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Jornal Brasileiro de Pneumologia

Print version ISSN 1806-3713

J. bras. pneumol. vol.38 no.5 São Paulo Sept./Oct. 2012

http://dx.doi.org/10.1590/S1806-37132012000500015 

REVIEW ARTICLE

 

Air pollution and the respiratory system*

 

 

Marcos Abdo ArbexI; Ubiratan de Paula SantosII; Lourdes Conceição MartinsIII; Paulo Hilário Nascimento SaldivaIV; Luiz Alberto Amador PereiraV; Alfésio Luis Ferreira BragaVI

ISenior Researcher. Center for Environmental Epidemiology Studies, Air Pollution Laboratory, Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil; and Professor of Pulmonology. Centro Universitário de Araraquara - Uniara, Araraquara University Center - School of Medicine, Araraquara, Brazil
IISenior Researcher. Center for Environmental Epidemiology Studies, Air Pollution Laboratory, Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil
IIISenior Researcher. Center for Environmental Epidemiology Studies, Air Pollution Laboratory, Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil; and Assistant Professor. Graduate Program in Public Health, Universidade Católica de Santos - UNISANTOS, Catholic University of Santos - Santos, Brazil
IVFull Professor. Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil
VSenior Researcher. Center for Environmental Epidemiology Studies, Air Pollution Laboratory, Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil; and Assistant Professor. Graduate Program in Public Health, Universidade Católica de Santos - UNISANTOS, Catholic University of Santos - Santos, Brazil
VISenior Researcher. Center for Environmental Epidemiology Studies, Air Pollution Laboratory, Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil; and Assistant Professor. Graduate Program in Public Health, Universidade Católica de Santos - UNISANTOS, Catholic University of Santos - Santos, Brazil

Correspondence to

 

 


ABSTRACT

Over the past 250 years-since the Industrial Revolution accelerated the process of pollutant emission, which, until then, had been limited to the domestic use of fuels (mineral and vegetal) and intermittent volcanic emissions-air pollution has been present in various scenarios. Today, approximately 50% of the people in the world live in cities and urban areas and are exposed to progressively higher levels of air pollutants. This is a non-systematic review on the different types and sources of air pollutants, as well as on the respiratory effects attributed to exposure to such contaminants. Aggravation of the symptoms of disease, together with increases in the demand for emergency treatment, the number of hospitalizations, and the number of deaths, can be attributed to particulate and gaseous pollutants, emitted by various sources. Chronic exposure to air pollutants not only causes decompensation of pre-existing diseases but also increases the number of new cases of asthma, COPD, and lung cancer, even in rural areas. Air pollutants now rival tobacco smoke as the leading risk factor for these diseases. We hope that we can impress upon pulmonologists and clinicians the relevance of investigating exposure to air pollutants and of recognizing this as a risk factor that should be taken into account in the adoption of best practices for the control of the acute decompensation of respiratory diseases and for maintenance treatment between exacerbations.

Keywords: Respiratory System; Air pollution; Pregnancy; Pulmonary disease, chronic obstructive; Asthma; Respiratory tract Infections.


 

 

Introduction

Although the effects of pollution had been described since antiquity, pollution began to have a major impact on the population with the advent of the Industrial Revolution. The rapid urbanization seen worldwide brought about a large increase in energy consumption and in pollutant emissions from stationary fossil fuel burning sources, such as industries, and from mobile sources, such as motor vehicles. Currently, approximately 50% of the people in the world live in cities and urban areas and are exposed to progressively higher levels of air pollutants.(1) The other half, especially in developing countries, uses solid fuels derived from biomass (wood, charcoal, dried animal dung, and agricultural residues) and, to a lesser extent, liquid fuels, as a source of energy for cooking, heating, and lighting.(1,2)

Because of the large contact area between the surface of the respiratory system and the environment, air quality directly affects respiratory health. In addition, a significant quantity of inhaled pollutants reach the systemic circulation through the lungs and can cause deleterious effects on various organs and systems.(3)

Global estimates suggest that external environmental pollution (outdoor pollution) causes 1.15 million deaths worldwide (corresponding to nearly 2% of the total number of deaths) and is responsible for 8.75 million disability-adjusted life years,(4) whereas pollution inside homes causes approximately 2 million premature deaths and results in 41 million disability-adjusted life years.(5) For Brazil, the World Health Organization has estimated that air pollution causes nearly 20,000 deaths/year, a value that is five times as high as the estimated number of deaths from environmental/passive smoking, and that indoor air pollution leads to 10,700 deaths/year.(4,5)

 

Air pollution: sources, site of action, and pathophysiology

Air pollution is a mixture of particles-particulate matter (PM)-and gases released into the atmosphere mainly by industries, motor vehicles, and thermoelectric power plants, as well as from biomass and fossil fuel burning. Pollutants can be classified as primary or secondary. Primary pollutants are released directly into the atmosphere, whereas secondary pollutants result from chemical reactions among primary pollutants.

The major primary pollutants monitored by the major environmental agencies in Brazil and worldwide are nitrogen oxides (NO2 or NOx), volatile organic compounds (VOCs), carbon monoxide (CO), and sulfur dioxide (SO2). One example of a secondary pollutant is ozone (O3), formed by the photo-oxidation-induced chemical reaction of VOCs and NO2 in the presence of ultraviolet rays from sunlight.(6,7)

The most studied pollutant is PM, which can be primary or secondary. It varies in number, size, shape, surface area, and chemical composition depending on its place of production and its emission source. The deleterious effects of PM on human health depend on PM size and chemical composition. The multiple chemical components of PM include a core of elemental or organic carbon; inorganic compounds, such as sulfates and nitrates; transition metal oxides; soluble salts; organic compounds, such as polycyclic aromatic hydrocarbons; and biological materials, such as pollen, bacteria, spores, and animal remains. On the basis of total suspended particle size, PM is classified as follows: constituent particles of up to 30 µm in diameter; constituent particles of less than 10 µm in diameter (PM10 or inhalable fraction); constituent particles of less than 2.5 µm in diameter (PM2.5 or fine PM); and constituent particles of less than 10 nm in diameter (PM0.1 or ultrafine PM).(6,7)

Chart 1 shows the major pollutants monitored by environmental protection agencies in urban areas, as well as their sources, their sites of action in the respiratory system, and their effects on human health.

 

How air pollutants affect the respiratory system

Several mechanisms have been suggested to explain the adverse effects of air pollutants. The most consistent and most widely accepted explanation is that, once in contact with the respiratory epithelium, high concentrations of oxidants and pro-oxidants in environmental pollutants such as PM of various sizes and compositions and in gases such as O3 and nitrogen oxides cause the formation of oxygen and nitrogen free radicals, which in turn induce oxidative stress in the airways. In other words, an increase in free radicals that are not neutralized by antioxidant defenses initiates an inflammatory response with release of inflammatory cells and mediators (cytokines, chemokines, and adhesion molecules) that reach the systemic circulation, leading to subclinical inflammation, which not only has a negative effect on the respiratory system but also causes systemic effects.(6,7)

Latency effects

The effects of pollutants on health can be acute or chronic. Acute effects are manifest shortly after exposure (hours or days). Chronic effects are usually assessed in longitudinal studies over years or decades.(8) Chart 2 summarizes the acute and chronic effects of pollutants on the respiratory system.

 

Susceptible groups

Children

Children are highly susceptible to exposure to air pollutants. Minute ventilation is higher in children than in adults because children have higher basal metabolic rates and engage in more physical activity than do adults, as well as because children spend more time outdoors than do adults. On the basis of body weight, the volume of air passing through the airways of a child at rest is twice that of an adult under similar conditions. Pollutant-induced irritation producing a weak response in adults can result in significant obstruction in children. In addition, the fact that their immune system is not fully developed increases the possibility of respiratory infections.(6,7,9)

Elderly individuals

Elderly individuals are susceptible to the adverse effects of exposure to air pollutants because they have a less efficient immune system (immunosenescence) and a progressive decline in pulmonary function that can lead to airway obstruction and exercise limitation. There is decreased chest wall compliance and lung hyperinflation requiring additional energy expenditure to perform respiratory movements, as well as functional decline of organ systems.(10)

Individuals with pre-existing chronic diseases

The third most susceptible group, regardless of age, comprises individuals with pre-existing chronic diseases affecting mainly the respiratory system (asthma, COPD, and fibrosis) or the circulatory system (arrhythmias, hypertension, and ischemic heart diseases), as well as those with chronic diseases such as diabetes and collagen diseases.(3)

Genetic susceptibility

The production of free radicals and the induction of inflammatory response by pollutants in the respiratory system can be neutralized by the antioxidant agents present in the aqueous layer lining the respiratory epithelium-glutathione S-transferase (GST), superoxide dismutase, catalase, tocopherol, ascorbic acid, and uric acid-which can prevent oxidative stress and represent the first line of defense against the adverse effects of pollutants.(11) Of the antioxidant agents present in the respiratory epithelium, GST is considered the most important(11) and is represented by three major classes of enzymes: GSTM1; GSTP1; and GSTT1.(11)

Polymorphisms in genes encoding the enzymes of the GST family can change the expression or function of these enzymes in the lung tissue and result in different responses to inflammation and oxidative stress and, consequently, in increased susceptibility to the adverse effects of air pollutants.(11) Studies conducted in Mexico showed that children with asthma with a deletion polymorphism of genes encoding the GSTM1 and GSTP1 enzymes had increased susceptibility to O3 exposure, this increased susceptibility being characterized by an increase in biomarkers of nasal inflammation, reduced peak expiratory flow, and increased dyspnea.(12,13)

 

Effects of air pollution during pregnancy

Exposure to air pollutants during pregnancy can impair fetal development and cause intrauterine growth retardation, prematurity, low birth weight, congenital anomalies, and, in cases that are more severe, intrauterine or perinatal death.(14)

The biological mechanisms underlying the effects of air pollutants during pregnancy have yet to be fully elucidated. Extensive cell proliferation, physiological immaturity, accelerated organ development, and changes in metabolism increase fetal susceptibility to maternal inhalation of air pollutants, and the maternal respiratory system can, in turn, be compromised by the action of pollutants, thereby affecting placental transport of oxygen and glucose.(15) In addition, pollutants can affect maternal blood coagulation because of an inflammatory response resulting from oxidative stress, increasing the possibility of placental infarction and chronic villitis.(16)

A meta-analysis of studies published between 1994 and 2003 revealed that a 10-µg/m3 increase in PM10 exposure was associated with a 5% increase in postnatal mortality from all causes and a 22% increase in mortality from respiratory diseases.(17) A study conducted in São Paulo, Brazil, revealed that a 1-µg/m3 increase in PM10 concentration and a 1-ppm increase in CO concentration were associated with a 0.6-g and a 12-g reduction in birth weight, respectively.(18) A study conducted in California, USA, and evaluating 81,186 births found an increased risk of maternal preeclampsia and fetal prematurity associated with higher levels of traffic-generated NOx and PM2.5.(19)

 

Effects of pollutants on the respiratory system

Effects on respiratory symptoms

Epidemiological studies have shown that exposure to gaseous pollutants and PM is associated with a higher incidence of upper airway symptoms, such as rhinorrhea, nasal obstruction, cough, laryngospasm, and vocal fold dysfunction,(20) and lower airway symptoms, such as cough, dyspnea, and wheezing, especially in children.(21) This exposure is also associated with an increase in cough and wheezing in adults with chronic lung disease and in healthy adults.(21)

Effects on pulmonary function

Pulmonary function is an important marker of the effects of air pollution on the exposed population, as well as being an early, objective, and quantitative predictor of cardiorespiratory morbidity and mortality. Studies have demonstrated the acute and chronic effects of pollutants on pulmonary function in children, adolescents, healthy adults, and individuals with a history of respiratory disease.(6,7)

Effects associated with acute exposure

Chang et al.(22) investigated the effects of variations in daily concentrations of PM10, SO2, CO, and NO2 on the pulmonary function of 2,919 students in the 12-16 year age bracket in the city of Taipei, Taiwan. A 1-ppm increase in CO concentration was associated with a 69.8-mL reduction in FVC (95% CI: -115.0 to -24.4) and a 73.7-mL reduction in FEV1 (95% CI: -118.0 to -29.7), with a 1-day lag effect. A 1-ppb increase in SO2 concentration was associated with a 12.9-mL reduction in FVC (95% CI: -20.7 to -5.1) and an 11.7-mL reduction in FEV1 (95% CI: -19.3 to -4.2), also with a 1-day lag effect. Variations in O3 and PM10 concentrations showed a small but significant negative association with FVC and FEV1 on the day of exposure.

A study conducted in London, England, compared pulmonary function parameters in 60 adults with mild or moderate asthma on two different occasions: after a two-hour walk along Oxford Street, the city's main commercial corridor, where only diesel-powered buses and taxis are allowed; and after a two-hour walk through Hyde Park (a city park). At the time of the study, PM2.5 and NO2 levels were, respectively, 3.0 and 6.5 times higher on Oxford Street than in Hyde Park. There was a 6.1% reduction in FEV1 (p = 0.04) and a 5.4% reduction in FVC (p = 0.001) after exposure on Oxford Street in relation to exposure in Hyde Park.(23)

Effects associated with chronic exposure

Gauderman et al. conducted a prospective study following 1,759 children in the 10-18 year age bracket in 12 communities in California, USA, with different levels of NO2, acid vapor, PM2.5, and elemental carbon. After controlling for confounding factors, the authors found that children residing in areas with higher environmental levels of PM showed a significant decline in FEV1 (of approximately 100 mL) when compared with those residing in less polluted areas. The effects were significant even in children without bronchial asthma. The proportion of children with an FEV1 < 80% at age 18 years was five times higher in more polluted communities than in less polluted communities (mean PM2.5 concentrations of 29.0 µg/m3 and 6.0 µg/m3, respectively).(24)

Those same authors investigated pulmonary function in 3,677 individuals, who were followed over an 8-year period (between ages 10 and 18 years) and who lived within 500 m or 1,500 m of a high-traffic road. At age 18 years, the adolescents living closer to the high-traffic road showed an 81.0-mL deficit in FEV1 and a 127.0-mL/s deficit in FEF25-75% when compared with those living farther away.(25)

A cross-sectional study conducted in Germany evaluated 2,593 women (mean age, 54.5 years) in 7 communities. Levels of NO2 and PM10 showed significant negative associations with FEV1, FVC, and FEV1/FVC. An annual increase of 7.0 µg/m3 in PM10 was associated with a 5.0% reduction in FEV1 and a 1.0% reduction in FEV1/FVC, and, for an annual increase of 16.0% in NO2, there was a 4.0% reduction in FEV1 and a 1.0% reduction in FEV1/FVC.(26)

A prospective study conducted in Switzerland evaluated 4,742 adults in the 18-60 year age bracket in 8 communities over an 11-year period. Over the study period, there was a mean drop of 5.3 µg/m3 in PM10 levels. A 10-µg/m3 decline in the mean annual PM10 concentration was associated with statistically significant reductions in the annual rates of decline in FEV1 (of 9%), FEF25-75% (of 16%), and FEV1/FVC (of 6%).(27)

Pollution and bronchial asthma

Epidemiological and toxicological studies have demonstrated the association between air pollution and bronchial asthma.(21) Air pollutants are associated with an increase in the number of emergency room visits and hospitalizations for acute asthma attacks, as well as with an increase in expiratory wheezing, respiratory symptoms, and use of rescue medication.(21)

The prevalence of bronchial asthma has increased worldwide, especially in highly industrialized urban areas. Prospective studies suggest that exposure to air pollutants can lead to the development of new cases of asthma. One example of this is the large increase in the incidence of asthma in China after the recent industrial development and, consequently, the large increase in the concentration of pollutants.(28)

Effects associated with acute exposure

In Athens, Greece, one group of researchers investigated the acute effects of PM10 and SO2 exposure on the number of emergency room visits by children and adolescents in the 0-14 year age bracket between 2001 and 2004. A 10-µg/m3 increase in PM10 and SO2 levels was associated with a 2.2% increase (95% CI: 0.1-5.1) and a 6.0% increase (95% CI: 0.9-11.3), respectively, in the number of asthma-related visits.(29)

A study involving children and adolescents in the 0-18 year age bracket and conducted in Copenhagen, Denmark, between 2001 and 2008, revealed an increase in the number of asthma-related hospitalizations due to increased levels of NOx (OR = 1.11; 95% CI: 1.05-1.17), NO2 (OR = 1.10; 95% CI: 1.04-1.16), PM10 (OR = 1.07; 95% CI: 1.03-1.12), and PM2.5 (OR = 1.09; 95% CI: 1.04-1.13).(30)

An association between increased pollutant levels and hospitalizations for asthma has been observed in the city of Araraquara, located in the center of the sugarcane-producing area of the state of São Paulo, Brazil. During the harvest period, when sugarcane straw burning is the largest pollutant emission source, the number of hospitalizations for asthma was 50% higher than was that during the period when there is no burning (p < 0.001). A 10-µg/m3 increase in the concentrations of PM of up to 30 µm in diameter was associated with an 11.6% increase in the number of hospitalizations (95% CI: 5.4-17.7), with a 1-day lag effect.(31)

A study conducted in the city of Rio Branco, Brazil, showed that, in the forest biomass burning season, the number of asthma-related visits among children under 10 years of age increased in parallel with the increase in PM2.5 concentrations measured in the city.(32)

During the Olympic Games in Atlanta, USA, measures to reduce urban pollution were implemented. During the three weeks of games, traffic counts dropped around 22%. Peak daily levels of O3, NO2, CO, and PM10 decreased 28%, 7%, 19%, and 17%, respectively, in comparison with the three weeks before and the three weeks after the Games. There was a 40% reduction in the number of consultations for asthma among children and an 11-19% decline in the number of asthma-related visits to the emergency rooms of the city among individuals of all ages.(33) During the Olympic Games in Beijing, PM2.5 and O3 concentrations decreased from 78.8 µg/m3 to 46.7 µg/m3 and from 65.8 ppb to 61 ppb, respectively, and the number of asthma-related emergency rooms visits decreased by 41.6%.(34)

Effects associated with chronic exposure

In a prospective study conducted in 12 communities with different O3 levels in California, USA, 3,535 schoolchildren with no history of asthma were followed over a 5-year period. In the follow-up period, 265 children developed asthma. In communities with high O3 concentrations, the risk of developing asthma was 3.3 times higher (95% CI: 1.9-5.8) in children who played three or more sports than in those who did not play any sports. In areas with low O3 concentrations, the number of sports played was not a risk factor for the development of asthma. The same was true for time spent outdoors, which was shown to be a direct risk factor for the development of asthma only in areas with high O3 concentrations.(35)

Ghering et al. followed the first 8 years of life of 3,863 children in communities in the north, west, and center of the Netherlands. At age 8 years, the children underwent allergy testing and bronchial hyperresponsiveness testing. Levels of PM2.5 were associated with a 28% increase in the incidence of asthma, a 29% increase in the prevalence of asthma, and a 15% increase in asthma symptoms.(36)

In Munich, Germany, 2,860 children were followed from birth to age 4 years and 3,061 were followed to age 6 years. The authors categorized residential distance to a main road as follows: < 50 m; 50-250 m; 250-1,000 m; and > 1,000 m. The study showed significant inverse associations between residential distance to a main road and the outcomes analyzed. Among those living less than 50 m from a main road, the highest ORs were for asthma (OR = 1.6; 95% CI: 1.03-2.37), hay fever (OR = 1.6; 95% CI: 1.1-2.3), and allergic sensitization to pollen (OR = 1.4; 95% CI: 1.2-1.6).(37)

A cohort study conducted in Switzerland between 1991 and 2002 and evaluating 2,725 nonsmoking adults in the 18-60 year age bracket showed that those living in more polluted areas were at a higher risk of developing asthma (a 30% increase in risk for every 1-µg/m3 increase in the concentration of traffic-generated PM10).(38)

Pollution and COPD

Patients with COPD are particularly vulnerable to additional stress on the airways caused by aggressive agents. Smoking is recognized as the most important factor for the development of COPD, especially in developed countries. However, over the last 10 years, an increasing number of studies have suggested that there are risk factors other than smoking in the genesis of COPD. These factors include exposure to indoor and outdoor air pollutants, occupational exposure to dust and fumes, history of recurrent respiratory infections in childhood, history of pulmonary tuberculosis, chronic asthma, intrauterine growth retardation, poor nutrition, and low socioeconomic status.(1)

Exposure to air pollution is associated with an increase in respiratory morbidity from COPD, including an increase in respiratory symptoms and a decrease in pulmonary function, as well as being a common cause of exacerbations leading to emergency room visits or hospitalizations.(39) Indoor biomass burning is a significant cause of COPD in nonsmoking women who are exposed to high concentrations of pollutants during cooking activities, especially in rural areas of developing countries, and this significantly contributes to the global increase in the disease.(1,2) While women with COPD caused by smoking have emphysema and goblet cell metaplasia more commonly than do those exposed to biomass burning, the latter group has more severe interlobular septal thickening, more pigment deposition in the lung parenchyma, more small airway fibrosis, and more severe intimal thickening of the pulmonary artery.(39)

Effects associated with acute exposure

An ecological study conducted in Hong Kong, China, investigated the association between air pollutants and hospitalizations for COPD between 2000 and 2004. Significant associations were observed between hospitalizations for COPD and levels of pollutants. The relative risk (RR) of hospitalization for every 10-µg/m3 increase in SO2, NO2, O3, PM10, and PM2.5 concentrations was, respectively, 1.007, 1.026, 1.040, 1.024, and 1.031. The effect started on the day of exposure and lasted until the fifth day, as well as being more pronounced in the winter than in the summer.(40)

A study conducted between 1986 and 1999 and involving 36 American cities showed that a 5-ppb increase in O3 levels and a 10-µg/m3 increase in PM10 levels were associated with an increase of 0.27% (95% CI: 0.1-0.5) and 1.5% (95% CI: 0.9-2.0), respectively, in the number of hospitalizations for COPD. Use of central air conditioning was found to reduce the adverse effects of air pollution.(41)

A study conducted between 2001 and 2003 in city of São Paulo, Brazil, and evaluating 1,769 patients over 40 years of age showed that an increase in the number of COPD-related emergency room visits was associated with increases in air concentrations of PM10 and SO2. Variations in PM10 and SO2 concentrations (28.2 µg/m3 and 7.8 µg/m3, respectively) were associated with a cumulative 6-day increase of 19% and 16% in COPD admissions, respectively. A 10-µg/m3 increase in PM10 concentration was associated with a 6.7% increase in the number of visits on the day of exposure.(42)

Effects of chronic exposure

Schikowski et al. followed 4,757 women in the 54-55 year age bracket in Germany, using diagnostic criteria for COPD established by the Global Initiative for Chronic Obstructive Lung Disease. The prevalence of COPD (stages I-IV) was found to be 4.5 %. A 7-µg/m3 increase in the 5-year mean PM10 concentration was associated with a 1.33 OR (95% CI: 1.03-1.72) for the development of COPD and a 5.1% decline in FEV1 (95% CI: 2.5-7.7). Women living less that 100 m from a high-traffic road were at a higher risk of developing COPD than were those living farther away (OR = 1.8; 95% CI: 1.1-3.0).(26) Those authors suggest that chronic exposure to traffic-generated PM10 increases the risk of developing COPD and accelerates pulmonary function loss.

A study conducted in Denmark followed 57,053 individuals between 1993 and 2004 and showed that 1,786 (3.4%) developed COPD. The authors found a positive association between COPD and exposure to traffic-generated pollutants after controlling for confounding factors, including smoking. The incidence of COPD was associated with the 35-year NO2 mean concentration (RR = 1.08; 95% CI: 1.02-1.14 for an interquartile range of 5.8 µg/m3).(43)

A meta-analysis of 15 studies showed that individuals exposed to biomass burning have a 2.4 higher OR (95% CI: 1.9-3.3) for the development of COPD than do those who were not exposed.(44) A recent meta-analysis of 25 studies showed that the risk in women exposed to biomass burning is similar to that in women who used another type of fuel (OR = 2.4; 95% CI: 1.5-9.9).(2)

In a meta-analysis, Kurmi et al. showed a positive association of use of solid fuel with COPD (OR = 2.8; 95% CI: 1.8-4.0) and chronic bronchitis (OR = 2.3; 95% CI: 1.9-2.8) when compared with use of other types of fuels.(45) The risk is similar to that reported for smokers who developed COPD (OR = 2.5) and is higher than that for individuals who developed COPD because of passive smoking or alpha-1 antitrypsin deficiency. On the basis of a comparison of the 1.1 billion smokers with the 3 billion individuals exposed to high concentrations of pollutants generated by solid fuel burning, Kodgule & Salvi hypothesized that the latter exposure is a more significant risk factor for the development of COPD.(46)

Pollution and acute respiratory infection

Acute lower respiratory tract infection is the leading cause of death in children up to 5 years of age. In this age group, this type of infection causes 2 million deaths per year. Half of such deaths are attributed to indoor exposure to pollutants from solid fuel burning.(46) A meta-analysis of 24 studies showed that indoor exposure to biomass burning increases the risk of pneumonia in children (OR = 1.8; 95% CI: 1.5-2.1).(47) Similarly, a recent meta-analysis of 25 studies found a significant and robust association between indoor biomass burning and acute respiratory infection in children (OR = 3.5; 95% CI: 1.9-6.4).(2)

Effects associated with acute exposure

Host et al. investigated the association of PM10 and PM2.5 concentrations with hospitalization for respiratory infection in 6 French cities between 2000 and 2003. The excess RR of hospitalization for respiratory infection for every 10-µg/m3 increase in PM10 and PM2.5 concentrations was 4.4% (95% CI: 0.9-8.0) and 2.5% (95% CI: 0.1-4.8), respectively. Children under 15 years of age constituted the most susceptible age group.(48)

Belleudi et al. investigated the effects of PM on the number of hospitalizations for pneumonia among individuals over 35 years of age admitted to any of five Roman hospitals between 2001 and 2005. A 10-µg/m3 increase in PM2.5 concentration was associated with a 2.8% increase in the number of hospitalizations for pneumonia, with a 2-day lag effect.(49)

Medina-Ramón et al., in a study conducted between 1986 and 1999 and involving 36 American cities, showed that, during the hottest period, a cumulative 2-day increase of 5 ppb in O3 concentration was associated with a 0.41% increase (95% CI: 0.26-0.57) in the number of hospitalizations for pneumonia. Similarly, a 10-µg/m3 increase in PM10 concentration was associated with a 0.8% increase in the number of hospitalizations for pneumonia on the day of exposure (95% CI: 0.5-1.2).(41)

Effects associated with chronic exposure

Between 2003 and 2005, Neupane et al. conducted a case-control study in Canada in which they investigated long-term exposure to NO2, PM2.5, and SO2 and the risk of hospitalization for pneumonia in individuals over 65 years of age. They evaluated 365 elderly individuals with radiologically confirmed community-acquired pneumonia and 494 controls. The groups were compared on the basis of individual exposure to NO2, PM2.5, and SO2 in the previous year. Long-term (> 1-year) exposure to high levels of NO2 and PM2.5 was significantly associated with hospitalization for community-acquired pneumonia.(50)

A cohort study conducted in the USA showed that a 10-µg/m3 increase in PM2.5 concentration was associated with a 20% increase in the risk of death from pneumonia and influenza in nonsmokers.(51)

Pollution and lung cancer

The World Health Organization estimates that, in 2008, there were 12.7 million new cases of cancer that caused 7.6 million deaths worldwide, the number of new cases of lung cancer and the number of deaths from lung cancer being 1.61 million and 1.18 million, respectively.(52) Studies have shown the effects of exposure to pollutants and the development of lung cancer, which is attributed to the direct action of carcinogens present in pollution and to the chronic inflammation induced by such carcinogens.(7,53)

A prospective study involving 500,000 adults in 50 states in the USA(54) showed that a 14% increase in the incidence of lung cancer was associated with a 10-µg/m3 in PM2.5 concentration. In a study conducted in European countries, 5% and 7% of the various types of lung cancer in nonsmokers and former smokers, respectively, were attributed to the effects of pollution.(55) An analysis of several cohort and case-control studies suggested that, on average, chronic exposure to air pollution increases the risk of lung cancer incidence by 20-30%.(7,56)

Air pollution and mortality

In a review of studies conducted in various countries and investigating the effects of acute changes in pollution levels, it was suggested that a 0.4-1.3% increase in the RR of death is associated with a 10-µg/m3 increase in PM2.5 levels or a 20-µg/m3 increase in PM10 levels.(57) The largest impact on mortality occurs among children under 5 years of age (RR = 1.6%) and among elderly individuals (RR = 2.0%), for every 10-µg/m3 increase in PM10 concentration.(57)

In the USA, the most relevant studies on the chronic effects of air pollution on mortality have estimated a 6-17% increase in cardiopulmonary mortality for a 10-µg/m3 increase in PM2.5 levels.(57)

 

Effects of air pollution on exercise

Air pollution and physical exercise - risks and benefits

During aerobic exercise, the inhaled air enters the airways mostly through the mouth and minute volume and diffusing capacity increase, facilitating the penetration of pollutants.(58) The quantity of ultrafine particles deposited in the respiratory tract is nearly five times higher during moderate exercise than at rest and increases as particle size decreases.(59)

Exercising near a high-traffic road increases carboxyhemoglobin levels (a 30-min run can increase carboxyhemoglobin levels to levels equivalent to those resulting from smoking 10 cigarettes/day) and reduces aerobic performance in athletes.(58)

Although the major recommendations of sports medicine societies do not include precautions against exercising in polluted environments, a recent statement from the American Heart Association(3) on the effects of pollution recommends that intensive exercise be avoided when air quality is unsatisfactory.

A recent review(60) investigating the effects of pollution on athlete performance concluded that exercising in environments with high levels of pollutants sharply reduces pulmonary and vascular function in individuals with asthma and in healthy individuals, and that long-term exercise in polluted environments is associated with reduced pulmonary function and can induce vascular dysfunction, probably due to systemic and airway oxidative stress, leading to reduced exercise performance. In brief, it is recommended that susceptible individuals (those with asthma, those with COPD, patients with cardiovascular disease, elderly individuals, and children) avoid exercising when air quality is poor.

 

Final considerations

Exposure to air pollutants poses a risk to human health as early as in intrauterine life.

Health professionals should recognize the importance of the effects of pollutants in clinical practice and properly assess the exposure profile of patients at home, in the workplace, and in the region of residence. If it is not possible to reduce the emission of pollutants in the short or medium term, it is perfectly possible to counsel patients regarding the adoption of preventive measures to reduce the effects of indoor and outdoor pollutants, reducing the adverse effects associated with this exposure. In addition, physicians should, as appropriate, not only make adjustments to the standard treatment when increases in air pollutant concentrations can aggravate pre-existing diseases but also, as citizens, use their knowledge to promote the adoption of measures to reduce pollutant levels in urban and rural areas.

 

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Correspondence to:
Marcos Abdo Arbex
Rua Dr. Arnaldo, 455, sala 1304
CEP 01246-903, São Paulo, SP, Brasil
Tel. 55 11 3061-8530 or 55 16 9714-2882
Email: arbexma@techs.com.br

Submitted: 23 July 2012.
Accepted, after review: 22 August 2012
Financial support: None.

 

 

* Study carried out at the Center for Environmental Epidemiology Studies, Air Pollution Laboratory, Department of Pathology, University of São Paulo School of Medicine, São Paulo, Brazil.