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Surface nitrogen dioxide concentrations inferred from Ozone Monitoring Instrument (OMI)

12.04.2007

3rd GEOS-Chem USERS` MEETING, Harvard University

Lok Lamsal and Randall Martin

Department of Physics and Atmospheric

Science, Dalhousie University

James Gleason

Goddard Space Flight Center

NASA

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Motivation

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    • Surface NO2 is a toxic pollutant that affects human health
    • Association between surface NO2 and non-accidental mortality (Burnett et al., 2004; Brook et al., 2007)
    • Association stronger than for PM2.5
    • Limited number of sites
    • Global map of surface NO2 not possible without satellite measurements

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Surface measurement sites in US and Canada

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OMI tropospheric NO2 columns as a proxy for deriving surface NO2

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    • Tropospheric column correlated with NO2 at surface (Ordóñez et al., 2006)
    • Tropospheric column a proxy
    • Similar work for ground level PM2.5 from van Donkelaar et al., 2006; Liu et al., 2004

Global distribution of tropospheric column NO2 (Sep. 2005)

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Derivation of surface NO2 from OMI

OMI grids

GEOS-CHEM grid

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    • Need model profile & OMI tropospheric column NO2.
    • GEOS-CHEM NO2 profile shape consistent with in situ measurements (Martin et al.,2004)

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GEOS-CHEM

In situ

Houston: 29°N-31°N, 96.25°W-93.75°W

Texas Air Quality Study aircraft campaign

16 August-13 September 2000

Averaged over OMI overpass time

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NO2 mixing ratio inferred from OMI

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Comparison between OMI surface NO2 and in situ measurements

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    • About 300 US & Canadian stations
    • Collocation radius 12 km, overpass time
    • Agreement incredible at Essex

r = .75

r = .48

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Comparison of ground based and OMI surface NO2

r = .65

r = .27

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Correlation of OMI NO2 with surface measurements

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    • Correlation coefficient for 307 stations
    • Correlation coefficient higher for polluted regions

Year 2005

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Comparison based on land use

ratio

ratio

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Why is OMI surface NO2 lower than in situ measurements?

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Ground based instruments (equipped with molybdenum converter) overestimate surface NO2.

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    • Equipped with molybdenum converter
    • Interference from HNO3, PAN, alkyl nitrates
    • Instrument with photolytic converter more accurate

Schaub et al., 2006; Ordóñez et al., 2006; Dunlea et al., 2007

interference large in summer

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Correction of GB measurements for interference from HNO3, PAN, and alkyl nitrates

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    • Determine correction factor from GEOS-CHEM

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    • Correction factor 🢣

Seasonal means of correction factor

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Correction of GB measurements for interference

Correction factor

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Correction of GB measurements for interference

Seasonal means of surface NO2 (2005)

GB after

correction

OMI

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