introduction to the role of tropospheric ozone and arctic climate
TRANSCRIPT
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8/9/2019 Introduction to the Role of Tropospheric Ozone and Arctic Climate
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Introduction to the Role ofTropospheric Ozone and Arctic
Climate
Ellen Baum
May 8, 2008
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There is a significant global role for
tropospheric ozone and climateTemperature impact from CO2 compared to other climate
forcings, relative to 1750
0
0.2
0.4
0.6
0.8
1
1.2
1.4
CO2 Short-lived Climate Forcings
Tem
peratureind
egreesC
Blackcarbon
Troposphericozone
Methane
Carbon
dioxide
Ramana
than,
2008
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Initial Arctic modeling suggests a seasonally, averagedtropospheric ozone-derive temperature increase of 0.28o C
Temperature impact from CO2 compared to other climate forcings,
relative to 1880
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
CO2 Short-lived Climate Forcings
T
emperatureind
egreesC
Blackcarbon
Troposphericozone
Methane
Carbon
dioxide
Calculatedfrom
Quinn,
et.al.,
ACP,
200
8
Note: Different models were used to derive Global(previous slide) and Arctic (this slide) values.
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Tropospheric ozone is formed in the
atmosphere, not emitted Tropospheric ozone is formed in the atmosphere
from precursor pollutants - oxides of nitrogen,volatile organic compounds, carbon monoxide,and methane in the presence of light and thusnot directly emitted like most other air pollutants.
Atmospheric lifetime of ozone is 1 to 2 weeks insummer and 1 to 2 months in winter.
Ozone produced in a polluted region of onecontinent can be transported to anothercontinent.
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How ozone heats the Arctic
The dominant heating pathway is probably transfer of heatproduced by Northern Hemisphere ozone into the Arctic.
Followed by transport of ozone from outside the Arctic To a smaller extent, ozone formation within the Arctic
At the same time, there remain research questions to teaseout the relative contributions and better understandprecursor roles, including
Contribution formed in the Arctic, both from in-Arctic
precursors and precursors transported into the Arctic. Howwill this change with a warmer Arctic?
Importance of lifetimes, locations and seasonality of theshorter-lived precursors
Relevance of looking at specific VOCs
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1950sPresent1980s
NMVOCs + NOx +CH4, CO
Ozone abatement strategies have evolvedalong with understanding of the O
3
issues
Abatement Strategy:
O3 smog recognizedas an URBAN problem:
Los Angeles,Haagen-Smit identifieschemical mechanism
Smog consideredREGIONAL problem;role of biogenicVOCs discovered A GLOBAL perspective:
Cimate impacts and
role of intercontinentaltransport, background
adapted from Fiore, 2002
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Different strategies and need for air
quality versus climate benefits Air quality programs to
reduce ozone levels
focus largely onreducing peak ozonelevels to protect humanhealth and cropproduction.
This favors strategiesreducing localprecursors - NOX and
non-methane VOCs that are majorcontributors to peakozone levels.
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Need lower background for
climate benefits To benefit climate by reducing net warming, a balanced approach must
be taken to reducing all major ozone precursors given their complexatmospheric interactions.
NOxis the most complicated precursor. In the shortrun, it reduces ozone and the radiative forcing fromozone. Over a longer period, however, reductionsincrease the lifetime of methane, and thereforecontribute to warming. Also the nitrate aerosol hasa cooling effect, which reductions remove.
Its unclear where the balance lies between thenegative impacts from increased in methane lifetimeand aerosols, particularly nitrate, and the positive
climate benefits from ozone reductions. Thissuggests that NOx reductions continue to bepursued for air quality benefits, with the recognitionthat climate benefits will need to come largely fromcarbon monoxide and methanereductions
NOx OH
CH4 lifetime
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Climate role of CO, NOx and NMVOC
Shindell, Oslo Workshop, from
IPCC 4AR, 2007
Because COalso uses OH
as anatmospheric
sink, reducingit will makemore OH
available as
methane sink.
from pre-industrial time
Using same calculations, andwithout double counting,
methane is 0.59 W/m2, plusanother 0.20 W/m2 frommethane emissions viaozone.
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Methane is different
Unlike other ozone precursors, methane is not a typical, short-livedozone precursor.
Because methane has a long atmospheric lifetime (8-10 years),emissions become well mixed.
Neither air quality nor climate benefits depend strongly on thelocation of the CH4 emission reductions, implying that the lowestcost emission controls can be targeted.
There are, though, regions where methane effects on O3 areenhanced. These include locations with high NOx emissions (e.g., insouthern California); regions near the down welling branches of theHadley cell, at roughly 30N and 30S (over the Sahara region ofNorth Africa, the Middle East), or regions with active convection
(Caribbean Sea and Gulf Coast of the United States).
Given that most of the ozone-related temperature in the Arcticcomes from global transport, the benefits of these reductionsshould be felt in the Arctic.
MODELED CLIMATE IMPACTS OF 50%
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MODELED CLIMATE IMPACTS OF 50%REDUCTIONS IN ANTHROPOGENIC
EMISSIONSCH4 NOx* VOC NOx
&VOC
CO
MethaneRadiative
Forcing (W/m2)
-0.3 +.06 -.01 +.05 -.02
OzoneRadiative
Forcing (W/m2)
-.07 -.06 -.01 -.07 -.01
Total Forcing
(W/m2)
-.37 0 -.02 -.02 -.03
EPA/OAQPS
Workshop, 2001
* doesnt include aerosolclimate effects
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Near-term climate impacts are critical to Arcticprotection
Given concerns about irreversible arctic climateimpacts that may occur within the next two
decades, should a 20 year GWP, instead of thetypical 100 year equivalency, be used to evaluatearctic impact reduction options?
Using 20 year impacts more than doubles thewarming benefits from methane emissionsreductions and would increase CO reductionwarming benefits by at least 50 percent.
This will also increase the economic value ofsuch emissions, which means much moreexpensive reductions than typically addressed incurrent supply curves are feasible.
Rypdal, 2005
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Where are emissions occurring?
Next four slides.
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CO, emissions, Edgar 2000
refineries, coke ovens, gas
works
Power generation
Industry
Oil production,
Charcoal production
Power generationIndustry
Residential
Transport road
Residential, Commercial
onroad transport
non-road land transport, ie.
rail
Air transport
ShippingIron and Steel
Deforestation
Savanna burning
Agriculture waste burning
Temperate fires
Waste incineration
m an g a u e
grassland f ires
Biofuels
FossilFuels
Agriculture/biomassburning
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NOX, 2000 FROM EDGAR
TROPICAL FOREST FIRES
BUILDING MATERIALS
NON-FERROUS
IRON AND STEEL
OIL PRODUCTIONSHIPPING
AVIATION
NON ROAD TRANSPORT
ROAD TRANSPORTRESIDENTIAL, COMMERICAL
REFINERIES, COKE OVENS,
GAS WORKS
POWER GENERATION
INDUSTRIAL
INDUSTRY
POWER GENERATION
RESIDENTIAL
SAVANNAH AND SHRUBS
FIRES
AG. WASTE BURNING
MID AND HIGH LAT FOREST
FIRES
MID AND HIGH LAT GRASS
FIRES
Biofuels
Fossil Fuels
Indu
-stry
Agriculture/biomassburning
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Non methane VOCS, 2000
REFINERIES,
GAS WORKS,COKE OVENS
INDUSTRYRESIDENTIAL
INDUSTRYPOWER
GENERATION
RESIDENTIALROAD
TRANSPORT
NON-ROADTRANSPORT
AIR
OIL
PROD
GAS
PRODUCTION/
TRANS
IRON &STEEL
SOLVENTS
TROPICAL
FOREST FIRES
SAVANNAH
FIRES
AG WASTE
BURNING
MID LAT
FOREST FIRES
MID LAT
SAVANNAH
FIRES
WASTE
HANDLING
Biofuels
Fossil
Fuels
Industry
Agriculture/biomass
burning
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METHANE, 2000 EDGAR
HUMAN
WASTEWATERDISPOSAL
WASTEWATER
TREATMENT
LANDFILLS
15
MID/HIGHLATITUDE
FOREST FIRESTAG WASTE
BURNING
SAVANNAH AND
SHRUB FIRES
TROPICAL
FOREST FIRES
ANIIMAL WASTE
MANAGEMENT
ENTERIC
FERMENTATION RICE
CULTIVATION
GAS
PRODUCTION
GAS FLARING
OIL PRCESSES
OIL PRODUCTION
COAL
PRODUCTION
COMMERCIAL/
RESIDENTIAL
BIOFUEL
RESIDENTIAL
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Conclusions
Traditional clean air regulation programs
addressing ozone will not benefit climate andthus the Arctic.
Substantial methane and CO reductions areneeded reduce ozone warming of the Arctic.
Research and analytical questions remain,
including whether targeting global hot spots toreduce ozone could have an enhanced benefit inthe Arctic.
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Climate impact, by source category, from
multiple emissions, in 2030, SRES A1B
From Unger, et. al. JGR, 2008
03 ST =ozoneimpact
03 LT = CH4
affects
Black numbera top eachcolumn is totalforcing
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Relative importance of different regions to annual mean
Arctic concentration at surface and atmosphere.
From Shindell, et. al. ACPD, 2008