Abstract
Air quality managers in areas exceeding air pollution standards are motivated to understand where there are further opportunities to reduce NOx emissions to improve ozone and PM2.5 air quality. In this project, we use a combination of aircraft remote sensing (i.e., GCAS), source apportionment models (i.e., CAMx), and regression models to investigate NOx emissions from individual source-sectors in Houston, TX. In prior work, GCAS column NO2 was shown to be close to the “truth” in validating column NO2 in model simulations. Column NO2 from CAMx was substantially low biased compared to Pandora (–20%) and GCAS measurements (–31%), suggesting an underestimate of local NOx emissions. We applied a flux divergence method to the GCAS and CAMx data to distinguish the linear shape of major highways and identify NO2 underestimates at highway locations. Using a multiple linear regression model, we isolated on-road, railyard, and “other” NOx emissions as the likeliest cause of this low bias, and simultaneously identified a potential overestimate of shipping NOx emissions. We modified on-road and shipping NOX emissions in a new CAMx simulation and increased the background NO2, and better agreement was found with GCAS measurements: bias improved from –31% to –10% and r2 improved from 0.78 to 0.80. This study outlines how remote sensing data, including fine spatial information from newer instruments such as TEMPO, can be used in concert with chemical transport models to provide actionable information for air quality managers to identify further opportunities to reduce NOx emissions.
Supplementary materials
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Supporting Information
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Contents of the file:
Figure S1. GCAS NO2 measurements separated by time-of-day
Figure S2. WRF-CAMx 36/12/4/1.333/0.444 km modeling domains.
Table S1. WRF v4.3.3 physics options and data sources used in this study
Table S2. Vertical layer mapping from 44 WRF layers to 30 CAMx layers
Table S3. Science options used for the CAMx model
Table S4. CAMx Source Apportionment configuration
Table S5. Average September 2021 NOx and VOC weekday emissions
Figure S3. Pie Chart of September 2021 NOx and VOC weekday emissions
Figure S4. Spatial distribution of on-road mobile shipping daily NOx emissions
Figure S5. Aggregated satellite-derived NOX emissions for the Houston, TX area
Figure S6. CAMx and MLR Source Apportionment: default and MLR adjusted
Figure S7. Sector contribution to NO2 Vertical Columns for the MLR
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