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Markus Amann
Air Pollution and Climate
Some thoughts about the linkages between
air pollution and climate,
including findings of the NASA workshop on
“Air Pollution as a Radiative Forcing”
(Hawaii, April 29-May 4, 2002)
Air Pollution and Climate
1. Air pollutants have a radiative forcing too
2. Air pollutants and greenhouse gases have
common sources
3. Linking air pollution and climate change
I. Air Pollutants have a radiative forcing
GHGs and air pollutants
with radiative forcing
• Kyoto GHGs:
– O3, CH4, N2O, HFC, PFC, SF6
• Air pollutants with direct radiative forcing:
– O3, SO2, aerosols (black and organic carbon, PM2.5)
• Air pollutants with indirect effects on radiative
forcing:
– All gases that influence OH (NOx, CO, VOC, H2O, etc.),
– O3 precursors (NOx, VOC, CO),
– Aerosol precursors (primary and secondary, including NH3)
Radiative forcing 1750-1900
Source: IPCC TAR WG1
Critical role of OH
Hydroxyl radical (OH) steers lifetime of CH4, HFCs, O3
OH determined by:
– Nitrogen oxides (NOx)
– Carbon monoxide (CO)
– Volatile organic compounds (VOCs)
– Methane (CH4)
– etc., including stratospheric H2O
NOx and climate change
Increase in NOx leads to
• decreased lifetime of CH4 and HFCs (via OH):
 radiative forcing
• increase in O3:
 radiative forcing
• increased N deposition  fertilization  CO2 uptake:
 radiative forcing
Net effect not yet clear, but significant impacts on
radiative forcing expected for 2100 (IPCC TAR, 2001)
Regional climate effects of aerosols
Present GCMs indicate that aerosols (may) influence
local climate
• Sulfates:
– Cooling effect
– Changes in precipitation observed in China related to
increase in China’s SO2?
– Did European SO2 affect precipitation in Africa (Sahel)?
• Black carbon:
– Warming effect
– Issue for bio-fuels
• Organic carbon:
– Cooling effect
– Net effect of PM from different sources?
Next GCMs will include air chemistry
Source: IPCC TAR WG1
II. Air Pollutants and Greenhouse Gases
have common sources
(1) Ancillary benefits of GHG reductions
Structural changes aimed at GHG control have ancillary
benefits for air pollution:
• SO2:
– reduced acidification (vegetation and fauna),
– health impacts
• O3:
– agricultural/vegetation damage,
– health impacts
• Aerosols (from SO2, NOx, primary PM, VOC, NH3):
– strong health impacts (loss in life expectancy),
– reduced solar radiation leads to less agricultural production
Ancillary benefits are local and short/medium term!
(2) Controlling common sources
offers cost-saving potential
Costs for meeting EU air quality targets (bill. €/yr):
(Syri et al., Energy Policy 2001)
Pre-Kyoto Kyoto, no trade Kyoto, full trade
66.1 58.7 (-11%) 61.0 (-8%)
(3) Trade-offs in emission controls
between air pollutants and GHGs
Effects of NH3 control on N2O/CH4:
• With maximum NH3 reductions in agriculture (-36%)
– N2O increases by +15% (+11 to +25%)
– CH4 decreases by -2% (-1 to -3%)
(Brink & Klimont, Atm.Env. 2001)
(4) Inclusion of air pollutants may
alter net radiative forcing
Including air pollution in calculations might alter
net radiative forcing and thus
modify policy recommendations, e.g.:
• Diesel:
Black carbon could compensate fuel saving effect in terms
of GHGs (M. Jacobsen, 2001)
• Bio-fuels for cooking:
Fossil LPG might cause less radiative forcing than bio-
fuels
(due to incomplete combustion products, e.g., VOC, CO,
BC, OC, etc.) (K. Smith, 2001)
(5) Multiple benefits of methane control
1. Ozone:
• CH4 is another precursor of ground-level O3,
contributes to hemispheric O3 background:
Could (hemispheric) control of methane substitute for
further NOx+VOC reductions?
2. Radiative forcing:
• CH4 emission cuts reduce radiative forcing directly
+ indirectly via shorter lifetime of CH4
• CH4 is Kyoto GHG
• Less radiative forcing via less tropospheric ozone
Methane reductions are possible
• SRES projects CH4 to
increase
• Technical control potential
about 50% (in EU)
• Control measures:
– Biogas
– Controlled landfills
– Reduced losses in gas
distribution
– Recovery in oil and gas
production
Cheap, often with negative
costs and multiple benefits
0
100
200
300
400
500
600
700
800
900
1000
1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100
SRESA2 SRESB1 SRESB2
III. Linking air pollution and climate change
Linking air pollution and climate change
• Link between air pollution and radiative forcing
did not receive full attention from science and
policy
• IPCC did not focus on air pollution scenarios
– SRES NOx, CO, VOC, BC projections not in line with SRES
storylines. Proposed emission increases would lead to
catastrophic air quality
– Recent legislation in Europe, Asia, US suggests significant
and sustainable reductions
NOx emissions in IPCC-SRES scenarios
0
50
100
150
200
250
300
350
400
1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100
Tg
NO
x
/yr
North America Europe FSU China East Asia
South Asia SRES A2 SRES B1 SRES B2
VOC emissions in IPCC-SRES scenarios
0
50
100
150
200
250
300
350
1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100
Tg
VOC/yr
North America Europe FSU China East Asia
South Asia SRES A2 SRES B1 SRES B2
CO emissions in IPCC-SRES scenarios
0
500
1000
1500
2000
2500
1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100
Tg
CO/yr
North America Europe FSU China East Asia
South Asia SRES A2 SRES B1 SRES B2
SO2 emissions in IPCC-SRES scenarios
0
50
100
150
200
250
1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100
Tg
SO
2
/yr
North America Europe FSU China East Asia
South Asia SRES A2 SRES B1 SRES B2
SRES scenarios: OH and lifetime of CH4
Source: IPCC TAR, 2001
Scope for
cost-effective multi-pollutant strategies
Climate impacts are long-term. Limited response to
emission changes expected for next 50 years.
• Ancillary benefits offer short/medium-term gains
in non-climate fields
• Air pollutants are short-lived GHGs.
Can control of radiative effects of air pollutants
offer faster response of climate system?
• Cost-savings of multi-pollutant approaches?
SO2 NOx NH3 VOC
Primary
PM+BC
Acidification   
Eutrophication  
Ground-level
ozone
 
Health impacts 
via sec. aerosols    
CH4
CO2+
GHGs

Radiative forcing  
via aerosols     
via OH   
A multi-pollutant/multi-effect problem
extended towards radiative forcing
Linking air pollution and climate
Not to remove need for CO2 control,
but to moderate warming
and to harvest co-benefits

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tfiam27-air_pollution_and_climate.ppt

  • 1. Markus Amann Air Pollution and Climate Some thoughts about the linkages between air pollution and climate, including findings of the NASA workshop on “Air Pollution as a Radiative Forcing” (Hawaii, April 29-May 4, 2002)
  • 2. Air Pollution and Climate 1. Air pollutants have a radiative forcing too 2. Air pollutants and greenhouse gases have common sources 3. Linking air pollution and climate change
  • 3. I. Air Pollutants have a radiative forcing
  • 4. GHGs and air pollutants with radiative forcing • Kyoto GHGs: – O3, CH4, N2O, HFC, PFC, SF6 • Air pollutants with direct radiative forcing: – O3, SO2, aerosols (black and organic carbon, PM2.5) • Air pollutants with indirect effects on radiative forcing: – All gases that influence OH (NOx, CO, VOC, H2O, etc.), – O3 precursors (NOx, VOC, CO), – Aerosol precursors (primary and secondary, including NH3)
  • 6. Critical role of OH Hydroxyl radical (OH) steers lifetime of CH4, HFCs, O3 OH determined by: – Nitrogen oxides (NOx) – Carbon monoxide (CO) – Volatile organic compounds (VOCs) – Methane (CH4) – etc., including stratospheric H2O
  • 7. NOx and climate change Increase in NOx leads to • decreased lifetime of CH4 and HFCs (via OH):  radiative forcing • increase in O3:  radiative forcing • increased N deposition  fertilization  CO2 uptake:  radiative forcing Net effect not yet clear, but significant impacts on radiative forcing expected for 2100 (IPCC TAR, 2001)
  • 8. Regional climate effects of aerosols Present GCMs indicate that aerosols (may) influence local climate • Sulfates: – Cooling effect – Changes in precipitation observed in China related to increase in China’s SO2? – Did European SO2 affect precipitation in Africa (Sahel)? • Black carbon: – Warming effect – Issue for bio-fuels • Organic carbon: – Cooling effect – Net effect of PM from different sources?
  • 9. Next GCMs will include air chemistry Source: IPCC TAR WG1
  • 10. II. Air Pollutants and Greenhouse Gases have common sources
  • 11. (1) Ancillary benefits of GHG reductions Structural changes aimed at GHG control have ancillary benefits for air pollution: • SO2: – reduced acidification (vegetation and fauna), – health impacts • O3: – agricultural/vegetation damage, – health impacts • Aerosols (from SO2, NOx, primary PM, VOC, NH3): – strong health impacts (loss in life expectancy), – reduced solar radiation leads to less agricultural production Ancillary benefits are local and short/medium term!
  • 12. (2) Controlling common sources offers cost-saving potential Costs for meeting EU air quality targets (bill. €/yr): (Syri et al., Energy Policy 2001) Pre-Kyoto Kyoto, no trade Kyoto, full trade 66.1 58.7 (-11%) 61.0 (-8%)
  • 13. (3) Trade-offs in emission controls between air pollutants and GHGs Effects of NH3 control on N2O/CH4: • With maximum NH3 reductions in agriculture (-36%) – N2O increases by +15% (+11 to +25%) – CH4 decreases by -2% (-1 to -3%) (Brink & Klimont, Atm.Env. 2001)
  • 14. (4) Inclusion of air pollutants may alter net radiative forcing Including air pollution in calculations might alter net radiative forcing and thus modify policy recommendations, e.g.: • Diesel: Black carbon could compensate fuel saving effect in terms of GHGs (M. Jacobsen, 2001) • Bio-fuels for cooking: Fossil LPG might cause less radiative forcing than bio- fuels (due to incomplete combustion products, e.g., VOC, CO, BC, OC, etc.) (K. Smith, 2001)
  • 15. (5) Multiple benefits of methane control 1. Ozone: • CH4 is another precursor of ground-level O3, contributes to hemispheric O3 background: Could (hemispheric) control of methane substitute for further NOx+VOC reductions? 2. Radiative forcing: • CH4 emission cuts reduce radiative forcing directly + indirectly via shorter lifetime of CH4 • CH4 is Kyoto GHG • Less radiative forcing via less tropospheric ozone
  • 16. Methane reductions are possible • SRES projects CH4 to increase • Technical control potential about 50% (in EU) • Control measures: – Biogas – Controlled landfills – Reduced losses in gas distribution – Recovery in oil and gas production Cheap, often with negative costs and multiple benefits 0 100 200 300 400 500 600 700 800 900 1000 1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 SRESA2 SRESB1 SRESB2
  • 17. III. Linking air pollution and climate change
  • 18. Linking air pollution and climate change • Link between air pollution and radiative forcing did not receive full attention from science and policy • IPCC did not focus on air pollution scenarios – SRES NOx, CO, VOC, BC projections not in line with SRES storylines. Proposed emission increases would lead to catastrophic air quality – Recent legislation in Europe, Asia, US suggests significant and sustainable reductions
  • 19. NOx emissions in IPCC-SRES scenarios 0 50 100 150 200 250 300 350 400 1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 Tg NO x /yr North America Europe FSU China East Asia South Asia SRES A2 SRES B1 SRES B2
  • 20. VOC emissions in IPCC-SRES scenarios 0 50 100 150 200 250 300 350 1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 Tg VOC/yr North America Europe FSU China East Asia South Asia SRES A2 SRES B1 SRES B2
  • 21. CO emissions in IPCC-SRES scenarios 0 500 1000 1500 2000 2500 1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 Tg CO/yr North America Europe FSU China East Asia South Asia SRES A2 SRES B1 SRES B2
  • 22. SO2 emissions in IPCC-SRES scenarios 0 50 100 150 200 250 1980 1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100 Tg SO 2 /yr North America Europe FSU China East Asia South Asia SRES A2 SRES B1 SRES B2
  • 23. SRES scenarios: OH and lifetime of CH4 Source: IPCC TAR, 2001
  • 24. Scope for cost-effective multi-pollutant strategies Climate impacts are long-term. Limited response to emission changes expected for next 50 years. • Ancillary benefits offer short/medium-term gains in non-climate fields • Air pollutants are short-lived GHGs. Can control of radiative effects of air pollutants offer faster response of climate system? • Cost-savings of multi-pollutant approaches?
  • 25. SO2 NOx NH3 VOC Primary PM+BC Acidification    Eutrophication   Ground-level ozone   Health impacts  via sec. aerosols     CH4 CO2+ GHGs  Radiative forcing   via aerosols      via OH    A multi-pollutant/multi-effect problem extended towards radiative forcing
  • 26. Linking air pollution and climate Not to remove need for CO2 control, but to moderate warming and to harvest co-benefits