covid
Buscar en
Medicina Universitaria
Toda la web
Inicio Medicina Universitaria Impact of air pollution in respiratory allergic diseases
Journal Information
Vol. 18. Issue 73.
Pages 212-215 (October - December 2016)
Share
Share
Download PDF
More article options
Visits
6830
Vol. 18. Issue 73.
Pages 212-215 (October - December 2016)
Review article
Open Access
Impact of air pollution in respiratory allergic diseases
Visits
6830
S.N. González-Díaz, A. Arias-Cruz
Corresponding author
aarias45@hotmail.com

Corresponding author at: Centro Regional de Alergia e Inmunología Clínica, Hospital Universitario “Dr. José Eleuterio González”, Universidad Autónoma de Nuevo León, Av. Madero y Gonzalitos s/n, Col. Mitras Centro, C.P. 64460 Monterrey, Nuevo León, Mexico.
, C. Macouzet-Sánchez, A.B. Partida-Ortega
Regional Center of Allergy and Clinical Immunology, “Dr. José Eleuterio González” University Hospital, Autonomous University of Nuevo León, Monterrey, Nuevo León, Mexico
This item has received

Under a Creative Commons license
Article information
Abstract
Full Text
Bibliography
Download PDF
Statistics
Abstract

Allergic respiratory disease, which includes allergic rhinoconjunctivitis and asthma, is one of the most common diseases, with a major impact on a patient's quality of life. Air pollution is one of the main factors associated with the development of allergic respiratory disease, it has been shown to impair lung development in children and adolescents. The origins of particulate matter produced from various sources, including those issued by traffic and the burning of fuels such as coal, gasoline and diesel. Diesel emissions represent the majority of the particulate matter in urban air pollution. It has been found that the co-exposure of diesel emissions and airborne allergens increases allergen-specific IgE levels, severity of asthma, inflammation and airway hyper-responsiveness. In vivo and in vitro studies have reported the activation of anti-transcription and pro-inflammatory mediators. Polycyclic aromatic hydrocarbons, metal components or metabolites may increase due to the formation of oxygen reactive species that interact with DNA, producing different types of damage as oxidative damage.

Keywords:
Air pollution
Environment
Allergy
Asthma
Allergic rhinitis
Full Text
Introduction

Allergic respiratory disease (ARD) is a frequent atopic condition, manifesting through allergic rhinoconjuntivitis and asthma. Affecting up to 40% of the population worldwide and with a significant impact over the quality of life of those who suffer from it.1,2 In recent years there has been a considerable increase of air pollutants due to the development of large cities with high industrial activity and linked to an ever increasing number of cars; thus becoming an emergent problem in many countries.3 In the US, the cost of asthma attributable to ozone and nitrogen dioxide exposure is 441 million dollars a year, 202 million dollars a year in Los Angeles alone.4 In a different American study, estimations suggest a cost of 18million dollars a year in health services directly or indirectly attributable to asthma crises linked to exposure to traffic-derivate pollutants.5

The development of an allergic disease takes place due to the interaction of genetic predisposition and environmental determinants. Air pollution is one of the main environmental factors linked to the onset of ARD, as well as its exacerbations.6Air pollution has been proven to alter the pulmonary development of children and teenagers.7,8

Air pollution

Air pollution is defined as the alteration of the pureness and quality of air caused by the emission of chemical or biological substances released naturally or produced by man and his everyday activities. Among these are particulate matter (PM) with a diameter of less than 10μm (PM 10), inhalable fine particulates if their diameter is less than 2.5μm (PM2.5) and ultrafine particulates (UFPs) which are smaller than 0.1μm.9According to the World Health Organization (WHO), PM2.5 is 25μm/m3, and the daily allowed exposure limit for PM10 is 50μm/m3.10As reported, every increase of 10mg/m3 of PM10 was linked to an 0.46% increase in the mortality rate in the US.11 In Mexico, the Official Mexican Standard (NOM by its Spanish acronym) NOM-025-SSA1-2014 establishes the permissible limit values for concentrations of PM10 and PM2.5 suspended particles in the environment, which are, for particles under 10 micrometers (PM10) and 2.5 micrometers (PM2.5), an average limit of 24h of 75μm/m3 and 45μm/m3 respectively.12

PMs are produced from several sources, including those emitted by traffic, carbon combustion, gas, diesel and other types of fuels. Secondary emissions from diesel represent the majority of particulate matter from urban air pollution.13 The size of the particle, its surface and its chemical composition determines the risk that it represents in a patient who is exposed to it regularly. According to their size, the MPs can easily access the airway, even reaching the alveoli and thereby causing direct damage as a result of irritation, or provoking oxidative stress by activating various signal transmission pathways and transcription factors.14

In 2008, Gluckman et al.15showed that prenatal and postnatal exposure to air pollution negatively influences developmental plasticity, resulting in a wide range of diseases in childhood. Recently, Fleisch et al.,16proved that exposure to contaminated air during pregnancy is associated with an increased risk of adverse birth outcomes. However, the negative impact of air pollution goes further. Deng et al.,17 found a significant association between the development of asthma and allergic rhinitis in Chinese children whose mothers were exposed to air pollution during pregnancy. All these findings could be explained by different epigenetic mechanisms, such as DNA methylation, where the different contaminants play an important role in the development of allergic diseases.

Ozone (O3) is a molecule composed of 3 oxygen atoms. It is formed from the dissociation of an oxygen molecule (O2) by joining a released atom to an O2 molecule. Tropospheric ozone is a colorless gas created by photochemical reactions between nitrogen oxide and volatile organic compounds from the combustion of gasoline, diesel or fossil fuels.18 It acts as a strong oxidant that has been associated with persistent structural damage and injury to lung tissue, which leads to exacerbation of asthma symptoms.8 Further epidemiological studies are needed to know and document the morbidity and mortality rates associated with ozone exposure.

Traffic smoke has been shown to have an association with accelerated growth of allergies and asthma in childhood.19 This process involves the residue oil fly ash (ROFA), which is a complex mixture of sulfates and metals, specifically vanadium, that have the potential ability to influence immunity and cause damage to various systems, being a critical factor in the hyper-responsiveness and injury of the airway.20

Air pollution and aerospheric allergies

Air pollutants have the ability to modify the allergenicity of certain pollens. They facilitate dispersion of the pollen allergen into smaller fractions. Specifically ozone, in an experimental model, produced a structural change in the coating layers of the pollen, inducing modification in pollen-plant interactions, pollen-human cells and potentiating the allergenic properties of pollen.21

Kim et al.22 reported that exposure to ozone was significantly associated with the rate of new sensitization to outdoor allergens, which could explain the mechanism for the increase in the prevalence of allergic rhinitis. Likewise, it has been found that the co-exposure to diesel and airborne allergens emissions increases the levels of allergen-specific IgE, asthma severity, and airway inflammation and hyper-reactivity.23

Air pollution and ARD

According to the World Health Organization (WHO), several million people around the world suffer from rhinitis, and an estimated 300million have asthma, and these diseases significantly affect the patient's quality of life and family environment, leading to a negative impact on the socioeconomic well-being of society. The major problem of environmental pollution in industrialized countries is responsible for nearly 2million deaths per year in developing countries.24

Air pollutants have the ability to affect the presentation of asthma in different ways: acting as a stimulator or trigger, aggravating pre-existing airway inflammation, and modifying the response to aeroallergens or substances that act as irritants in the airways.25

The way in which air pollutants impact the development of asthma and allergies has been the subject of investigation and controversy. Two studies in California found that contaminants related to vehicular traffic can cause asthma in older children. Another study reported that children exercising in areas with high concentrations of ozone were more likely to develop asthma.26 A Japanese study looked for an association between asthma and nitrogen oxide (NO2) levels, with a sample universe of 2506 children studied over a period of 4 years, and concluded that children living at a distance of less than 50m from roads with heavy vehicle loads were more prone to asthma development.27

There is a “modern” indicator of pollution, NO2, which has been attributed to an increase in the presentation of asthma and wheezing.28 However, in another study, the agent was unrelated to the prevalence of allergic symptoms. What was demonstrated was the increased risk of recent symptoms of both allergic rhinitis and asthma in schoolchildren associated with SO2 and CO levels.29

Diesel engine particles (DEP), the main constituents of urban air pollutants, have been shown to be able to modulate the pulmonary immune response by stimulating the function of dendritic cells and thus induce inflammatory processes in the airway.30 Diesel emissions contain small particles of various sizes, ranging from nanoparticles to coarser particles, the latter of which are the most easily drawn into the lungs and can be kept suspended in the atmosphere for long periods of time. These consist of a carbonaceous core with a large surface area to which other chemicals are adhered, such as polycyclic aromatic hydrocarbons (PAHs) as well as heterocyclic, aldehydes and aliphatic hydrocarbons.31

These diesel particles are able to reach the cell's surface and activate molecular mechanisms by stimulating human airway epithelial cells to produce cytokines, which lead to inflammation. In in vitro studies, once these particles reach the epithelial cells, IL-8, macrophages, granulocyte colony stimulating factor, T cells and intracellular adhesion molecules (ICAMs) are released, which are found in significantly higher amounts in patients with asthma. It has also been shown to affect gene expression by inducing eotaxin from epithelial cells.32

Salvi et al., studied the effects of high-level diesel inhalation in a chamber; a significant increase in inflammatory cells (neutrophils, B lymphocytes, mast cells, CD4 and CD8 lymphocytes) was demonstrated, along with the positive regulation of ICAM.33Reactive oxygen species, due to the effects of DEP and their consequent release of IL-8, ICAM-1, GM-CSF and RANTES, are inhibited on exposure to antioxidant agents such as N-acetylcysteine.32

The mechanisms which cause double chain DNA break in pulmonary cells have been found to be secondary to the impact of air pollution in the mRNA expression in humans due to the activity of the telomerase and phosphorylation of H2AX histone. DNA damage induced by particulate matter made of metals (copper, iron, nickel, vanadium, zinc and lead) and polycyclic aromatic hydrocarbons (PAHs) is metabolized and then covalently bonded in the DNA.34The components of the metals or the metabolites of PAHs can be increased in the formation of oxygen reactive species that interact with the DNA, producing damage of different types, such as oxidative damage.35

Variations in environmental influences on individual genotypes can lead to heterogeneous endotypes of asthma. Several phenotypes of severe clinical expression may overlap in one patient, and the same clinical phenotype may result in different endotypes, which would be reflected in the severity of the disease and its response to conventional treatments.36

Intramural contaminants

Today, a large number of people from industrialized cities spend most of their time at either their home or their job. It has been reported that more than half of the air inhaled during one's life comes from an intramural environment.37 The sources of intramural contaminants come mainly from cigarette smoke, combustion products such as candles or incense, and volatile organic compounds emitted by building materials, paints, furniture with sponge cushions and products containing polyvinyl chloride (PVC). In a study of newborns in Germany, the concentrations of intramural contaminants (PM1, PM 2.5 and PM10) were higher than the PM10 extramural values recommended by the European Union.38

Choi et al. found that the average concentration of individual compounds of volatile organic compounds was consistently higher in the households of children diagnosed with asthma, rhinitis, and eczema compared to the homes of children in a control group. These results suggest that intramural air exacerbates and/or induces the multiple symptoms of allergy, asthma, rhinitis and eczema.39

Conclusions

Air pollution is a key factor in the development and increase of ARD exacerbations. The epigenetic, cellular and molecular mechanisms that directly or indirectly intervene in allergic diseases, and how they contribute to the negative impact of patients’ quality of life have not yet been extensively described. Patients are advised to minimize prolonged exposure to pollutants by methods such as reducing extramural activities on days with high levels of air pollution and promoting reforestation of non-allergenic trees in urban areas. As health personnel, we have the obligation to unite our efforts, participate actively in forums and support national and international environmental policies with the purpose of reducing the impact and consequences of this health problem in the future.

Conflict of interest

The authors have no conflicts of interest to declare.

References
[1]
P. Nucci, M. Sacchi, F. Pichi, et al.
Pediatric conjunctivitis and air pollution exposure: a prospective observational study.
Semin Ophthalmol, (2016), pp. 1-5
[2]
R.L. Clifford, M.J. Jones, J.L. Macisaac, et al.
Inhalation of diesel exhaust and allergen alters human bronchial epithelium DNA methylation.
J Allergy Clin Immunol, 139 (2017), pp. 112-121
[3]
G. D’amato, R. Pawankar, C. Vitale, et al.
Climate change and air pollution: effects on respiratory allergy.
Allergy Asthma Immunol Res, 8 (2016), pp. 391-395
[4]
S. Brandt, L. Perez, N. Künzli, et al.
Cost of near-roadway and regional air pollution-attributable childhood asthma in Los Angeles County.
J Allergy Clin Immunol, 134 (2014), pp. 1028-1035
[5]
S.J. Brandt, L. Perez, N. Künzli, et al.
Costs of childhood asthma due to traffic-related pollution in two California communities.
Eur Respir J, 40 (2012), pp. 363-370
[6]
S.N. Yang, C.C. Hsieh, H.F. Kuo, et al.
The effects of environmental toxins on allergic inflammation.
Allergy Asthma Immunol Res, 6 (2014), pp. 478-484
[7]
M.J. Epton, R.D. Dawson, W.M. Brooks, et al.
The effect of ambient air pollution on respiratory health of school children: a panel study.
Environ Health, 7 (2008), pp. 16
[8]
W.J. Gauderman, H. Vora, R. Mcconnell, et al.
Effect of exposure to traffic on lung development from 10 to 18 years of age: a cohort study.
[9]
Erratum to mechanistic impact of outdoor air pollution on asthma and allergic diseases.
[10]
J. Saravia, G.I. Lee, S. Lomnicki, et al.
Particulate matter containing environmentally persistent free radicals and adverse infant respiratory health effects: a review.
J Biochem Mol Toxicol, 27 (2013), pp. 56-68
[11]
B. Chen, H. Kan.
Air pollution and population health: a global challenge.
Environ Health Prev Med, 13 (2008), pp. 94-101
[12]
Norma Oficial Mexicana NOM-025-SSA1-2014. Diario Oficial de la Federación. EstadosUnidosMexicanos. 20/08/2014.
[13]
M. Riedl, D. Diaz-Sanchez.
Biology of diesel exhaust effects on respiratory function.
J Allergy ClinImmunol, 115 (2005), pp. 221-228
quiz 9
[14]
G. D’amato, L. Cecchi, M. D’amato, et al.
Urban air pollution and climate change as environmental risk factors of respiratory allergy: an update.
J Investig Allergol Clin Immunol, 20 (2010), pp. 95-102
[15]
P.D. Gluckman, M.A. Hanson, C. Cooper, et al.
Effect of in utero and early-life conditions on adult health and disease.
N Engl J Med, 359 (2008), pp. 61-73
[16]
A.F. Fleisch, S.L. Rifas-shiman, P. Koutrakis, et al.
Prenatal exposure to traffic pollution: associations with reduced fetal growth and rapid infant weight gain.
Epidemiology, 26 (2015), pp. 43-50
[17]
Q. Deng, C. Lu, Y. Li, et al.
Exposure to outdoor air pollution during trimesters of pregnancy and childhood asthma, allergic rhinitis, and eczema.
Environ Res, 150 (2016), pp. 119-127
[18]
Pollution prevention and abatement handbook, 1998: toward cleaner production/in collaboration with the United Nations Enviromnent Programme and the United Nations Industrial Development Organization. ISBN 0-8213-3638-X.
[19]
U. Gehring, A.H. Wijga, M. Brauer, et al.
Traffic-related air pollution and the development of asthma and allergies during the first 8 years of life.
Am J RespirCrit Care Med, 181 (2010), pp. 596-603
[20]
G. Bowatte, C.J. Lodge, L.D. Knibbs, et al.
Traffic-related air pollution exposure is associated with allergic sensitization, asthma, and poor lung function in middle age.
J Allergy Clin Immunol, 139 (2017), pp. 122-129
[21]
O. Naas, M. Mendez, M. Quijada, et al.
Chemical modification of coating of Pinushalepensis pollen by ozone exposure.
Environ Pollut, 214 (2016), pp. 816-821
[22]
B.J. Kim, J.W. Kwon, J.H. Seo, et al.
Association of ozone exposure with asthma, allergic rhinitis, and allergic sensitization.
Ann Allergy Asthma Immunol, 107 (2011), pp. 214-219
e211
[23]
E.B. Brandt, M.B. Kovacic, G.B. Lee, et al.
Diesel exhaust particle induction of IL-17A contributes to severe asthma.
J Allergy ClinImmunol, 132 (2013), pp. 1194-1204
e2
[24]
R. Pawankar, G.W. Canonica, S.T. Holgate, et al.
Libro Blanco sobre Alergia de la WAO.
World Allergy Organization, (2011),
[25]
G. Baldwin, R.N. Nastoff, F. Pharagood-Wade.
Estudios de Casos en Medicina Ambiental (ECMA): Factores Ambientales que Provocan Asma.
ATSDR Agency for Toxic Substances and Diseases Registry, (2008),
[26]
W.J. Gauderman, E. Avol, F. Gilliland, et al.
The effect of air pollution on lung development from 10 to 18 years of age.
N Engl J Med, 351 (2004), pp. 1057-1067
[27]
M. Shima, Y. Nitta, M. Ando, et al.
Effects of air pollution on the prevalence and incidence of asthma in children.
Arch Environ Health, 57 (2002), pp. 529-535
[28]
S.T. Holgate, S.H. Koren, J.M. Samet, et al.
Air pollution and health.
Stephen Academic Press, (1999), pp. 561-584
ISBN 0-12-352335-4
[29]
C. Pénard-morand, D. Charpin, C. Raherison, et al.
Long-term exposure to background air pollution related to respiratory and allergic health in schoolchildren.
Clin Exp Allergy, 35 (2005), pp. 1279-1287
[30]
S. Provoost, T. Maes, M.A. Willart, et al.
Diesel exhaust particles stimulate adaptive immunity by acting on pulmonary dendritic cells.
J Immunol, 184 (2010), pp. 426-432
[31]
M. Riedl, D. Diaz-Sanchez.
Biology of diesel exhaust effects on respiratory function.
J Allergy Clin Immunol, 115 (2005), pp. 221-228
[32]
H. Takizawa, T. Ohtoshi, S. Kawasaki, et al.
Diesel exhaust particles induce NF-kappa B activation in human bronchialepithelial cells in vitro: importance in cytokine transcription.
J Immunol, 162 (1999), pp. 4705-4711
[33]
S.S. Salvi, C. Nordenhall, A. Blomberg, et al.
Acute exposure to diesel exhaust increases IL-8 and GRO-alpha production in healthy human airways.
Am J RespirCrit Care Med, 161 (2000), pp. 550-557
[34]
M. Borgie, F. Ledoux, A. Verdin, et al.
Genotoxic and epigenotoxic effects of fine particulate matter from rural and urban sites in Lebanon on human bronchial epithelial cells.
Environ Res, 136 (2015), pp. 352-362
[35]
A. Valavanidis, K. Fiotakis, T. Vlahogianni, et al.
Characterization of atmospheric particulates, particle-bound transition metals and polycyclic aromatic hydrocarbons of urban air in the centre of Athens (Greece).
Chemosphere, 65 (2006), pp. 760-768
[36]
S. Wenzel.
Severe asthma: from characteristics to phenotypes to endotypes.
Clin Exp Allergy, 42 (2012), pp. 650-658
[37]
J. Sundell.
On the history of indoor air quality and health.
[38]
U. Franck, O. Herbarth, S. Röder, et al.
Respiratory effects of indoor particles in young children are size dependent.
Sci Total Environ, 409 (2011), pp. 1621-1631
[39]
H. Choi, N. Schmidbauer, J. Sundell, et al.
Common household chemicals and the allergy risks in pre-school age children.
Copyright © 2017. Universidad Autónoma de Nuevo León
Download PDF
Article options