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This study explores methods for deriving surface concentrations of pollutants (NO2, HCHO, NH3, SO2) from satellite column densities. The research focuses on determining the profile shape distribution and boundary layer thickness using observational data and reanalysis. The study examines the similarity of profile shapes for reactive species and investigates dimensional analysis for determining the profile shapes. The results demonstrate the potential for data-driven modeling of surface concentrations using satellite observations and reanalysis data.
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S5P NO2 2018 Observational data-driven surface concentration derived from satellite columns Kang Sun, Dan Li, Yuanjie Zhang, Michael Shook, Rachel Silvern, and TEMPO team CrIS NH3 2013-2017
Introduction • Satellite data provide excellent spatiotemporal coverage • Emissions, distributions, trends of pollutants (NO2, HCHO, NH3, SO2 …) • However, satellite products are often vertical (sub) column density, instead of surface concentrations • Regulations, exposure, land-atmospheric exchange, intercomparisons • Profiles simulated by a chemical transport model (CTM) are conventionally used to infer surface concentrations from satellite columns CrIS NH3 Kharol et al. 2018 OMI-GEOS-Chem NO2 Lamsal et al. 2013 OMI-GEOS-Chem HCHO Zhu et al. 2017
PBLH in CTMs • It is a challenge to accurately model boundary layer processes in meteorological models and CTMs • GEOS-Chem is driven by GEOS-FP or MERRA-2 • CMAQ/WRF-Chem are often driven by NARR • Computationally demanding to match CTM with the spatiotemporal coverage and spatial resolution of next generation satellites GEOS-FP PBLH vs. high spectral resolution lidar (HSRL) PBLH (Zhu et al. 2016) NARR PBLH vs. CALIPSO PBLH (2012-2013) CALIPSO data from Ralph Kuehn, SSEC UW-Madison
Column to surface volume mixing ratio (VMR) • Vertical column Ω integrated from surface pressure ps to upper boundary pt; q is specific humidity; g is gravitational acceleration; MA is dry air molecular mass; x(p) is VMR profile: • Define shape factor γ as (PBLP is thickness of PBL in pressure): • Apparently γ = 1 if • Combining (1) and (2): (1) (2)
Representing profiles • g and MA are constants • Ω is readily available from satellite products, with error estimation and validation • γ represents how the profile distributes in and out of the PBL • PBLP is closely related to the physical height of PBL (PBLH) • Is it possible to obtain the profile distribution and PBL thickness from observations? • Hypothesis 1: the profile shapes for reactive species (NO2, HCHO, NH3) have some level of similarity and γdoes not need to be spatiotemporally resolved • Hypothesis 2: PBLH/P can be unbiasedly determined by combining observations and reanalysis
Determining γ by dimensional analysis • The lifetimes of target species (e.g., NO2, HCHO) are longer than PBL mixing time scale (< 1 hour), but shorter than the exchange time scale between PBL and free troposphere (~ 1 day) • The sources and sinks are mainly in the PBL • Five relevant variables: p, ps, PBLP, x, xPBL (average PBL concentration) • Three primary dimensions: length, mass, time • Buckingham-PI (∏) theorem: 5-3 = 2 dimensionless groups • As a dimensional analysis exercise, the functional relationship f() has to be determined from observations • γis readily determined from f()
NASA DISCOVER-AQ campaigns Systematic sampling of PBL/lower FT 838 spirals ~5 km diameter With missed approaches down to ~30 m AGL 4-17 local sun time
Determining PBLP/H from DAQ profiles • Top of PBL manually labelled from DISCOVER-AQ profiles (MD: 253, CA: 170, TX: 195, CO: 220) based on multiple tracers • Compared with independent manual labels for MD (Don Lenschow) and CA (Michael Shook)
Similarity in dimensionless profiles: NO2 Grouped by campaigns, 12-14 local time Grouped by local time, all campaigns
Similarity in dimensionless profiles: HCHO Grouped by campaigns, 12-14 local time Grouped by local time, all campaigns
Observational data-driven PBL thickness • Meteorological data records when commercial aircrafts take off/land • Aircraft Meteorological Data Reports orAMDAR • UScontributionsarealsooftencalledACARS • PBL profiles at hourly scales based on AMDAR/ACARS Zhang et al. JGR 2018 ACARS PBLH
Validating ACARS PBLH • ACARS: • Continuous, hourly observations • Low bias • Sparse in space • Reanalysis (e.g., NARR) • Spatial/temporally resolved • Comprehensive geophysical variables (T, wind, fluxes) • Variant biases • Data-driven model to merge both datasets • Collaboration with Dan Li, Boston University MD: BWI, PHL, DCA TX: IAH, HOU CO: DEN
Physical oversampling surface concentrations • x(i): derived surface VMR at pixel i; x(j): mean value at grid j • S(i,j) is the integrated spatial sensitivity of satellite pixel i over the area of grid cell j • σ(i) is the error of derived surface VMR, estimated by error propagation: Sun, Zhu et al. AMT 2018
Application for TEMPO • Ensemble average of dimensionless aircraft profiles approximate profiles seen by a TEMPO pixel • Diurnal profile shape evolution in DISCOVER-AQ data can be leveraged for TEMPO • Commercial airline data (ACARS) capture diurnal variation of PBLH • Besides NARR, HRRR PBLH are available at 3-km, 1-hour resolutions over CONUS from 2016
Profile shapes in CTMs: comparison • Observed profiles: DISCOVER-AQ MD (top) and CA (bottom) • Filtered by 10-15 local time • CTM: nested GEOS-Chem0.5°×0.625° horizontal resolution over North America • Driven by MERRA-2 • Sampled at spiral locations and 13:30 local time • CTM shows lower gradients at PBL/lower troposphere • Computationally demanding to match CTM with the spatiotemporal coverage and spatial resolution of next generation satellites Observation-based profiles (γ and PBLP)?
Similarity in dimensionless profiles: NH3 Grouped by campaigns, 12-14 local time Grouped by local time, all campaigns