Satellite NO2 data improve national land use regression models for ambient NO2 in a small densely populated country

Abstract Land use regression (LUR) modelling has increasingly been applied to model fine scale spatial variation of outdoor air pollutants including nitrogen dioxide (NO2). Satellite observations of tropospheric NO2 improved LUR model in very large study areas, including Canada, United States and Australia. The aim of our study was to assess the value of satellite observations of NO2 in modelling the spatial variation of annual average NO2 concentrations in a small densely populated country. We used surface level annual average NO2 concentration and geographic information system data from 144 monitoring sites spread over the Netherlands: 26 regional background, 78 urban background and 40 traffic sites for developing land use regression models. For the 144 monitoring sites we obtained the annual average tropospheric NO2 concentration for 2007 from the Ozone Monitoring Instrument (OMI) satellite sensor. These OMI data reflect a spatial scale of about 10 × 10 km. We calculated the correlation between satellite and surface level NO2 concentrations for all sites and for background sites only. We next evaluated whether adding satellite observations improved land use regression models. Annual average satellite observations of tropospheric NO2 correlated well spatially with annual average urban plus regional background (R = 0.74, n = 104 sites) and especially regional background NO2 concentrations (R = 0.88, n = 26). The correlation was moderate for all sites, including traffic locations (R = 0.51, n = 144). A LUR model including satellite NO2 observations performed better (overall R2 = 0.84) than LUR models including geographical coordinates or indicator variables (overall R2 65–74%) in modeling concentrations at the 104 background sites across the Netherlands. Satellite NO2 observations agreed well with measured surface concentrations at background locations and improved land use regression models, even in a small densely populated country.

[1]  M. Brauer,et al.  Creating National Air Pollution Models for Population Exposure Assessment in Canada , 2011, Environmental health perspectives.

[2]  Heikki Saari,et al.  The ozone monitoring instrument , 2006, IEEE Transactions on Geoscience and Remote Sensing.

[3]  R. Beelen,et al.  Comparison of land-use regression models between Great Britain and the Netherlands , 2010 .

[4]  K. F. Boersma,et al.  Testing and improving OMI DOMINO tropospheric NO2 using observations from the DANDELIONS and INTEX-B validation campaigns , 2008 .

[5]  Henk Eskes,et al.  Evaluation of stratospheric NO2 retrieved from the Ozone Monitoring Instrument : intercomparison, diurnal cycle and trending , 2011 .

[6]  Petros Koutrakis,et al.  Daily ambient NO2 concentration predictions using satellite ozone monitoring instrument NO2 data and land use regression. , 2014, Environmental science & technology.

[7]  Julian D. Marshall,et al.  Remote sensing of exposure to NO2: Satellite versus ground-based measurement in a large urban area , 2013 .

[8]  Linking NO2 surface concentration and integrated content in the urban developed atmospheric boundary layer , 2013 .

[9]  Edzer Pebesma,et al.  Mapping of background air pollution at a fine spatial scale across the European Union. , 2009, The Science of the total environment.

[10]  Pavlos S. Kanaroglou,et al.  The sensitivity of OMI-derived nitrogen dioxide to boundary layer temperature inversions , 2009 .

[11]  Henk Eskes,et al.  Error analysis for tropospheric NO2 retrieval from space , 2004 .

[12]  Henk Eskes,et al.  Validation of urban NO 2 concentrations and their diurnal and seasonal variations observed from the SCIAMACHY and OMI sensors using in situ surface measurements in Israeli cities , 2009 .

[13]  Altaf Arain,et al.  A review and evaluation of intraurban air pollution exposure models , 2005, Journal of Exposure Analysis and Environmental Epidemiology.

[14]  K. F. Boersma,et al.  Validation of OMI tropospheric NO2 observations during INTEX-B and application to constrain NOx emissions over the eastern United States and Mexico , 2008 .

[15]  R. Martin Satellite remote sensing of surface air quality , 2008 .

[16]  J. Gulliver,et al.  A review of land-use regression models to assess spatial variation of outdoor air pollution , 2008 .

[17]  J. Huba,et al.  Simulation of the seeding of equatorial spread F by circular gravity waves , 2013 .

[18]  Julian D Marshall,et al.  A national satellite-based land-use regression model for air pollution exposure assessment in Australia. , 2014, Environmental research.

[19]  Kees de Hoogh,et al.  Western European land use regression incorporating satellite- and ground-based measurements of NO2 and PM10. , 2013, Environmental science & technology.

[20]  Joseph P. Pinto,et al.  Ground-level nitrogen dioxide concentrations inferred from the satellite-borne Ozone Monitoring Instrument , 2008 .

[21]  Bert Brunekreef,et al.  Stability of measured and modelled spatial contrasts in NO2 over time , 2011, Occupational and Environmental Medicine.

[22]  Xiong Liu,et al.  Relationship Between Column-Density and Surface Mixing Ratio: Statistical Analysis of O3 and NO2 Data from the July 2011 Maryland DISCOVER-AQ Mission , 2014 .

[23]  K. F. Boersma,et al.  Near-real time retrieval of tropospheric NO 2 from OMI , 2006 .

[24]  Bert Brunekreef,et al.  Development of Land Use Regression models for PM(2.5), PM(2.5) absorbance, PM(10) and PM(coarse) in 20 European study areas; results of the ESCAPE project. , 2012, Environmental science & technology.

[25]  Julian D Marshall,et al.  National satellite-based land-use regression: NO2 in the United States. , 2011, Environmental science & technology.