Chemical composition of PM2.5 and PM10 in Mexico City during winter 1997.

PM2.5 and PM10 were measured over 24-h intervals at six core sites and at 25 satellite sites in and around Mexico City from 23 February to 22 March 1997. In addition, four 6-h samples were taken each day at three of the core sites. Sampling locations were selected to represent regional, central city, commercial, residential, and industrial portions of the city. Mass and light transmission concentrations were determined on all of the samples, while elements, ions and carbon were measured on approximately two-thirds of the samples. PM10 concentrations were highly variable, with almost three-fold differences between the highest and lowest concentrations. Fugitive dust was the major cause of PM10 differences, although carbon concentrations were also highly variable among the sampling sites. Approximately 50% of PM10 was in the PM2.5 fraction. The majority of PM mass was comprised of carbon, sulfate, nitrate, ammonium and crustal components, but in different proportions on different days and at different sites. The largest fine-particle components were carbonaceous aerosols, constituting approximately 50% of PM2.5 mass, followed by approximately 30% secondary inorganic aerosols and approximately 15% geological material. Geological material is the largest component of PM10, constituting approximately 50% of PM10 mass, followed by approximately 32% carbonaceous aerosols and approximately 17% secondary inorganic aerosols. Sulfate concentrations were twice as high as nitrate concentrations. Sulfate and nitrate were present as ammonium sulfate and ammonium nitrate. Approximately two-thirds of the ammonium sulfate measured in urban areas appears to have been transported from regions outside of the study domain, rather than formed from emissions in the urban area. Diurnal variations are apparent, with two-fold increases in concentration from night-time to daytime. Morning samples had the highest PM2.5 and PM10 mass, secondary inorganic aerosols and carbon concentrations, probably due to a shallow surface inversion and rush-hour traffic.

[1]  L. Richards Comments on the oxidation of NO2 to nitrate—day and night , 1983 .

[2]  D. Loomis,et al.  Air pollution and infant mortality in Mexico City. , 1999, Epidemiology.

[3]  Judith C. Chow,et al.  Chemical Mass Balance Source Apportionment of PM10 during the Southern California Air Quality Study , 1994 .

[4]  Judith C. Chow,et al.  Descriptive analysis of PM2.5 and PM10 at regionally representative locations during SJVAQS/AUSPEX , 1996 .

[5]  J. Chow,et al.  Estimating Middle-, Neighborhood-, and Urban-Scale Contributions to Elemental Carbon in Mexico City with a Rapid Response Aethalometer , 2001, Journal of the Air & Waste Management Association.

[6]  Judith C. Chow,et al.  Comparison of IMPROVE and NIOSH Carbon Measurements , 2001 .

[7]  G. Cass,et al.  Characteristics of atmospheric organic and elemental carbon particle concentrations in Los Angeles. , 1986, Environmental science & technology.

[8]  J. Chow,et al.  PM2.5 chemical source profiles for vehicle exhaust, vegetative burning, geological material, and coal burning in Northwestern Colorado during 1995. , 2001, Chemosphere.

[9]  J. Chow,et al.  Evaluation of filter-based aerosol measurements during the 1987 Southern California Air Quality Study , 1994, Environmental monitoring and assessment.

[10]  J. Chow,et al.  Spatial Differences in Outdoor PM10 Mass and Aerosol Composition in Mexico City , 2002, Journal of the Air & Waste Management Association.

[11]  Judith C. Chow,et al.  Differences in the carbon composition of source profiles for diesel- and gasoline-powered vehicles , 1994 .

[12]  Sheldon Landsberger,et al.  Elemental analysis of airborne particles , 1999 .

[13]  J. Huntzicker,et al.  Secondary formation of organic aerosol in the Los Angeles basin: A descriptive analysis of organic and elemental carbon concentrations , 1991 .

[14]  Susanne V. Hering,et al.  Air Sampling Instruments for Evaluation of Atmospheric Contaminants , 1989 .

[15]  J C Chow,et al.  Measurement methods to determine compliance with ambient air quality standards for suspended particles. , 1995, Journal of the Air & Waste Management Association.

[16]  J. L. Martinez,et al.  The IMADA-AVER Boundary Layer Experiment in the Mexico City Area , 1998 .

[17]  R A Etzel,et al.  Effects of air pollution on the respiratory health of asthmatic children living in Mexico City. , 1996, American journal of respiratory and critical care medicine.

[18]  L. Kiefert,et al.  Organic matter content of rural dusts in Australia , 1998 .

[19]  Judith C. Chow,et al.  Fine Particle and Gaseous Emission Rates from Residential Wood Combustion , 2000 .

[20]  I. Marr Principles of environmental sampling , 1991 .

[21]  J. Chow,et al.  PM[sub 10] and PM[sub 2. 5] compositions in California's San Joaquin Valley , 1993 .

[22]  M. Catalán-Vázquez,et al.  Air pollution and respiratory health in Mexico City. , 1997, Journal of occupational and environmental medicine.

[23]  Judith C. Chow,et al.  A laboratory resuspension chamber to measure fugitive dust size distributions and chemical compositions , 1994 .

[24]  J C Chow,et al.  Particulate Air Pollution in Mexico City: A Collaborative Research Project. , 1999, Journal of the Air & Waste Management Association.

[25]  John H. Seinfeld,et al.  Relative humidity and temperature dependence of the ammonium nitrate dissociation constant , 1982 .

[26]  J C Chow,et al.  Middle- and Neighborhood-Scale Variations of PM10 Source Contributions in Las Vegas, Nevada. , 1999, Journal of the Air & Waste Management Association.

[27]  Judith C. Chow,et al.  Ammonium Nitrate, Nitric Acid, and Ammonia Equilibrium in Wintertime Phoenix, Arizona , 1994 .

[28]  E. Jáuregui The dust storms of Mexico City , 1989 .

[29]  I. Romieu,et al.  Air pollution and school absenteeism among children in Mexico City. , 1992, American journal of epidemiology.

[30]  W. Whitten,et al.  Real-Time Characterization of the Organic Composition and Size of Individual Diesel Engine Smoke Particles , 1998 .

[31]  J. Chow,et al.  Cross-border transport and spatial variability of suspended particles in Mexicali and California's Imperial Valley , 2000 .

[32]  Judith C. Chow,et al.  The dri thermal/optical reflectance carbon analysis system: description, evaluation and applications in U.S. Air quality studies , 1993 .

[33]  Mike Ashmore,et al.  Exposure of commuters to carbon monoxide in Mexico city—I. Measurement of in-vehicle concentrations , 1995 .

[34]  G. Cass,et al.  Los Angeles Summer Midday Particulate Carbon: Primary and Secondary Aerosol , 1991 .

[35]  X. Bian,et al.  Boundary layer evolution and regional‐scale diurnal circulations over the and Mexican plateau , 2000 .

[36]  S. Zhong,et al.  Meteorological factors associated with inhomogeneous ozone concentrations within the Mexico City basin , 1998 .

[37]  J C Chow,et al.  Source characterization of major emission sources in the imperial and Mexicali Valleys along the US/Mexico border. , 2001, The Science of the total environment.

[38]  L. H. Keith,et al.  Sampling and analysis of airborne pollutants , 1993 .

[39]  J. Chow,et al.  Chemical composition of fugitive dust emitters in Mexico City , 2001 .