Evaluation of the surface PM2.5 in Version 1 of the NASA MERRA Aerosol Reanalysis over the United States
Introduction
PM2.5 – fine aerosol particles with diameters ≤2.5 μm near the surface – have received considerable attention because of their negative effects on regional air quality and on human health (e.g., Pope et al., 2009, Pope and Dockery, 2013). Air quality monitoring networks currently exist over the globe, but they generally offer sparse geographic coverage. Thus, many studies have emerged trying to estimate surface PM2.5 from satellite measurements, especially using the Aerosol Optical Depth (AOD) (e.g., Wang and Christopher, 2003, Engel-Cox et al., 2004), leading to discussions on the ability of retrieving air quality from space.
Satellites have the advantage of providing global coverage and long-term observations. However, important considerations must be made using satellite observations regarding, for example, cloud contamination, uncertainties in AOD retrievals, and sensor-specific data gaps (e.g., lack of AOD retrievals from the Moderate resolution Imaging Spectroradiometer (MODIS) sensor over bright surfaces for the dark-target aerosol retrieval algorithm). Additionally, AOD is a column-integrated observation and PM2.5 concentration is a surface measurement, and estimates that use AOD as the only predictor of PM2.5 can have unusually large uncertainties as a result. Several studies have shown the importance of considering the influence of other parameters on PM2.5 space-based retrievals, such as the relative humidity or the altitude of the aerosol layer (e.g., Liu et al., 2005, Engel-Cox et al., 2006, van Donkelaar et al., 2006, Schaap et al., 2009, Gupta and Christopher, 2009b, Gupta and Christopher, 2009a, Crumeyrolle et al., 2014, Toth et al., 2014). For example, van Donkelaar et al., 2010, van Donkelaar et al., 2015 use a combination of AOD retrieved from satellites and the GEOS-Chem chemical transport model to represent the vertical placement of aerosol and aerosol optical properties to produce PM2.5 estimates on a global scale.
Data assimilation tools combine the high temporal and spatial extent of a global model, constrained by available observations (e.g. AOD in the Modern Era Retrospective analysis for Research and Applications aerosol reanalysis (MERRAero)). Therefore, they can potentially provide a better characterization of PM2.5 than either a model or observational network alone. Several studies (Li et al., 2013, Chen et al., 2014, Schwartz et al., 2014) have shown that assimilation of MODIS AOD and/or surface PM2.5 observations within the WRF-Chem model improves simulated surface PM2.5 relative to observations over the US. Saide et al. (2014) showed that the assimilation of AOD from planned geostationary satellites is expected to improve air quality forecasts when included in a current model that already assimilates MODIS AOD. Compared to observed relationships between AOD and PM2.5, which cannot account for the influence of elevated aerosol layers on the column AOD, a data assimilation-equipped model includes simulation of the aerosol vertical profile, including transport of aerosols from remote and or elevated surfaces.
In this study, we assess the quality of the simulated surface PM2.5 in MERRAero (see below) using ground-based measurements from the US Environmental Protection Agency (EPA) and Interagency Monitoring of PROtected Visual Environments (IMPROVE) networks over the continental United States. While MERRAero includes assimilation of bias-corrected AOD from the MODIS instrument on both Terra and Aqua satellites, it does not assimilate any data capable of directly constraining its aerosol vertical placement or composition, so it remains important to evaluate these aspects of the model. The accuracy of the aerosol reanalysis PM2.5 diagnostic depends on the quality of AOD observed, the quality of the background forecast (speciation, size and vertical structure), the aerosol optical properties assumed to convert modeled aerosol mass to AOD, and the parameterization of error covariances in the aerosol data assimilation algorithm. Therefore, we use independent (non-assimilated) measurements from the AERONET network available over the United States to evaluate MERRAero AOD and airborne High Spectral Resolution Lidar (HSRL) measurements during air quality field campaigns over part of the US and CALIOP data to assess the quality of MERRAero aerosol vertical structure.
In Section 2, we summarize the GEOS-5 aerosol modeling and data assimilation system. Section 3 briefly describes all data products used in this study. In Section 4, MERRAero surface PM2.5 is evaluated over the continental US using the data collected by the EPA and IMPROVE networks. In Section 5, we assess the quality of MERRAero AOD by doing comparisons to AERONET retrievals over the US, followed by the evaluation of the vertical distribution with lidar observations from CALIOP and from airborne HSRL instruments during the NASA DISCOVER-AQ (Deriving Information on Surface Conditions from COlumn and VERtically Resolved Observations Relevant to Air Quality) and SEAC4RS (Studies of Emissions and Atmospheric field Composition, Clouds and Climate Coupling by Regional Surveys) field campaigns. Concluding remarks appear in Section 6.
Section snippets
GEOS-5 and the MERRA Aerosol Reanalysis (MERRAero)
MERRA Version 1 (Rienecker et al., 2011) is a NASA meteorological reanalysis for the satellite era that uses a new version of the Goddard Earth Observing System Data Assimilation System Version 5 (GEOS-5). Atmospheric assimilation focuses on the historical analyses of the hydrological cycle on a broad range of weather and climate time scales, and it places the NASA EOS suite of observations in a climate context. The MERRA time period covers the modern era of remotely sensed data, from 1979
EPA AQS and CSN networks
The US EPA collects observations of surface PM2.5 using a filter-based method on a 24-h schedule from midnight to midnight local time (Malm et al., 2011). The filter is weighed in analytical laboratories before and after the sample collection interval to obtain a PM2.5 mass concentration (μg/m 3) (i.e. by dividing the total mass of PM2.5 particles by the volume of air sampled). The data are available from the EPA Air Quality System (AQS). For this study, daily PM2.5 local conditions (EPA
MERRAero comparison with PM2.5 surface measurements
For this study, MERRAero PM2.5 (defined in Section 2.4) has been sampled at EPA-AQS and IMPROVE observation locations and times. Daily averages (in observation local time) were calculated using hourly output from MERRAero. Since PM2.5 concentrations are generally higher and less uniform in urban areas, such stations are not representative of the grid-box mean values that MERRAero estimates. For this reason, we restrict our analysis to data over suburban and rural sites. In addition, as an
MERRAero AOD and vertical distribution validation
Since some discrepancies are found between MERRAero PM2.5 estimates and in-situ measurements, in this section we turn our attention to two important aspects of MERRAero that are of relevance to the diagnosis of PM2.5. We start by evaluating MERRAero's AOD against independent AERONET observations in order to ascertain that assimilation of MODIS data produces reliable AOD estimates, and by extension reasonable aerosol column loadings. We then examine the aerosol vertical structure in MERRAero by
Concluding remarks
Version 1 of the MERRA Aerosol Reanalysis (MERRAero) assimilates bias-corrected MODIS AOD, producing a time series of 3-D aerosol gridded fields for the Aqua period (mid 2002 to present). While AOD observations may constrain the total column amount of aerosol, it requires the specification of accurate aerosol optical properties. Single-channel AOD observations have no information content on aerosol speciation or vertical structure, leading to only partially constrained surface PM2.5
Acknowledgments
We would like to thank the NASA Center for Climate Simulations (NCCS) at Goddard Space Flight Center and author P. Colarco acknowledges his own participation through the NASA 12-ACMAP12-0064.
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