potential for co-firing can be indicated by estimated presence (probability estimate>0.5). 5
  • 6.
  • 7. Important Issues: ◦ Possible spatial interdependence ◦ Dependence of county-level co-firing on presence of coal-fired power plant(s)
  • 8. Theoretical Framework ◦ Natural conditionality of co-firing on presence of coal-fired power plants. ◦ Probability of co-firing y within the ith county is conditional on the expected probability of a coal power plant in the same county (E[ci]) & other location factors captured in an information factor matrix X. ◦ Prob(yi=1| E[ci], X) = F(E[ci|Lα], Xβ)
  • 9. County-level probability for placement of coal-fired power plants was analyzed as a first stage (Model A)  Two models created for final stage (co-firing probability (potential)) 1. Model B: Known coal power plant frequency included as independent variable 2. Model C: First stage (Model A) estimates included as independent variable
  • 10. Standard probit regression ◦ Assumes binary response (0,1) ◦ Does not account for spatial dependencies  Bayesian spatial autoregressive probit ◦ Assumes binary response (0,1) ◦ Accounts for spatial dependencies  Preliminary Chi-squared tests conducted on dependent variables for spatial dependence prior to assessing Bayesian spatial autoregressive probit
  • 11. Dependent ◦ Location of coal-fired power plants & co-firing status (EPA, DOE)  Independent ◦ Electricity demand (EIA) ◦ Infrastructure (EPA, US Census) ◦ Coal availability and price ◦ Renewable energy policy ◦ Resource availability of biomass (TPO, NASS) ◦ Sub-regional variation
  • 12. Energy demand ◦ Population ◦ County area  Infrastructure ◦ Rail presence ◦ Road presence ◦ River & stream presence  Renewable energy policy ◦ Renewable energy portfolio standards (RPS) by 2001  Resource availability of biomass ◦ Wood mill residues ◦ Corn yield (stover)
  • 13. Spatial autoregressive probit: no significant improvement over standard probit  Energy demand proxies such as county area & urban percentage of county area were highly significant  Infrastructural proxies of road presence & stream presence (namely road x stream interaction) were highly significant.
  • 14. Known frequency of coal-fired power plant highly significant.  Significant proxies ◦ Electricity Price ◦ Rail Presence ◦ Road presence x stream presence ◦ Wood mill residues ◦ RPS implementation ◦ One sub-regional indicator
  • 15. Component from Model A not significant  Significant proxies ◦ Rail Presence ◦ Road presence x stream presence ◦ Wood mill residues ◦ RPS implementation ◦ Two sub-regional indicators
  • 16. 5 counties with high potential but no current co-firing facilities  Indicated counties have high values for electricity demand, infrastructure & mill residues  Model success rate = 96%
  • 17. 3 counties with high potential but no current co-firing facilities  Indicated counties have high values for infrastructure & mill residues  Model success rate = 96%
  • 18. Notable positive relationship between electricity price and probability of co-firing biomass  Adoption of RPS was significant for both final models, denoting a strong relationship between energy policy and co-firing  Counties identified by Models B & C had fairly high values for relevant infrastructure and biomass supply (mill residues)
  • 19. Inclusion of known coal-fired power plant frequency in Model B did not decrease significance of infrastructural proxies  Infrastructure variables such as road presence are vital to co-firing operations with or without current presence of coal-fired power plants  Sub-regional variation has a greater effect on co- firing probability in the absence of known coal- fired power plant frequency
  • 20. Physical potential of co-firing biomass is highly influenced by variables indicating  Supply infrastructure  Current availability of wood mill residues  Implementation of RPS has a significant positive effect on co-firing  Valuable county-level preliminary examination of co-firing potential across the Northern region.
  • 21. Dr. Michael Goerndt goerndtm@missouri.edu Department of Forestry University of Missouri