Abstract:We present an improved tropospheric nitrogen dioxide column retrieval algorithm (DOMINO v2.0) for OMI based on better air mass factors (AMFs) and a correction for across-track stripes resulting from calibration errors in the OMI backscattered reflectances. Since October 2004, NO2 retrievals from the Ozone Monitoring Instrument (OMI), a UV/Vis nadir spectrometer onboard NASA's EOS-Aura satellite, have been used with success in several scientific studies focusing on air quality monitoring, detection o… Show more
“…Averaged over India, the magnitude of simulated NO 2 columns (with optimized inventory) is about 10% higher than observed by OMI. The overall error for individual retrieved tropospheric column NO 2 is reported as~25% plus 1.0×10 15 molecules/ cm 2 in DOMINO version 2.0 retrievals [Boersma et al, 2011]. Even though the usefulness of the optimized top-down estimate is limited by these uncertainties, it provides useful information about trends and spatial coverage to policymakers and air quality modelers.…”
Section: Comparison Between Intex-b and Final Top-down Emissionsmentioning
confidence: 99%
“…In brief, tropospheric NO 2 column is derived in three main steps involving the calculation of (1) slant column (using Differential Optical Absorption Spectroscopy (DOAS) approach in the 405-465 nm spectral window), (2) tropospheric slant column (using modeling/ assimilation approach), and (3) tropospheric vertical column (using air mass factor-AMF). OMI retrieval errors have an absolute component of~1.0×10 15 molecules/cm 2 and a relative AMF component of 25% [Boersma et al, 2011]. More details on the retrievals and error budgets are discussed by Boersma et al [2011].…”
Section: Satellite Datamentioning
confidence: 99%
“…OMI retrieval errors have an absolute component of~1.0×10 15 molecules/cm 2 and a relative AMF component of 25% [Boersma et al, 2011]. More details on the retrievals and error budgets are discussed by Boersma et al [2011]. In this work, we use daily level-2 (Version 2.0) data from DOMINO with solar zenith angles <80º, cloud radiance fraction less than 50%, and cloud fraction less than 0.2.…”
Section: Satellite Datamentioning
confidence: 99%
“…However, it should be noted that the top-down estimate E is subject to various sources of uncertainty including uncertainties in OMI retrievals [Boersma et al, 2011] and the model simulations [Kumar et al, 2012], and nonlinearity between emission of NO x and column NO 2 due to NO x transport between the grid cells [Martin et al, 2003, Kuenen, 2006. Uncertainty due to transport between the grid cells is expected to be small because the iteration process compensates for transport to neighboring grid cells [Kuenen, 2006].…”
Section: Comparison Between Intex-b and Final Top-down Emissionsmentioning
[1] In this work, we map and develop for the first time an independent satellite constrained NO x emission inventory for India for 2005 using an inverse technique and iterative procedure. We used OMI tropospheric NO 2 column retrievals over the Indian region, with tropospheric NO 2 columns simulated by the WRF-Chem model using the INTEX-B emission inventory. We determined the local relationship between modeled emissions and tropospheric columns and iteratively apply this relationship to OMI observations to derive an optimized NOx emission inventory on a 0.5°×0.5°grid. The optimized total NO x emissions for India amount to 1.9 TgN/y and agree within 25% with EDGARv4.1 and the INTEX-B estimate. Our top-down inventory captures many of the missing hotspots in the original inventory and suggests that the INTEX-B inventory overestimates emissions over the Western and Eastern Indo-Gangetic region and underestimates point sources. We further evaluate the effect of the top-down inventory on surface ozone, which clearly indicates significant changes in spatial distribution. Citation: Ghude, S.
“…Averaged over India, the magnitude of simulated NO 2 columns (with optimized inventory) is about 10% higher than observed by OMI. The overall error for individual retrieved tropospheric column NO 2 is reported as~25% plus 1.0×10 15 molecules/ cm 2 in DOMINO version 2.0 retrievals [Boersma et al, 2011]. Even though the usefulness of the optimized top-down estimate is limited by these uncertainties, it provides useful information about trends and spatial coverage to policymakers and air quality modelers.…”
Section: Comparison Between Intex-b and Final Top-down Emissionsmentioning
confidence: 99%
“…In brief, tropospheric NO 2 column is derived in three main steps involving the calculation of (1) slant column (using Differential Optical Absorption Spectroscopy (DOAS) approach in the 405-465 nm spectral window), (2) tropospheric slant column (using modeling/ assimilation approach), and (3) tropospheric vertical column (using air mass factor-AMF). OMI retrieval errors have an absolute component of~1.0×10 15 molecules/cm 2 and a relative AMF component of 25% [Boersma et al, 2011]. More details on the retrievals and error budgets are discussed by Boersma et al [2011].…”
Section: Satellite Datamentioning
confidence: 99%
“…OMI retrieval errors have an absolute component of~1.0×10 15 molecules/cm 2 and a relative AMF component of 25% [Boersma et al, 2011]. More details on the retrievals and error budgets are discussed by Boersma et al [2011]. In this work, we use daily level-2 (Version 2.0) data from DOMINO with solar zenith angles <80º, cloud radiance fraction less than 50%, and cloud fraction less than 0.2.…”
Section: Satellite Datamentioning
confidence: 99%
“…However, it should be noted that the top-down estimate E is subject to various sources of uncertainty including uncertainties in OMI retrievals [Boersma et al, 2011] and the model simulations [Kumar et al, 2012], and nonlinearity between emission of NO x and column NO 2 due to NO x transport between the grid cells [Martin et al, 2003, Kuenen, 2006. Uncertainty due to transport between the grid cells is expected to be small because the iteration process compensates for transport to neighboring grid cells [Kuenen, 2006].…”
Section: Comparison Between Intex-b and Final Top-down Emissionsmentioning
[1] In this work, we map and develop for the first time an independent satellite constrained NO x emission inventory for India for 2005 using an inverse technique and iterative procedure. We used OMI tropospheric NO 2 column retrievals over the Indian region, with tropospheric NO 2 columns simulated by the WRF-Chem model using the INTEX-B emission inventory. We determined the local relationship between modeled emissions and tropospheric columns and iteratively apply this relationship to OMI observations to derive an optimized NOx emission inventory on a 0.5°×0.5°grid. The optimized total NO x emissions for India amount to 1.9 TgN/y and agree within 25% with EDGARv4.1 and the INTEX-B estimate. Our top-down inventory captures many of the missing hotspots in the original inventory and suggests that the INTEX-B inventory overestimates emissions over the Western and Eastern Indo-Gangetic region and underestimates point sources. We further evaluate the effect of the top-down inventory on surface ozone, which clearly indicates significant changes in spatial distribution. Citation: Ghude, S.
“…We used tropospheric NO2 column amounts retrieved from measurements of visible and ultraviolet back scattered radiation by the Ozone Monitoring Instrument (OMI) [22] onboard the NASA EOS Aura satellite and provided by KNMI as the DOMINO version 2 data product [23,24]. OMI provides global coverage daily at the 13 × 24 km 2 nominal spatial resolution; the measurements are taken in the early afternoon, as the Aura satellite operates in a sun-synchronous polar orbit with an equator crossing at 13:45 LST.…”
Observational constraints to biomass burning (BB) NOx emissions as provided by satellite measurements of nitrogen dioxide (NO2) critically depend on quantitative assumptions regarding the atmospheric NOx lifetime. In this study, we investigated NOx emissions from the extreme wildfires that occurred in the European part of Russia in summer 2010 by using an original inverse modeling method that allowed us to avoid any a priori assumptions regarding the NOx lifetime. The method was applied to the tropospheric NO2 columns retrieved from the measurements performed by the OMI satellite instrument, while the relationship between BB NOx emissions and tropospheric NO2 columns was simulated with the CHIMERE mesoscale chemistry transport model. Our analysis indicated that this relationship depends strongly on BB emissions of volatile organic compounds and that a dependence of the effective NOx lifetime on the NOx fluxes can be essentially nonlinear. Our estimates of the total NOx emissions in the study region are found to be at least 40% larger compared to the respective data from the GFASv1.0 and GFED4.1s global fire emission inventories.
[1] Transported pollution has been recognized as making a potentially strong impact on air quality in the western U.S., but large uncertainties remain in quantifying its contribution. Assessing the role of pollution transport in relation to local emissions and meteorology is especially important in light of possibly lower ozone standards and projected increases in transpacific pollution transport. We apply the Weather Research and Forecasting with Chemistry model to analyze the role of upwind pollution ("inflow") to surface ozone over California during the Arctic Research of the Composition of the Troposphere from Aircraft and Satellites campaign in June-July 2008 over California. Comparisons of the model to surface and aircraft observations, ozonesondes, and satellite retrievals show an overall good agreement; a low bias (~5 ppb) in free tropospheric ozone is attributed to low ozone at the boundaries and likely places our estimated inflow contribution on the lower side. Most other studies applied sensitivity analyses, while we use a synthetic ozone tracer, which provides a quantitative estimate of the budget. We estimate that on average 10 ± 9 ppb of surface afternoon ozone over California is attributed to ozone and ozone precursors entering the region from outside. This contribution features a significant spatial and temporal variability. While in most high ozone events, transported pollution plays a small role compared to local influences, for some instances, the impact can be substantial. Omitting data impacted by wildfires, we estimate the 90th percentile of the relative contribution of O 3 INFLOW to 8 h ozone >75 ppb as 10%. Our results also indicate that inflow might have a stronger impact on surface ozone in less polluted compared to polluted areas.
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