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Jan Abrell, Johannes Herold , Florian Leuthold Chair of Energy - PowerPoint PPT Presentation

Modeling the Diffusion of Carbon Capture and Storage under Emission Control and Technology Learning IAEE, Vienna, 10 September 2009 Jan Abrell, Johannes Herold , Florian Leuthold Chair of Energy Economics and Public Sector Management Agenda 1.


  1. Modeling the Diffusion of Carbon Capture and Storage under Emission Control and Technology Learning IAEE, Vienna, 10 September 2009 Jan Abrell, Johannes Herold , Florian Leuthold Chair of Energy Economics and Public Sector Management

  2. Agenda 1. Innovation in Energy Technologies 2 2. Concept of Technology Learning Concept of Technology Learning 3. The Model 4 4. Scenarios and Results Scenarios and Results 5. Conclusion 6. Literature 6. Literature - 2 -

  3. Innovation in Energy Technology • CCS, on and off-shore wind are considered as the most important low- carbon energy technologies for the German market • Under today's emission restrictions, electricity producers miss economic incentives to apply CCS or other innovative high cost energy technologies • No early bird market as in consumer electronics high knowledge spillovers • No early bird market as in consumer electronics, high knowledge spillovers • But innovative technologies often have a high potential for improvement • The higher generation costs of CCS electricity are assumed to decline over g g y time through learning effects if the technology is applied • We therefore develop an economic, dynamic model to simulate the diffusion of CCS technology and wind under the German base-load regime, while taking into account expected learning effects • CCS and wind are often referred to as being competitors to each other, focusing on one might harm the other. - 3 -

  4. Introduction to Technology Learning • First observed by Wright (1936) in airplane manufacture as decreasing labor time requirements as workers gained experience with a certain task g • A more comprehensive analysis by the Boston Consulting Group found learning rates between 10 to 25% along industries, each time cumulative output doubles output doubles   b C a CC * t t C 0  a 0  b CC 0  C technology cost in t t  CC CC Cumulated C l d i installed ll d Capacity C i i in t t  b learning exponent • Study by Rubin et al (2006) indicates that the learning rate for CCS power plants capital costs could be expected around 10% • However • However, we found no data on expected plants efficiency improvement, we found no data on expected plants efficiency improvement which is accounted for in the model - 4 -

  5. The Model • Diffusion of CCS is modeled in a perfectly competitive market, in which the producer chooses a welfare maximizing production portfolio of g different generation technologies • Available technologies are: nuclear, lignite, natural gas combined cycle, wind on- and off-shore and lignite CCS wind on- and off-shore and lignite CCS • Each technology is characterized by specific capital costs, efficiency, plant life and CO 2 emission per MWh el , which are limited • In case of CCS, this leads to an emission reduction of 80% compared to the standard technology. - 5 -

  6. Model Formulation • Player faces a linear inverse demand function of the form: a  a D D P  t t t b t      X X D D a b b P P g τ t t t t t , ,  g τ t   X Plants production of technolo gy g in t installed in  g t , ,     fl fl CAP CAP flex flex excap excap X X * *      g t g g t g g t , , , , , , , ,  fl age dependent fullload hours g τ t , , ,   CAP avaiable capacity of technolo gy g installed in  g  flex excap * exogenous capacity   g t g , , , - 6 -

  7. Model Formulation • Capacity depreciation modeled as decreasing availability of plants   0 , 95 0 , 91 0 , 86 0 , 81 0 , 75 0 , 69 0 0     0 , 95 0 , 91 0 , 86 0 , 81 0 , 75 0 , 69 0 fl     τ , t 0 0 , 95 95 0 0 , 91 91 0 0 , 86 86 0 0 , 81 81 0 0 , 75 75 0 0 , 69 69       0 , 95 0 , 91 0 , 86 0 , 81 0 , 75  CAP CAP ICAP ICAP  g t ilag g t , ( ) , g ,  ICAP investment into new capacity g g , t t  imax ICAP g g t ,  imax i investment t t constraint t i t g - 7 -

  8. Model Formulation    f   E cpr p X ( ( 1 ) ) * *     g g t t g g g g t t  , , , , , , , ,   f g f M  g , ( , ) ,  E Emissions of p plant using g technology gy g g g g , t t  cpr , Emission capture rate of technology g g t   carbon emission factor of fuel f f    e E max t t g g t t , , g max  e exogenous emission restrictio n t - 8 -

  9. Modeling of Learning     g     cap p  g g PI pi , 0 0     *  g t g  , , 0 cap ICAP    g g , 0 ,     t   0.1 CCS        g g   gen      g , 0 *        g g t g g   , , , , 0 gen X X g   , 0 _   g , ,   _ _     t ,     0 0 . 025 025 CCS - 9 -

  10. Model Formulation • We maximize sum of future discounted welfare • Welfare is calculated as the integral under the demand curve less the • Welfare is calculated as the integral under the demand curve less the production cost which consist of fuel and other variable cost as well as investment cost.     D P ( ) pf   t t             f     t P P D D dD dD   X X c c   PI PI ICAP ICAP       max max ( ( ) ) * t t t g t g g t g t , , , ,     X      g t    , , t f g M t  g g ( , ) , , 0 ICAP g t , CAP g t , E g g , t t • Modeled as non linear program in GAMS and solved using the CONOPT • Modeled as non-linear program in GAMS and solved using the CONOPT solver - 10 -

  11. Scenarios Scenario Description Base Case No learning rates, CO 2 emissions are limited Scenario 1: Permit allocation is reduced by 1% each period to increase attractiveness of Emission the low-carbon technology CCS. Reduction Scenario 2: Scenario 2: No investment into nuclear power plant capacity allowed No investment into nuclear power plant capacity allowed Phase out of nuclear Scenario 3: Learning effects which lower capital costs and increase efficiency are L Learning effects i ff t i implemented for the CCS technology and wind, nuclear still allowed for l t d f th CCS t h l d i d l till ll d f Learning effects which lower capital costs and increase efficiency are implemented for the CCS technology and wind, nuclear not allowed for - 11 -

  12. Data Nuclear NGCC Lignite Lignite Wind Wind CCS CCS onshore onshore offshore offshore Full load [h/yr] 7500 7000 7000 7000 1750 3500 hours Initial Initial [%] [%] 35 35 58 58 44 44 32 32 0 0 0 0 Efficienc y €/kW €/kW 2500 2500 750 750 1200 1200 2100 2100 1500 1500 3000 3000 Initial Initial capital costs Years 40 30 40 40 20 20 Life time Life time O&M [€/MWh] 3 2 3 6 2 2 + 7 (TS) costs - 12 -

  13. Learning and Fuel Parameters Technology Elasticity eta gen g;0 [TWh] Elasticity CC cap g;0 [GW] CCS -0.025 10 0.1 4 Wind onshore - - 0.18 20 Wind offshore - - 0.18 4 Uranium Natural Lignite Fuel Gas [ [€/MWh th ] th ] 5 20 5 Price Price Carbon [CO2/MW 0 0,2 0,4 hth] emission factor Price % 1 2 1 - 13 -

  14. Model Results Base Case • Lignite electricity production up to the emission constraint • No endogenous investment in wind capacity No endogenous investment in wind capacity • Nuclear the most competitive alternative to lignite - 14 -

  15. Scenario 1: Emission Reduction • Lignite electricity production up to the emission constraint • No endogenous investment in wind capacity No endogenous investment in wind capacity • Nuclear fills the opening gap from reduced lignite capacity - 15 -

  16. Scenario 2: Emission Reduction, no Nuclear • Major investment in CCS technology • Endogenous investment in wind, for offshore the capacity limit not reached Endogenous investment in wind, for offshore the capacity limit not reached • Highest electricity price scenario 83€/MWh in average - 16 -

  17. Scenario 3: Emission Reduction, Nuclear Phase-out, Learning g • Investment into offshore wind from 1012 until capacity restriction is reached • More diverse generation portfolio, CCS acts as a bridge technology More diverse generation portfolio, CCS acts as a bridge technology • Average electricity price of 68€/MWh - 17 -

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