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Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City
With the purpose of estimating the source contributions of nonmethane hydrocarbons (NMHC) to the atmosphere at three different sites in the Mexico City Metropolitan Area, 92 ambient air samples were measured from February 23 to March 22 of 1997. Light- and heavy-duty vehicular profiles were determin...
Autores principales: | , , , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
TheScientificWorldJOURNAL
2002
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6009718/ https://www.ncbi.nlm.nih.gov/pubmed/12806010 http://dx.doi.org/10.1100/tsw.2002.147 |
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author | Mugica, V. Watson, J. Vega, E. Reyes, E. Ruiz, M.E. Chow, J. |
author_facet | Mugica, V. Watson, J. Vega, E. Reyes, E. Ruiz, M.E. Chow, J. |
author_sort | Mugica, V. |
collection | PubMed |
description | With the purpose of estimating the source contributions of nonmethane hydrocarbons (NMHC) to the atmosphere at three different sites in the Mexico City Metropolitan Area, 92 ambient air samples were measured from February 23 to March 22 of 1997. Light- and heavy-duty vehicular profiles were determined to differentiate the NMHC contribution of diesel and gasoline to the atmosphere. Food cooking source profiles were also determined for chemical mass balance receptor model application. Initial source contribution estimates were carried out to determine the adequate combination of source profiles and fitting species. Ambient samples of NMHC were apportioned to motor vehicle exhaust, gasoline vapor, handling and distribution of liquefied petroleum gas (LP gas), asphalt operations, painting operations, landfills, and food cooking. Both gasoline and diesel motor vehicle exhaust were the major NMHC contributors for all sites and times, with a percentage of up to 75%. The average motor vehicle exhaust contributions increased during the day. In contrast, LP gas contribution was higher during the morning than in the afternoon. Apportionment for the most abundant individual NMHC showed that the vehicular source is the major contributor to acetylene, ethylene, pentanes, n-hexane, toluene, and xylenes, while handling and distribution of LP gas was the major source contributor to propane and butanes. Comparison between CMB estimates of NMHC and the emission inventory showed a good agreement for vehicles, handling and distribution of LP gas, and painting operations; nevertheless, emissions from diesel exhaust and asphalt operations showed differences, and the results suggest that these emissions could be underestimated. |
format | Online Article Text |
id | pubmed-6009718 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2002 |
publisher | TheScientificWorldJOURNAL |
record_format | MEDLINE/PubMed |
spelling | pubmed-60097182018-07-04 Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City Mugica, V. Watson, J. Vega, E. Reyes, E. Ruiz, M.E. Chow, J. ScientificWorldJournal Research Article With the purpose of estimating the source contributions of nonmethane hydrocarbons (NMHC) to the atmosphere at three different sites in the Mexico City Metropolitan Area, 92 ambient air samples were measured from February 23 to March 22 of 1997. Light- and heavy-duty vehicular profiles were determined to differentiate the NMHC contribution of diesel and gasoline to the atmosphere. Food cooking source profiles were also determined for chemical mass balance receptor model application. Initial source contribution estimates were carried out to determine the adequate combination of source profiles and fitting species. Ambient samples of NMHC were apportioned to motor vehicle exhaust, gasoline vapor, handling and distribution of liquefied petroleum gas (LP gas), asphalt operations, painting operations, landfills, and food cooking. Both gasoline and diesel motor vehicle exhaust were the major NMHC contributors for all sites and times, with a percentage of up to 75%. The average motor vehicle exhaust contributions increased during the day. In contrast, LP gas contribution was higher during the morning than in the afternoon. Apportionment for the most abundant individual NMHC showed that the vehicular source is the major contributor to acetylene, ethylene, pentanes, n-hexane, toluene, and xylenes, while handling and distribution of LP gas was the major source contributor to propane and butanes. Comparison between CMB estimates of NMHC and the emission inventory showed a good agreement for vehicles, handling and distribution of LP gas, and painting operations; nevertheless, emissions from diesel exhaust and asphalt operations showed differences, and the results suggest that these emissions could be underestimated. TheScientificWorldJOURNAL 2002-03-29 /pmc/articles/PMC6009718/ /pubmed/12806010 http://dx.doi.org/10.1100/tsw.2002.147 Text en Copyright © 2002 V. Mugica et al. https://creativecommons.org/licenses/by/3.0/ This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited. |
spellingShingle | Research Article Mugica, V. Watson, J. Vega, E. Reyes, E. Ruiz, M.E. Chow, J. Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City |
title | Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City |
title_full | Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City |
title_fullStr | Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City |
title_full_unstemmed | Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City |
title_short | Receptor Model Source Apportionment of Nonmethane Hydrocarbons in Mexico City |
title_sort | receptor model source apportionment of nonmethane hydrocarbons in mexico city |
topic | Research Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6009718/ https://www.ncbi.nlm.nih.gov/pubmed/12806010 http://dx.doi.org/10.1100/tsw.2002.147 |
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