transport of asian ozone pollution into surface air over the western u.s. in spring
DESCRIPTION
Transport of Asian ozone pollution into surface air over the western U.S. in spring. Meiyun Lin. HTAP, NASA JPL, 2/2/2012. - PowerPoint PPT PresentationTRANSCRIPT
Geophysical Fluid Dynamics Laboratory
Transport of Asian ozone pollution into surface air over the western U.S. in spring
Meiyun LinMeiyun Lin
Lin, M., A. M. Fiore, L. W. Horowitz, O. R. Cooper, V. Naik, J. S. Holloway, B. J. Johnson, A. M. Middlebrook, S. J. Oltmans, I. B. Pollack, T. B. Ryerson, J. Warner, C. Wiedinmyer, J. Wilson, and B. Wyman (2012),J. Geophys. Res., doi:10.1029/2011JD016961, in press.
HTAP, NASA JPL, 2/2/2012
Process-oriented analysis of multi-Process-oriented analysis of multi-platform observations with a new, global platform observations with a new, global high-resolution chemistry-climate modelhigh-resolution chemistry-climate model
Sondes
AQS/CASTNet
GFDL AM3 Problems: 1) Coinciding ozone maxima of stratospheric and anthropogenic origin [e.g. Stohl and Trickl 1999; Cooper et al 2004; Ambrose et al., 2011]
2) Limitations of tropospheric CTMs in capturing observed dynamic variability in ozonesondes [e.g. Jaegle et al., 2003; Liang et al., 2007; Jonson et al., 2010]
3) Prior multi-model evaluations on campaign /monthly mean basis [e.g. Dentener et al 2006; Stevenson et al., 2006; Fiore et al., 2009]
Our Approach:1) Global high-res (50 km) with fully coupled strat+trop chemistry [Donner et al., 2011]; Nudged to GFS
2) Analyze transport events on daily basis, leveraging intensive measurements from CalNex 2010
Maximum in the western U.S. (4-7 ppb)
Large-scale conclusions independent of resolution
High-res spatially refines estimates: 1-2 ppbv (~20%) higher over the high-altitude areas
Diagnosed as difference between pairs of simulations: Base – Zero Asian anthrop.
Mean Asian impacts on U.S. surface O3 in spring: high-resolution model spatially refines estimates
Daily max 8-h average O3 in surface air, May-June 2010 average
C48 (~200 km)
C180 (~50 km)
How good is the model?
Emissions: Asian INTEX-B scaled to 2010, US NEI2005, ACCMIP elsewhere
The GFDL AM3 model explains 50-90% of observed daily O3 variability in Point Reyes sonde
Cooper et al., 2011
Lin, M et al., in prep, 2012
CalNex sondes
All sites: 30-90%
SondeAM3/C180 (~50 km)AM3/C48 (~200 km)
< 3 km
3-6 km
6-9 km
Source attribution?
Trans-Pacific transport of Asian pollution plumes to WUS often coincides with ozone injected from stratosphere
Observed GFDL AM3 Zero Asian emissions O3-strat
~50% from O3-strat
20-30% from Asia
Ozone (ppbv) Ozone (ppbv)
Improved stratospheric ozone tracer (O3-strat), w/ tropopause diagnosed by the e90 tracer of Prather et al. [2010]
How much does Asian pollution contribute to surface high-O3 events?
Careful attribution of O3 sources in continental inflow Necessitate a model representing dynamic variability of UT/LS O3
and STE
Observed GFDL AM3 Zero Asian emissions O3-strat
Full chemistry AM3 captures the interleaving and mixing of Asian pollution and stratospheric air
Primarily strat
Obs (CASTNet/AQS) AM3/C180 total ozone AM3/C180 Asian ozone
Asian pollution contribution to high surface O3 events,confounding to attain tighter standard in WUS
June 212010
June 222010
Tighter standard… harder to attain with domestic control
Max daily 8-h average
Transport of Asian pollution on the isentropic surfacesto the lower troposphere over the LA Basin
Previously identified isentropic transport mechanism [Brown-Steiner and Hess, 2011]
Asian enhancements to trop column O3 on May 8, 2010
Vertical cross-section of Asian O3 along California coast
θ[K]
[ppb]
Asian ozone available to be intercepted by the elevated terrain or entrained into the daytime boundary layer (~1-4 km in depth)
The Asian enhancement increases for total O3 in the 70-80 ppb range over Southern California, Arizona
25th
Lessons learned:
1) Conduct process-oriented analysis of factors contributing to model differences2) High-resolution model analysis of continental inflow processes 3) Evaluate models with high temporal frequency observations4) A common emission inventory across models
Recommendations for TF HTAP:
Ongoing work relevant for TF HTAP:
1) Mixing of pollution and stratospheric air in continental inflow Necessitate models representing key features for accurate attribution 2) Asian emissions can contribute ~8-15 ppb to observed high-O3 events
Implications for attaining more stringent standards 3) Potential to forecast intercontinental O3 transport events from space Require further work to be quantitative
1) Stratospheric contribution to high surface O3 events in WUS (Poster)
2) Historical variability, trends, and source attribution for 1980-2010… Stratospheric exchange, fires, emissions, and climate (e.g. ENSO)
Extra slides
The new GFDL CM3/AM3 chemistry-climate model
AM3 cubed sphere grid C48 (~200x200 km2) C180 (~50x50 km2)M. Lin, et al., JGR, 2012
Donner et al., Golaz et al., Griffies et al., J. Climate, 2011
Naik et al., in prep
48 vertical levels Surface 86 km
Atmospheric Chemistry 86 km
0 km
Atmospheric Chemistry 86 km
0 km
Atmospheric Dynamics & PhysicsRadiation, Convection (includes wet
deposition of tropospheric species), Clouds, Vertical diffusion, and Gravity wave
Atmospheric Dynamics & PhysicsRadiation, Convection (includes wet
deposition of tropospheric species), Clouds, Vertical diffusion, and Gravity wave
Chemistry of gaseous species (O3, CO, NOx, hydrocarbons) and aerosols
(sulfate, carbonaceous, mineral dust, sea salt, secondary organic)
Dry Deposition
Aerosol-Cloud Interactions
Chemistry of Ox, HOy, NOy, Cly, Bry, and Polar Stratospheric Cloud (PSC)
ForcingSolar Radiation
Well-mixed Greenhouse Gas ConcentrationsVolcanic Emissions
ForcingSolar Radiation
Well-mixed Greenhouse Gas ConcentrationsVolcanic Emissions
Ozone–Depleting Substances (ODS)
Ozone–Depleting Substances (ODS)
Modular Ocean Model version 4 (MOM4)&
Sea Ice Model
Modular Ocean Model version 4 (MOM4)&
Sea Ice Model
Pollutant Emissions (anthropogenic, ships,
biomass burning, natural, & aircraft)
Pollutant Emissions (anthropogenic, ships,
biomass burning, natural, & aircraft)
Land Model version 3(soil physics, canopy physics, vegetation
dynamics, disturbance and land use)
Land Model version 3(soil physics, canopy physics, vegetation
dynamics, disturbance and land use)
SSTs/SIC from observations or CM3 CMIP5 Simulations
SSTs/SIC from observations or CM3 CMIP5 Simulations
GFDL-CM3GFDL-CM3GFDL-AM3GFDL-AM3 AM3 option to nudge to “reanalysis winds”
How good is the model?
Transpacific transport of Asian pollution: the view from satellite
(1018 molecules cm-2)
AIRS retrievals of CO total columns (version 5.2 level 3 daily 1ºx1º gridded products, McMillan et al., 2011)
Potential for developing space-based “indicators” for day-to-day variability in Asian ozone pollution over WUS?
r
Advanced warning of Asian impacts on WUS surface O3?
Qualitatively promising… but short data set, need further testing
Grand Canyon NP
Correlation of Asian ozone pollution enhancement at Grand Canyon NP in GFDL AM3 with AIRS CO columns, considering time lags of 1-3 days, May-June 2010
Asian enhancements to MDA8 O3 at WUS National Parks peak 1-2 days after AIRS CO averaged over NE Pacific
Qualitatively promising… but short data setNeed further test for a quantitative relationship and extending to
other years?
AIR
S C
O o
ver
NE
Pac
ific
(10
18 m
ole
c cm
-2)
AM
3 A
sian
O3
at 3
WU
S s
ites
(p
pb
)
Distinguish “stratospheric” vs. “tropospheric” air masses using the e90 tracer proposed by Prather et al. [2010]; allowing double tropopause
Set O3-strat identical to O3 in “stratospheric” air masses; subject to chemical and depositional loss in “tropospheric” air masses
Transport of O3-strat and e90 both driven by meteorology
Stratospheric ozone tracer