Scenarios, Emissions Uncertainty, Climate Change, and Air Quality

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Scenarios, Emissions Uncertainty, Climate Change, and Air Quality Steven J. Smith Joint Global Change Research Institute College Park, MD Mid-Atlantic Regional Air Management Association SIP Coordination Workshop & Board Meeting September 27, 2010 ssmith@pnl.gov PNNL-SA-71073

Outline This talk will describe current international efforts to produce scenarios of future greenhouse gas and pollutant emissions, the associated historical estimates, emissions uncertainty, and (briefly) some relationships between climate change and regional air quality. Global Emissions Scenarios Representative Concentration Pathways Multiple Future Scenarios to Address Uncertainty Long-Range Transport Emissions Uncertainty SO2, BC, and CO2 Climate and Local Air Quality Greenhouse Gas Emissions Mitigation Climate Changes Summary

NEW GLOBAL EMISSIONS SCENARIOS THE REPRESENTATIVE CONCENTRATION PATHWAYS (RCPs)

WHAT ARE SCENARIOS Scenarios are images of the future. They are neither predictions nor forecasts. Rather, each scenario is one alternative image of how the future might unfold. A set of scenarios assists in the understanding of possible future developments of complex systems. IPCC Special Report on Emissions Scenarios (2000) Scenarios (in a climate context) can consist of: Demographic, Social, and Economic Characteristics Technology Availability and Performance Emissions and Land-Use Changes Atmospheric Composition and Air Pollution Physical Climate Changes Climate Impacts RCPs

WHY NEW SCENARIOS The current set of scenarios (SRES) used for coordinated, international analysis of climate change were constructed in the late 1990s. New scenarios are needed because: Starting data for the scenarios is outdated The models that produce the scenarios have been improved New scenario data are needed for analysis There have been some major changes to the process: The research community will produce new scenarios, not the IPCC. A full range of scenarios, climate policy and non-policy, will be included. This set of scenarios were developed for analysis of climate change They span a range of future radiative forcing. All scenarios assume central assumptions for future emissions controls While pollutant emissions are included, they do not span the full range of potential emissions, particularly on the upper end.

THE RCP SCENARIOS CO 2 Emissions and Total Radiative Forcing Graphs: Detlef van Vuuren 120 10 100 MES-A2R 8.5 9 MES-A2R 8.5 8 Emissions (GtCO2) 80 60 40 20 AIM 6.0 MiniCAM 4.5 Radiative Forcing (W/m2) 7 6 5 4 3 0 IMAGE 2.9 IMAGE 2.6 2 1-20 0 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 AIM 6.0 MiniCAM 4.5 IMAGE 2.9 IMAGE 2.6 Future emissions and potential emissions limits due to climate policy are uncertain. Four scenarios were selected to span the potential range.

RCP Emissions While the RCP scenarios are defined by radiative forcing, a full suite of GHG and pollutant emissions are included. The RCPs provide: regional emissions of GHGs and pollutant substances, globally gridded emissions (at 0.5 ) of short-lived compounds, and GHG concentration pathways. GHG Emissions: CO 2, CH 4, N 2 O, Fluorinated Gases Pollutant Emissions: NO x, CO, NMVOCs, SO 2, BC, OC, NH 3 Regional and gridded emissions are provided in 12 source sectors in order to allow for later spatial/temporal desegregation and NMVOC speciation. Air Transportation International Shipping Ground transportation Electric power plants, energy conversion, extraction and distribution Solvents Industry (combustion and process emissions) Buildings (Residential and Commercial) Ag. waste burning on fields Agriculture (agricultural soils, other agriculture) Grassland burning Waste (landfills, waste water, non-energy incineration) Forest burning (Deforestation & Forest Fires)

BC Emissions: 1850-2100 Forest/grassland Burning, Domestic, & Industry sectors dominate. BC from these sectors is more difficult to eliminate Emissions decline over the 21st century, but not as fast as SO 2. Transportation sector contribution has become significant. Emissions also decrease relative to ref under a climate policy Some of this is reduced deforestation, which has limited climate impact from aerosols. Historical values (Bond et al 2009; & others) plus GCAM RCP4.5 (Thomson et al 2010)

BC Emissions: 1850-2100 Emissions peak with industrialization and then decline Declines due to emission controls and broader shifts in technology/activity Because of sectoral concentration, fairly rapid reductions are possible

Future Pollutant Emissions Scenarios Scenarios from multiple groups indicate uncertainty in year 2000 emissions and uncertainty in the future emissions path SO2 Emissions ultimately decline in all scenarios Newer scenarios have Lower current-day emissions Lower future emissions (faster reductions in China than previous projections) Also low emissions (in RCPs) as co-benefit of climate policy Graph: S Smith (HTAP 2010 Assessment Chapter A3)

Future Pollutant Emissions Scenarios Emissions increase in the SRES scenarios due to lack of emission controls NOx emissions decline in these scenarios (but not as quickly as SO2) Expanded use of combustion technologies, particularly transport and off-road uses, partially counters increased emission controls Graph: S Smith (HTAP 2010 Assessment Chapter A3)

Intercontinental transport is becoming a significant factor in pollution control Long-range transport of pollutants is impacting local and regional pollutant levels, particularly in the Northern Hemisphere. An assessment of current scientific understanding of these effects is underway: Hemispheric Transport of Air Pollution 2010 (Assessment) A significant fraction of local ozone concentrations can be due to transport from outside the region. Long-range impacts on particulate concentrations are smaller due to shorter lifetime of precursor compounds. The impact of long-range transport is projected to increase as emissions from Asia increase in the future.

Emissions And Uncertainty

Emissions Uncertainty: Carbon Dioxide Countries report emissions and uncertainty to UNFCCC Source: Simon Eggleston IPCC TSU

Emissions Uncertainty: Carbon Dioxide Not clear if uncertainty is consistently estimated Source: Simon Eggleston IPCC TSU

Emissions Uncertainty: SO 2 Uncertainty in US SO 2 emissions is relatively low Uncertainty from independent sources cancel Major emissions sources are measured Uncertainty was larger In the past Uncertainty in China SO 2 emissions is fairly large Larger uncertainty in driving forces, sulfur content, and ash retention. Most emissions from coal combustion, less cancelation in uncertainty across sectors. Source: Smith et al. (2010)

Emissions Uncertainty: Black Carbon Uncertainty in BC emissions much larger Due to incomplete combustion, inherently more uncertain BC fraction of particulate also uncertain Uncertainty in major emissions sectors (e.g. cookstoves) potentially correlated Emissions from super-emitters important and uncertain Source: Bond et al. (2007)

Emissions Uncertainty: UK Inversion to match observations Atmospheric measurements + models can potentially be used to validate emissions inventories Source: A Manning (2010)

Emissions Uncertainty: NOx in Europe Atmospheric & satellite data + models (red) can also potentially be used to validate emissions inventories (blue & green) Source: Konovalov et al. (2008)

Air Pollution co-benefits of Climate Policy Co-benefits from climate policy won t solve air quality problems, but this would help. Substantial reductions in carbon dioxide emissions result in a cobenefit of reductions in pollutant emissions Reductions in fossil fuel use reduce emissions of criteria air pollutants Reductions in CH 4 generally reduce tropospheric ozone

Summary Uncertainty has not been systematically included in inventories Much of the analysis involves expert judgment of uncertainties. Changes in inventory values over time indicate that uncertainty is not trivial. Methodological and other changes result in non-random errors. On the global/national level, there may be more work on greenhouse gases rather than criteria pollutant emissions. Reporting and assumptions likely not consistent On-going work on validation of emission inventories Inverse modeling can provide an independent check. Can be useful also for large point sources (e.g. VOCs). Combination of surface and satellite observations shows promise. Climate change and climate policy will impact pollution control Co-benefits of GHG emissions reduction would occur. Climate changes will alter background conditions (chemistry, weather events)