using omi no 2 and camx simulations to estimate emissions from point and area sources
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Using OMI NO 2 and CAMx simulations to estimate emissions from point and area sources. Benjamin de Foy, Saint Louis University NASA Air Quality Applied Sciences Team 6 th Meeting 15-17 January 2014, Rice University. - PowerPoint PPT PresentationTRANSCRIPT
Using OMI NO2 and CAMx simulations to estimate emissions from point and area sources
Benjamin de Foy, Saint Louis UniversityNASA Air Quality Applied Sciences Team 6th Meeting
15-17 January 2014, Rice University
Estimation of direct emissions and atmospheric processing of reactive mercury using inverse modeling
B. de Foy, J.B. Heo, J. J. Schauer, Atmospheric Environment, 2014
Least-Squares Inversion combines Back-trajectories, Forward Dispersion from Forest Fires and the Free Troposphere,
Chemical Tracers and a Chemical Box Model
Test Emissions Estimates usingWRF & CAMx simulations
Domain 1, 27km cell size Domain 2, 9km cell size
Year-long WRF simulations for 2005
Emissions Estimation Methods:Box Model / Gaussian Fit / Exponentially-
Modified Gaussian Fit
Duncan, B. N., Yoshida, Y., de Foy, B., Lamsal, L. N., Streets, D. G., Lu, Z., & Krotkov, N. A. (2013). The observed response of Ozone Monitoring Instrument (OMI) NO2 columns to NOx emission controls on power plants in the United States: 2005–2011. Atmospheric Environment.“Introduction to Atmospheric Chemistry”, Daniel Jacob
Emissions Estimation Methods:Box Model / Gaussian Fit / Exponentially-
Modified Gaussian Fit
Lu, Zifeng, et al. "OMI Observations of Interannual Increase in SO2 Emissions from Indian Coal-Fired Power Plants during 2005− 2012." Environmental science & technology (2013).Fioletov, V. E., et al. "Estimation of SO2 emissions using OMI retrievals." Geophysical Research Letters 38.21 (2011).
Emissions Estimation Methods:Box Model / Gaussian Fit / Exponentially-
Modified Gaussian Fit
Beirle, S., Boersma, K. F., Platt, U., Lawrence, M. G., & Wagner, T. (2011). Megacity emissions and lifetimes of nitrogen oxides probed from space. Science, 333(6050), 1737-1739.Valin, L. C., Russell, A. R., & Cohen, R. C. (2013). Variations of OH radical in an urban plume inferred from NO2 column measurements. Geophysical Research Letters.
Simulation Test Cases: No ChemistryEastward PlumesUniform Plume Directions
Idealized Winds:5m/s from the West(31 days)
WRF Winds for 2005(365 days)
Simulation Test Cases: 1 hr Chemical LifetimeEastward PlumesUniform Plume Directions
Idealized Winds:5m/s from the West(31 days)
WRF Winds for 2005(365 days)
Emissions Estimation Methods: Box Model
Input Box ModelIdeal WRF
Emissions (kton/year)No Chemistry 47.0 44.2 33.912-hr Chemistry 47.0 39.5 23.71-hr Chemistry 47.0 14.7 5.0Wind Speed (m/s) 5 0 - 2.5
Average plume for 2005interpolated to 2km gridwith box used for estimation
Emissions Estimation Methods:Gaussian Fit
Average of 2005 Plume 2D Gaussian Fit
Emissions Estimation Methods:Gaussian Fit
Input Box Model Gaussian FitIdeal WRF Ideal WRF
Emissions (kton/year)No Chemistry 47.0 44.2 33.9 47.9 55.512-hr Chemistry 47.0 39.5 23.7 48.2 49.31-hr Chemistry 47.0 14.7 5.0 36.4 22.6Wind Speed (m/s) 5 0 - 2.5 5 0 - 2.5Plume Direction Eastward Uniform Uniform UniformLifetime (hr)No Chemistry Infinity 0.9 1.912-hr Chemistry 12 0.9 1.71-hr Chemistry 1 0.7 1.3
Emissions Estimation Methods:Exponentially-Modified Gaussian Fit
1-hr Chemical Lifetime, WRF Winds, Eastward Plume
No Chemistry, WRF Winds, Eastward Plume
1D plot of the sum along the y-axis of the rotated plume
Emissions Estimation Methods:Exponentially-Modified Gaussian Fit
Input Box Model Gaussian Fit EMG FitIdeal WRF Ideal WRF Ideal WRF
Emissions (kton/year)No Chemistry 47.0 44.2 33.9 47.9 55.5 46.7 48.012-hr Chemistry 47.0 39.5 23.7 48.2 49.3 46.7 46.21-hr Chemistry 47.0 14.7 5.0 36.4 22.6 46.1 40.1Wind Speed (m/s) 5 0 - 2.5 5 0 - 2.5 5 5 - 10Plume Direction Eastward Uniform Uniform Uniform Eastward EastwardLifetime (hr)No Chemistry Infinity 0.9 1.9 425 400012-hr Chemistry 12 0.9 1.7 11.4 10.21-hr Chemistry 1 0.7 1.3 1.0 1.1
Conclusions: Using OMI NO2 and CAMx simulations to estimate emissions from point and area sources
Box Model Gaussian Fit EMG FitEmissions Estimate: Linear dependence on plume speed estimate
Plume Speeds: Robust Weak Winds Stronger Winds
Plume Direction: Robust Uniform Dispersion
Accurate Plume Rotation
Chemistry: Sensitive Fairly Robust Robust
Lifetime Estimate: Input to model based on plume speed and box
size
Dispersion, very short
Chemical, biased low
Benjamin de Foy, Saint Louis University