european energy policy analysis with gtap model in a … · · 2016-09-26european energy policy...
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European energy policy analysis with GTAP model in a consequential prospective LCA framework
Thomas Dandres*, Pablo Tirado, Caroline Gaudreault and Réjean Samson
Swiss LCA Forum
9 September 2016 *Contact: [email protected]
Introduction
Assessing policies with LCA
Method
Objectives
Case study: 2005-2025 European energy policies
Prospective LCA: technological and economic background
Consequential LCA: direct and indirect consequences
Results
Comparison of two European energy policies
Environmental impacts of the economic growth
Uncertainty analysis
Conclusion
PRESENTATION OUTLINE
Large scale policies may harm the environment and the human society
Example: national biofuel policies may cause indirect land use changes emitting significant amounts of CO2 and increase prices of food products
There is a need to assess large scale policies from a global perspective
What are the characteristics of policies?
and what are the needs to conduct LCAs of policies?
May have indirect effects
Cause large changes in many life cycles
Over a long period of time
INTRODUCTION
Prospective LCA
Consequential LCA
Non-marginal variations
Consequential LCA is based on economic modeling, therefore an international policy assessment requires an economic model able to:
Investigate prospective scenarios
Handle non-marginal variations
Model all economic sectors to cover indirect effects
General equilibrium economic models meet these criteria
Especially:
INTRODUCTION
Hertel (1997)
• 57 economic sectors
• 113 regions
• Semi-dynamic
• Open source
• Many applications (GTAP7)
Introduction
• Assessing policies with LCA
Method
Objectives
Case study: 2005-2025 European energy policies
Prospective LCA: technological and economic background
Consequential LCA: direct and indirect consequences
Results
• Comparison of two European energy policies
• Environmental impacts of the economic growth
• Uncertainty analysis
Conclusion
PRESENTATION OUTLINE
PhD Project (2007-2012) = scientific development + case study
Scientific objective
Develop a method based on consequential and prospective LCA to study large changes occurring in several life cycles on the long term
Case study objective
Evaluate environmental impacts of a significant development of wood-bioenergy in Europe (heat and electricity sectors)
METHODOLOGY – PROJECT OBJECTIVES
What policies?
2 European energy policies implemented during 2005-2025 • A baseline policy (business as usual) and a bioenergy policy (large
increase of biomass use for heat and electricity generation)
METHODOLOGY – CASE STUDY
COAL
BIOMASS
COAL BIOMASS
« BIOENERGY »
Policy
2025 2025 2005
« BASELINE »
Policy
COAL
URANIUM
NATURAL GAS
OIL
BIOMASS
WASTE
HYDRO
WIND
OTHER RENEWABLE
IMPORTATIONS Prospective scenarios for electricity generation
(adapted from Mantzos et al. 2004)
Prospective scenarios
Baseline and bioenergy scenarios (PRIMES/POLE)
Describe evolution of European energy sector
Prospective data
Economy forecast (macroeconomic drivers of GTAP)
• Population
• Gross domestic product (GDP)
• Capital
• Skilled and unskilled labor forces
Technological innovation
• European energy sector: literature and experts
• Other economic sectors: extrapolation from total factor productivity (TFP)
METHODOLOGY – PROSPECTIVE LCA
METHODOLOGY – CONSEQUENTIAL PROSPECTIVE LCA
GTAP7
Changes in industrial productions
(physical unit)
International databases
INDIRECT ENVIRONMENTAL
IMPACT
GLOBAL
ENVIRONMENTAL IMPACT
Technology
innovation
Economy
forecast
IMPACT2002+
DIRECT ENVIRONMENTAL
IMPACT
Attributional prospective LCA
Changes in industrial productions
(monetary value)
Large scale
policy
Direct environmental impacts
European heat and electricity sector
Indirect environmental impacts
All other economic sectors (all regions)
Dandres et al. (2011, 2012)
Introduction
• Assessing policies with LCA
Method
• Objectives
• Case study: 2005-2025 European energy policies
• Prospective LCA: technological and economic background
• Consequential LCA: direct and indirect consequences
Results
Comparison of two European energy policies
Environmental impacts of economic growth
Uncertainty analysis
Conclusion
PRESENTATION OUTLINE
Environmental impacts can be expressed
By region and by period (example: ecosystems)
RESULTS – COMPARISON OF TWO EUROPEAN ENERGY POLICIES
Environmental impacts can be expressed
By region and by period (example: ecosystems)
By economic sector and midpoint category (example: ecosystems)
RESULTS – COMPARISON OF TWO EUROPEAN ENERGY POLICIES
Environmental impacts can be expressed
By region and by period (example: ecosystems)
By economic sector and midpoint category (example: ecosystems)
By endpoint category (world scale)
RESULTS – COMPARISON OF TWO EUROPEAN ENERGY POLICIES
Environmental impacts can be expressed
By region and by period (example: ecosystems)
By endpoint category (world scale)
By economic sector and midpoint category (example: ecosystems)
Environmental impacts due to economic growth and benefits/impacts of the bioenergy policy
RESULTS – COMPARISON OF TWO EUROPEAN ENERGY POLICIES
RESULTS – UNCERTAINTY
Many sources of uncertainty
Economic and technological forecasts
GTAP database and parameters
GTAP model
Databases mapping (GTAP ↔ UNDATA ↔ ecoinvent)
Ecoinvent data and IMPACT2002+ method
Uncertainty analysis
27 prospective scenarios (GTAP simulations)
• combination of economic, technological and GTAP parameters changed by: +50%; +0%; -50%
1 what-if scenario: EU-US joint bioenergy policy
Monte-Carlo simulations (LCA uncertainty)
RESULTS – UNCERTAINTY ANALYSIS
GTAP7
Changes in industrial productions
(physical unit)
International databases
INDIRECT ENVIRONMENTAL
IMPACT
GLOBAL ENVIRONMENTAL
IMPACT
28 prospective
scenarios
IMPACT2002+
DIRECT ENVIRONMENTAL
IMPACT
Attributional prospective LCA
Changes in industrial productions
(monetary value)
Large
perturbation
Monte-Carlo
simulations
0
1020
30
40
50
60
70
80
90100
-1.5E+05
-1.0E+05
-5.0E+04
0.0E+00
5.0E+04
1.0E+05
1.5E+05
2.0E+05
2.5E+05
D G A H E P V I F B M Q C N Y R S J O K Z @W L X T U #
% DALY
Scenarios
Human health Certainty (%)
0
1020
30
40
50
60
70
80
90100
-3.0E+11
-2.0E+11
-1.0E+11
0.0E+00
1.0E+11
2.0E+11
3.0E+11
D G A H E P V I F B M Q C N Y R S J O K Z @W L X T U #
% kg CO2 eq.
Scenarios
Climate change Certainty (%)
0
10
20
30
40
50
60
70
80
90
100
-2.0E+11
-1.5E+11
-1.0E+11
-5.0E+10
0.0E+00
5.0E+10
1.0E+11
1.5E+11
D G A H E P V I F B M Q C N Y R S J O K Z @W L X T U #
% PDF.m².year
Scenarios
Ecosystem Certainty (%)
0
10
20
30
40
50
60
70
80
90
100
-1.5E+13
-1.0E+13
-5.0E+12
0.0E+00
5.0E+12
1.0E+13
1.5E+13
D G A H E P V I F B M Q C N Y R S J O K Z @W L X T U #
% MJ Primary
Scenarios
Natural resources Certainty (%)
RESULTS – UNCERTAINTY ANALYSIS
Scenarios with low economic growth
and/or low technological development
Reference
scenario
GHG emissions Human Health
Ecosystems Resources
EU-US
bionergy
policy
Introduction
• Assessing policies with LCA
Method
• Objectives
• Case study: 2005-2025 European energy policies
• Prospective LCA: technological and economic background
• Consequential LCA: direct and indirect consequences
Results
• Comparison of two European energy policies
• Environmental impacts of the economic growth
• Uncertainty analysis
Conclusion
PRESENTATION OUTLINE
CONCLUSION
Macro LCA approach
Consequential prospective LCA made to study large scale policies (with non-marginal variations)
Policy assessment
European bioenergy policy (heat and electricity) is better than the baseline policy for human health, climate change and natural resources but not for ecosystems
Uncertainty
Modeled uncertainty does not really affect the comparison of the two policies
PUBLICATION AND REFERENCES
Assessing non-marginal variations with consequential LCA: Application to
European energy sector (2011). Dandres, T., Gaudreault, C., Tirado-Seco, P., &
Samson, R. Renewable and Sustainable Energy Reviews, 15(6), 3121-3132. doi: DOI:
10.1016/j.rser.2011.04.004
Macroanalysis of the economic and environmental impacts of a 2005-2025
European Union bioenergy policy using the GTAP model and life cycle
assessment (2012). Dandres, T., Gaudreault, C., Tirado-Seco, P., & Samson, R.
Renewable and Sustainable Energy Reviews, 16(2), 1180-1192. doi:
10.1016/j.rser.2011.11.003
Uncertainty management in a macro life cycle assessment of a 2005–2025
European bioenergy policy (2014). Dandres, T., Gaudreault, C., Seco, P. T., &
Samson, R. Renewable and Sustainable Energy Reviews, 36(0), 52-61.
doi:http://dx.doi.org/10.1016/j.rser.2014.04.042
• Hertel, T. W. (1997). Global Trade Analysis - Modeling and Applications: Cambridge
University Press.
• Mantzos, L., Capros, P., & Zeka-Paschou, M. (2004). European Energy and Transports
Scenarios on Key Drivers. In Directorate-General for Energy and Transport (Ed.), (pp. 262).
CYCLE 2016 - 5th international Forum on the life cycle
management of products and services
Implementing sustainability through life cycle thinking
METHODOLOGY – GTAP SETUP (20 ECONOMIC SECTORS)
Grains and crops
Processed
food
Forestry
Wood products
Paper products
Mining and
extraction
Coal
extraction Oil
extraction
Gas
extraction
Petroleum
and coal
products
Gas
manufacture
and
distribution
Electricity
and heat
Textiles and
clothing
Light
manufacturing
Heavy
manufacturing
Water
Utilities and
construction
Transport and
communication
Other services
Livestock
and meat
products