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Raphael Trotignon - PhD Defense Under the supervision of Professor Christian de Perthuis THE EUROPEAN UNION CO 2 EMISSION TRADING SCHEME: FROM EX ANTE AND EX POST ANALYSIS TO THE PROJECTION IN 2020 October 17th, 2012 Paris Dauphine University (D520) Climate Economics Chair - [email protected] IN SEARCH OF THE CARBON PRICE

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  • Raphael Trotignon - PhD Defense Under the supervision of Professor Christian de Perthuis

    THE EUROPEAN UNION CO2 EMISSION TRADING SCHEME:

    FROM EX ANTE AND EX POST ANALYSIS TO THE PROJECTION IN 2020

    October 17th, 2012 – Paris Dauphine University (D520)

    Climate Economics Chair - [email protected]

    IN SEARCH OF THE CARBON PRICE

    mailto:[email protected]

  • 2

    Introduction

    • This thesis is the result of five years studying the European Emission Trading Scheme, the most complete experience of carbon pricing to date • An empirical analysis based on ex ante/ex post comparison • Supplemented by the creation of a simulation model, an original approach • In a context full of uncertainties, nobody knows the “right” carbon price: it is necessary to combine the three core flexibility mechanisms associated to the EU ETS to understand the market development (Chapter I) • Analysis build by progressively integrating in the model: baseline emissions and abatement (Chapter II), the use of offsets (Chapter III), and banking and borrowing (Chapter IV) • Eventually, shift from an ex post use to a prospective use of the model to 2020 (Chapter V)

  • 3

    I. Ex ante vs. ex post

    Beginning of 2005 Beginning of 2008 Beginning of 2012

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    Total cap (free+auction+offsets)

    Cap (free+auction)

    Baseline as in 2005

    - 2 GtCO2

    - 350 MtCO2

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    sTotal cap (free+auction+offsets)

    Cap (free+auction)

    Verified Emissions

    Baseline as in 2008

    - 500 MtCO2 - 5 GtCO2

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    Total cap (free+auction+offsets)

    Cap (free+auction)

    Verified Emissions

    Baseline as in 2010

    - 850 MtCO2+ 1,2 GtCO2

    + 225 MtCO2

    • Difference between initial expectations and actual outcome: – Past emission reductions (carbon price and economic crisis) – Decentralized use of offsets, supplemental to the cap – Interactions with other policies – Weakened anticipations

  • 4

    I. The observed price

    Source: Climate Economics Chair

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    OTC Point Carbon BNS EUA05-07 ICE ECX EUA DEC12

    Expectations in line with early analysts forecasts Illiquid market

    EU ETS Directive adoption

    Decisions on NAP1

    Cold winter

    Phase 1 surplus not transferable to Phase 2

    Release of 2005 verified emissions

    Discussions on 2020 targetsNAP 2 decisions

    Financial and economic crisis

    New equilibirum in a context of slow recovery

    Roadmap 2050Fukushima Energy

    efficiency

    Debt crisis and worsening growth outlookSet aside debate

    Climate Energy Package

    Phase 1 spot price December 2012 Future price

    • The price is very different from initial expectations • A “classic” for cap-and-trade programs (SO2, Kyoto, RGGI) • Capacity to drive short term and long term reductions in this context? • Given uncertainties, the key for understanding the market is the dynamics provided by the three flexibility mechanisms

    Observed spot and DEC12 price over 2005-2012

  • 5

    I. Methodology

    Counterfactual or baseline emissions

    Reduction costs Initial distribution

    of allowances

    Behavior of participants with Flexibility mechanisms

    Use of offsets

    Banking Borrowing

    Analysis of the past Prospective

    exercise

    Trading

  • 6

    Outline

    Part I - Emissions trading: the key role of flexibility Part II - A prototype of ZEPHYR-Flex based on abatement and trading Part III - The use of carbon offsets: Good or Evil? Part IV - The calibration of ZEPHYR-Flex and the results on the first two trading periods Part V - Looking ahead: a multi-level regulation challenge

  • 7

    II. Baseline emissions

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    EU ETS industrial production (calculated from Eurostat, 2005=100)

    CO2 Emissions EU27 (UNFCCC 1A1 and 1A2 sectors, 2005=100)

    GDP EU27 (Eurostat 2005=100)

    •Emissions as they would be without carbon policies • Scenarios based on the past relationship between GDP growth and emissions • Using production indexes as a sectoral breakdown of gross production rates • And an elasticity of emissions to production (0.6 in general; 1.2 in case of economic choc) Limit: Not differentiated by sector

    Relationship between growth and emissions

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    120

    2005 2006 2007 2008 2009 2010 2011 2012e

    Electricity production

    Rest of combustion

    Refineries

    Iron and steel

    Cement

    Rest of industry

    EU ETS weighted index

    Production growth by sector used for sectoral baselines

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    0% 10% 20% 30% 40%

    Car

    bo

    n P

    rice

    (€

    /tC

    O2

    )

    Reductions below the baseline

    EU ETS

    ?

    8

    II. Abatement

    • Hypothesis on abatement costs of participating entities, by sector

    • Cost can evolve over time

    Relationship between price and abatement EU ETS level

    Price

    Quantities

    Marginal abatement cost curve of a given installation

    PEUA

    EpEUA E0

    Total cost of emissions reduction

    Opportunity cost(the value of emission reductions at the market price is greater than the internal reduction costs)

    E0-EpEUA: reduced emissions at price PEUA

    • In the model, abatement is done instantly • Perfect recognition of opportunity cost • A share of reductions are removed from the emission baseline the following years

  • 9

    II. Results with trading only

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    Carbon Price

    Carbon price (Phase 1) Carbon price (Phase 2)Bluenext EUA 2005-07 Bluenext EUA 2008-12

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    Total cap, baseline and verified emissions

    Simulated emissions

    Baseline Emissions

    Cap (free+auction)

    CITL Verified Emissions

    Total cap (free+auction+offsets)

    With trading only (no banking, no borrowing, no offsets): • Does not replicate observations • Despite the existence of a net surplus, trades are necessary for short installations to be compliant • Trading is very efficient to lower compliance costs price is zero as soon as baseline emissions are below the cap (assumption of zero transaction costs in the model)

  • 10

    Outline

    Part I - Emissions trading: the key role of flexibility Part II - A prototype of ZEPHYR-Flex based on abatement and trading Part III - The use of carbon offsets: Good or Evil? Part IV - The calibration of ZEPHYR-Flex and the results on the first two trading periods Part V - Looking ahead: a multi-level regulation challenge

  • 11

    III. Offsets: Good or Evil?

    • Major characteristic of the EU ETS: articulation with the Kyoto Protocol’s flexibility mechanisms, with quantitative and qualitative restrictions • The attitude towards offsets has changed: initially worshiped, Kyoto offsets are now perceived as aggravating “disequilibrium” on the EUA market • In the thesis:

    • Observation of prices • Use of offsets at the installation level Effect on past EUA equilibrium price with ZEPHYR-Flex Scenario for the use of offsets up to 2020

  • 12

    III. Price evidence

    • Existence of spot discount depends on whether the limit is binding or not • Different time discounts if offsets and allowances are not perceived as fully equivalent for future use

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    Pri

    ce/M

    argi

    nal

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    st

    Emissions/Abatementy = -0,0395x

    R² = 0,233y = -0,0365xR² = 0,6049

    y = -0,0391xR² = 0,6161

    y = -0,0383xR² = 0,5132

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    Ln(F

    ut/

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    (T-t) in years

    DEC08 DEC09 DEC10 DEC11 DEC12 DEC13Linear (DEC08) Linear (DEC09) Linear (DEC10) Linear (DEC11) Linear (DEC12)

    Announcement of

    Phase 3 qualitative

    restrictions

  • 13

    III. Observed and forecasted use

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    2008 2009 2010 2011Average use of

    annual limit

    Constant users 83% 73% 92% 98% 86%

    All except 2011 108% 118% 127% 118%

    All except 2010 118% 96% 128% 114%

    86% 70% 78%

    All except 2009 91% 148% 147% 129%

    83% 151% 117%

    85% 182% 133%

    Only in 2008 133% 133%

    All except 2008 116% 115% 104% 112%

    127% 71% 99%

    95% 109% 102%

    Only in 2009 135% 135%

    171% 186% 179%

    Only in 2010 281% 281%

    Only in 2011 256% 256%

    Absent users 0%

    Average intensity of offsets use, by category of behavior etc…

    + Assumptions : •Phase 3 rules •Phase 3 offset supply •Evolution of behavior

    Simulated use of offsets up to 2020

  • 14

    III. Lessons from Linking

    • Decentralized rules can lead to more uncertainty on the cap, and thus on future price and emission trajectory • Legacy from the Kyoto framework: relying on outside standards can raise regulatory issues • Applying ex post restrictions: intervention on the rules/criteria can have an opposite effect in the short term

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    Simulated Carbon price (Phase 1) Simulated Carbon price (Phase 2)

    Bluenext spot price 2005-07 Bluenext Spot price 2008-12

    • Clearly an arbitrage by participants on the market, leading to a relatively high use of offsets (550Mt in four years), and lower compliance costs • Nevertheless, economic optimum not fully established

    • information problems • reputational concerns • transaction costs

  • 15

    Outline

    Part I - Emissions trading: the key role of flexibility Part II - A prototype of ZEPHYR-Flex based on abatement and trading Part III - The use of carbon offsets: Good or Evil? Part IV - The calibration of ZEPHYR-Flex and the results on the first two trading periods Part V - Looking ahead: a multi-level regulation challenge

  • 16

    IV. Complete version of the model

    We add the time flexibility into ZEPHYR-Flex: the banking and borrowing provisions Time flexibility mechanisms implies to represent the anticipations of participants which play an essential role in our calibration exercise. Three decision criteria (see behavior table in Annex):

    1/ Present internal position (EUA Stock – Baseline Emissions)

    Perfectly known

    2/ Anticipated future internal position (Expected growth compared to free allocations) over an anticipation period

    Imperfectly anticipated

    3/ Market position through anticipation of bullish or bearish price Random (parameterized)

  • 17

    IV. Results after calibration

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    Bluenext spot price 2005-07 Bluenext spot price 2008-12

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    Verified EmissionsBaseline EmissionsCap (free+auction)CITL Verified EmissionsTotal cap (free+auction+offsets)

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    Banked Hedged EUAs Banked Compliance EUAs

  • 18

    • The EU ETS induced a cumulated amount of emission reduction of about 1,540 Mt over the first two Phases. 60% have been obtained outside the scheme’s perimeter through the use of carbon offsets (900 Mt) • The total compliance costs are estimated at 30 bn€ (reductions, offsets and auctions); exchange of allowances between participants represents a value of 18 bn€ over the first two phases • Given the level of the allowance cap, the cumulated net banking is close to 2,000 Mt at the end of 2012 Anticipations are preventing the price from being zero

    Dynamic of behavior in the future ? (shift to auctions, change of behavior following an intervention from public authority…)

    IV. Results after calibration

  • 19

    Outline

    Part I - Emissions trading: the key role of flexibility Part II - A prototype of ZEPHYR-Flex based on abatement and trading Part III - The use of carbon offsets: Good or Evil? Part IV - The calibration of ZEPHYR-Flex and the results on the first two trading periods Part V - Looking ahead: a multi-level regulation challenge

  • 20

    V. Baseline with policy interactions

    Renewable Energy and Energy Efficiency policies can affect EU ETS perimeter’s emissions independently from the EUA price: Integration in the model as a progressively lowered elasticity between production growth and baseline emissions growth (average of 60 Mt/yr in Phase 2 to 100 Mt/yr in 2020)

    EMISSIONS CAP 30% BELOW BAU

    BAU EMISSIONS

    Reductions from: energy efficiency policestechnology policiesprice response in trading scheme

    10 %

    15 %

    SUPPLEMENTARY POLICIES UNDERACHIEVE

    (a)

    5 %

    SUPPLEMENTARY POLICIES OVERACHIEVE

    (b)

    Source: Baron (2012)

  • 21

    V. Simulation of interventions

    Three intervention scenarios are tested with the model:

    • The introduction of a reserve price of 20€/t at auctions • A back-loading (or set-aside) of allowances as proposed by the Commission on July, 25th 2012 • A reevaluation of the allowance cap to 2020 and 2030 compatible with the Roadmap 2050

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    Set aside 400Mt Set aside 900MtSet aside 1200Mt

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    Roadmap (change of anticipation)

  • 22

    V. Lessons

    • Some intervention measures can induce more uncertainty and instability, as they would not allow firms to set up “correct” anticipations by themselves • It is very difficult to send the “right” incentives to market players in the absence of explicit long term targets that are connected with the current and medium term cap (US SO2 trading program included a 30 years cap) • The unforeseen evolution of the macro-economic context, the state of international carbon markets and the link with an offsetting mechanism are factors which can be extraordinarily stimulating but also undermining if not dealt with “appropriately”

  • 23

    Limits, and how to extend this work

    Abatement • The abatement costs curves by sectors, and their potential shift over time • The effect of abatement on the baseline, and on cost curves: short term versus long term reductions, innovation effect…

    Baseline emissions

    • Sector elasticities • Interactions with other policies • Explicit link with relevant drivers (energy prices, country growth etc.)

    Compliance and hedging behavior

    • Transaction data (banking, borrowing, maybe more) • Identification to a decision model ?

    Modeling and Linking other markets • Aviation, Australia, California ?

  • Thank you for your attention

    October 17th, 2012 – Paris Dauphine University (D520)

    Climate Economics Chair - [email protected]

    mailto:[email protected]

  • 25

    Working papers and peer reviewed articles

    • Trotignon, R. and Delbosc, A. (2008), Allowance Trading Patterns During the EU ETS Trial Period: What does the CITL reveal?, Climate Report n°13, CDC Climat Research, June 2008 • Ellerman, A. D. and Trotignon, R. (2009), Cross Border Trading and Borrowing in the EU ETS, The Energy Journal, Volume 30 (Special Issue 2), Climate Change Policies After 2012, 2009 • Trotignon, R. and Leguet, B. (2009), How Many CERs by 2013?, Mission Climat of Caisse des depots, Working Paper n°2009-5, August 2009 • Trotignon, R. and Solier, B. (2011), The European Market on the Road to Phase 3, in De Perthuis, C. and Jouvet, P-A., eds. (2011), Climate Economics in Progress 2011, Chapter 2, Economica, October 2011 • Trotignon, R (2012), Combining cap-and-trade with offsets: lessons from the EU-ETS, Climate Policy, Vol. 12, Iss. 3, 2012 • De Perthuis, C. and Trotignon, R. (2012), The European CO2 allowances market: issues in the transition to Phase III, Climate Economics Chair, Information and Debates n°14, March 2012

  • 26

    Complete version of ZEPHYR-Flex

    Total Allowances for Year Y (annual cap)

    MACCs

    Market exchanges: Supply/Demand equilibirum for Year YThe price starts from zero and goes up as long as ∑Buy +/- ∑Hedging-Spec > ∑Sales + ∑Auctions + ∑Offsets

    Verified EmissionsYear Y

    Free Allocation Auctions

    Installation 1 Installation 2 Installation 10,000Installation 3 …

    EUA StockBaseline

    Emissions

    AnticipatedFuture price

    Buying Selling Banking Borrowing Hedging/Speculation

    Position for Year Y

    Anticipated position over the period

    Year N+1

    Use of Kyoto offset for Year Y (exogenous)

    Emission ReductionsYear Y

    EUA equilibrium price Year Y

    EUA Price

    Bought/SoldYear Y

    Banking/BorrowingYear Y