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M. Amann G. Klaassen , R. Mechler, J. Cofala, C. Heyes International Institute for Applied Systems Analysis (IIASA). Modelling synergies and trade-offs between mitigation of GHGs and air pollution with the RAINS model. Linkages between air pollution and climate.
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M. Amann G. Klaassen, R. Mechler, J. Cofala, C. HeyesInternational Institute for Applied Systems Analysis (IIASA) Modelling synergies and trade-offs between mitigation of GHGs and air pollution with the RAINS model
Linkages between air pollution and climate • Air pollutants have radiative forcing: • Ozone controls serve air quality and climate concerns • Aerosols/PM damage human health and influence climate • Environmental impacts of CC and AP are interlinked • Synergies and trade-offs in emission controls
Introducing GHGs into RAINS • Develop cost curves for GHGs (CO2, CH4, N2O, HFC, PFC, SF6) in addition to SO2, NOx, VOC, NH3, PM, (BC, CO) • Country-by-country, medium-term up to 2030 • Include structural changes as means for emission controls • Capture synergies and trade-offs
Data and assumptions • Latest RAINS energy- & cost data • For EU-25, excluding Cyprus and Malta (EU-23) • For 2020
Reference case (REF) • CAFE “without climate measures” energy projections for 2020 • Air pollution control according to recent EU legislation (NEC Directive, LCP Directive, Auto-Oil, etc.)
Scenario 1: Fuel-shift CO2 control in the power sector • Cost-effective fuel shift measures to reduce CO2 emissions in the power sector by 15 % • Subject to exogenous electricity demand
Changes in emissionscompared to REF, EU-23 Fuel-shift Multi-gas Bio-fuel Fuel-shift Multi-gas Bio-fuel 0 0 CO2[Mt] SO2[kt] -50 -50 -100 -100 -150 -150 -200 -200 -250 -250 10 30 0 20 -10 10 -20 0 -30 -40 -10 PM2.5[kt] -50 NOx[kt] -20 -60 -30 -70 -80 -40 Fuel-shift Multi-gas Bio-fuel Fuel-shift Multi-gas Bio-fuel
Differences in premature deaths(cases/year, compared to REF) Fuel-shift Multi-gas Bio-fuel 1000 0 -1000 -2000 -3000 -4000
Scenario 2: Multi-gas Multi-GHG control • In each country, the equivalent CO2 reductions of the Fuel-shift scenario are achieved with CO2and CH4 controls
Fuel shifts applied in the Fuel-shift and Multi-gas scenarios
Changes in emissionscompared to REF, EU-23 Fuel-shift Multi-gas Bio-fuel Fuel-shift Multi-gas Bio-fuel 0 0 CO2[Mt] SO2[kt] -50 -50 -100 -100 -150 -150 CH4 CH4 -200 -200 -250 -250 10 30 0 20 -10 10 -20 0 -30 -40 -10 PM2.5[kt] -50 NOx[kt] -20 -60 -30 -70 -80 -40 Fuel-shift Multi-gas Bio-fuel Fuel-shift Multi-gas Bio-fuel
Differences in premature deaths(cases/year, compared to REF) Fuel-shift Multi-gas Bio-fuel 1000 0 -1000 -2000 -3000 -4000
Scenario 3: Bio-fuels Increased biomass use in households • Shift to biomass use for domestic heating:10% of light fuel oil is replaced by biomass
Changes in emissionscompared to REF, EU-23 CO2[Mt] SO2[kt] CH4 PM2.5[kt] NOx[kt]
Differences in premature deaths(cases/year, compared to REF)
Further work • Finalization of cost curves for other GHGs • Optimization tool: • Separate and joint optimization of emission controls for air pollutants and GHGs: • With constraints (targets) for air quality • With constraints (targets) for radiative forcing/GWP • Simulation of emission trading, emission taxes • Implementation for developing countries
Conclusions (1) • Important synergies and trade-offs exist between air pollution control and GHG mitigation • Integration can maximize synergies and avoid trade-offs • To be truly cost-effective, climate policies have to account for cost savings of reducing traditional air pollutants - both for industrialized and developing countries
Conclusions (2) Multi-pollutant/multi-effect/multi-scale strategies: • offer more flexibility and increased potential for economic efficiency • harness multiple benefits of measures when costs are increasing • connect global long-term climate objectives with concrete local near-term benefits