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GEOS-Chem Users Meeting April 12, 2007
U.S. INFLUENCE ON TROPOSPHERIC OZONE AND THE EFFECTS OF RECENT EMISSION REDUCTIONS
Modeling: Rynda Hudman*, Lee Murray, Daniel Jacob, Solene Turquety, Dylan Millet, Shiliang Wu
NEI 99 Emissions: Alice Gilliland
ICARTT Observations: Melody Avery, Tim Bertram, Ron Cohen, Jack Dibb, Frank Flocke, Allen Goldstein, John Holloway, Andy Neuman, Tom Ryerson, Glen Sachse, Hanwant Singh, P J Wooldridge
ICA
RT
T F
light
Tra
cks
North America Europe
NOx stationary sources 50%
Anthropogenic CO 60%
4
2
6
8
Alt (km)
10
O3 (ppbv)
BB NA FF Lightning
NOx/flash4X larger than previously assumed!
Export well constrained
effects on O3 & OPE Northern Hemisphere Burden
ICARTT CONSTRAINTS ON SUMMERTIME EMISSIONS & HEMISPHERIC OZONE
May-August 2004 NA Fire Inventory
[Turquety et. al, 2007]
EPA National Emissions Inventory 1999 v1 (w/ modifications to VOCs) Power plant and Industry NOx 50%Anthropogenic CO 60%
GEOS-CHEM SIMULATION(v7.02.04 w/ modifications below)
NOx Lightning EmissionsLightning X4 over U.S.
& distributed to tropopause [Price and Rind, 1992]
Modifications from ICARTT constraints in blue (improved)
Flash counts (flashes/km2/s)
CO emissions
NOx
emission
GEOS-CHEM VS. ICARTT Mean comparison along the flight tracks
Large UT NOx bias
BL bias in CO and NOx
Ozone FT bias 5-10 ppbv
Measurements (WP-3D, DC-8): CO (J. Holloway, G. Sachse), NOx (T. Ryerson, R. Cohen, W. Brune), PAN (F. Flocke, H. Singh), HNO3 (A. Neuman, J. Dibb), ozone (T. Ryerson, M. Avery)
Observed Simulated Improved Simulation
DC-8 Midwest Median NO2
Median Model / Observed NOx (0-2 km)
[ratio]
Large overestimate powerplant/industry dominated Midwest and in the South
50% reduction in power and industry source as determined by Frost et al., [2006] improves boundary layer NO2 simulation
ICARTT OBSERVATIONS CONFIRM LARGE DECREASE SINCE 1999 IN INDUSTRY/POWER SOURCE
Measurements (WP-3D, DC-8): T. Ryerson (NO2), Ron Cohen/Tim Bertram (NO2)
NO2 (ppbv)
OZONE REDUCTIONS RESULTING FROM DECREASE IN NOx EMISSIONS
Can we see changes in OPE due NOx emission reductions in dO3/dCO in U.S. outflow?
Requires good estimate of CO source…..
ECO
ENOOPE
dCO
dO x3
Regional differences in ozone, can be explained by OPE:
OPE
Midwest: 2.5-3.5
Southeast: 4-5.5
BOTH AIRCRAFT AND SURFACE DATA SUGGEST NEI 99 CO EMISSIONS ARE 2.5 TIMES TOO HIGH
Air
craf
t (0
-1.5
km
)C
heb
og
ue
Po
int
(su
rfac
e)
OBSERVED SIMULATED (NEI99) SIMULATED (anthro CO reduced by 60%)
Measurments:
J. Holloway, G. Sachse
Measurments: A. Goldstein/ Dylan Millet
Hudman et al. [2007b]
SCATTERPLOT OF SIMULATED TO OBSERVED CO
Parrish [2006] finds on-road source overestimated by 50% in NEI 99 (~33% reduction in NEI source due to this bias)
CO decrease trend 3.7% yr-1 (1987-2002), ( 12% reduction in anthropogenic CO source since 1999 due to trend)
From these estimates 2004 emissions 45% lower than NEI 99 (Our estimate 60%)
ANTHROPOGENIC CO SOURCE IN THE UNITED STATES IN SUMMER IS NOW LOWER THAN BIOGENIC SOURCE
CO ANTHROPOGENIC EMISSION (11.5, 4.6)CO SOURCE FROM ANTHROPOGENIC VOC OXIDATION (1.8, 1.8)CO SOURCE FROM ISOPRENE OXIDATION (6.7, 6.7)CO SOURCE FROM OTHER BIOGENIC OXIDATION (2.4, 2.4)
NEI 99 NEI 99 with 60% reduction in CO
51%
10%
30%
8%
<1%
CO SOURCE FROM OTHER BIOMASS BURNING OVER CONTINENTAL U.S.(0.16, 0.16) Note: Fires in Canada and Alaska ~19 Tg CO
SOURCE TYPE (Tg CO)
30%
11%43%
15%
1%
OZONE-CO CORRELATIONS SHOW DECADAL INCREASE
ObservationsSlope = 0.47 +/- 0.01R2 = 0.54SimulationSlope = 0.36 +/- 0.02R2 = 0.21
ObservationsSlope = 0.41 +/- 0.03R2 = 0.47SimulationSlope = 0.34 +/- 0.03R2 = 0.17
50 100 150 200 250 300 50 100 150 200 250 3000
20
40
60
80
100
120
140
CO [ppbv] CO [ppbv]
O3 [
pp
bv]
Chebogue PointAircraft (0 - 1.5 km)
Obs during the early 90s show dO3/dCO ~ 0.3 – 0.4 [Chin et al., 1994; Parrish et al., 1998].
Change consistent with decadal changes in emissions and OPE over the Northeaster United States
Overestimate of tropical background
WINDS FROM W-SE
ALL WIND DIRECTIONS
Aircraft (0-1.5 km, 11-5pm LT) Chebogue Point
SUMMERTIME NORTH AMERICAN OZONE ENHANCEMENTS
Biomass Lightning Anthropogenic
Simulated Observed All
North American
Source
NOx
Emission (Tg N)
Ozone Production Efficiency
Hemispheric ozone
enhancement (Tg, %)
Lightning 0.28 32.5 9.1 (5.1%)
Biomass burning
0.32 17.55.6 (3.1%)
Fossil fuel 0.72 15 10.9 (6.1 %)
All 1.32 19 25.6 (14.3 %)
NA Enhancement to Hemispheric Ozone
ICARTT DC-8~ Equal contributions for lightning and anthropogenic emissions in free troposphere and to NH burden
OBSERVED dO3/dCO INCREASE OVER THE PAST DECADE CONSISTENT WITH UNDERSTANDING OF OPE AND SOURCES
dO3/dCO OPE (dO3/dNOx) * NOx/CO source ratio (dNOx/dCO)
Consider NE U.S.,
July 1 – August 15, 2004 (With ICARTT Constraints)
Anthro = 1.2 Tg CO, 0.10 Tg N Biogenic = 0.87 Tg CO
July 1 – August 1994
4.9% anthro decrease/year in urban air [Parrish, 2006] Total CO 26% higher
22% stationary NOx reduction [Hudman et al., 2007] Anthro NOx 15% higher
OPE lower by ~9%
NOx/CO source ratio lower by ~19%
~28% increase in dO3/dCO expected 0.3-0.4 (90s) 0.4-0.5 (present)
Multiply dO3/dCO * ECO 1.5 Gmol ozone d-1
(Ozone flux consistent with 1990s estimates)
Fuel - based inventory + CO & CO/NOx ambient trends inferred emissions
[Parrish et al., 2006]
EVALUATION OF EPA NEI99 ON-ROAD TRANSPORT EMISSIONS
On-road emission estimates
*Note: 2004 trends report is same as NEI99
On-Road transport inventories (1995)
On-road CO emissions too high by 50%
UNITED STATES NOx REGULATIONS AIMED AT REDUCING OZONE SMOG
• 1998 - The EPA NOx SIP Call mandated that 22 eastern states & DC revise their SIPs to meet NOx emissions reductions by 2003 (Phase 1) and further reduction by 2007 (Phase 2).
• 2003 - All 22 states reduced NOx point source emissions to their Phase 1 levels.
• 2004 - Frost et al., [2006] determined that as a result emission rates of power plant NOx have decreased approximately 50% between 1999 and 2003.
• 2005 - NOx levels in the U.S. will likely continue to drop. In March 2005, the EPA issued the Clean Air Interstate Rule, which will, permanently reduce NOx emissions to 60% of 2003 levels in 25 eastern states, and the DC.
1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008
50% NOx PP reduction
Frost et al., [2006]NOx SIP
SIP Phase 1
SIP Phase 2
CAIR
Frost et al., [2006]
0.75 1.50 2.25
CH2O (ppbv)
298
168
157
164
166
156
119
138
173
114
0
54
0.0 0.5 1.0 1.5
Propane (ppbv)
2
4
6
8
10
12
Alti
tude
(km
)
257
142
154
184
210
209
155
172
204
133
0
77
ObservationsGEOS-Chem
CO OVERESTIMATE IS NOT CAUSED BY INSUFFICIENT VENTILATION OR BIOGENIC SOURCE
Boundary layer ventilation is constrained by vertical profile of short-lived VOCs
Biogenic VOCs are well-constrained by successful simulation of formaldehyde
Propane: E. Atlas CH2O: Alan Fried
[Provided by D. Millet]
CHEBOGUE POINT CO TIMESERIESBias still exists during outflow events
7/1 8/1
UT NOx OBSERVATIONS POINT TO A LARGER THAN EXPECTED LIGHTNING NOx SOURCE
Hudman et al. [2007a]
GEOS-Chem (Lightning X4)Observed
NOx (8-12 km)
[ppb
v]
DOESN’T APPEAR TO BE A NOx LIFETIME ISSUE
NO: W. Brune, NO2: R. Cohen/T Bertram
Lightning parameterization (flashes/km2/s):
Land : ~CTH4.9 , Ocean: ~CTH1.73
CTH= Cloud Top Height
Price and Rind [1992]
GEOS-Chem Vertical Distribution
GEOS-Chem
NLDN
[Fla
shes
km
2 s]
FLASH RATES WELL SIMULATED POINTING TO A LARGER YIELD/FLASH AT NORTHERN MIDLATITUDES
Flash Comparison
Pickering et al., [1998]
[Huntrieser et al., 2005]
PEAK CURRENT AS A FUNCTION OF LATITUDE
[Ken Pickering]
NO PRODUCTION RATE CALCULATED FROMR RECENT CAMPAIGNS
Standard GEOS-Chem mean flash rate was 125 mol flash-1 (Improved X4 500 mol flash-1)
OZONE COMPARISON INTEX-NA SOUTHEAST U.S. Increase in lightning yield X4 to 500 mol/flash has ~10 ppbv effect on
ozone
NO2O3
Hudman et al. [2007a]…suggests great sensitivity of ozone to climate change
Observed Simulated Improved Simulation
2004 was not an anomalous lightning year
Hudman et al. [2007b]
NORTH AMERICAN ENHANCEMENT TO HEMISPHERIC OZONE