- Open Access
Traffic-related air pollution and respiratory symptoms among asthmatic children, resident in Mexico City: the EVA cohort study
- Maria-Consuelo Escamilla-Nuñez1_705,
- Albino Barraza-Villarreal1_705,
- Leticia Hernandez-Cadena1_705,
- Hortensia Moreno-Macias1_705,
- Matiana Ramirez-Aguilar2_705,
- Juan-Jose Sienra-Monge3_705,
- Marlene Cortez-Lugo1_705,
- Jose-Luis Texcalac1_705,
- Blanca del Rio-Navarro3_705 and
- Isabelle Romieu1_705Email author
© Escamilla-Nuñez et al. 2008
- Received: 02 May 2008
- Accepted: 16 November 2008
- Published: 16 November 2008
Taffic-related air pollution has been related to adverse respiratory outcomes; however, there is still uncertainty concerning the type of vehicle emission causing most deleterious effects.
A panel study was conducted among 147 asthmatic and 50 healthy children, who were followed up for an average of 22 weeks. Incidence density of coughing, wheezing and breathing difficulty was assessed by referring to daily records of symptoms and child's medication. The association between exposure to pollutants and occurrence of symptoms was evaluated using mixed-effect models with binary response and poisson regression.
Wheezing was found to relate significantly to air pollutants: an increase of 17.4 μg/m3 (IQR) of PM2.5 (24-h average) was associated with an 8.8% increase (95% CI: 2.4% to 15.5%); an increase of 34 ppb (IQR) of NO2 (1-h maximum) was associated with an 9.1% increase (95% CI: 2.3% to16.4%) and an increase of 48 ppb (IQR) in O3 levels (1 hr maximum) to an increase of 10% (95% CI: 3.2% to 17.3%). Diesel-fueled motor vehicles were significantly associated with wheezing and bronchodilator use (IRR = 1.29; 95% CI: 1.03 to 1.62, and IRR = 1.32; 95% CI: 0.99 to 1.77, respectively, for an increase of 130 vehicles hourly, above the 24-hour average).
Respiratory symptoms in asthmatic children were significantly associated with exposure to traffic exhaust, especially from natural gas and diesel-fueled vehicles.
- Respiratory Symptom
- Mexico City
- Asthmatic Child
- Traffic Density
- Incidence Rate Ratio
In Mexico City as well as in other cities, several studies have documented the adverse effect on respiratory health, caused by exposure to air pollutants . This effect appears to be greater among asthmatic children, among whom increase in respiratory symptoms, acute decrease in lung function and and an increase in emergency visits have been reported [2–4]. In Mexico City, asthma exacerbation represents 7.8% of emergency room visits at the Hospital Infantil de Mexico "Federico Gomez", the largest children's hospital in Mexico City . In 2003, the Ministry of Health reported that asthma was the 12th cause of death among children under 5 years of age, and the 20th cause of death among children between 5 and 14 years old .
Experimental evidence in animals and humans has suggested that diesel may have a greater negative impact on respiratory health than other air pollutants . The Mexico City Metropolitan area is one of the biggest and most polluted urban areas in the world and close to 85% of air pollutants in this area come from motor vehicles. One of the main pollutants consists of fine particles (PM2.5), 20% of which comes from industry, 32% from diesel and 25% from gasoline . In vitro experimental studies have shown the toxic effects of particles collected in Mexico City [9, 10]. However, no specific data exists indicating the impact of traffic exhaust, particularly diesel on the respiratory health of asthmatic and healthy children, residing in Mexico City. Therefore, we carried out a prospective longitudinal study (EVA, Emission vehicular and asthma study) in order to evaluate the effect of exposure to traffic-related air pollutants, such as PM2.5, nitrogen dioxide (NO2) and elemental carbon. These factors were related to respiratory symptoms and medication use among asthmatic and healthy children, resident in the southeastern area of Mexico City, where there is heavy truck traffic.
The design of this study has already been described . In brief, one hundred and fity eight asthmatic children, attending the Hospital Infantil de Mexico Federico Gómez, one of the largest pediatric hospitals in the city (Mexico City) were invited to participate in the study. The diagnosis and severity of their asthma was assessed in terms of clinical symptoms and response to treatment and rated by a pediatric allergist as either mild (intermittent or persistent), moderate, or severe, following the guidelines described in the Global Initiative for Asthma (GINA) (Global Initiative for Asthma 2006) . Fifty nonasthmatic children were recruited on a voluntary basis, by requesting that each asthmatic child should invite a schoolmate or a friend from their neighborhood. The children in each group ranged between 6 and 14 years of age. They lived in the study area, attended public schools located close to their homes, their attendance was voluntary and they were not selected using probability-based sampling.
Asthmatic and healthy children were recruited between July 2003 and March 2005 and followed up for an average of 22 weeks and evaluated at the same hospital every 2 weeks. At the beginning of the study, parents completed a general-purpose questionnaire, (adapted from existing survey material), outlining sociodemographic variables, past health history, and potential indoor environmental exposures (tobacco smoke and pets in the home). Information concerning allergy test results, medication, and medical visits during the 2 preceding years was obtained from the medical record. At the first visit and every 15 days thereafter, children were given a symptoms diary to be filled out by the mother. This diary was reviewed by the health staff at each visit. All procedures were explained to the parents, who signed an informed consent form. The children also gave their informed assent. Complete data from the daily dairies was available for the147 asthmatic children and 50 healthy children and this was included in the analysis.
Daily records from the health diary provided information on the presence or absence of coughing, wheezing (defined as wheezing and/or difficulty breathing) and on the child's medication use (corticosteroids, such as beclometasone and flixotide among others, and bronchodilators for example salbutamol, as well as others).
Exposure was estimated from outdoor PM2.5 (particulate matter < 2.5 μm in aerodynamic diameter), NO2 and O3 concentrations, as recorded by the Mexico City government at four fixed-sites for central monitoring [Red Automática de Monitoreo Afmosférico (RAMA)] at locations within the study area (Cerro de la Estrella and Hangares, Merced, Universidad Autonoma Metropolitana, Iztapalapa and La Perla). Daily average, maximum moving average and 8-hr maximum ozone, nitrogen dioxide, and PM2.5 concentrations along with meteorologic data (temperature and humidity) were obtained for all (505) days, during the study period. Sulfur dioxide and carbon monoxide were not taken into consideration because of the low levels of these pollutants during the study period and their high correlation with other pollutants (correlation CO with NO2 r = 0.65 p < 0.00 and correlation of SO2 and PM2.5 r = 0.47 p < 0.00).
The home of each participating child was georeferenced using a geographic information system (GIS), and each child was assigned to the closest monitoring station. All children attended public schools, located close to their homes, and no fixed-site monitoring station was located > 5 km from a child's residence or school.
Air pollutants, climatic variables and traffic density during the study period
1 hr maximum, O3 (ppb)
1 hr maximum, NO2(ppb)
24-hr average, PM2.5 (μg/m3)
PM2.5 absorbance (10 -5m-1)&
Temperature minimum, (°C)
Traffic density, hourly average†
Distance from the main avenue to the child's residence(m) †
The protocol for this study was approved by the biosecurity, ethics and research committees of the participating institutions (Instituto Nacional de Salud Publica de Mexico and Hospital Infantil de Mexico "Federico Gomez", Hospital Pediatrico Iztapalapa).
A bivariate analysis was carried out, where the basal characteristics of asthmatic and healthy children were compared, using the t-test (under the normality assumption), the Fisher exact test, or the χ2 test where appropriate. The incidence density of symptoms and bronchodilator use episodes were calculated with reference to the health diary. An epidsode was defined as a manifestation of respiratory symptoms or the need for bronchidilator use, during 2 or more days and a child had to be free of symptoms or bronchodilator use for at least 3 days in order for the initiation of a new episode to be defined.
In order to analyze the occurrence of daily symptoms or bronchodilator use, we employed mixed models with random intercept, with a binary response for longitudinal data, in order to determine the effects of a pollutant (O3, NO2, PM2.5) . The models were run, evaluating pollution effects on the same day and as a result of days prior to the occurrence of the event, assessing accumulation lags for pollutants (from 2 to 5 days). Models were adjusted for sex, severity of asthma, atopy, minimum temperature from the previous day and chronologic time. Other variables such as age, body mass index (weight/height2), socioeconomic status, outdoor activities, exposure to environmental tobacco smoke, pets, carpet in the home, and season did not modify the regression coefficients by more than 1%. The goodness of fit for longitudinal models was evaluated and χ2 values relative to deviance in each of these models did not indicate any lack of adjustment . We also determined the association between respiratory symptoms and the amount of PM2.5 absorbed in a subsample of filters collected in 20 schools. The analysis included 66 children for a total of 376 days of follow up (mean of 6 days per child), using mixed models.
Poisson models were used in order to analyze the association of road traffic with the incidence of symptoms and bronchodilatador use . The dependent variable included the number of new events of respiratory symptoms or bronchodilator use. The exposure variable included the assigned vehicle count, considering the nearest avenue to the child's residence (that is because traffic density was measured on a specific day during the study period, for each intersection selected). The time that each child participated in the study was considerated as offset. These models were also adjusted by sex, severity of asthma, atopy and the distance between the traffic road and the child's residence. We explored the absence of overdispersion and the residuals. We used STATA 9.0 (StataCorp, Texas USA 2005) for statistical analysis.
Basic characteristics of the study population
(n = 147)
(n = 50)
Sex (% male)
Age [years(mean ± SD)]
9.6 ± 2.1
9.3 ± 2.2
38.0 (28.0, 48.0)
32.3 (26.0, 44.6)
139.7 (125.0, 148.0)
132.5 (126.8, 146.2)
Maternal schooling [years(mean ± SD)]
9.7 ± 3.0
9.3 ± 3.1
Paternal smoking at home (%)
Maternal smoking at home (%)
Pets at home (%)
Carpet at home (%)
Humidity at home (%)
Prick test positivity (%)
Moderate persistent asthma (%)
Mild persistent asthma (%)
Mild intermittent asthma (%)
Symptoms within the past 12 months (%)
Wheezing at least one time ‡
Exposure to traffic
The 24-hr average PM2.5 level was 27.8 μg/m3 (standard deviation (SD) = 14.9). The 1-hr maximum average O3 level was 86.5 ppb (SD = 34.4), and the 1-hr maximum average NO2 level was 68.6 ppb (SD = 25.8). The mean daily PM2.5 absorbance was 10.3 (SD = 4.9) 10-5 m-1 (Table 1). PM2.5 were significantly correlated with O3 and NO2 (r = 0.54, and 0.62, respectively). The correlation between O3 and NO2 was 0.48. Traffic density was regrouped according to vehicle type and expressed as a 24-hour hourly average. The largest fraction of vehicles consisted of private cars (76.1%); SBPT represented 15.3%, school buses and other buses, pick up trucks and heavy trucks represented 8.7% of the hourly 24-h average(data not shown).
Incidence density of respiratory symptom episodes and medication use among children 2003–2005
Use of corticosteroids
Use of bronchodilators
PM2.5 absorbance was positively related to respiratory symptoms. An increase of an IQR (8.5 absorbance 10-5m-1) was associated with a 55% increase in coughing risk (OR = 1.55; 95% CI: 0.89 to 2.69) and with a 50% increase in wheezing risk (OR = 1.50; 95% CI: 0.83 to 2.72). Nevertheless, these associations were not significant, probably because of the small sample size employed for this subanalysis.
Among healthy children, we only observed a significant association between NO2 levels and coughing (OR = 1. 22; 95% CI: 1.03 to 1.45 for an increase of 28.5 ppb in 1-hr maximum NO2 levels over 2 days). No significant association was observed between PM2.5 or O3 levels and respiratory symptoms (data not shown).
Effect of traffic on the risk of respiratory symptoms and bronchodilator use among asthmatic children
Type of vehicle*
Use of Bronchodilator
IRR 95% CI+
IRR 95% CI
IRR 95% CI
Distance from main avenue to the child's residence (meters)
When we considered distance to the main road as representing an index for exposure to traffic, the risk of wheezing decreased significantly with greater distance (IRR = 0.69; 95% CI: 0.49 to 0.98, with an increase in distance of 212 m (IQR)).
In this study, we observed that asthmatic children living in urban areas with high traffic density had a greater daily incidence of both respiratory symptoms and bronchodilator use.
The effects were present for PM2.5, NO2 and O3 and increased with exposure over several days in the case of NO2 and O3. Traffic count on the nearest main avenue to the child's residence was also related to respiratory symptoms.
Our results are consistent with those of previous studies, reporting on the increased risk of coughing, wheezing, breathing difficulty, medication and hospital admissions among asthmatic children, which is associated with exposure to O3 , NO2[19, 20], particulate matter (PM10 and PM2.5), and heavy truck traffic [22–24] Our study, as in the one carried out by Mar and co-workers , using a panel of asthmatic children, found an association between respiratory symptoms (coughing and wheezing) and particulate matter. Likewise, a prospective study carried out in southern New England  involving 271 asthmatic children showed that O3 and PM2.5 concentrations below those recommended by the EPA were associated with an increase in the likelihood of wheezing, chest tightness and persistent coughing among children permanently on medication. In the case of co-pollutant models, only the O3 effect continued to be significant, concerning symptoms and medication use. In our study, O3 levels were related to both coughing and wheezing and this effect persisted in the co-pollutant models. Nitrogen dioxide and PM2.5 are two of the pollutants most often considered in order to assess the impact of road traffic on air pollution [23, 25–27] Both pollutants have been related to an increase in respiratory symptoms [28–30]. In our study, NO2 levels had a greater effect than PM2.5 and this effect increased with cumulative exposure, whereas the effect of the PM2.5 level was only evident on the same day as the exposure occurred. Sulfur dioxide has been related to respiratory emergency room admission among children ; however this effect was not manifest in multipollutant models. In our study, SO2 levels were low (mean 0.011 ppm, SD = 0.009) and when this pollutant was included in our models, results remained similar.
Other indicators of exposure to road traffic such as distance to main avenues and traffic density [22–24] have been shown to relate to respiratory symptoms. In our study, we found a significant increase in wheezing and use of bronchodilators, relating to an increase in traffic count. This effect was observed for all types of vehicles but was greater in the case of SBPT and buses and trucks, although separating effects according to type of vehicle may pose a problem given the correlation which exists between traffic classes (coefficient of correlations from 0.5 to 0.7). In Mexico, out of 2 million 654 thousand vehicles, 3% correspond to heavy trucks and 1% to SBPT  and both of these are known to be a source of PM2.5 and NO2. Many public transportation buses use natural compressed gas, which produces a greater quantity of NO2 than common natural gas. When accounting for the distance from the child's residence to the main avenue, both the traffic count (positively) and the distance (inversely) were significantly related to respiratory symptoms. We measured PM2.5 absorbance in a subsample and found a positive association between respiratory symptoms and PM2.5 absorbance. Although the sample size for this analysis was small, our results further support the importance of diesel exposure, as observed in other studies [30, 33].
A limitation to our study lies in the fact that environmental exposure was evaluated in terms of the daily reports from the RAMA central monitoring locations, potentially causing misclassification. Although exposure to pollutants was evaluated ecologically, exposure for each child was assigned according to a spatial GIS, in order to determine the monitoring site closest to the child's residence. As children mostly lived close to their schools, we believe that our exposure assessment is valid. Additionally, we conducted local monitoring of PM2.5 during 15 days in each of the 37 schools. The correlation between the RAMA monitors and the school monitors was 0.77. In any event, the measurement error in exposure assessment is likely to be random and would therefore tend to underestimate the association. Participants in this study were selected on a voluntary basis and were not therefore representative of the asthmatic and healthy population of Mexican children. In fact in our sample, 60.5% of the asthmatic children were boys, whereas data from the Hospital Infantil de Mexico "Federico Gomez" suggest a ratio of 1.6 for boys versus girls, in the age range of our children (personal communication Dr. Blanca Del Rio). One advantage of our study consists in its prospective nature, as this permitted an assessment of the association between daily changes in air pollution levels and symptoms, by using longitudinal data analysis techniques, including random effects to represent specific differences in children's health responses (symptoms), over time. Our results remained similar after adjusting for home characteristics, such as the presence of pets or carpeting in the children's room and climatic variables. The consistency of our results regarding air pollutant levels and traffic count, in relation to respiratory symptoms and bronchodilator use indicates a causal relationship.
The biological factors that may account for the occurrence of respiratory symptoms associated with exposure to air pollutants are not completely understood. Some studies suggest that an increase in the inflammatory response could account for this association [34, 35], particularly among susceptible individuals, such as asthmatic children. Oxidative stress has been shown to be a major underlying feature of the toxic effect of air pollutants. It acts as a trigger for a number of redox sensitive signaling pathways, such as inflammatory response and citokine production [36–39]. Toxicity may therefore be caused by an imbalance of biologic pro-oxidants and antioxidant processes  linked to increased exposure to oxidants or to the presence of impaired antioxidant defenses. In addition, some genetic characteristics may also increase susceptibility to air pollutants . However, better understanding of the physiological effects of exposure to air pollutants, particularly diesel, is required in order to improve the prevention and control of respiratory impairment related to exposure, especially among asthmatic children.
Our prospective data indicate that among asthmatic children, traffic-related air pollutants correlate with an increase in coughing, wheezing and bronchodilator use. Among healthy children an increase in coughing was observed. During the study period, the Mexican norm for PM2.5 and ozone were exceeded on 7.2% and 43.3% of the days, respectively, whereas PM2.5 was exceeded on 48.1% of days, when the EPA standard was referred to . Given the important adverse effects of these traffic exhaust pollutants, greater, stringent control of vehicular emission and traffic is required, especially close to schools and in areas where children participate in outdoor activities. These results have significant public health policy implications, as a large proportion of schools in Mexico City and other countries are located very close to roads carrying heavy traffic.
We thank the schoolchildren who took part in the study, the personnel who carried out the fieldwork. The study was supported by the Mexican Sciences and Technology Council (CONACYT), grant 38911-M and Salud-2002-C01-7624.
- Romieu I, Samet JM, Smith KR, Bruce N: Outdoor air pollution and acute respiratory infections among children in developing countries. J Occup Environ Med 2002, 44:640–649.View ArticlePubMedGoogle Scholar
- Holguin F, Tellez-Rojo MM, Hernandez M, Cortez M, Chow JC, Watson JG, Mannino D, Romieu I: Air pollution and heart rate variability among the elderly in Mexico City. Epidemiology 2003,14(5):521–527.View ArticlePubMedGoogle Scholar
- Romieu I, Sienra-Monge JJ, Ramirez-Aguilar M, Tellez-Rojo MM, Moreno-Macias H, Reyes-Ruiz NI, del Rio-Navarro BE, Ruiz-Navarro MX, Hatch G, Slade R, et al.: Antioxidant supplementation and lung functions among children with asthma exposed to high levels of air pollutants. Am J Respir Crit Care Med 2002,166(5):703–709.View ArticlePubMedGoogle Scholar
- Urch B, Silverman F, Corey P, Brook JR, Lukic KZ, Rajagopalan S, Brook RD: Acute blood pressure responses in healthy adults during controlled air pollution exposures. Environ Health Perspect 2005,113(8):1052–1055.View ArticlePubMedPubMed CentralGoogle Scholar
- Sienra-Monge JJ, Del Rio-Navarro BE: Asma aguda. Bol Med Hosp Infant Mex 1999, 56:185–194.Google Scholar
- Secretaria de Salud Direccion de Epidemiologia: taría de Salud. Sistema Nacional de Información en Salud. Mortalidad. Información . [http://sinais.salud.gob.mx/descargas/xls/m_007.xls] 2000–2005.
- Saxon A, Diaz-Sanchez D: Air pollution and allergy: you are what you breathe. Nat Immunol 2005,6(3):223–226.View ArticlePubMedGoogle Scholar
- Secretaria de Salud Mexico: Programa de Acción en Salud Ambiental (PRASA), 2001–2006. Mexico, DF; 111–112.Google Scholar
- Fortoul TI, Valverde M, Lopez MC, Bizarro P, Lopez I, Sanchez I, Colin-Barenque L, Avila-Costa MR, Rojas E, Ostrosky-Shejet P: Single-cell gel electrophoresis assay of nasal epithelium and leukocytes from asthmatic and nonasthmatic subjects in Mexico City. Arch Environ Health 2003,58(6):348–352.PubMedGoogle Scholar
- Osornio-Vargas AR, Bonner JC, Alfaro-Moreno E, Martinez L, Garcia-Cuellar C, Ponce-de-Leon Rosales S, Miranda J, Rosas I: Proinflammatory and cytotoxic effects of Mexico City air pollution particulate matter in vitro are dependent on particle size and composition. Environ Health Perspect 2003, 111:1289–1293.View ArticlePubMedPubMed CentralGoogle Scholar
- Barraza-Villarreal A, Sunyer J, Hernandez-Cadena L, Escamilla-Nuñez MC, Sienra-Monge JJ, Ramírez-Aguilar M, Cortez-Lugo M, Holguin F, Diaz-Sánchez D, Olin AC, et al.: Air pollution, airway inflammation, and lung function in a cohort study of Mexico City schoolchildren. Environ Health Perspect 2008, 116:832–838.View ArticlePubMedPubMed CentralGoogle Scholar
- Global Initiative for Asthma (GINA): Global Initiative for Asthma (GINA): GINA Report, Global Strategy for Asthma Management and Prevention. [http://www.ginasthma.org/Guidelineitem.asp??l1=2&l2=1&intId=60] 2007.Google Scholar
- Watson JG, Chow JC, Fraizer CA: X-ray flourescence analysis of ambient air samples. In Elemental analysis of airborne particle Advance in environmental process control technologies. Volume 1. Edited by: Landsberger S, Creatchman M. Newark, New jersey: Sciences Publisher Gordon and Breach; 1999:67–96.Google Scholar
- Levy JI, Lee K, Spengler JD, Yanagisawa Y: Impact of residential nitrogen dioxide exposure on personal exposure: an international study. J Air Waste Manag Assoc 1998, 48:553–560.View ArticlePubMedGoogle Scholar
- Cyrys J, Heinrich J, Hoek G, Meliefste K, Lewné M, Gehring U, Bellander T, Fischer P, van Vliet P, Brauer M, et al.: Comparison between different traffic-related particle indicators: elemental carbon (EC), PM2.5 mass, and absorbance. J Expo Anal Environ Epidemiol 2003, 13:134–143.View ArticlePubMedGoogle Scholar
- Diggle PJ, Heagerty P, Liang KY, Zeger SL: Analysis of longuitudinal data. 2nd edition. Oxford: Oxford University Press; 2002.Google Scholar
- Cameron Ac, Trivedi PK: Regression analysis of count data. Cambridge, United Kingdom: Cambridge University Press; 1998.View ArticleGoogle Scholar
- Gent JF, Triche EW, Holford TR, Belanger K, Bracken MB, Beckett WS, Leaderer BP: Association of low-level ozone and fine particles with respiratory symptoms in children with asthma. JAMA 2003, 290:1859–1867.View ArticlePubMedGoogle Scholar
- Oosterlee A, Drijver M, Lebret E, Brunekreef B: Chronic respiratory symptoms in children and adults living along streets with high traffic density. Occup Environ Med 1996, 53:241–247.View ArticlePubMedPubMed CentralGoogle Scholar
- Shima M, Adachi M: Effect of outdoor and indoor nitrogen dioxide on respiratory symptoms in schoolchildren. Int J Epidemiol 2000,29(5):862–870.View ArticlePubMedGoogle Scholar
- Mar TF, Larson TV, Stier RA, Claiborn C, Koenig JQ: An analysis of the association between respiratory symptoms in subjects with asthma and daily air pollution in Spokane, Washington. Inhal Toxicol 2004, 16:809–815.View ArticlePubMedGoogle Scholar
- Weiland SK, Mundt KA, Ruckmann A, Keil U: Self-reported wheezing and allergic rhinitis in children and traffic density on street of residence. Ann Epidemiol 1994, 4:243–247.View ArticlePubMedGoogle Scholar
- Heinrich J, Wichmann HE: Traffic related pollutants in Europe and their effect on allergic disease. Curr Opin Allergy Clin Immunol 2004,4(5):341–348.View ArticlePubMedGoogle Scholar
- van Vliet P, Knape M, de Hartog J, Janssen N, Harssema H, Brunekreef B: Motor vehicle exhaust and chronic respiratory symptoms in children living near freeways. Environ Res 1997, 74:122–132.View ArticlePubMedGoogle Scholar
- Cyrys J, Hochadel M, Gehring U, Hoek G, Diegmann V, Brunekreef B, Heinrich J: GIS-based estimation of exposure to particulate matter and NO2 in an urban area: stochastic versus dispersion modeling. Environ Health Perspect 2005, 113:987–992.View ArticlePubMedPubMed CentralGoogle Scholar
- Gehring U, Cyrys J, Sedlmeir G, Brunekreef B, Bellander T, Fischer P, Bauer CP, Reinhardt D, Wichmann HE, J H: Traffic-related air pollution and respiratory health during the first 2 yrs of life. Eur Respir J 2002,19(4):690–698.View ArticlePubMedGoogle Scholar
- Kunzli N, Kaiser R, Medina S, Studnicka M, Chanel O, Filliger P, Herry M, Horak F Jr, Puybonnieux-Texier V, Quenel P, et al.: Public-health impact of outdoor and traffic-related air pollution: a European assessment. Lancet 2000, 356:795–801.View ArticlePubMedGoogle Scholar
- Brauer M, Hoek G, van Vliet P, Meliefste K, Fischer PH, Wijga A, Koopman LP, Neijens HJ, Gerritsen J, Kerkhof M, et al.: Air pollution from traffic and the development of respiratory infections and asthmatic and allergic symptoms in children. Am J Respir Crit Care Med 2002,166(8):1092–1098.View ArticlePubMedGoogle Scholar
- Brunekreef B, Janssen NA, de Hartog J, Harssema H, Knape M, van Vliet P: Air pollution from truck traffic and lung function in children living near motorways. Epidemiology 1997,8(3):298–303.View ArticlePubMedGoogle Scholar
- Morgenstern V, Zutavern A, Cyrys J, Brockow I, Gehring U, Koletzko S, Bauer CP, Reinhardt D, Wichmann HE, Heinrich J: Respiratory health and individual estimated exposure to traffic-related air pollutants in a cohort of young children. Occup Environ Med 2007, 64:8–16.View ArticlePubMedGoogle Scholar
- Sunyer J, Atkinson R, Ballester F, Le Tertre A, Ayres JG, Forastiere F, Forsberg B, Vonk JM, Bisanti L, Anderson RH, et al.: Respiratory effects of sulphur dioxide: a hierarchical multicity analysis in the APHEA 2 study. Occup Environ Med 2003,60(8):e2.View ArticlePubMedPubMed CentralGoogle Scholar
- Transporte y vialidad en el Distrito Federal Google Scholar
- Heinrich J, Gehring U, Cyrys J, Brauer M, Hoek G, Fischer P, Bellander T, Brunekreef B: Exposure to traffic related air pollutants: self reported traffic intensity versus GIS modelled exposure. Occup Environ Med 2005,62(8):517–523.View ArticlePubMedPubMed CentralGoogle Scholar
- Li XY, Gilmour PS, Donaldson K, MacNee W: Free radical activity and pro-inflammatory effects of particulate air pollution (PM10) in vivo and in vitro. Thorax 1996,51(12):1216–1222.View ArticlePubMedPubMed CentralGoogle Scholar
- Takizawa H: Diesel exhaust particles and their effect on induced cytokine expression in human bronchial epithelial cells. Curr Opin Allergy Clin Immunol 2004,4(5):355–359.View ArticlePubMedGoogle Scholar
- Kelly FJ: Oxidative stress: its role in air pollution and adverse health effects. Occup Enviorn Med 2003,60(8):612–616.View ArticleGoogle Scholar
- Mudway IS, Kelly FJ: Ozone and the lung: a sensitive issue. Mol Aspects Med 2000,21(1–2):1–48.View ArticlePubMedGoogle Scholar
- Nel A: Atmosphere. Air pollution-related illness: effects of particles. Science 2005, 308:804–806.View ArticlePubMedGoogle Scholar
- Schlesinger RB, Kunzli N, Hidy GM, Gotschi T, Jerrett M: The health relevance of ambient particulate matter characteristics: coherence of toxicological and epidemiological inferences. Inhal Toxicol 2006, 18:95–125.View ArticlePubMedGoogle Scholar
- Corradi M, Alinovi R, Goldoni M, Vettori M, Folesani G, Mozzoni P, Cavazzini S, Bergamaschi E, Rossi L, Mutti A: Biomarkers of oxidative stress after controlled human exposure to ozone. Toxicol Lett 2002,134(1–3):219–225.View ArticlePubMedGoogle Scholar
- Romieu I, Ramirez-Aguilar M, Sienra-Monge JJ, Moreno-Macias H, del Rio-Navarro BE, David G, Marzec J, Hernandez-Avila M, London S: GSTM1 and GSTP1 and respiratory health in asthmatic children exposed to ozone. Eur Respir J 2006, 28:953–959.View ArticlePubMedGoogle Scholar
- Environmental Protection Agency: Red de Transferencia de Tecnología Centro de Información sobre Contaminación de Aire (CICA) para la frontera entre EE. UU. – México. Normas de aire ambiental basadas en la salud. [http://www.epa.gov/ttn/catc/cica/airq_s.html]
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