Emission and chemistry of organic carbon in the gas and aerosol phase at a sub-urban site near Mexico City in March 2006 during the MILAGRO study

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Abstract

Volatile organic compounds (VOCs) and carbonaceous aerosol were measured at a sub-urban site near Mexico City in March of 2006 during the MILAGRO study (Megacity Initiative: Local and Global Research Objectives). Diurnal variations of hydrocarbons, elemental carbon (EC) and hydrocarbon-like organic aerosol (HOA) were dominated by a high peak in the early morning when local emissions accumulated in a shallow boundary layer, and a minimum in the afternoon when the emissions were diluted in a significantly expanded boundary layer and, in case of the reactive gases, removed by OH. In comparison, diurnal variations of species with secondary sources such as the aldehydes, ketones, oxygenated organic aerosol (OOA) and watersoluble organic carbon (WSOC) stayed relatively high in the afternoon indicating strong photochemical formation. Emission ratios of many hydrocarbon species relative to CO were higher in Mexico City than in the U.S., but we found similar emission ratios for most oxygenated VOCs and organic aerosol. Secondary formation of acetone may be more effi-cient in Mexico City than in the U.S., due to higher emissions of alkane precursors from the use of liquefied petroleum gas. Secondary formation of organic aerosol was similar between Mexico City and the U.S. Combining the data for all measured gas and aerosol species, we describe the budget of total observed organic carbon (TOOC), and find that the enhancement ratio of TOOC relative to CO is conserved between the early morning and mid afternoon despite large compositional changes. Finally, the influence of biomass burning is investigated using the measurements of acetonitrile, which was found to correlate with levoglucosan in the particle phase. Diurnal variations of acetonitrile indicate a contribution from local burning sources. Scatter plots of acetonitrile versus CO suggest that the contribution of biomass burning to the enhancement of most gas and aerosol species was not dominant and perhaps not dissimilar from observations in the U.S.

Figures

  • Fig. 1. Status of the instruments that were used to measure VOCs, organic aerosol, CO, ozone and OH at the ground site T1.
  • Table 1. VOC measurements used from the different instruments.∗
  • Fig. 2. Comparison between measured data for organic mass (OM), organic carbon (OC) and water-soluble organic carbon (WSOC). The red lines indicate the 1:1 relationships. The black lines indicate the expected range of data if there were an offset of 2µgC m−3 in the OC data.
  • Fig. 3. Diurnal variations of selected gas-phase species at the T1 site during MILAGRO. The black lines indicate the mean mixing ratios in hourly bins, and the blue shaded areas indicate the standard deviations in these hourly means.
  • Fig. 4. Diurnal variations of organic aerosol data from the T1 site during MILAGRO. The black lines indicate the mean mass loadings in hourly bins, and the blue shaded areas indicate the standard deviations in these hourly means. The black dashed line in panel B indicates the diurnal variation assuming an offset of 2µgC m−3 in the OC measurement.
  • Fig. 5. Distribution of wind directions (panels (a) and (b)) and measured CO (panels (c) and (d)) during the early morning (panels (a) and (c)) and mid-afternoon (panels (b) and (d)) periods. Data in low and variable winds were omitted by requiring a minimum wind speed of 0.5 m s−1.
  • Fig. 6. Scatter plots of (a) acetylene, (b) propane, (c) C8-aromatics and (d) 1-butene versus CO at the T1 site during MILAGRO. Emission ratios versus CO (ER) are given in units of ppbv ppmv−1.
  • Fig. 7. Scatter plots of (a) hydrocarbon-like organic aerosol (HOA) and (b) elemental carbon (EC) versus CO at the T1 site during MILAGRO.

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APA

De Gouw, J. A., Welsh-Bon, D., Warneke, C., Kuster, W. C., Alexander, L., Baker, A. K., … Zaveri, R. (2009). Emission and chemistry of organic carbon in the gas and aerosol phase at a sub-urban site near Mexico City in March 2006 during the MILAGRO study. Atmospheric Chemistry and Physics, 9(10), 3425–3442. https://doi.org/10.5194/acp-9-3425-2009

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