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Environmental air pollution: respiratory effects

Poluição do ar ambiental: efeitos respiratórios

Ubiratan de Paula Santos1a, Marcos Abdo Arbex2,3a, Alfésio Luis Ferreira Braga3,4a, Rafael Futoshi Mizutani5a, José Eduardo Delfini Cançado6a, Mário Terra-Filho7a, José Miguel Chatkin8,9a

DOI: 10.36416/1806-3756/e20200267

ABSTRACT

Environmental air pollution is a major risk factor for morbidity and mortality worldwide. Environmental air pollution has a direct impact on human health, being responsible for an increase in the incidence of and number of deaths due to cardiopulmonary, neoplastic, and metabolic diseases; it also contributes to global warming and the consequent climate change associated with extreme events and environmental imbalances. In this review, we present articles that show the impact that exposure to different sources and types of air pollutants has on the respiratory system; we present the acute effects-such as increases in symptoms and in the number of emergency room visits, hospitalizations, and deaths-and the chronic effects-such as increases in the incidence of asthma, COPD, and lung cancer, as well as a rapid decline in lung function. The effects of air pollution in more susceptible populations and the effects associated with physical exercise in polluted environments are also presented and discussed. Finally, we present the major studies on the subject conducted in Brazil. Health care and disease prevention services should be aware of this important risk factor in order to counsel more susceptible individuals about protective measures that can facilitate their treatment, as well as promoting the adoption of environmental measures that contribute to the reduction of such emissions.

Keywords: Air pollution; Particulate matter; Respiratory tract diseases; Pulmonary disease, chronic obstructive; Asthma; Respiratory tract infections; Lung neoplasms.

RESUMO

A poluição do ar ambiental é um dos principais fatores de risco de morbidade e mortalidade global. Ela tem impacto direto na saúde humana, sendo responsável pelo aumento de incidência e de óbitos por doenças cardiorrespiratórias, neoplásicas e metabólicas; também contribui para o aquecimento global e para as consequentes alterações do clima associadas a eventos extremos e aos desequilíbrios ambientais. Nesta revisão, apresentamos artigos que evidenciam o impacto da exposição a diferentes fontes e tipos de poluentes do ar no sistema respiratório; apresentamos os efeitos agudos - como aumento de sintomas e no número de atendimentos em serviços de emergência, internações e óbitos - e crônicos - como o aumento da incidência de asma, DPOC e câncer de pulmão, assim como o declínio acelerado da função pulmonar. Também são apresentados e discutidos os efeitos da poluição atmosférica em populações mais suscetíveis e dos efeitos associados à realização de exercícios físicos em ambientes poluídos. Por fim, apresentamos os principais estudos brasileiros sobre o assunto. Os serviços de atenção à saúde e de prevenção de doenças devem ficar atentos a esse importante fator de risco para orientar indivíduos mais suscetíveis sobre medidas de proteção que possam facilitar seu tratamento, além de estimular a adoção de medidas ambientais que contribuam para a redução dessas emissões.

Palavras-chave: Poluição do ar; Material particulado; Doenças respiratórias; Doença pulmonar obstrutiva crônica; Asma; Infecções respiratórias; Neoplasias pulmonares.

INTRODUCTION



A major problem in the world today is air pollution, not only because of its impact on climate change but also because of its impact on public and individual health, being an important risk factor for increased morbidity and mortality.



Although exposure to air pollution has records that date back more than 20 centuries ago, until the well-known episodes of a sudden increase in pollutants that occurred in the Meuse Valley (Belgium, 1930), in Donora (Pennsylvania, USA, 1948), and above all in London (United Kingdom, 1952), studies on the effects of exposure to air pollutants were restricted to work environments and to exposure to toxic agents used in wars.(1) It was only from the mid-20th century onward that the subject began to be studied more and more,(2) with the first document on the effects of air pollution on health, prepared by the WHO and published in 1958, recommending that pollutant levels be reduced for health protection.(3,4)



Air pollution is estimated to have been responsible for approximately 5 million deaths worldwide in 2017, 70% of which being caused by outdoor environmental air pollution. Environmental and household air pollution jointly rank fifth among the five leading risk factors for death worldwide (Table 1).(5)



AIR POLLUTION AND ITS MAJOR SOURCES



The majority of emissions of pollutants are a result of human activity. Currently, the main sources of pollution in urban areas are motor vehicles and industries. (6) In some countries, including Brazil, the main source of environmental pollution originating from non-urban areas is the burning of biomass (sugarcane fields, pastures, savanna, and forests). Natural emissions, such as those from dust storms in large desert areas, those from accidental fires, and nitrogen oxides (NOx) emissions from lightning, may contribute secondarily to the generation of air pollutants.(6,7)



Pollutants are classified as either primary or secondary. Primary pollutants are those emitted directly into the atmosphere by industries, thermoelectric power plants, and motor vehicles powered by fuels. Primary pollutants include sulfur dioxide (SO2); nitrogen oxides (NOx: NO and NO2); particulate matter (PM)-total suspended particles less than 10 µm in aerodynamic diameter (PM10) and less than 2.5 µm in aerodynamic diameter (PM2.5)-; and carbon monoxide (CO). In some countries, volatile organic compounds (VOCs) and metals are also monitored. Fine and ultrafine particles, since they have a higher surface/mass ratio and can be transferred to the systemic circulation, have a more marked effect.(8) Secondary pollutants are those formed from chemical reactions induced by NOx-catalyzed photochemical oxidation of VOCs, which, in the presence of ultraviolet rays from sunlight, give rise to ozone.(9) Other secondary pollutants are formed through a process of nucleation and condensation of gaseous pollutants (NO2 and SO2) and acid mists, such as NOx and secondary PM, formed by sulfates and nitrates.(1,7,10)



Exposure to air pollution varies widely across countries, regions, cities, and households. A study based on 2017 data estimates that 42% of people were exposed to fine PM (PM2.5) above concentrations considered to be of minimal risk and 43% of those people were exposed to ozone worldwide.(5)



IMPACT ON HEALTH



Globally, most deaths and years of life lost due to premature death or lived with disability (disability-adjusted life years) that are secondary to air pollution exposure are a result of cardiopulmonary disease, lung cancer, or type 2 diabetes (Table 2).(5) A study using a novel approach(11) reported values that were higher than those calculated by the Global Burden of Disease (GBD) models(12): an estimated 8.8 million deaths globally in 2015(11) versus 4.24 million.(12) In addition, the loss of life expectancy was reported to be 2.9 years worldwide in 2015.(13) In two of the aformentioned studies, the number of environmental air pollution-related deaths in 2015 in Brazil was estimated to be 52,300(12) and 102,000,(11) environmental air pollution being the ninth leading risk factor for mortality.(12)



Why and how air pollution has an impact on health: mechanisms involved in respiratory effects



The damage caused by particulate and gaseous pollutants depends on the inhaled concentration of such pollutants, the defenses of the respiratory system, and the solubility of gaseous pollutants. The possible mechanisms involved in cardiorespiratory effects include inflammation and oxidative stress induced by reactive oxygen and nitrogen species (RONS) generated by inhaled pollutants.(14,15) Recent studies suggest a relevant role for inhaled environmentally persistent free radicals (EPFR) produced by combustion of catechols, phenols, and hydroquinones, which can remain in the air for up to 21 days.(16)



Chronic or acute inhalation of PM, O3, and EPFR generates RONS, which trigger an inflammatory process and amplify it through the endogenous production of more RONS. If RONS production overcomes antioxidant defenses, there is activation of the mitogen-activated protein kinase (MAPK) complex, involved in the activation of nuclear transcription factors, such as NF-κB and AP-1, which stimulate the synthesis of RNA and the production of pro-inflammatory cytokines IL-8 and TNF-α, possibly inducing the formation of DNA adducts.(14,17) Air pollution has also been associated with epigenetic effects that, although potentially reversible without the occurrence of mutations, can produce changes in DNA expression, potentiating the inflammatory effects of pollutants.(8)



Air pollution has also been associated with reduced function of regulatory T lymphocytes, increased IgE levels, and increased production of CD4+ and CD8+ T lymphocytes, along with a greater Th2 response to stimuli by antigens in polluted environments, which would be associated with diseases such as rhinitis and asthma.(6,8)



Air pollution: respiratory effects



Air pollution is associated with various health effects, in addition to respiratory effects (Figure 1). Acute respiratory effects are those associated with recent exposure (hours or days), whereas chronic ones are a result of prolonged exposure, usually longer than 6 months.



With regard to acute effects, there is a consistent association between increased pollutant levels and increased numbers of emergency room visits, hospitalizations, and deaths, especially among individuals with chronic respiratory diseases, children, and elderly individuals.(18) A study involving 112 cities in the USA found a 1.68% increase in mortality due to respiratory disease for every 10 μg/m3 increase in PM2.5 concentration.(19) A systematic review and meta-analysis of 110 time-series studies conducted in several regions of the world revealed a 1.51% increase in mortality from respiratory diseases for every 10 μg/m3 increase in PM2.5 concentration.(20) In addition, a study conducted in Latin America(21) revealed a 2% increase in the risk of mortality from respiratory and cardiovascular diseases for every 10 µg/m3 increase in PM2.5 concentration, which is in line with the findings of studies conducted in Europe and North America.



The effects of chronic exposure have been associated with increased overall mortality from respiratory diseases, increased incidence of asthma and COPD, increased incidence of and mortality from lung cancer, reduced lung function, and a deficit in lung development during childhood.(22,23) One of the first studies on the subject, conducted in six major cities in the USA, revealed that the risk of death from cardiopulmonary diseases was 26% higher among individuals living in more polluted cities than among those living in less polluted cities.(24) These findings have been confirmed in other studies, including a prospective study involving 500,000 adults from all 50 U.S. states that revealed 9% and 18% increases in the risk of mortality from cardiopulmonary diseases and lung cancer, respectively, that were associated with a 10-µg/m3 increase in PM2.5 concentration.(25)



Pollution and rhinitis



A growing number of studies show an association between environmental air pollution and increased incidence and exacerbation of rhinitis. Authors suggest that genetic factors alone do not appear to be sufficient to justify the increase observed in the prevalence and exacerbation of allergic diseases, in particular, eczema, rhinitis and asthma. Exposure to PM10 and PM2.5 appears as a factor that has a major impact in increasing the prevalence of these diseases, especially in children and adolescents.(6,27)



Pollution and asthma



Exposure to pollutants such as PM, NO2, ozone, and carbon, as well as to motor vehicle traffic-related air pollution, is associated with a higher number of exacerbations, hospitalizations, and deaths in patients with asthma.(6,28,29)



One of the first studies evaluating the acute effects of air pollution, which involved 3,676 children from 12 locations in the state of California, USA,(30) showed that children with asthma who were exposed to NO2, PM10, and PM2.5 had a higher prevalence of respiratory symptoms and a greater need for medication than did children without asthma. The most significant association was with exposure to NO2, with a 2.7 times higher prevalence of symptoms for every 24 ppb increase in NO2 concentration. A study conducted in Hubei province, China, with 4,454 individuals who died from asthma between 2013 and 2018 found increases of 7%, 9%, and 11% in mortality that were associated with PM2.5, O3, and NO2, respectively.(31)



In recent years, studies have revealed that air pollution is also associated with an increased incidence of asthma, especially in children and adolescents,(6,23,32-34) with less robust data on adults. (35,36) One of the first prospective studies on the subject, also conducted in California, showed an association between chronic exposure to ozone and an increased incidence of asthma.(37) Another study evaluated the global incidence of air pollution-related asthma. For 2015, 4 milllion new cases of asthma (13% of global incidence) were estimated to be associated with exposure to NO2 in children and young people under 18 years of age, 150,000 of which were in Brazil and Paraguay (aggregate data). (38) In adults, a study conducted in Australia showed that individuals exposed to NO2 for at least 5 years and those living less than 200 m from a major road were at an increased risk of developing asthma and experiencing a marked decline in lung function.(39)



Pollution and COPD



Since the 1990s, epidemiological studies have shown an association between air pollution and acute respiratory events in individuals with COPD, with an increased number of exacerbations, emergency room visits, hospitalizations, and deaths.(40) One of the first studies on the subject, which evaluated hospitalizations secondary to COPD exacerbation that were associated with exposure to pollutants, found that, for every 10 μm/m3 increase in PM10 concentration, there was a 2.5% increase in hospitalizations. A recent study(41) involving 303,887 individuals in the United Kingdom revealed that a 5 μg/m3 increase in PM2.5 concentration was associated with 83 mL and 62 mL reductions in FEV1 and FVC, respectively, as well as with a 52% increase in COPD prevalence.



More recent studies suggest that exposure to pollutants is associated with an increased incidence of COPD.(23,41) A cohort study conducted in Norway involving 57,000 individuals found an 8% increase in COPD incidence that was associated with a 5.8 µg/m3 increase in NO2 concentration.(42) Another recently published cohort study,(43) involving 7,071 individuals in six U.S. metropolitan regions between 2000 and 2018, found an increased percentage of areas of pulmonary emphysema, as assessed by HRCT, that were associated with exposure to O3, PM2.5, NOx, and carbon particles. A study analyzing 2017 data estimated that 1.1 million COPD deaths were attributable to air pollution worldwide,(5) representing 34.6% of all COPD deaths in that year.(44)



Pollution and lung function



In recent years, evidence has been accumulating on the effects of air pollution on lung function, confirming the findings of earlier studies.(45,46) The effects of air pollution appear to be more marked during the first years of life, including during the intrauterine period. Jedrychowski et al.(47) evaluated maternal exposure to PM2.5 during the second trimester of pregnancy and found lower FEV1 and FVC values (differences of 87 mL and 91 mL, respectively) at 5 years of age in children whose mothers had higher exposure to PM2.5. In the city of Guangzhou, China, a study of highly polluted areas (an annual average PM10 concentration between 80 and 96 µg/m3) showed that higher levels of pollution are associated with a reduction in the growth rate of FEF25-75% and FEV1 in boys.(48)



A prospective study(49) that followed children from age 10 to age 18 years in 12 cities in California found a reduction in the total growth of FEV1 that was associated with PM2.5, NO2, acid vapor, and carbon particles. The proportion of young individuals who, at age 18 years, had an FEV1 of less than 80% of the predicted value was 4.9 times higher (a prevalence of 7.9%) in the communities with the highest levels of PM2.5 than in the communities with the lowest levels.



A study conducted in the city of São Paulo, Brazil, involving taxi drivers and traffic controllers revealed that exposure to high levels of PM2.5 was associated with a nonsignificant reduction in FEV1 and FVC, but there was a significant increase in FEF25-75%, suggesting possible interstitial changes due to exposure to polllutants.(50)



Pollution and respiratory infections



Exposure to air pollutants increases the risk of upper and lower airway infections. Exposure to PM was responsible for 433,000 deaths from respiratory infections globally in 2017, especially affecting children and elderly individuals.(5) A systematic review estimated a 12% increase in the risk of pneumonia in children for every annual average increase of 10 μg/m3 in PM2.5 concentration.(51) In line with this, a systematic review and meta-analysis using six European cohorts and involving 16,000 children showed an up to 30% increase in NO2 exposure-related risk of pneumonia.(35)



Current studies suggest a possible contributing effect of air pollution on the spread of SARS-CoV-2 (COVID-19). A study conducted in Italy revealed that, in cities where the concentrations of air pollutants were higher before the epidemic, there was an accelerated spread of the virus, as well as a higher number of infected individuals, when compared with less polluted cities. (52,53) A recently published study that characterized, with the use of satellites, the global concentration of PM2.5 and its anthropogenic fraction, estimated that exposure to PM would have contributed 15% (95% CI: 7-33%) to global COVID-19 mortality, being an important cofactor for increasing the risk of COVID-19 morbidity and mortality.(54,55)



Pollution and lung cancer



The International Agency for Research on Cancer considers environmental air pollution carcinogenic to humans, because it increases the risk of lung cancer. (56) Although a positive association has also been found between exposure to this type of pollution and bladder cancer, a causal relationship has yet to be established. According to global data,(5) an estimated 2.16 million new cases of lung cancer and 1.88 million lung cancer deaths occurred in 2017, lung cancer being the leading cause of cancer death among men and the third leading cause of cancer death among women. It is estimated that 14% (n = 265,000) of lung cancer deaths are attributable to environmental air pollution,(5) a proportion that ranges from 1% to 25% across countries. The mean risk for developing lung cancer ranges across studies from 20% to 30% for a 10 µg/m3 increase in PM10 concentration and a 5 µg/m3 increase in PM2.5 concentration.(56,57)



Air pollution can induce genotoxic effects that include formation of DNA adducts, breaks in DNA strands, and damage to DNA bases due to oxidation, genetic mutations, chromosomal damage to somatic cells, gametic mutations, and oncogenic transformation. Molecular epidemiological studies in humans reveal associations between the frequencies of DNA damage (such as adducts in lymphocytes) and cytogenetic damage (such as chromosomal translocations and micronuclei) and exposures to PM and/or carcinogenic polycyclic aromatic hydrocarbons. Multiple proven effects lend plausibility to the association between air pollution and lung cancer development through a direct effect, as well as to tumor development via oxidative stress and persistent inflammation.(56)



Pollution and physical exercise



Low physical activity is an important risk factor for mortality and was associated with 1.26 million deaths in 2017. Regular mild- to moderate-intensity exercise contributes to reducing or delaying the onset of chronic diseases by up to 10 years.(58)



Exercising in air-polluted environments can have health consequences in susceptible populations, such as children, the elderly, and individuals with chronic diseases, as well as resulting in poorer physical performance in athletes.(59,60) A study conducted in communities with high ozone concentrations in California(61) found that the risk of developing asthma was 3.3 times higher in children playing three or more sports per week than in children playing no sports. Sports had no effect in cities with low ozone concentrations.



In healthy individuals, the respiratory effects of air pollution do not appear to be significant.(62) A study conducted in London, United Kingdom,(63) compared changes over time in lung function and sputum inflammatory markers in adults with asthma who walked for 2 h in a park and, on a separate occasion, along a busy traffic street. Participants with asthma showed a significant decline in lung function and an increase in inflammatory markers after walking along a busy traffic street.(63) A study with a similar design that compared healthy individuals, individuals with COPD, and individuals with stable coronary disease revealed that, in all participants, walking for 2 h in a park led to an increase in lung function, an increase that was absent or reduced after walking along a busy traffic street.(59) Studies in humans(59) and studies using mathematical models(64,65) have shown that, for healthy individuals and even for individuals with chronic diseases, mild-to-moderate exercise in polluted environments, even where pollution levels are above the reference values recommended by the WHO,(7) has beneficial effects that override the effects of inhalation of an increased load of pollutants. Therefore, the balance of studies suggests that mild-to-moderate exercise is beneficial even in polluted places.(8,60,64,65)



Other pulmonary conditions



Recent studies have shown an association of exposure to air pollution with sleep apnea,(8) increased risk of bronchiolitis obliterans, increased risk of death in lung transplant recipients,(66) and increased risk of progression to interstitial lung disease.(67)



SUSCEPTIBLE/VULNERABLE POPULATIONS



Intrinsic and extrinsic factors increase the vulnerability and/or susceptibility of individuals to the adverse effects of air pollutants. In addition to age, having a preexisting chronic disease, such as asthma, COPD, pulmonary fibrosis, arrhythmias, hypertension, ischemic heart disease, diabetes, autoimmune diseases, and obesity, makes individuals more vulnerable.(8,68)



Individuals with poor socioeconomic status are most vulnerable, since they are likely to be exposed for longer periods on their way to work and tend to live closer to industrial areas. In addition, they live in overcrowded households, in areas without appropriate green spaces, and have diets poor in fruits and vegetables, which are rich in antioxidants.(8,68)



Pregnant women



Exposure to air pollutants during pregnancy can compromise fetal development and cause intrauterine growth restriction, prematurity, low birth weight, congenital anomalies, and intrauterine and perinatal death.(8,69)



Intense cell proliferation, physiological immaturity, accelerated organ development, and changes in metabolism increase the fetus' susceptibility to inhalation of air pollutants by the mother, and the mother in turn can have her respiratory system compromised by the action of pollutants, which can thereby affect the transport of oxygen and nutrients across the placenta. Exposure to high concentrations of PM is associated with placental inflammation, abnormal trophoblastic invasion, and decreased placental angiogenesis, impacting fetal development.(69)



Children



Worldwide, 93% of children live in environments in which air pollutant concentrations are above those recommended by the WHO.(70) The WHO estimates that one in every four deaths of children under 5 years of age is directly or indirectly related to environmental risks.(70) Global analyses for 2015 estimated the number of deaths from respiratory infections resulting from exposure to environmental air pollution among children aged 5 years or younger to be 727,000.(71) Children have higher minute ventilation and higher basal metabolic rates and engage in more physical activity than do adults, as well as spending more time outdoors.



The fact that children's immune system is not fully developed increases their susceptibility to respiratory infections.(8,70) Inside the womb, fetuses can be affected by pollutants inhaled by the mother, with can have health consequences in adulthood, such as an increased risk of asthma.(8,70,72)



Elderly individuals



The elderly population is growing because of increased life expectancy and steadily declining birth rates. In 2013, elderly individuals aged 80 years or older represented 14% of the world population.



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 lung function, which can lead to decreased exercise tolerance. Wu et al.,(73) in a study conducted in Beijing, China, observed a greater increase in hospitalizations for air pollution-related pneumonia in the elderly compared with younger age groups. A cohort study conducted in the USA(74) that used Medicare data showed that, between 2000 and 2012, acute exposures to fine PM and ozone during the warmest seasons of the year (spring and summer) were associated with an increased risk of all-cause mortality among elderly individuals. The same effect was observed even on days with concentrations below the air quality limits set by the U.S. Environmental Protection Agency.



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. Polymorphisms in genes responsible for controlling oxidative stress (NQO1, GSTM1, and GSTP1) and in inflammatory genes (TNF) alter the presence and intensity of respiratory symptoms and change lung function and the risk of developing asthma in response to pollutants.(75)



Of the antioxidant agents present in the respiratory epithelium, the GST family is considered one of the most important, being represented by three major classes of enzymes: GSTM1; GSTP1; and GSTT1.(76) Polymorphisms in genes encoding the enzymes of the GST family can change the expression or function of these enzymes in the lung tissue, resulting in different responses to inflammation and oxidative stress and, consequently, in increased susceptibility to the adverse effects of air pollutants.(76) A study conducted by Prado et al.(77) found a marked loss of lung function in sugarcane workers exposed to air pollution who had deletions in the GSTM1 and GSTT1 genes.



Studies have also revealed the epigenetic effect of exposure to PM, an effect that can override genetic susceptibility. Altered epigenetic regulation of white blood cells and various other tissue cells, especially PM-induced changes in DNA methylation, appears to contribute to the health effects associated with air pollution.(23)



BRAZIL: RELEVANT STUDIES ON THE EFFECTS OF AIR POLLUTION



Since the late 1970s, the effects of air pollutants, from both vehicular and industrial sources and from biomass burning, have been systematically studied in Brazil.



Air pollution from fossil fuel burning



Over the past 30 years, 170 studies on the subject conducted in Brazil have been published. From 1975 onward, the Air Pollution Experimental Laboratory of the University of São Paulo School of Medicine Department of Pathology, in the city of São Paulo, located in the state of São Paulo, Brazil, carried out experimental and epidemiological studies to assess the adverse effects of exposure to air pollutants. The first study exposed rats to the environmental air in the city of São Paulo and to the environmental air in the city of Atibaia, also located in the state of São Paulo and where the air, at the time, was considered cleaner. After 6 months of exposure, there were changes in mucus rheological properties, destruction of cilia, and, consequently, increased bacterial colonization of the respiratory epithelium, all of which led to the death of 50% of the rats exposed to the air in the city of São Paulo.(78) In parallel, using models from ecological time series studies, another study showed that daily increases in NOx concentration were associated with increased mortality from respiratory diseases in children aged 5 years or younger in the city of São Paulo.(79) Another study by the group showed that lung autopsy samples from residents of the city of Guarulhos, located in the state of São Paulo and where pollution levels were high at the time of the study, presented more evidence of histopathologic damage than did those from residents of the cities of Ourinhos and Ribeirão Preto, also located in the state of São Paulo but where pollution levels were lower, even after controlling for smoking.(80)



In another study, mice were exposed to different concentrations of inhaled fine PM, and even those exposed to low concentrations showed oxidative stress, inflammation, and lung tissue damage.(81)



Ecological time series studies have shown associations between increased emergency room visits in children with respiratory diseases and increased air pollution(82); between increased hospitalizations for respiratory diseases in children and adolescents and increased concentrations of PM10 and SO2(83); and between increased emergency room visits due to pneumonia and influenza,(84) as well as due to asthma and COPD(85,86) in adults and increased air pollution.



A study conducted on workers exposed to environmental air pollution in the city of São Paulo, located in the state of São Paulo, Brazil, revealed that, those with the highest level of exposure had a reduction in FVC compared with those with the lowest level of exposure.(50) Chart 1 summarizes the major studies on the respiratory impact of urban air pollution conducted in Brazil.



Air pollution from biomass burning



Over the past 20 years, studies conducted in Brazil have assessed the impacts that forest fires (especially in the Brazilian Amazon) and pre-harvest sugarcane burning (especially in the state of São Paulo) have on the health of the exposed population (Chart 2).



Studies conducted in urban areas located in sugarcane producing regions in the state of São Paulo have shown that, during the sugarcane burning season, there were increases in emergency room visits for inhalation therapy(87) and for pneumonia,(88) as well as an increase in hospitalizations of children and elderly individuals for all respiratory diseases,(89) specifically for asthma.(90) In Monte Aprazível, a town in the state of São Paulo, rhinitis prevalence increased and lung function decreased in children during the sugarcane burning season.(91) Another study revealed that, during manual harvesting of burnt cane, workers had exacerbated respiratory symptoms, reduced lung function, reduced antioxidant enzyme activity, and increased oxidative stress markers.(77) In another group of sugarcane workers, it was found that, during the sugarcane burning season, there were changes in mucus properties and impairment of nasal mucociliary clearance.(92)



Emissions from fires in the Amazon region can be transported long distances and, in addition to affecting the global climate,(93) can impact the health of children and the elderly.(94,95) Studies conducted in the state of Mato Grosso have shown that increased exposure to PM contributed to increased hospitalizations of children less than 5 years of age due to respiratory diseases(96) and to acute decreases in PEF.(97)



In an experimental study in mice, animals received repeated intranasal instillation of PM from different sources, and PM from biomass burning were found to be more toxic than PM from vehicular traffic.(98)



FINAL CONSIDERATIONS



Environmental air pollution affects billions of people every day worldwide, having a major impact on morbidity and mortality, as well as contributing to global warming.



The presence of chronic systemic diseases increases the susceptibility of individuals to the adverse effects of air pollutants, manifesting from mild forms of illness to death, which occurs in patients with increased susceptibility. Recent studies show that exposure to air pollutants can cause asthma, COPD, and lung cancer. Exposure of pregnant women to air pollutants has serious adverse effects on the fetus that, if not lethal, can result in compromised health in childhood, adolescence, adulthood, and old age. Regular physical exercise can contribute to minimizing the effects of air pollution.



The most effective measures for reducing the impact of air pollution on human health are those related to reducing emissions. Expansion of public transportation, the use of cleaner fuels in vehicles, industries, and households, as well as a change in building construction standards, which require a lot of energy, are feasible and necessary measures to reduce global warming and its direct effects on human health.(99) It is estimated that reducing emission levels to those recommended by the WHO and the Paris Agreement can lead to up to 60% decrease in pollution-related deaths annually. (11) In this context, physicians should be able to inform and advise the population about healthy eating habits, regular physical exercise, and chronic disease control. Physicians should also contribute to strengthening the necessary measures to reduce emissions in favor of environmental recovery. The current SARS-CoV-2 virus pandemic, which follows the SARS and MERS outbreaks in 2000 and 2012, respectively, shows that we cannot adopt a passive behavior regarding environmental imbalances caused by the way the planet is developed and occupied.



REFERENCES



1. Stanek LW, Brown JS, Stanek J, Gift J, Costa DL. Air pollution toxicology--a brief review of the role of the science in shaping the current understanding of air pollution health risks. Toxicol Sci. 2011;120 Suppl 1:S8-S27. https://doi.org/10.1093/toxsci/kfq367



2. Bell ML, Davis DL. Reassessment of the lethal London fog of 1952: novel indicators of acute and chronic consequences of acute exposure to air pollution. Environ Health Perspect. 2001;109 Suppl 3(Suppl 3):389-394. https://doi.org/10.1289/ehp.01109s3389



3. World Health Organization. Institutional Repository for Information Sharing [homepage on the Internet]. Geneva: WHO; c1958 [cited 2020 Jul 1]. Air pollution: fifth report of the Expert Committee on Environmental Sanitation [‎meeting held in Geneva from 18 to 23 November 1957]‎. Available from: https://apps.who.int/iris/handle/10665/40416



4. World Health Organization. Evolution of WHO air quality guidelines: past, present and future. Copenhagen: WHO Regional Office for Europe; 2017.



5. GBD 2017 Risk Factor Collaborators. Global, regional, and national comparative risk assessment of 84 behavioural, environmental and occupational, and metabolic risks or clusters of risks for 195 countries and territories, 1990-2017: a systematic analysis for the Global Burden of Disease Study 2017 [published correction appears in Lancet. 2019 Jan 12;393(10167):132] [published correction appears in Lancet. 2019 Jun 22;393(10190):e44]. Lancet. 2018;392(10159):1923-1994.



6. Guarnieri M, Balmes JR. Outdoor air pollution and asthma. Lancet. 2014;383(9928):1581-1592. https://doi.org/10.1016/S0140-6736(14)60617-6



7. World Health Organization. Institutional Repository for Information Sharing [homepage on the Internet]. Copenhagen: WHO Regional Office for Europe; c2006 [cited 2020 Jul 1]. Air quality guidelines global update 2005: particulate matter, ozone, nitrogen dioxide and sulfur dioxide. Available from: https://apps.who.int/iris/handle/10665/107823



8. Schraufnagel DE, Balmes JR, Cowl CT, De Matteis S, Jung SH, Mortimer K, et al. Air Pollution and Noncommunicable Diseases: A Review by the Forum of International Respiratory Societies' Environmental Committee, Part 1: The Damaging Effects of Air Pollution. Chest. 2019;155(2):409-416. https://doi.org/10.1016/j.chest.2018.10.042



9. Zhang R, Lei W, Tie X, Hess P. Industrial emissions cause extreme urban ozone diurnal variability. Proc Natl Acad Sci U S A. 2004;101(17):6346-6350. https://doi.org/10.1073/pnas.0401484101



10. Monge ME, D'Anna B, Mazri L, Giroir-Fendler A, Ammann M, Donaldson DJ, et al. Light changes the atmospheric reactivity of soot. Proc Natl Acad Sci U S A. 2010;107(15):6605-6609. https://doi.org/10.1073/pnas.0908341107



11. Lelieveld J, Klingmüller K, Pozzer A, Burnett RT, Haines A, Ramanathan V. Effects of fossil fuel and total anthropogenic emission removal on public health and climate. Proc Natl Acad Sci U S A. 2019;116(15):7192-7197. https://doi.org/10.1073/pnas.1819989116



12. Cohen AJ, Brauer M, Burnett R, Anderson HR, Frostad J, Estep K, et al. Estimates and 25-year trends of the global burden of disease attributable to ambient air pollution: an analysis of data from the Global Burden of Diseases Study 2015 [published correction appears in Lancet. 2017 Jun 17;389(10087):e15] [published correction appears in Lancet. 2018 Apr 21;391(10130):1576]. Lancet. 2017;389(10082):1907-1918. https://doi.org/10.1016/S0140-6736(17)30505-6



13. Lelieveld J, Pozzer A, Pöschl U, Fnais M, Haines A, Münzel T. Loss of life expectancy from air pollution compared to other risk factors: a worldwide perspective. Cardiovasc Res. 2020;116(11):1910-1917. https://doi.org/10.1093/cvr/cvaa025



14. Rao X, Zhong J, Brook RD, Rajagopalan S. Effect of Particulate Matter Air Pollution on Cardiovascular Oxidative Stress Pathways. Antioxid Redox Signal. 2018;28(9):797-818. https://doi.org/10.1089/ars.2017.7394



15. Al-Kindi SG, Brook RD, Biswal S, Rajagopalan S. Environmental determinants of cardiovascular disease: lessons learned from air pollution. Nat Rev Cardiol. 2020;17(10):656-672. https://doi.org/10.1038/s41569-020-0371-2



16. Sly PD, Cormier SA, Lomnicki S, Harding JN, Grimwood K. Environmentally Persistent Free Radicals: Linking Air Pollution and Poor Respiratory Health?. Am J Respir Crit Care Med. 2019;200(8):1062-1063. https://doi.org/10.1164/rccm.201903-0675LE



17. Zhao J, Li M, Wang Z, Chen J, Zhao J, Xu Y, et al. Role of PM2.5 in the development and progression of COPD and its mechanisms. Respir Res. 2019;20(1):120. https://doi.org/10.1186/s12931-019-1081-3



18. Brunekreef B, Holgate ST. Air pollution and health. Lancet. 2002;360(9341):1233-1242. https://doi.org/10.1016/S0140-6736(02)11274-8



19. Zanobetti A, Schwartz J. The effect of fine and coarse particulate air pollution on mortality: a national analysis. Environ Health Perspect. 2009;117(6):898-903. https://doi.org/10.1289/ehp.0800108



20. Atkinson RW, Kang S, Anderson HR, Mills IC, Walton HA. Epidemiological time series studies of PM2.5 and daily mortality and hospital admissions: a systematic review and meta-analysis. Thorax. 2014;69(7):660-665. https://doi.org/10.1136/thoraxjnl-2013-204492



21. Fajersztajn L, Saldiva P, Pereira LAA, Leite VF, Buehler AM. Short-term effects of fine particulate matter pollution on daily health events in Latin America: a systematic review and meta-analysis. Int J Public Health. 2017;62(7):729-738. https://doi.org/10.1007/s00038-017-0960-y



22. Chen Z, Salam MT, Eckel SP, Breton CV, Gilliland FD. Chronic effects of air pollution on respiratory health in Southern California children: findings from the Southern California Children's Health Study. J Thorac Dis. 2015;7(1):46-58.



23. Thurston GD, Kipen H, Annesi-Maesano I, Balmes J, Brook RD, Cromar K, et al. A joint ERS/ATS policy statement: what constitutes an adverse health effect of air pollution? An analytical framework. Eur Respir J. 2017;49(1):1600419. https://doi.org/10.1183/13993003.00419-2016



24. Dockery DW, Pope CA 3rd, Xu X, Spengler JD, Ware JH, Fay ME, et al. An association between air pollution and mortality in six U.S. cities. N Engl J Med. 1993;329(24):1753-1759. https://doi.org/10.1056/NEJM199312093292401



25. Pope CA 3rd, Burnett RT, Thun MJ, Calle EE, Krewski D, Ito K, et al. Pope CA 3rd, Burnett RT, Thun MJ, et al. Lung cancer, cardiopulmonary mortality, and long-term exposure to fine particulate air pollution. JAMA. 2002;287(9):1132-1141. https://doi.org/10.1001/jama.287.9.1132



26. Peters A, Hoffmann B, Brunekreef B, Künzli N, Joss MK, Probst-Hensch N, et al. The Health Impact of Air Pollution. An expert report of the International Society for Environmental Epidemiology (ISEE) and the European Respiratory Society (ERS). Lausanne: ERS; 2019.



27. Brandt EB, Myers JM, Ryan PH, Hershey GK. Air pollution and allergic diseases. Curr Opin Pediatr. 2015;27(6):724-735. https://doi.org/10.1097/MOP.0000000000000286



28. Huang SK, Zhang Q, Qiu Z, Chung KF. Mechanistic impact of outdoor air pollution on asthma and allergic diseases [published correction appears in J Thorac Dis. 2015 Oct;7(10):E521]. J Thorac Dis. 2015;7(1):23-33.



29. Orellano P, Quaranta N, Reynoso J, Balbi B, Vasquez J. Effect of outdoor air pollution on asthma exacerbations in children and adults: Systematic review and multilevel meta-analysis. PLoS One. 2017;12(3):e0174050. https://doi.org/10.1371/journal.pone.0174050



30. McConnell R, Berhane K, Gilliland F, London SJ, Vora H, Avol E, et al. Air pollution and bronchitic symptoms in Southern California children with asthma. Environ Health Perspect. 1999;107(9):757-760. https://doi.org/10.1289/ehp.99107757



31. Liu Y, Pan J, Zhang H, Shi C, Li G, Peng Z, et al. Short-Term Exposure to Ambient Air Pollution and Asthma Mortality. Am J Respir Crit Care Med. 2019;200(1):24-32. https://doi.org/10.1164/rccm.201810-1823OC



32. Anderson HR, Favarato G, Atkinson RW. Long-term exposure to air pollution and the incidence of asthma: meta-analysis of cohort studies. Air Qual Atmos Health. 2013;6:47-56. https://doi.org/10.1007/s11869-011-0144-5



33. McConnell R, Islam T, Shankardass K, Jerrett M, Lurmann F, Gilliland F, et al. Childhood incident asthma and traffic-related air pollution at home and school. Environ Health Perspect. 2010;118(7):1021-1026. https://doi.org/10.1289/ehp.0901232



34. Bowatte G, Lodge C, Lowe AJ, Erbas B, Perret J, Abramson MJ, et al. The influence of childhood traffic-related air pollution exposure on asthma, allergy and sensitization: a systematic review and a meta-analysis of birth cohort studies. Allergy. 2015;70(3):245-256. https://doi.org/10.1111/all.12561



35. Jacquemin B, Siroux V, Sanchez M, Carsin AE, Schikowski T, Adam M, et al. Jacquemin B, Siroux V, Sanchez M, et al. Ambient air pollution and adult asthma incidence in six European cohorts (ESCAPE). Environ Health Perspect. 2015;123(6):613-621. https://doi.org/10.1289/ehp.1408206



36. Young MT, Sandler DP, DeRoo LA, Vedal S, Kaufman JD, London SJ. Ambient air pollution exposure and incident adult asthma in a nationwide cohort of U.S. women. Am J Respir Crit Care Med. 2014;190(8):914-921. https://doi.org/10.1164/rccm.201403-0525OC



37. McDonnell WF, Abbey DE, Nishino N, Lebowitz MD. Long-term ambient ozone concentration and the incidence of asthma in nonsmoking adults: the AHSMOG Study. Environ Res. 1999;80(2 Pt 1):110-121. https://doi.org/10.1006/enrs.1998.3894



38. Achakulwisut P, Brauer M, Hystad P, Anenberg SC. Global, national, and urban burdens of paediatric asthma incidence attributable to ambient NO2 pollution: estimates from global datasets. Lancet Planet Health. 2019;3(4):e166-e178. https://doi.org/10.1016/S2542-5196(19)30046-4



39. Bowatte G, Erbas B, Lodge CJ, Knibbs LD, Gurrin LC, Marks GB, et al. Traffic-related air pollution exposure over a 5-year period is associated with increased risk of asthma and poor lung function in middle age. Eur Respir J. 2017;50(4):1602357. https://doi.org/10.1183/13993003.02357-2016



40. Li J, Sun S, Tang R, Qiu H, Huang Q, Mason TG, et al. Major air pollutants and risk of COPD exacerbations: a systematic review and meta-analysis. Int J Chron Obstruct Pulmon Dis. 2016;11:3079-3091. https://doi.org/10.2147/COPD.S122282



41. Doiron D, de Hoogh K, Probst-Hensch N, Fortier I, Cai Y, De Matteis S, et al. Air pollution, lung function and COPD: results from the population-based UK Biobank study. Eur Respir J. 2019;54(1):1802140. https://doi.org/10.1183/13993003.02140-2018



42. Andersen ZJ, Hvidberg M, Jensen SS, Ketzel M, Loft S, Sørensen M, et al. Chronic obstructive pulmonary disease and long-term exposure to traffic-related air pollution: a cohort study. Am J Respir Crit Care Med. 2011;183(4):455-461. https://doi.org/10.1164/rccm.201006-0937OC



43. Wang M, Aaron CP, Madrigano J, Hoffman EA, Angelini E, Yang J, et al. Association Between Long-term Exposure to Ambient Air Pollution and Change in Quantitatively Assessed Emphysema and Lung Function. JAMA. 2019;322(6):546-556. https://doi.org/10.1001/jama.2019.10255



44. GBD 2017 Causes of Death Collaborators. Global, regional, and national age-sex-specific mortality for 282 causes of death in 195 countries and territories, 1980-2017: a systematic analysis for the Global Burden of Disease Study 2017 [published correction appears in Lancet. 2019 Jun 22;393(10190):e44] [published correction appears in Lancet. 2018 Nov 17;392(10160):2170]. Lancet. 2018;392(10159):1736-1788.



45. Schwartz J. Lung function and chronic exposure to air pollution: a cross-sectional analysis of NHANES II. Environ Res. 1989;50(2):309-321. https://doi.org/10.1016/S0013-9351(89)80012-X



46. Ackermann-Liebrich U, Leuenberger P, Schwartz J, Schindler C, Monn C, Bolognini G, et al. Lung function and long term exposure to air pollutants in Switzerland. Study on Air Pollution and Lung Diseases in Adults (SAPALDIA) Team. Am J Respir Crit Care Med. 1997;155(1):122-129. https://doi.org/10.1164/ajrccm.155.1.9001300



47. Jedrychowski WA, Perera FP, Maugeri U, Mroz E, Klimaszewska-Rembiasz M, Flak E, et al. Effect of prenatal exposure to fine particulate matter on ventilatory lung function of preschool children of non-smoking mothers. Paediatr Perinat Epidemiol. 2010;24(5):492-501. https://doi.org/10.1111/j.1365-3016.2010.01136.x



48. He QQ, Wong TW, Du L, Jiang ZQ, Gao Y, Qiu H, et al. Effects of ambient air pollution on lung function growth in Chinese schoolchildren. Respir Med. 2010;104(10):1512-1520. https://doi.org/10.1016/j.rmed.2010.04.016



49. Gauderman WJ, Avol E, Gilliland F, Vora H, Thomas D, Berhane K, et al. The effect of air pollution on lung development from 10 to 18 years of age [published correction appears in N Engl J Med. 2005 Mar 24;352(12):1276]. N Engl J Med. 2004;351(11):1057-1067. https://doi.org/10.1056/NEJMoa040610



50. Santos UP, Garcia ML, Braga AL, Pereira LA, Lin CA, de André PA, et al. Association between Traffic Air Pollution and Reduced Forced Vital Capacity: A Study Using Personal Monitors for Outdoor Workers. PLoS One. 2016;11(10):e0163225. https://doi.org/10.1371/journal.pone.0163225



51. Mehta S, Shin H, Burnett R, North T, Cohen AJ. Ambient particulate air pollution and acute lower respiratory infections: a systematic review and implications for estimating the global burden of disease. Air Qual Atmos Health. 2013;6(1):69-83. https://doi.org/10.1007/s11869-011-0146-3



52. Conticini E, Frediani B, Caro D. Can atmospheric pollution be considered a co-factor in extremely high level of SARS-CoV-2 lethality in Northern Italy?. Environ Pollut. 2020;261:114465. https://doi.org/10.1016/j.envpol.2020.114465



53. Setti L, Passarini F, Gennaro G, Di Gilio A, Palmisani J, Buono P, et al. Evaluation of the potential relationship between Particulate Matter (PM) pollution and COVID-19 infection spread in Italy. Societá Italiana di Medicina Ambientale [Internet]; 2020. Available from: https://www.guapo-air.org/sites/default/files/2020-03/Evaluation%20of%20the%20potential%20relationship%20between%20Particulate%20Matter%20%28PM%29%20pollution%20and%20COVID-19%20infection%20spread%20in%20Italy.pdf



54. Wu X, Nethery RC, Sabath MB, Braun D, Dominici F. Air pollution and COVID-19 mortality in the United States: Strengths and limitations of an ecological regression analysis. Sci Adv. 2020;6(45):eabd4049. https://doi.org/10.1126/sciadv.abd4049



55. Pozzer A, Dominici F, Haines A, Witt C, Münzel T, Lelieveld J. Regional and global contributions of air pollution to risk of death from COVID-19. Cardiovasc Res. 2020;116(14):2247-2253. https://doi.org/10.1093/cvr/cvaa288



56. World Health Organization. International Agency for Research on Cancer [homepage on the Internet]. Lyon: IARC; 2015 [cited 2020 Jul 1]. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. Outdoor Air Pollution. vol 109. Available from: https://publications.iarc.fr/Book-And-Report-Series/Iarc-Monographs-On-The-Identification-Of-Carcinogenic-Hazards-To-Humans/Outdoor-Air-Pollution-2015



57. Hamra GB, Guha N, Cohen A, Laden F, Raaschou-Nielsen O, Samet JM, et al. Outdoor particulate matter exposure and lung cancer: a systematic review and meta-analysis [published correction appears in Environ Health Perspect. 2014 Sep;122(9):A236]. Environ Health Perspect. 2014;122(9):906-911. https://doi.org/10.1289/ehp/1408092



58. Handschin C, Spiegelman BM. The role of exercise and PGC1alpha in inflammation and chronic disease. Nature. 2008;454(7203):463-469. https://doi.org/10.1038/nature07206



59. Sinharay R, Gong J, Barratt B, Ohman-Strickland P, Ernst S, Kelly FJ, et al. Sinharay R, Gong J, Barratt B, et al. Respiratory and cardiovascular responses to walking down a traffic-polluted road compared with walking in a traffic-free area in participants aged 60 years and older with chronic lung or heart disease and age-matched healthy controls: a randomised, crossover study [published correction appears in Lancet. 2018 Jan 27;391(10118):308]. Lancet. 2018;391(10118):339-349. https://doi.org/10.1016/S0140-6736(17)32643-0



60. Giles LV, Koehle MS. The health effects of exercising in air pollution. Sports Med. 2014;44(2):223-249. https://doi.org/10.1007/s40279-013-0108-z



61. McConnell R, Berhane K, Gilliland F, London SJ, Islam T, Gauderman WJ, et al. Asthma in exercising children exposed to ozone: a cohort study [published correction appears in Lancet 2002 Mar 9;359(9309):896]. Lancet. 2002;359(9304):386-391. https://doi.org/10.1016/S0140-6736(02)07597-9



62. Zuurbier M, Hoek G, Oldenwening M, Meliefste K, van den Hazel P, Brunekreef B. Respiratory effects of commuters' exposure to air pollution in traffic. Epidemiology. 2011;22(2):219-227. https://doi.org/10.1097/EDE.0b013e3182093693



63. McCreanor J, Cullinan P, Nieuwenhuijsen MJ, Stewart-Evans J, Malliarou E, Jarup L, et al. Respiratory effects of exposure to diesel traffic in persons with asthma. N Engl J Med. 2007;357(23):2348-2358. https://doi.org/10.1056/NEJMoa071535



64. Johan de Hartog J, Boogaard H, Nijland H, Hoek G. Do the health benefits of cycling outweigh the risks?. Environ Health Perspect. 2010;118(8):1109-1116. https://doi.org/10.1289/ehp.0901747



65. Tainio M, de Nazelle AJ, Götschi T, Kahlmeier S, Rojas-Rueda D, Nieuwenhuijsen MJ, et al. Can air pollution negate the health benefits of cycling and walking?. Prev Med. 2016;87:233-236. https://doi.org/10.1016/j.ypmed.2016.02.002



66. Nawrot TS, Vos R, Jacobs L, Verleden SE, Wauters S, Mertens V, et al. The impact of traffic air pollution on bronchiolitis obliterans syndrome and mortality after lung transplantation. Thorax. 2011;66(9):748-754. https://doi.org/10.1136/thx.2010.155192



67. Rice MB, Li W, Schwartz J, Di Q, Kloog I, Koutrakis P, et al. Ambient air pollution exposure and risk and progression of interstitial lung abnormalities: the Framingham Heart Study. Thorax. 2019;74(11):1063-1069. https://doi.org/10.1136/thoraxjnl-2018-212877



68. Schraufnagel DE, Balmes JR, Cowl CT, De Matteis S, Jung SH, Mortimer K, et al. Air Pollution and Noncommunicable Diseases: A Review by the Forum of International Respiratory Societies' Environmental Committee, Part 2: Air Pollution and Organ Systems. Chest. 2019;155(2):417-426. https://doi.org/10.1016/j.chest.2018.10.041



69. Choe SA, Jang J, Kim MJ, Jun YB, Kim SY. Association between ambient particulate matter concentration and fetal growth restriction stratified by maternal employment. BMC Pregnancy Childbirth. 2019;19(1):246. https://doi.org/10.1186/s12884-019-2401-9



70. World Health Organization. Air pollution and child health-Prescribing Clean Air. World Health Organization, Geneva: WHO; 2018.



71. Lelieveld J, Haines A, Pozzer A. Age-dependent health risk from ambient air pollution: a modelling and data analysis of childhood mortality in middle-income and low-income countries. Lancet Planet Health. 2018;2(7):e292-e300. https://doi.org/10.1016/S2542-5196(18)30147-5



72. Bharadwaj P, Zivin JG, Mullins JT, Neidell M. Early-Life Exposure to the Great Smog of 1952 and the Development of Asthma. Am J Respir Crit Care Med. 2016;194(12):1475-1482. https://doi.org/10.1164/rccm.201603-0451OC



73. Wu J, Wu Y, Tian Y, Wu Y, Wang M, Wang X, et al. Association between ambient fine particulate matter and adult hospital admissions for pneumonia in Beijing, China. Atmospheric Environ. [published online ahead of print, 2020 Jun 15]. https://doi.org/10.1016/j.atmosenv.2020.117497 https://doi.org/10.1016/j.atmosenv.2020.117497



74. Di Q, Dai L, Wang Y, Zanobetti A, Choirat C, Schwartz JD, et al. Association of Short-term Exposure to Air Pollution With Mortality in Older Adults. JAMA. 2017;318(24):2446-2456. https://doi.org/10.1001/jama.2017.17923



75. Yang IA, Fong KM, Zimmerman PV, Holgate ST, Holloway JW. Genetic susceptibility to the respiratory effects of air pollution. Thorax. 2008;63(6):555-563. https://doi.org/10.1136/thx.2007.079426



76. Minelli C, Wei I, Sagoo G, Jarvis D, Shaheen S, Burney P. Interactive effects of antioxidant genes and air pollution on respiratory function and airway disease: a HuGE review. Am J Epidemiol. 2011;173(6):603-620. https://doi.org/10.1093/aje/kwq403



77. Prado GF, Zanetta DM, Arbex MA, Braga AL, Pereira LA, de Marchi MR, et al. Burnt sugarcane harvesting: particulate matter exposure and the effects on lung function, oxidative stress, and urinary 1-hydroxypyrene. Sci Total Environ. 2012;437:200-208. https://doi.org/10.1016/j.scitotenv.2012.07.069



78. Saldiva PH, King M, Delmonte VL, Macchione M, Parada MA, Daliberto ML, et al. Respiratory alterations due to urban air pollution: an experimental study in rats. Environ Res. 1992;57(1):19-33. https://doi.org/10.1016/S0013-9351(05)80016-7



79. Saldiva PH, Lichtenfels AJ, Paiva PS, Barone IA, Martins MA, Massad E, et al. Association between air pollution and mortality due to respiratory diseases in children in São Paulo, Brazil: a preliminary report. Environ Res. 1994;65(2):218-225. https://doi.org/10.1006/enrs.1994.1033



80. Souza MB, Saldiva PH, Pope CA 3rd, Capelozzi VL. Respiratory changes due to long-term exposure to urban levels of air pollution: a histopathologic study in humans. Chest. 1998;113(5):1312-1318. https://doi.org/10.1378/chest.113.5.1312



81. Riva DR, Magalhães CB, Lopes AA, Lanças T, Mauad T, Malm O, et al. Low dose of fine particulate matter (PM2.5) can induce acute oxidative stress, inflammation and pulmonary impairment in healthy mice. Inhal Toxicol. 2011;23(5):257-267. https://doi.org/10.3109/08958378.2011.566290



82. Lin CA, Martins MA, Farhat SC, Pope CA 3rd, Conceição GM, Anastácio VM, et al. Air pollution and respiratory illness of children in São Paulo, Brazil. Paediatr Perinat Epidemiol. 1999;13(4):475-488. https://doi.org/10.1046/j.1365-3016.1999.00210.x



83. Braga AL, Conceição GM, Pereira LA, Kishi HS, Pereira JC, Andrade MF, et al. Air pollution and pediatric respiratory hospital admissions in São Paulo, Brazil. J Environ Med. 1999;1(2):95-102. https://doi.org/10.1002/(SICI)1099-1301(199904/06)1:2<95::AID-JEM16>3.0.CO;2-S



84. Martins LC, Latorre Mdo R, Cardoso MR, Goncalves FL, Saldiva PH, Braga AL. Air pollution and emergency room visits due to pneumonia and influenza in São Paulo, Brazil [Article in Portuguese]. Rev Saude Publica. 2002;36(1):88-94. https://doi.org/10.1590/S0034-89102002000100014



85. Martins LC, Latorre Mdo R, Saldiva PH, Braga AL. Air pollution and emergency room visits due to chronic lower respiratory diseases in the elderly: an ecological time-series study in São Paulo, Brazil. J Occup Environ Med. 2002;44(7):622-627. https://doi.org/10.1097/00043764-200207000-00006



86. Arbex MA, de Souza Conceição GM, Cendon SP, Arbex FF, Lopes AC, Moysés EP, et al. Urban air pollution and chronic obstructive pulmonary disease-related emergency department visits. J Epidemiol Community Health. 2009;63(10):777-783. https://doi.org/10.1136/jech.2008.078360



87. Arbex MA, Böhm GM, Saldiva PH, Conceição GM, Pope AC 3rd, Braga AL. Assessment of the effects of sugar cane plantation burning on daily counts of inhalation therapy. J Air Waste Manag Assoc. 2000;50(10):1745-1749. https://doi.org/10.1080/10473289.2000.10464211



88. Arbex MA, Pereira LA, Carvalho-Oliveira R, Saldiva PH, Braga AL. The effect of air pollution on pneumonia-related emergency department visits in a region of extensive sugar cane plantations: a 30-month time-series study. J Epidemiol Community Health. 2014;68(7):669-674. https://doi.org/10.1136/jech-2013-203709



89. Cançado JE, Saldiva PH, Pereira LA, Lara LB, Artaxo P, Martinelli LA, et al. The impact of sugar cane-burning emissions on the respiratory system of children and the elderly. Environ Health Perspect. 2006;114(5):725-729. https://doi.org/10.1289/ehp.8485



90. Arbex MA, Martins LC, de Oliveira RC, Pereira LA, Arbex FF, Cançado JE, et al. Air pollution from biomass burning and asthma hospital admissions in a sugar cane plantation area in Brazil. J Epidemiol Community Health. 2007;61(5):395-400. https://doi.org/10.1136/jech.2005.044743



91. Riguera D, André PA, Zanetta DM. Sugar cane burning pollution and respiratory symptoms in schoolchildren in Monte Aprazível, Southeastern Brazil. Rev Saude Publica. 2011;45(5):878-886. https://doi.org/10.1590/S0034-89102011005000052



92. Goto DM, Lança M, Obuti CA, Galvão Barbosa CM, Nascimento Saldiva PH, Trevisan Zanetta DM, et al. Effects of biomass burning on nasal mucociliary clearance and mucus properties after sugarcane harvesting. Environ Res. 2011;111(5):664-669. https://doi.org/10.1016/j.envres.2011.03.006



93. Longo KM, Freitas SR, Andreae MO, Yokelson R, Artaxo P. Biomass burning in Amazonia: Emissions, long-range transport of smoke and its regional and remote impacts Amazonia and Global Change (2009) Geophys Monogr Ser. Vol. 186. Washington DC: AGU; 2009. p. 207-232. https://doi.org/10.1029/2008GM000847



94. do Carmo CN, Hacon S, Longo KM, Freitas S, Ignotti E, Ponce de Leon A, et al. Association between particulate matter from biomass burning and respiratory diseases in the southern region of the Brazilian Amazon [Article in Portuguese]. Rev Panam Salud Publica. 2010;27(1):10-16.



95. Ignotti E, Valente JG, Longo KM, Freitas SR, Hacon Sde S, Netto PA. Impact on human health of particulate matter emitted from burnings in the Brazilian Amazon region. Rev Saude Publica. 2010;44(1):121-130. https://doi.org/10.1590/S0034-89102010000100013



96. Silva AM, Mattos IE, Ignotti E, Hacon Sde S. Particulate matter originating from biomass burning and respiratory. Rev Saude Publica. 2013;47(2):345-352. https://doi.org/10.1590/S0034-8910.2013047004410



97. Jacobson Lda S, Hacon Sde S, de Castro HA, Ignotti E, Artaxo P, Saldiva PH, et al. Acute effects of particulate matter and black carbon from seasonal fires on peak expiratory flow of schoolchildren in the Brazilian Amazon. PLoS One. 2014;9(8):e104177. https://doi.org/10.1371/journal.pone.0104177



98. Mazzoli-Rocha F, Carvalho GM, Lanzetti M, Valença SS, Silva LF, Saldiva PH, et al. Respiratory toxicity of repeated exposure to particles produced by traffic and sugar cane burning. Respir Physiol Neurobiol. 2014;191:106-113. https://doi.org/10.1016/j.resp.2013.11.004



99. Landrigan PJ, Fuller R, Acosta NJR, Adeyi O, Arnold R, Basu NN, et al. The Lancet Commission on pollution and health [published correction appears in Lancet. 2018 Feb 3;391(10119):430]. Lancet. 2018;391(10119):462-512. https://doi.org/10.1016/S0140-6736(17)32345-0



100. Sobral HR. Air pollution and respiratory diseases in children in São Paulo, Brazil. Soc Sci Med. 1989;29(8):959-964. https://doi.org/10.1016/0277-9536(89)90051-8



101. Saldiva PH, Pope CA 3rd, Schwartz J, Dockery DW, Lichtenfels AJ, Salge JM, et al. Air pollution and mortality in elderly people: a time-series study in Sao Paulo, Brazil. Arch Environ Health. 1995;50(2):159-163. https://doi.org/10.1080/00039896.1995.9940893



102. Braga AL, Saldiva PH, Pereira LA, Menezes JJ, Conceição GM, Lin CA, et al. Health effects of air pollution exposure on children and adolescents in São Paulo, Brazil. Pediatr Pulmonol. 2001;31(2):106-113. https://doi.org/10.1002/1099-0496(200102)31:2<106::AID-PPUL1017>3.0.CO;2-M



103. Conceição GM, Miraglia SG, Kishi HS, Saldiva PH, Singer JM. Air pollution and child mortality: a time-series study in São Paulo, Brazil. Environ Health Perspect. 2001;109 Suppl 3(Suppl 3):347-350. https://doi.org/10.1289/ehp.109-1240551



104. Martins MC, Fatigati FL, Véspoli TC, Martins LC, Pereira LA, Martins MA, et al. Martins MC, Fatigati FL, Véspoli TC, et al. Influence of socioeconomic conditions on air pollution adverse health effects in elderly people: an analysis of six regions in São Paulo, Brazil. J Epidemiol Community Health. 2004;58(1):41-46. https://doi.org/10.1136/jech.58.1.41



105. Mauad T, Rivero DH, de Oliveira RC, Lichtenfels AJ, Guimarães ET, de Andre PA, et al. Chronic exposure to ambient levels of urban particles affects mouse lung development. Am J Respir Crit Care Med. 2008;178(7):721-728. https://doi.org/10.1164/rccm.200803-436OC



106. Gouveia N, Corrallo FP, Leon ACP, Junger W, Freitas CU. Air pollution and hospitalizations in the largest Brazilian metropolis. Rev Saude Publica. 2017;51:117. https://doi.org/10.11606/S1518-8787.2017051000223



107. de Barros Mendes Lopes T, Groth EE, Veras M, Furuya TK, de Souza Xavier Costa N, Ribeiro Júnior G, et al. Pre- and postnatal exposure of mice to concentrated urban PM2.5 decreases the number of alveoli and leads to altered lung function at an early stage of life. Environ Pollut. 2018;241:511-520. https://doi.org/10.1016/j.envpol.2018.05.055



108. Rodrigues PCO, Ignotti E, Rosa AM, Hacon SS. Spatial distribution of asthma-related hospitalizations of the elderly in the Brazilian Amazon. Rev Bras Epidemiol. 2010;13(3):523-532. https://doi.org/10.1590/S1415-790X2010000300015



109. de Oliveira Alves N, Vessoni AT, Quinet A, Fortunato RS, Kajitani GS, Peixoto MS, et al. Biomass burning in the Amazon region causes DNA damage and cell death in human lung cells. Sci Rep. 2017;7(1):10937. https://doi.org/10.1038/s41598-017-11024-3



 

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