Influence of traffic on the PM10 and PM2.5 urban aerosol fractions in Madrid (Spain).

A preliminary assessment carried out in Madrid demonstrates the difficulty of compliance with the new European PM(10) tolerances. Daily and annual limiting values would be exceeded at almost all the network stations under the terms of the directive's second stage. An experimental study, based on the chemical characterisation of the PM(10) and PM(2.5) fractions sampled at a representative urban site, provides the major mass contents of these two fractions. These are mainly related to two different particle sources: combustion processes including traffic emissions and mineral-origin particles. Nonmineral carbon is the major component of particulate matter in this region, mostly in the PM(2.5) fraction, increasing its contribution in wintertime. The second largest component identified in the PM(10) mass, is associated with crustal origin particles and is more relevant in summer, whereas the second largest contributor to PM(2.5) is secondary particles. In general, PM(10) and PM(2.5) concentrations show good agreement with traffic-related pollutants, such as nitrogen oxides and CO, being time-correlated in winter pollution episodes. PM(1) and PM(2.5) have been simultaneous and continuously measured indicating road transport as the main source of these finer fractions. Mineral contribution has been mainly identified in the coarser particles associated with dust resuspension and some long-range transport events of Saharan dust, although they are also present in the finer PM(2.5) fraction.

[1]  G. Kallos,et al.  Saharan dust contributions to PM10 and TSP levels in Southern and Eastern Spain , 2001 .

[2]  M. Pujadas,et al.  Passive remote sensing of nitrogen dioxide as a tool for tracking air pollution in urban areas: the Madrid urban plume, a case of study , 2000 .

[3]  Xavier Querol,et al.  PM10 and PM2.5 source apportionment in the Barcelona Metropolitan area, Catalonia, Spain , 2001 .

[4]  F. Lurmann,et al.  Evaluation of the TEOM method for measurement of ambient particulate mass in urban areas. , 1997, Journal of the Air & Waste Management Association.

[5]  Field trials of the TEOM® and Partisol for PM10 monitoring in the St Austell china clay area, Cornwall, UK , 1999 .

[6]  X. Querol,et al.  Assessment of airborne particulate levels in Spain in relation to the new EU-directive , 2001 .

[7]  U. Ackermann-Liebrich,et al.  Particulate matter < 10 μm (PM10) and total suspended particulates (TSP) in urban, rural and alpine air in Switzerland , 1995 .

[8]  Roy M. Harrison,et al.  Sources and processes affecting concentrations of PM10 and PM2.5 particulate matter in Birmingham (U.K.) , 1997 .

[9]  Xavier Querol,et al.  Monitoring of PM10 and PM2.5 around primary particulate anthropogenic emission sources , 2001 .

[10]  X. Querol,et al.  Levels of particulate matter in rural, urban and industrial sites in Spain. , 2004, The Science of the total environment.

[11]  Tony Fletcher,et al.  PM10 and PM2.5 concentrations in Central and Eastern Europe: results from the Cesar study , 2001 .

[12]  Angel Lopez-Soler,et al.  Seasonal evolution of suspended particles around a large coal-fired power station: particulate levels and sources , 1998 .

[13]  R. Harrison,et al.  Comparative receptor modelling study of airborne particulate pollutants in Birmingham (United Kingdom), Coimbra (Portugal) and Lahore (Pakistan) , 1997 .

[14]  D. Palazzo,et al.  Europe’s Environment: The Second Assessment, by the Environment Agency, Office for Official Publications of the European Communities, Elsevier, Oxford, United Kingdom, 1998, 293 pp. , 2000 .

[15]  J. Chow,et al.  Sources and chemistry of PM10 aerosol in Santa Barbara County, CA , 1996 .

[16]  Inocencio Font Tullot Climatología de España y Portugal , 1983 .

[17]  Xavier Querol,et al.  Origin of high summer PM10 and TSP concentrations at rural sites in Eastern Spain , 2002 .