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EU Climate Policy:
(Some) Issues At Stake
EU Climate Policies
Towards a Low-Carbon Economy
23th October 2015, Bilbao
2/17
Source: PIK (2008)
Reduction requirements for anthropogenic greenhouse 2°C:
IPCC (AR4): Halving of global GHG2000 by 2050
Global Climate Policy Background: 2°C Target
3/17
Contributing a “fair” share
Guidelines for EUnilateral Climate Policy
Efficiency
Effectiveness
Equity
Fundamental interdependencies:
• Without efficiency normative equity disputes get enforced.
• Without equity (fairness) the incentives for cooperation decline.
• Without broad cooperation global effectiveness will not be feasible.
Pushing international agreements
Reducing emissions at least cost
E3
4/17
Source: PEW (2009)
e.g.: EU-Russia / Kyoto-WTO-deal
Milestones since 2005:
Brazil China India Mexico South Africa
• G8+5:
Pushing International Climate Policy Agreements
• Bali / Copenhagen: Climate regime under the UN umbrella („Kyoto Plus“)
• Cancún (2010): Ceiling of global warming to 2°C
5/17
Commitments:
• Kyoto EU burden sharing agreement for period 2008-2012 (issued 1999)
• EU climate and energy package 2020 (issued in 2009)
• EU climate and energy policy up to 2030 (issued in 2014)
• Low-carbon economy up to 2050 (plan)
Contributing a “Fair” Share
6/17
Population (P) × per capita income (G/P)
GNP
× energy intensity (E/G)
primary
energy
× CO2-intensity (C/E) = Emissions (C)
No (realistic) options:
• Human population control
• Economic growth constraints
Options:
• Energy efficiency improvements
• Fuel switching
• Carbon capture and storage
Reducing Emissions At Least Cost
First-best rules for cost-effective emission reduction:
- One target (emission reduction)  one instrument (emissions trading)
- Markets then work out the optimal mix of fuel switching (incl. renewable
energy shares), energy efficiency improvements, structural change etc.
7/17
The Good News: EU Emissions Trading Works
EU ETS in operation since 2005:
• Large-scale implementation of market-based climate policy (cap-and-trade)
• First multi-jurisdictional emissions trading system
Reforms to improve on cost-effectiveness (from 2013 onwards):
• EU-wide cap with harmonized emission allocation rules instead of (27)
national allocation plans in phases 1 (2005-2007) and 2 (2008-2012)
• Shift from free allocation towards auctioning of emission allowances
• Increased coverage of EU ETS by sectors (aviation, petro-chemicals,
ammonia, aluminium) und gases (nitrous oxide, perflurocarbons)
• Enhanced access to project-based where-flexibility mechanisms (CDM)
8/17
The Bad News: A Myriad of Targets and Instruments
The EU 20-20-20 (by 2020) climate and energy policy package:
GHG Target:
-20% compared to 1990
-14% compared to 2005
EU ETS
-21% compared
to 2005
Non ETS sectors
-10% compared to 2005
27 Member State targets, stretching from -20% to +20%
Two obvious deviations from cost-effective climate policy design:
• Segmentation of EU emission market (differences in marginal abatement costs)
• Overlapping regulation (e.g. green quota on top of EU ETS emission ceiling)
 Energy efficiency +20% compared to business-as-usual
 Renewables‘ share 20% primary energy share in 2020
 GHG emissions -20%/-30% compared to 1990
Target
 Biofuels 10% transport fuel share in 2020
Object Reference
Source: EU (2008)
9/17
Success? On Track With Targets But …
10/17
Excess Cost of EU Emission Market Segmentation
EU emission market segmentation:
• 1 international EU ETS market
• At least 27 domestic non-ETS markets (each of them subject to specific regulations)
Source: Böhringer et al. (2009)
p*
11/17Binding green quota

Total abatement requirement
Green (G)
Black (B)
abatementG
0 abatementB
0
MAC (€/t)
Excess cost of
green quota
Abatement options:
• Installing renewables (Green)
• Others (Black)
MAC (€/t)MAC: marginal abatement cost
Excess Cost of Overlapping Regulation
• If green quota becomes binding (alike positive feed-in tariffs), the
economy will be too green, i.e., excessively based on renewable energy.
• If white quota becomes binding (alike efficiency standards), the economy
will be too white, i.e., excessively energy efficient.
Source: Böhringer and Rosendahl (2011)
Another green paradox:
“Green serves the dirtiest”
p0
A
p1
A
12/17
Excess Cost of Overlapping Regulation
Examples from real life:
• Feed-in tariffs for renewables (Germany):
- Photovoltaics:
CO2 abatement cost: 400 - 1000 €/t
- Wind power:
CO2 abatement cost: 50 - 200 €/t
• EU fuel efficiency standards (120 g/km)
- CO2 abatement cost: > 200 €/t
• EU ban on light bulbs
- Opportunity costs > ? €/t
Compared to: EU CO2 allowance price < 10 €/t
13/17
Excess Cost of (Over-)Regulation: EU-20-20-20
0,00
0,10
0,20
0,30
0,40
0,50
0,60
0,70
0,80
0,90
Cost(in%ofEUGDP)
Source: Böhringer and Keller (2011)
Cost-effective CO2 reduction
Excess cost of emission market segmentation
Excess cost of renewable energy target
Excess cost of energy efficiency standard
1. Comprehensive EU emissions trading to reach 20% CO2 emission reduction
2. Segmentation into ETS and non-ETS markets
3. Additional green quota in electricity production (35%)
4. Additional reduction of primary energy use by 20% vis-à-vis BaU
14/17
Energy Security Impacts
Pitfalls:
• Amibiguous effects across common energy security indicators
• Lack of a rigorous welfare foundation for energy security
Source: Böhringer and Bortolamedi (2015)
15/17
Innovation Impacts
Source: Böhringer et al. (2015)
Regression analysis for German EEG:
• Positive average effect of EEG on innovation (patent filings)
• Caveats for technology-specific innovation impacts:
– Insignificant coefficients for solar
– Significant but negative coefficients for biofuels or geothermal
16/17
Conclusions
• With the focus on climate protection; additional targets for renewable
energy or energy efficiency become binding and induce (substantial)
excess cost.
Additional objectives such as energy security must be clearly
defined and specific regulations rigorously assessed :
• Definition of welfare concept and meaningful indicators
• Economic cost-benefit analysis
• Choice of appropriate instruments for policy implementation
• Emission market segmentation induces non-negligible cost.
Review over(-lapping) regulation!
EU climate policy is doomed to be more costly than necessary:
17/17
Thank you for attention!
Research funding from bizkaia talent is gratefully acknowledged.

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Efficiency losses from overlapping regulation of eu carbon emissions

  • 1. 1/17 EU Climate Policy: (Some) Issues At Stake EU Climate Policies Towards a Low-Carbon Economy 23th October 2015, Bilbao
  • 2. 2/17 Source: PIK (2008) Reduction requirements for anthropogenic greenhouse 2°C: IPCC (AR4): Halving of global GHG2000 by 2050 Global Climate Policy Background: 2°C Target
  • 3. 3/17 Contributing a “fair” share Guidelines for EUnilateral Climate Policy Efficiency Effectiveness Equity Fundamental interdependencies: • Without efficiency normative equity disputes get enforced. • Without equity (fairness) the incentives for cooperation decline. • Without broad cooperation global effectiveness will not be feasible. Pushing international agreements Reducing emissions at least cost E3
  • 4. 4/17 Source: PEW (2009) e.g.: EU-Russia / Kyoto-WTO-deal Milestones since 2005: Brazil China India Mexico South Africa • G8+5: Pushing International Climate Policy Agreements • Bali / Copenhagen: Climate regime under the UN umbrella („Kyoto Plus“) • Cancún (2010): Ceiling of global warming to 2°C
  • 5. 5/17 Commitments: • Kyoto EU burden sharing agreement for period 2008-2012 (issued 1999) • EU climate and energy package 2020 (issued in 2009) • EU climate and energy policy up to 2030 (issued in 2014) • Low-carbon economy up to 2050 (plan) Contributing a “Fair” Share
  • 6. 6/17 Population (P) × per capita income (G/P) GNP × energy intensity (E/G) primary energy × CO2-intensity (C/E) = Emissions (C) No (realistic) options: • Human population control • Economic growth constraints Options: • Energy efficiency improvements • Fuel switching • Carbon capture and storage Reducing Emissions At Least Cost First-best rules for cost-effective emission reduction: - One target (emission reduction)  one instrument (emissions trading) - Markets then work out the optimal mix of fuel switching (incl. renewable energy shares), energy efficiency improvements, structural change etc.
  • 7. 7/17 The Good News: EU Emissions Trading Works EU ETS in operation since 2005: • Large-scale implementation of market-based climate policy (cap-and-trade) • First multi-jurisdictional emissions trading system Reforms to improve on cost-effectiveness (from 2013 onwards): • EU-wide cap with harmonized emission allocation rules instead of (27) national allocation plans in phases 1 (2005-2007) and 2 (2008-2012) • Shift from free allocation towards auctioning of emission allowances • Increased coverage of EU ETS by sectors (aviation, petro-chemicals, ammonia, aluminium) und gases (nitrous oxide, perflurocarbons) • Enhanced access to project-based where-flexibility mechanisms (CDM)
  • 8. 8/17 The Bad News: A Myriad of Targets and Instruments The EU 20-20-20 (by 2020) climate and energy policy package: GHG Target: -20% compared to 1990 -14% compared to 2005 EU ETS -21% compared to 2005 Non ETS sectors -10% compared to 2005 27 Member State targets, stretching from -20% to +20% Two obvious deviations from cost-effective climate policy design: • Segmentation of EU emission market (differences in marginal abatement costs) • Overlapping regulation (e.g. green quota on top of EU ETS emission ceiling)  Energy efficiency +20% compared to business-as-usual  Renewables‘ share 20% primary energy share in 2020  GHG emissions -20%/-30% compared to 1990 Target  Biofuels 10% transport fuel share in 2020 Object Reference Source: EU (2008)
  • 9. 9/17 Success? On Track With Targets But …
  • 10. 10/17 Excess Cost of EU Emission Market Segmentation EU emission market segmentation: • 1 international EU ETS market • At least 27 domestic non-ETS markets (each of them subject to specific regulations) Source: Böhringer et al. (2009) p*
  • 11. 11/17Binding green quota  Total abatement requirement Green (G) Black (B) abatementG 0 abatementB 0 MAC (€/t) Excess cost of green quota Abatement options: • Installing renewables (Green) • Others (Black) MAC (€/t)MAC: marginal abatement cost Excess Cost of Overlapping Regulation • If green quota becomes binding (alike positive feed-in tariffs), the economy will be too green, i.e., excessively based on renewable energy. • If white quota becomes binding (alike efficiency standards), the economy will be too white, i.e., excessively energy efficient. Source: Böhringer and Rosendahl (2011) Another green paradox: “Green serves the dirtiest” p0 A p1 A
  • 12. 12/17 Excess Cost of Overlapping Regulation Examples from real life: • Feed-in tariffs for renewables (Germany): - Photovoltaics: CO2 abatement cost: 400 - 1000 €/t - Wind power: CO2 abatement cost: 50 - 200 €/t • EU fuel efficiency standards (120 g/km) - CO2 abatement cost: > 200 €/t • EU ban on light bulbs - Opportunity costs > ? €/t Compared to: EU CO2 allowance price < 10 €/t
  • 13. 13/17 Excess Cost of (Over-)Regulation: EU-20-20-20 0,00 0,10 0,20 0,30 0,40 0,50 0,60 0,70 0,80 0,90 Cost(in%ofEUGDP) Source: Böhringer and Keller (2011) Cost-effective CO2 reduction Excess cost of emission market segmentation Excess cost of renewable energy target Excess cost of energy efficiency standard 1. Comprehensive EU emissions trading to reach 20% CO2 emission reduction 2. Segmentation into ETS and non-ETS markets 3. Additional green quota in electricity production (35%) 4. Additional reduction of primary energy use by 20% vis-à-vis BaU
  • 14. 14/17 Energy Security Impacts Pitfalls: • Amibiguous effects across common energy security indicators • Lack of a rigorous welfare foundation for energy security Source: Böhringer and Bortolamedi (2015)
  • 15. 15/17 Innovation Impacts Source: Böhringer et al. (2015) Regression analysis for German EEG: • Positive average effect of EEG on innovation (patent filings) • Caveats for technology-specific innovation impacts: – Insignificant coefficients for solar – Significant but negative coefficients for biofuels or geothermal
  • 16. 16/17 Conclusions • With the focus on climate protection; additional targets for renewable energy or energy efficiency become binding and induce (substantial) excess cost. Additional objectives such as energy security must be clearly defined and specific regulations rigorously assessed : • Definition of welfare concept and meaningful indicators • Economic cost-benefit analysis • Choice of appropriate instruments for policy implementation • Emission market segmentation induces non-negligible cost. Review over(-lapping) regulation! EU climate policy is doomed to be more costly than necessary:
  • 17. 17/17 Thank you for attention! Research funding from bizkaia talent is gratefully acknowledged.