Polycyclic Aromatic Hydrocarbons and Their Effects on the Occurrence of Chronic Obstructive Pulmonary Disease (COPD): A Review

authors:

avatar Mohammad Javad Mohammadi ORCID 1 , 2 , avatar Gholamreza Goudarzi 2 , avatar Behzad Fouladi Dehaghi ORCID 3 , avatar Kourosh Zarea ORCID 4 , avatar Maryam Hormati 5 , avatar Masoume Taherian 5 , avatar Fatemeh Kiani 5 , *

Department of Environmental Health Engineering, School of Public Health and Environmental Technologies Research Center, Ahvaz Jundishapur University of Medical Sciences, Ahvaz, Iran
Department of Environmental Health Engineering, School of Public Health and Air Pollution and Respiratory Diseases Research Center, Ahvaz Jundishapur University of Medical Sciences, Ahvaz, Iran
Department of Occupational Health, School of Health, Environmental Technology Research Center, Ahvaz Jundishapur University of Medical Sciences, Ahvaz, Iran
Nursing Care Research Center in Chronic Diseases, Department of Nursing, School of Nursing and Midwifery, Ahvaz Jundishapur University of Medical Sciences, Ahvaz, Iran
Student Research Committee, Ahvaz Jundishapur University of Medical Sciences, Ahvaz, Iran

how to cite: Mohammadi M J, Goudarzi G , Fouladi Dehaghi B, Zarea K, Hormati M, et al. Polycyclic Aromatic Hydrocarbons and Their Effects on the Occurrence of Chronic Obstructive Pulmonary Disease (COPD): A Review. Jundishapur J Chronic Dis Care. 2022;11(3):e122852. https://doi.org/10.5812/jjcdc-122852.

Abstract

Background:

Polycyclic aromatic hydrocarbons (PAHs) are among the most important compounds that cause adverse health outcomes in humans, such as poor lung function, bronchitis, asthma, shortness of breath, circulatory disorders, lung cancer, cardiovascular diseases, and mortality.

Objectives:

This review aims to investigate the effects of PAHs on the occurrence of chronic obstructive pulmonary disease (COPD).

Methods:

A narrative review of the literature was done from 1979 to 2021 in various databases: Science Direct, PubMed, Web of Science, Springer, and Google Scholar. We found 76 and 14 articles by searching the databases and other sources, respectively. Twelve articles were included after screening. The literature indicates the significant adverse effect of PAHs on the occurrence of COPD.

Results:

Heavy industries (oil, steel, gas, and petroleum) are the primary sources of PAHs. Polycyclic aromatic hydrocarbons induce respiratory diseases, as they are destructive to the lung, leading to COPD. Sex, age, nutritional status, health, duration of exposure to PAHs, and body response to the pollutants affect the complications.

Conclusions:

High PAH levels can increase the risk of COPD, respiratory diseases, and incremental lifetime cancer risk (ILCR).

1. Background

Polycyclic aromatic hydrocarbons (PAHs) are a large group of organic compounds with two or more aromatic fused rings. These compounds can be divided into two categories based on the structure, including light (1 - 2 rings) and high molecular weight (2 - 4 rings) (1, 2). These compounds have low solubility in water and are very lipophilic. Besides, PAHs have low vapor pressure and are adsorbed on particles (3, 4). Polycyclic aromatic hydrocarbons are produced because of the incomplete pyrolysis of fossil fuels and enter the environment through various combustion processes.

Among the PAHs, 16 compounds are most important due to the lack of rapid biological decomposition by microorganisms and toxicity to the environment. The most important PAHs include benzo[a]anthracene, chrysene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, benzo[ghi]perylene, indeno[1,2,3-cd]pyrene, dibenz[a,h]anthracene, fluorene, phenanthrene, anthracene, naphthalene, acenaphthylene, acenaphthene, fluoranthene, and pyrene (1, 5, 6). Power plants, home heating systems, petroleum and oil industries, fuel combustion (diesel, coal), forest fires, tanker and ship accidents, cigarette and tobacco smoke, coke ovens, coal, asphalt, casting, volatile ash particles, solid waste incineration, and traffic exhausts are the primary sources of PAHs emissions (7-13).

Based on the USEPA classification, PAHs are among the main compounds that cause carcinogenicity in humans and animals (3, 14, 15). The route of exposure (inhalation, skin, and food), exposure duration, age, sex, nutritional status, and personal health are the most critical factors affecting the health effects of these compounds (16, 17). As known, PAHs in the body have short-term and long-term effects. The primary health effects are eye irritation, nausea, diarrhea, thrombosis, seizures, genotoxicity, mutagenicity, cancer risk, cardiovascular disease, neurological disease, respiratory disease, cataracts, kidney damage, and chronic obstructive pulmonary disease (18-24). Chronic obstructive pulmonary disease (COPD) is a lung disease chronically identified by a few airway signs (25, 26). The main symptoms of COPD include shortness of breath, cough, and sputum production (27-30). Diagnosis of COPD is based on shortness of breath, measured by lung function tests (31, 32). Treatments of COPD include smoking cessation, long-term oxygen therapy, vaccination, rehabilitation, bronchodilators, and corticosteroids (33, 34). The main factors that cause COPD are smoking and exposure to disease factors due to occupation and indoor fires (27, 35-37). Cold weather can also play a role, as most exacerbations usually occur in winter (38, 39).

Due to the importance of respiratory system function to other systems of the human body and the effects of PAHs on respiratory health function, leading to and exacerbating COPD, this narrative review aimed to investigate PAHs and their impact on the occurrence of COPD.

2. Method

2.1. Evidence Acquisition

This narrative review study was conducted on references available in various databases: Science Direct, PubMed, Web of Science, Springer, and Google Scholar (Table 1). Years of publication (1979 - 2021) and English language were the main criteria for search limitation.

Table 1. Search Terms and Query Results
TermGoogle ScholarWeb of ScienceSpringerScience DirectPubMedUnique Results
Chronic obstructive pulmonary disease783310232576
Polycyclic aromatic hydrocarbons and respiratory systems703015202254
Health effect381710141636
Polycyclic aromatic hydrocarbons and chronic obstructive pulmonary disease25148121334
Polycyclic aromatic hydrocarbons and lung2010481125
Total231104477787225

2.2. Data Collection

The study was performed with 225 articles retrieved by keywords “chronic obstructive pulmonary disease,” “polycyclic aromatic hydrocarbons and respiratory systems,” “health effect,” “polycyclic aromatic hydrocarbons and chronic obstructive pulmonary disease,” and “polycyclic aromatic hydrocarbons and lung.” Relevant papers were reviewed to establish the possible link between PAHs and COPD.

2.3. Search Strategy

According to the criteria mentioned above, after an initial screening of 225 titles, 135 were duplicated and excluded. There were 76 articles found through database searching besides 14 articles found in other sources. In the next stage, 34 studies were screened after review, and 18 full-text articles entered the analysis process. Finally, 12 articles were selected for this study.

2.4. Ethical Approval

Ethical approval was acquired from the Ethics Committee of Ahvaz Jundishapur University of Medical Sciences (code of ethics: IR.AJUMS.REC.1400.667). According to the national guidelines, such studies do not require individual consent.

3. Result and Discussion

3.1. Air Pollution

Increasing air pollution in recent decades due to economic development and the dramatic progress of human societies has significantly endangered the health outcomes of humans (40, 41). The emission of a large amount of particulate matter and gases into the atmosphere due to excessive burning of fossil fuels, increasing use of vehicles, and failure to use solutions to reduce gases emitted from industries has caused adverse economic and health effects (42). The US Environmental Protection Agency (USEPA) has determined carbon monoxide (CO), lead (Pb), nitrogen dioxide (NO2), particulate matter (PM10 and PM2.5), ozone (O3), and sulfur dioxide (SO2) as criteria pollutants whose daily amounts are expressed by air quality index (AQI) (43). The most important sources of air pollution are fixed sources (power plants and industries) and mobile sources (personal and public vehicles) that emit primary and secondary pollutants. Unlike primary pollutants, including SO2, NO2, ground-level O3, CO, PM2.5, PM10, Pb, volatile organic compounds (VOCs), and hydrocarbons (HC) that enter ambient air with no changes, secondary pollutants, including photochemical smog, O3, formaldehyde, and peroxyacetyl nitrate (PAN), enter the atmosphere after producing from reactions between primary pollutants and UV radiation and atmospheric components (44). Air pollution in terms of emission sources is classified into two categories of natural resources (volcanic and forest fire activities, natural dust, smoke, and burning of minerals) and human resources (motor vehicles, factories, and industrial manufacturers with quality and poor construction activities) (45-48). The emission of toxic air pollutants can cause health effects, including high or partial respiratory irritation, chronic heart, and respiratory disease, lung cancer, acute respiratory infections in children, chronic bronchitis in adults, and exacerbating previous lung disease and asthma attacks (49-51). In addition, long-term and short-term exposure to pollutants is associated with premature death and decreased life expectancy (52).

3.2. Chronic Obstructive Pulmonary Disease

The lung is among the most critical organs in the human body, which plays a vital role in protecting the organs and cell function. It is an organ intermittently exposed to pollutants. As a critical organ in the respiratory system, the lung plays a vital role in the proper functioning of the body organs. Because humans depend on respiration for survival, their lungs are active every second, so maintaining their health is especially important. Chronic obstructive pulmonary disease is an excessive inflammatory response of the lung to respiratory pollutants that, with irreversible obstruction of the airways, causes progressive, gradual, and irreversible restriction of pulmonary airflow (53). Besides, COPD reduces the flow of air through the airways in the lung. The classification of these diseases, which are the most common causes of death due to respiratory disorders, includes diseases that close the airway in or out of the lungs and reduce respiratory capacity by various action mechanisms, such as the destruction of lung parenchymal tissue (54). This disease causes the airways to become narrow, damaged, and filled with secretions. As a result, the exhaled air, which requires the natural elasticity of bronchi to escape, is trapped inside the lungs during the reduction of elasticity in air sacs and the dilation of bronchi (55). Inflammatory cells are activated in the airways following contact with disease-causing agents, especially cigarette and tobacco smoke, and the destructive enzymes caused by these cells cause damage to lung tissue, loss of cilia of epithelial cells, and airway obstruction, and restrict air passage through these ducts. As a result of immunodeficiency in the airways and alveoli, especially phagocytic dysfunction of macrophages, a person becomes prone to recurrent lung infections (56).

Diseases such as chronic bronchitis, emphysema, and asthma, which are classified as COPD and occur after exposure to stimulants, suspended particles, or occupational exposure such as mining or textile industry over a long time, are diagnosed by imaging, blood tests, and lung function tests (spirometry) (55, 56). Other risk factors include lung infections and exposure to allergens (such as pet skin and dust), cigarette smoke, and air pollution (57). Many people worldwide who suffer from chronic lung disease experience common symptoms, one of which is a persistent cough with chest pain that does not improve even after medication. Coughing helps protect the airways from inhalation stimuli and clear the sputum (mucus) in the airways, but a persistent cough with sputum and blood is a sign of abnormal lung function. Other symptoms include shortness of breath (even during daily activities), increased or discolored color, increased concentration, amount and smell of mucus (if the mucus changes color from clear to yellow or green or contains blood, it is a clear sign of a problem in the lungs), persistent wheezing (which is a sign of narrowing the airways that does not allow the air to flow fast enough), swelling in the lower body, fatigue, and headaches in the morning (58-60). These symptoms can be a sign of the disease in people that, if not appropriately treated, cause increasingly severe and irreversible damage to the lungs and the risk of lung cancer (28, 61). Although there is no definitive cure for these diseases, prescribed drugs, oxygen therapy, and surgery are methods for the relative improvement of the symptoms. However, if no action is taken for patients, reducing blood-oxygen damages the heart and brain and causes ischemic heart disease, cerebrovascular disease, and eventually death (3).

3.3. Polycyclic Aromatic Hydrocarbons and Their Effects on COPD

Polycyclic aromatic hydrocarbons are colorless to white or pale yellow lipophilic organic compounds with different isomers, consisting of two or more fused aromatic rings (30, 62). Some, including anthracene, chrysin, triphenylene, pentacene, and benzo [a] pyrene, are used in paints, plastics, pesticides, and road asphalt. These compounds are often present in the environment as complex mixtures; for example, soot is one of these complex compounds (63). These compounds are environmental pollutants and a large group of carcinogens found in the environment, including air, water, soil, and food. Besides, PAHs are a serious threat to human health due to cytotoxic and mutagenic effects (62).

Human activities such as maritime transport, tankers, refineries, oil and gas industries, and incomplete combustion of fossil fuels and tobacco smoke are the sources of petrogenic and pyrolytic-created PAHs. They are a combination of cyclic polyaromatic compounds in the environment that are rapidly oxidized during adsorption on dust particles and airborne particles by reaction with the sun's ultraviolet rays, and their chemical half-life is increased by exposure to zinc. They also react with ozone, nitrous oxide, and sulfur dioxide. Hence, due to their very high resistance, exposure to these suspended particles is more dangerous than contact with primary PAHs (64). Polycyclic aromatic hydrocarbons are mostly insoluble in water and, after entering the body for excretion, are converted into more soluble compounds. These secondary compounds can form derivatives of polycyclic aromatic compounds, which are persistent organic pollutants, 16 of which have been identified as hazardous carcinogenic compounds by the International Environmental Protection Agency. Through skin contact, eating, drinking, and breathing, they enter the body and bind to DNA to cause mutations and carcinogenesis, although the absorption of PAHs by eating is usually slow (65). The effects of PAHS on humans depend on the rate at which they enter the body and the compounds to which a person is simultaneously exposed. Although polycyclic aromatic compounds can be present in all fatty tissues, they tend to be stored in the kidneys and liver, and small amounts are stored in the spleen and adrenal glands (5). These compounds are converted in body tissues to some less dangerous compounds and some more harmful compounds than the original PAHs. Laboratory studies have shown that PAHs do not tend to stay in tissues for long periods, and most of them are excreted in feces and urine after a few days. The type and severity of the effects of PAHs on human health depend on several factors, such as the amount of these compounds entering the body, the duration of contact with these compounds, the body response that varies with age, sex, nutritional status, and health, and the source or route of exposure to such compounds (66).

In our study, PAHs were linked to the occurrence of COPD. However, further studies with more pollutants and complications are required to attain more definite results. Due to the increasing trend of chronic diseases, especially COPD, and their influential factors, the findings of this study can be helpful and practical for health system decision-makers and politicians.

3.4. Conclusions

This study assessed the effects of PAHs on COPD. The results demonstrated that PAHs could cause significant loss of life and affect millions of people because of synergistic effects on the lung and respiratory systems. Also, COPD has had an increasing trend in recent years. The findings can have broad applications for increasing knowledge of the relationship between PAHs and respiratory disease, especially asthma and COPD. Actions to decrease PAHs emissions can reduce the incidence rate of COPD.

Acknowledgements

References

  • 1.

    Goudarzi G, Alavi N, Babaei AA, Geravandi S, Idani E, Salmanzadeh S, et al. Investigation of Ambient Polycyclic Aromatic Hydrocarbons in a Populated Middle Eastern City. Polycycl Aromat Compd. 2020:1-16. https://doi.org/10.1080/10406638.2020.1823857.

  • 2.

    Goudarzi G, Geravandi S, Alavi N, Idani E, Salmanzadeh S, Yari AR, et al. Association between cancer risk and polycyclic aromatic hydrocarbons' exposure in the ambient air of Ahvaz, southwest of Iran. Int J Biometeorol. 2018;62(8):1461-70. [PubMed: 29959528]. https://doi.org/10.1007/s00484-018-1543-1.

  • 3.

    Saponaro S, Bonomo L, Petruzzelli G, Romele L, Barbafieri M. Polycyclic aromatic hydrocarbons (PAHs) slurry phase bioremediation of a manufacturing gas plant (MGP) site aged soil. Water Air Soil Pollut. 2002;135(1/4):219-36. https://doi.org/10.1023/a:1014716502484.

  • 4.

    Henner P, Schiavon M, Morel J, Lichtfouse E. Polycyclic aromatic hydrocarbon (PAH) occurrence and remediation methods. Analusis. 1997;25(9-10):M56-9.

  • 5.

    Abdel-Shafy HI, Mansour MS. A review on polycyclic aromatic hydrocarbons: Source, environmental impact, effect on human health and remediation. Egypt J Pet. 2016;25(1):107-23. https://doi.org/10.1016/j.ejpe.2015.03.011.

  • 6.

    Wax RS, Christian MD. Practical recommendations for critical care and anesthesiology teams caring for novel coronavirus (2019-nCoV) patients. Can J Anaesth. 2020;67(5):568-76. [PubMed: 32052373]. [PubMed Central: PMC7091420]. https://doi.org/10.1007/s12630-020-01591-x.

  • 7.

    Goudarzi G, Idani E, Alavi N, Salmanzadeh S, Babaei AA, Geravandi S, et al. Association of polycyclic aromatic hydrocarbons of the outdoor air in Ahvaz, southwest Iran during warm-cold season. Toxin Reviews. 2017;36(4):1-8. https://doi.org/10.1080/15569543.2017.1304422.

  • 8.

    Pongpiachan S, Hattayanone M, Choochuay C, Mekmok R, Wuttijak N, Ketratanakul A. Enhanced PM10 bounded PAHs from shipping emissions. Atmos Environ. 2015;108:13-9. https://doi.org/10.1016/j.atmosenv.2015.02.072.

  • 9.

    Davila DR, Romero DL, Burchiel SW. Human T cells are highly sensitive to suppression of mitogenesis by polycyclic aromatic hydrocarbons and this effect is differentially reversed by alpha-naphthoflavone. Toxicol Appl Pharmacol. 1996;139(2):333-41. [PubMed: 8806850]. https://doi.org/10.1006/taap.1996.0173.

  • 10.

    Partanen TJ, Boffetta P, Heikkila PR, Frentzel-Beyme RR, Heederik D, Hours M, et al. Cancer risk for European asphalt workers. Scand J Work Environ Health. 1995;21(4):252-8. [PubMed: 8552998]. https://doi.org/10.5271/sjweh.34.

  • 11.

    Marti-Cid R, Llobet JM, Castell V, Domingo JL. Evolution of the dietary exposure to polycyclic aromatic hydrocarbons in Catalonia, Spain. Food Chem Toxicol. 2008;46(9):3163-71. [PubMed: 18675309]. https://doi.org/10.1016/j.fct.2008.07.002.

  • 12.

    Salamone MF, Heddle JA, Katz M. The mutagenic activity of thirty polycyclic aromatic hydrocarbons (PAH) and oxides in urban airborne particulates. Environ Int. 1979;2(1):37-43. https://doi.org/10.1016/0160-4120(79)90092-8.

  • 13.

    Nadal M, Marques M, Mari M, Domingo JL. Climate change and environmental concentrations of POPs: A review. Environ Res. 2015;143(Pt A):177-85. [PubMed: 26496851]. https://doi.org/10.1016/j.envres.2015.10.012.

  • 14.

    Fang HY, Cai QG, Chen H, Li QY. Mechanism of formation of physical soil crust in desert soils treated with straw checkerboards. Soil Tillage Res. 2007;93(1):222-30. https://doi.org/10.1016/j.still.2006.04.006.

  • 15.

    Rajesh D, Sunil C, Lalita R, Sushila S. Impact assessment of soils treated with refinery effluent. Eur J Soil Biol. 2009;45(5-6):459-65. https://doi.org/10.1016/j.ejsobi.2009.06.002.

  • 16.

    Henkler F, Stolpmann K, Luch A. Exposure to polycyclic aromatic hydrocarbons: bulky DNA adducts and cellular responses. Molecular, clinical and environmental toxicology. Springer; 2012. p. 107-31.

  • 17.

    Linden B. Air pollution: Outdoor air quality and health. Br J Card Nurs. 2019;14(6):1-4.

  • 18.

    Kumar V, Kothiyal NC, Vikas P, Sharma R; Saruchi. Sources, distribution, and health effect of carcinogenic polycyclic aromatic hydrocarbons (PAHs) – current knowledge and future directions. J Chin Adv Mater Soc. 2016;4(4):302-21. https://doi.org/10.1080/22243682.2016.1230475.

  • 19.

    Maragkidou A, Arar S, Al-Hunaiti A, Ma Y, Harrad S, Jaghbeir O, et al. Occupational health risk assessment and exposure to floor dust PAHs inside an educational building. Sci Total Environ. 2017;579:1050-6. [PubMed: 27887828]. https://doi.org/10.1016/j.scitotenv.2016.11.055.

  • 20.

    Ferguson KK, McElrath TF, Pace GG, Weller D, Zeng L, Pennathur S, et al. Urinary Polycyclic Aromatic Hydrocarbon Metabolite Associations with Biomarkers of Inflammation, Angiogenesis, and Oxidative Stress in Pregnant Women. Environ Sci Technol. 2017;51(8):4652-60. [PubMed: 28306249]. [PubMed Central: PMC5771235]. https://doi.org/10.1021/acs.est.7b01252.

  • 21.

    Guerreiro CBB, Horalek J, de Leeuw F, Couvidat F. Benzo(a)pyrene in Europe: Ambient air concentrations, population exposure and health effects. Environ Pollut. 2016;214:657-67. [PubMed: 27140679]. https://doi.org/10.1016/j.envpol.2016.04.081.

  • 22.

    Mrozik A, Piotrowska-Seget Z, Labuzek S. Bacterial degradation and bioremediation of polycyclic aromatic hydrocarbons. Pol J Environ Stud. 2003;12(1).

  • 23.

    Geravandi S, Goudarzi G, Mohammadi MJ, Taghavirad SS, Salmanzadeh S. Sulfur and Nitrogen Dioxide Exposure and the Incidence of Health Endpoints in Ahvaz, Iran. Health Scope. 2015;4(2). https://doi.org/10.17795/jhealthscope-24318.

  • 24.

    Kelly FJ, Fussell JC. Size, source and chemical composition as determinants of toxicity attributable to ambient particulate matter. Atmos Environ. 2012;60:504-26. https://doi.org/10.1016/j.atmosenv.2012.06.039.

  • 25.

    Kasper D, Fauci A, Hauser S, Longo D, Jameson J, Loscalzo J. Harrison's principles of internal medicine, 19e. 1. Mcgraw-hill New York, NY, USA:; 2015.

  • 26.

    Khaniabadi YO, Daryanoosh SM, Hopke PK, Ferrante M, De Marco A, Sicard P, et al. Acute myocardial infarction and COPD attributed to ambient SO2 in Iran. Environ Res. 2017;156:683-7. [PubMed: 28477578]. https://doi.org/10.1016/j.envres.2017.04.028.

  • 27.

    Vestbo J, Hurd SS, Agusti AG, Jones PW, Vogelmeier C, Anzueto A, et al. Global strategy for the diagnosis, management, and prevention of chronic obstructive pulmonary disease: GOLD executive summary. Am J Respir Crit Care Med. 2013;187(4):347-65. [PubMed: 22878278]. https://doi.org/10.1164/rccm.201204-0596PP.

  • 28.

    Khaefi M, Geravandi S, Hassani G, Yari AR, Soltani F, Dobaradaran S, et al. Association of Particulate Matter Impact on Prevalence of Chronic Obstructive Pulmonary Disease in Ahvaz, Southwest Iran during 2009–2013. Aerosol Air Qual Res. 2017;17(1):230-7. https://doi.org/10.4209/aaqr.2015.11.0628.

  • 29.

    Decramer M, Janssens W, Miravitlles M. Chronic obstructive pulmonary disease. Lancet. 2012. https://doi.org/10.1016/S0140-6736(11)60968-9.

  • 30.

    Mohammadi MJ, Geravandi S, Vosoughi M, Salmanzadeh S, Goudarzi G. An Association between air quality and COPD in Ahvaz, Iran. Jundishapur J Chronic Dis Care. 2015;4(1). https://doi.org/10.5812/jjcdc.26621.

  • 31.

    Nathell L, Nathell M, Malmberg P, Larsson K. COPD diagnosis related to different guidelines and spirometry techniques. Respir Res. 2007;8:1-7. [PubMed: 18053200]. [PubMed Central: PMC2217523]. https://doi.org/10.1186/1465-9921-8-89.

  • 32.

    Saki H, Goudarzi G, Jalali S, Barzegar G, Farhadi M, Parseh I, et al. Study of relationship between nitrogen dioxide and chronic obstructive pulmonary disease in Bushehr, Iran. Clin Epidemiol Glob Health. 2020;8(2):446-9. https://doi.org/10.1016/j.cegh.2019.10.006.

  • 33.

    Goudarzi GR, Geravandi S, Salmanzadeh S, Mohammadi MJ. An estimation of respiratory deaths and COPD related to SO2 pollutant in Tabriz, northwest of Iran (2011). Razi J Med Sci. 2015;22(131):44-50.

  • 34.

    Rabe KF, Hurd S, Anzueto A, Barnes PJ, Buist SA, Calverley P, et al. Global strategy for the diagnosis, management, and prevention of chronic obstructive pulmonary disease: GOLD executive summary. Am J Respir Crit Care Med. 2007;176(6):532-55. [PubMed: 17507545]. https://doi.org/10.1164/rccm.200703-456SO.

  • 35.

    Geravandi S, Goudarzi G, Yari AR, Idani E, Yousefi F, Soltani F, et al. An estimation of COPD cases and respiratory mortality related to ground-level ozone in the metropolitan Ahvaz during 2011. Arch Hyg Sci. 2016;5(1):15-21.

  • 36.

    Mathers CD, Loncar D. Projections of global mortality and burden of disease from 2002 to 2030. PLoS Med. 2006;3(11). e442. [PubMed: 17132052]. [PubMed Central: PMC1664601]. https://doi.org/10.1371/journal.pmed.0030442.

  • 37.

    Kennedy SM, Chambers R, Du W, Dimich-Ward H. Environmental and occupational exposures: do they affect chronic obstructive pulmonary disease differently in women and men? Proc Am Thorac Soc. 2007;4(8):692-4. [PubMed: 18073405]. https://doi.org/10.1513/pats.200707-094SD.

  • 38.

    J. Barnes P. Corticosteroids. Asthma and COPD. 2009. p. 639-53. https://doi.org/10.1016/b978-0-12-374001-4.00051-1.

  • 39.

    Thamizh Vani D. A prospective, comparative study of effect of Roflumilast in Chronic Obstructive Pulmonary Disease and its efficacy in reducing exacerbations. Kilpauk Medical College, Chennai; 2018.

  • 40.

    Liu W, Xu Z, Yang T. Health Effects of Air Pollution in China. Int J Environ Res Public Health. 2018;15(7). [PubMed: 30002305]. [PubMed Central: PMC6068713]. https://doi.org/10.3390/ijerph15071471.

  • 41.

    Tahery N, Zarea K, Cheraghi M, Hatamzadeh N, Farhadi M, Dobaradarn S, et al. Chronic Obstructive Pulmonary Disease (COPD) and Air Pollution: A Review. Jundishapur J Chronic Dis Care. 2021;10(1). https://doi.org/10.5812/jjcdc.110273.

  • 42.

    Samet J, Krewski D. Health effects associated with exposure to ambient air pollution. J Toxicol Environ Health A. 2007;70(3-4):227-42. [PubMed: 17365585]. https://doi.org/10.1080/15287390600884644.

  • 43.

    Goudarzi G, Alavi N, Geravandi S, Idani E, Behrooz HRA, Babaei AA, et al. Health risk assessment on human exposed to heavy metals in the ambient air PM10 in Ahvaz, southwest Iran. Int J Biometeorol. 2018;62(6):1075-83. [PubMed: 29464337]. https://doi.org/10.1007/s00484-018-1510-x.

  • 44.

    Heinsohn RJ, Kabel RL. Sources and control of air pollution: Engineering principles. Office of Scientific and Technical Information; 1998.

  • 45.

    Dastoorpoor M, Riahi A, Yazdaninejhad H, Borsi SH, Khanjani N, Khodadadi N, et al. Exposure to particulate matter and carbon monoxide and cause-specific Cardiovascular-Respiratory disease mortality in Ahvaz. Toxin Reviews. 2020;40(4):1-11. https://doi.org/10.1080/15569543.2020.1716256.

  • 46.

    Effatpanah M, Effatpanah H, Jalali S, Parseh I, Goudarzi G, Barzegar G, et al. Hospital admission of exposure to air pollution in Ahvaz megacity during 2010–2013. Clin Epidemiol Glob Health. 2020;8(2):550-6. https://doi.org/10.1016/j.cegh.2019.12.001.

  • 47.

    Faraji Ghasemi F, Dobaradaran S, Saeedi R, Nabipour I, Nazmara S, Ranjbar Vakil Abadi D, et al. Levels and ecological and health risk assessment of PM2.5-bound heavy metals in the northern part of the Persian Gulf. Environ Sci Pollut Res Int. 2020;27(5):5305-13. [PubMed: 31848967]. https://doi.org/10.1007/s11356-019-07272-7.

  • 48.

    Wark K, Warner CF. Air pollution: its origin and control. Office of Scientific and Technical Information; 1981.

  • 49.

    Momtazan M, Geravandi S, Rastegarimehr B, Valipour A, Ranjbarzadeh A, Yari AR, et al. An investigation of particulate matter and relevant cardiovascular risks in Abadan and Khorramshahr in 2014–2016. Toxin Reviews. 2018;38(4):290-7. https://doi.org/10.1080/15569543.2018.1463266.

  • 50.

    Sun L, Sun Z, Wu L, Zhu Z, Zhang F, Shang Z, et al. Prevalence and risk factors of acute posttraumatic stress symptoms during the COVID-19 outbreak in Wuhan, China. MedRxiv. 2021. https://doi.org/10.1101/2020.03.06.20032425.

  • 51.

    Al Osman M, Yang F, Massey IY. Exposure routes and health effects of heavy metals on children. Biometals. 2019;32(4):563-73. [PubMed: 30941546]. https://doi.org/10.1007/s10534-019-00193-5.

  • 52.

    Goudarzi G, Geravandi S, Mohammadi MJ, Salmanzadeh S, Vosoughi M, Sahebalzamani M. The relationship between air pollution exposure and chronic obstructive pulmonary disease in Ahvaz, Iran. Chron Dis J. 2015;3(1):14-20. https://doi.org/10.22122/cdj.v3i1.119.

  • 53.

    Cooney A, Mee L, Casey D, Murphy K, Kirwan C, Burke E, et al. Life with chronic obstructive pulmonary disease: striving for 'controlled co-existence'. J Clin Nurs. 2013;22(7-8):986-95. [PubMed: 23279604]. https://doi.org/10.1111/j.1365-2702.2012.04285.x.

  • 54.

    Betsuyaku T, Miyazaki M. Mechanism of chronic obstructive pulmonary disease. Respiration Circulation. 2012;60(10):1021-7.

  • 55.

    Andreou G, Vlachos F, Makanikas K. Effects of chronic obstructive pulmonary disease and obstructive sleep apnea on cognitive functions: evidence for a common nature. Sleep Disord. 2014;2014:768210. [PubMed: 24649370]. [PubMed Central: PMC3932644]. https://doi.org/10.1155/2014/768210.

  • 56.

    Gentry S, Gentry B. Chronic Obstructive Pulmonary Disease: Diagnosis and Management. Am Fam Physician. 2017;95(7):433-41. [PubMed: 28409593].

  • 57.

    Mizgerd JP. Lung infection--a public health priority. PLoS Med. 2006;3(2). e76. [PubMed: 16401173]. [PubMed Central: PMC1326257]. https://doi.org/10.1371/journal.pmed.0030076.

  • 58.

    Calverley P, Georgopoulos D. Chronic obstructive pulmonary disease: symptoms and signs. Eur Respir Monogr. 2006;38(7). [PubMed: 16396952]. https://doi.org/10.1183/1025448x.00038002.

  • 59.

    Price D, Freeman D, Cleland J, Kaplan A, Cerasoli F. Earlier diagnosis and earlier treatment of COPD in primary care. Prim Care Respir J. 2011;20(1):15-22. [PubMed: 20871945]. [PubMed Central: PMC6602161]. https://doi.org/10.4104/pcrj.2010.00060.

  • 60.

    Roche N, Chavannes NH, Miravitlles M. COPD symptoms in the morning: impact, evaluation and management. Respir Res. 2013;14:1-8. [PubMed: 24143997]. [PubMed Central: PMC3816156]. https://doi.org/10.1186/1465-9921-14-112.

  • 61.

    Durham AL, Adcock IM. The relationship between COPD and lung cancer. Lung Cancer. 2015;90(2):121-7. [PubMed: 26363803]. [PubMed Central: PMC4718929]. https://doi.org/10.1016/j.lungcan.2015.08.017.

  • 62.

    Schneider K, Roller M, Kalberlah F, Schuhmacher-Wolz U. Cancer risk assessment for oral exposure to PAH mixtures. J Appl Toxicol. 2002;22(1):73-83. [PubMed: 11807932]. https://doi.org/10.1002/jat.828.

  • 63.

    Shuttleworth KL, Cerniglia CE. Environmental aspects of PAH biodegradation. Appl Biochem Biotechnol. 1995;54(1-3):291-302. [PubMed: 7486983]. https://doi.org/10.1007/BF02787927.

  • 64.

    Howsam M, Jones KC. Sources of PAHs in the Environment. PAHs and Related Compounds. Springer; 1998. p. 137-74. https://doi.org/10.1007/978-3-540-49697-7_4.

  • 65.

    Ewa B, Danuta MS. Polycyclic aromatic hydrocarbons and PAH-related DNA adducts. J Appl Genet. 2017;58(3):321-30. [PubMed: 27943120]. [PubMed Central: PMC5509823]. https://doi.org/10.1007/s13353-016-0380-3.

  • 66.

    Goudarzi G, Idani E, Alavi N, Salmanzadeh S, Babaei AA, Geravandi S, et al. Association of polycyclic aromatic hydrocarbons of the outdoor air in Ahvaz, southwest Iran during warm-cold season. Toxin Reviews. 2017;36(4):282-9. https://doi.org/10.1080/15569543.2017.1304422.

Copyright © 2022, Jundishapur Journal of Chronic Disease Care. This is an open-access article distributed under the terms of the Creative Commons Attribution-NonCommercial 4.0 International License (http://creativecommons.org/licenses/by-nc/4.0/) which permits copy and redistribute the material just in noncommercial usages, provided the original work is properly cited.