Commuters' exposure to PM2.5, CO, and benzene in public transport in the metropolitan area of Mexico City

被引:117
作者
Gómez-Perales, JE
Colvile, RN
Nieuwenhuijsen, MJ
Fernández-Bremauntz, A
Gutiérrez-Avedoy, VJ
Páramo-Figueroa, VH
Blanco-Jiménez, S
Bueno-López, E
Mandujano, F
Bernabé-Cabanillas, R
Ortiz-Segovia, E
机构
[1] Univ London Imperial Coll Sci Technol & Med, Fac Life Sci, Dept Environm Sci & Technol, London SW7 2AZ, England
[2] Inst Nacl Ecol Reg & Global, Direcc Gen Invest Contaminac Urbana, Mexico City 04530, DF, Mexico
[3] Univ Autonoma Metropolitana Iztapalapa, Ctr Nacl Invest & Capicitac Ambiental, Inst Nacl Ecol, Mexico City 09340, DF, Mexico
[4] Direcc Gen Gest Ambiental Aire, Gobierno Dist Fed, Mexico City 11800, DF, Mexico
关键词
Mexico City; public transport; commuters' exposure; PM2.5; CO; benzene;
D O I
10.1016/j.atmosenv.2003.11.008
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A survey was carried out to measure commuters' exposure to PM2.5, CO, benzene, and the chemical composition of PM2.5 on different routes and modes of transport in Mexico City. PM2.5 (n = 62), CO (n = 54) and benzene (n = 22) are presented from morning (6:30-9:30 a.m.) and evening (17:30-20:30) rush hours on minibuses, buses and Metro (underground or subway system). Three routes were selected from a previous commuters' exposure study covering some of the most important thoroughfares of the valley. For PM2.5, mass concentration was determined for all the samples. Nitrates, sulphates, inorganic elements and carbon fraction were analysed. CO was sampled using electrochemical sensors and 6-1 canisters with flow controller devices were used to collect integrated samples for benzene. Minibuses had a slightly higher geometric mean PM2.5 concentration in the morning than other modes of transport, but the ranking of geometric mean PM2.5 by mode of transport is opposite in the evening and the variability within modes is approximately double the difference between modes. The highest single measurement was a concentration of 137 mug m(-3) on a bus during an evening rush hour. The main component identified in PM2.5 was carbon. Carbon monoxide levels in this study were approximately 3 times lower than those found in a commuter exposure study conducted in 1991. A strong association was shown between wind speed and PM2.5 exposure in minibuses (r(2) = 0.50) and buses (r(2) = 0.54). The relationship between wind speed and CO exposure was strong only in minibuses (r(2) = 0.52). (C) 2003 Elsevier Ltd. All rights reserved.
引用
收藏
页码:1219 / 1229
页数:11
相关论文
共 45 条
[1]   Determinants of fine particle (PM2.5) personal exposure levels in transport microenvironments, London, UK [J].
Adams, HS ;
Nieuwenhuijsen, MJ ;
Colvile, RN .
ATMOSPHERIC ENVIRONMENT, 2001, 35 (27) :4557-4566
[2]   Assessment of road users' elemental carbon personal exposure levels, London, UK [J].
Adams, HS ;
Nieuwenhuijsen, MJ ;
Colvile, RN ;
Older, MJ ;
Kendall, M .
ATMOSPHERIC ENVIRONMENT, 2002, 36 (34) :5335-5342
[3]   Design and validation of a high-flow personal sampler for PM2.5 [J].
Adams, HS ;
Kenny, LC ;
Nieuwenhuijsen, MJ ;
Colvile, RN ;
Gussman, RA .
JOURNAL OF EXPOSURE ANALYSIS AND ENVIRONMENTAL EPIDEMIOLOGY, 2001, 11 (01) :5-11
[4]   Fine particle (PM2.5) personal exposure levels in transport microenvironments, London, UK [J].
Adams, HS ;
Nieuwenhuijsen, MJ ;
Colvile, RN ;
McMullen, MAS ;
Khandelwal, P .
SCIENCE OF THE TOTAL ENVIRONMENT, 2001, 279 (1-3) :29-44
[5]   PIXE analysis of atmospheric aerosols from a simultaneous three site sampling during the autumn of 1993 in Mexico City [J].
Aldape, F ;
Flores, J ;
Garcia, R ;
Nelson, JW .
NUCLEAR INSTRUMENTS & METHODS IN PHYSICS RESEARCH SECTION B-BEAM INTERACTIONS WITH MATERIALS AND ATOMS, 1996, 109 :502-505
[6]   Mortality and ambient fine particles in southwest Mexico City, 1993-1995 [J].
Borja-Aburto, VH ;
Castillejos, M ;
Gold, DR ;
Bierzwinski, S ;
Loomis, D .
ENVIRONMENTAL HEALTH PERSPECTIVES, 1998, 106 (12) :849-855
[7]   Concentrations of benzene and toluene in the atmosphere of the Southwestern area at the Mexico City Metropolitan Zone [J].
Bravo, H ;
Sosa, R ;
Sánchez, P ;
Bueno, E ;
González, L .
ATMOSPHERIC ENVIRONMENT, 2002, 36 (23) :3843-3849
[8]  
BRICE ROBERT M., 1966, J AIR POLLUT CONTR ASS, V16, P597
[9]  
*CARB, 1992, 044 SOP CARB
[10]   Airborne coarse particles and mortality [J].
Castillejos, M ;
Borja-Aburto, VH ;
Dockery, DW ;
Gold, DR ;
Loomis, D .
INHALATION TOXICOLOGY, 2000, 12 :61-72