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Proceeding Paper

Environment and Public Health: Air Pollution and Chronic Diseases †

by
Pinelopi Petropoulou
1,*,
Ioli Artopoulou
2,
Ioannis Kalemikerakis
1 and
Ourania Govina
1
1
Department of Nursing, University of West Attica, 12243 Aigaleo, Greece
2
Department of Prosthodontics, School of Dentistry, National and Kapodistrian University of Athens, 11527 Zografou, Greece
*
Author to whom correspondence should be addressed.
Presented at the 16th International Conference on Meteorology, Climatology and Atmospheric Physics—COMECAP 2023, Athens, Greece, 25–29 September 2023.
Environ. Sci. Proc. 2023, 26(1), 118; https://doi.org/10.3390/environsciproc2023026118
Published: 29 August 2023

Abstract

:
Air pollution is a major environmental risk to human health and wellbeing, and a major cause of mortality and morbidity worldwide. Particularly affected are the vulnerable populations of women, pregnant women, children, people with disabilities, and the elderly, who make up the majority of the world’s poor. In this work, we present a series of pieces of evidence linking the main air pollutants to chronic diseases in adults and children. The WHO has concluded that air pollution affects children’s neurodevelopmental and cognitive abilities, and can cause chronic diseases, such as childhood asthma and cancer. Epidemiological studies have shown significant effects caused by PM 2.5 and PM 10 particles toward mortality from different types of cancer. Finally, household air pollution increases the risk for a wide range of adverse cardiorespiratory, pediatric, and maternal health outcomes, particularly in poorer low- and middle-income countries.

1. Introduction

Atmospheric gusts are collectively classified as a known human carcinogen that affects public health. Benzene is a frequent component of air pollution, and strategies must protect individuals from unavoidable exposure to it and other airborne carcinogens [1].
Free access to clean air is undoubtedly a fundamental human right. A person breathes an average of 10 million times in a year. Children naturally breathe faster than adults, and living in a polluted environment results in more pollutants being absorbed [2]. Toxic pollutants, through the respiratory function, can reach all the organs of the human body, and cause disorders in, or impairment of, their function, as a result of which they become burdened, and vulnerable to other diseases [3].
Air pollution is linked to chronic diseases, such as heart disease, stroke, lung disease, various types of cancer, and a reduction in life expectancy and healthy life years. Air pollutants are collectively classified as a known human carcinogen and, more broadly, affect the health of hundreds of millions of people worldwide [4].
The foci of pollution are mainly: factories, power plants, vehicles powered by fossil fuels, dust and waste burning, and pollution caused by coal [5].
Although some high-income countries have shown improvement in their air quality in recent decades, approximately 90% of the world’s population still live in areas that do not meet the standard air quality guidelines presented by the WHO [6].
The WHO estimates that nearly 3 billion people worldwide rely on polluting fuels, such as wood, coal, crop waste, animal manure, or charcoal, combined with inefficient cooking and heating stoves within households [7].
The burden of cardiorespiratory, pediatric, and maternal diseases related to household air pollution has decreased globally, but remains high in the world’s poorest regions [7].
The aim of this study was to draw attention to: (a) the relationship between indoor and outdoor air pollution and increased morbidity and mortality worldwide, and especially in low- and middle-income countries; and (b) the current gap in the form of specialized environmental policies and ways of life to stop this relationship.

2. Materials and Methods

Following PRISMA guidelines, we searched the PubMed database for clinical trials and meta-analyses from 2018 to 2023 that provided the full research text for free, with the keywords “air pollution and chronic diseases”. A total of 42 articles were identified, of which 15 were rejected after their title was studied. Then, 27 abstracts were studied; 3 were rejected from the study of abstracts, and 3 from the full-text study. A total of 21 articles were included in the present study, of which 11 were clinical studies, and 10 were meta-analyses (Figure 1).

3. Results

It is known that air pollution can have several acute and long-term effects on human health. Several epidemiological studies have shown that the degree of exposure to ambient particulate matter (PM) or nitrogen dioxide (NO2) is associated with daily mortality, mainly from cardiovascular and respiratory diseases. The size of the PM has a negative correlation with its level of lung toxicity, which means that PM 2.5 has more harmful effects than PM 10. Fine PM 2.5 particles (with an aerodynamic diameter < 2.5μm) cause a huge burden of disease. Findings suggest a positive association between the PM 2.5 constituents and cause-related mortality, particularly due to myocardial infarction. Emerging evidence suggests that long-term ambient PM 2.5 levels increase the magnitude of the association between PM 2.5 and elderly systolic blood pressure and cardiovascular risk [6,7,8,9].
Evidence suggests that nitrogen dioxide and ozone adversely affect human health, impacting respiratory function, and causing hospitalization and premature death in any population, including subgroups of vulnerable adults and children. A review of cohort studies found positive associations between long-term NO2 concentrations and mortality, and limited evidence linking O3 and mortality [10].
Environmental pollution from particulate matter is a high risk factor for mortality worldwide. The burden of disease is extremely high in China, and it has been estimated that approximately 1.2 million deaths in 2017 are attributable to particulate matter. PM 2.5 is a mixture of various organic and inorganic substances, and among the main components are organic carbon, elemental carbon, and ammonium nitrate sulfate. Along with measures to monitor and control air pollutants, future strategic plans should incorporate the protection of populations vulnerable to these components, especially those with chronic diseases [4,11].
Significant harmful effects of PM 2.5 on lung cancer mortality, and mortality from liver cancer, colon cancer, bladder cancer, and kidney cancer have been observed, while PM 10 has shown harmful effects on mortality from lung cancer, pancreatic cancer, and laryngeal cancer. Therefore, they may act through different mechanisms. Meta-analyses of cohort studies have shown that exposure to the main air pollutants is associated with increased mortality from all cancers, and an increased risk of chronic liver disease [12,13]. The results also show that an increase in exposure to PM 2.5 significantly increases the risk of liver cancer, liver cirrhosis, and fatty liver disease. Future research is needed, to strengthen the association between certain types of air pollutants and specific chronic liver diseases [13].
The epidemiological literature on the associations between exposure to the ambient air pollutants PM 2.5, PM 10, and NO2 and the incidence of breast cancer has recently developed strongly. It has been estimated from dose–response functions that approximately 1700 cases of breast cancer could be attributed annually to exposure to NO2 or associated air pollutants, but it is not yet possible to claim that this association is a consequence of NO2 exposure itself. Premenopausal women appear to be at more risk than postmenopausal women, but further studies are needed, to better understand the role of pollutants in the pathophysiology of breast cancer, especially in premenopausal women. Breast cancer deserves consideration, in order to fully appreciate the burden of air pollution on women’s health [14].
The development of COPD has been associated with air pollutants from outdoor and indoor sources, such as burning solid fuels and cooking. The degree of exposure to PM depends not only on the air quality of indoor and outdoor environments, but also on the percentage of time a person spends in these spaces. Although public policy has a primary role in reducing air pollution, modifications in personal lifestyles can reduce the harmful effects of PM. Interventions to reduce the exposure to PM air pollutants in the daily life of patients with COPD can be important [15]. The use of an air purifier indoors has been shown to reduce the incidence of COPD and childhood asthma, as has the use of a personal mask outdoors on days with increased air pollution [16,17].
A meta-analysis including 59 studies showed that short-term exposure to all gases and particulate pollutants was significantly associated with the risk of the acute exacerbation of COPD (AECOPD). Among them, O3 and NO2 showed the strongest associations, SO2 and CO showed weak correlations, and PM 10 showed a higher correlation than PM 2.5 between particle types, with the strongest effect on the exposure day and lag. The incidence of COPD can be reduced through the control of the air pollutants PM 2.5 and NO2. Furthermore, as both MMP-9 and IL-8 are neutrophil-associated inflammatory markers, air-pollution-induced airway inflammation is primarily driven by neutrophils. Therefore, the development of drugs that target neutrophil-mediated inflammation will be important in future therapies [18].
Biomass fuel (wood, charcoal, coal, manure, and crop residues) for cooking and/or heating is associated with an increased risk of esophageal squamous cell carcinoma (ESCC). Importantly, the ESCC risk varies according to the study setting and population. While current evidence demonstrates an association between age, gender, and lifestyle (smoking and alcohol use), environmental factors may be responsible for the increased risk in low-income countries. The biomass fuel status should be considered in the risk assessment for squamous esophageal carcinoma in low-income countries [19].
There is now substantial evidence linking household air pollution to a wide range of cardiorespiratory, pediatric, and maternal conditions, with these disease categories being specifically highlighted by the WHO. Household exposure to air pollution is among the top 10 risk factors for disease, with the highest prevalence seen in poorer communities in low- and middle-income countries [20].
Traffic-related air pollution, particularly exposure to benzene, was almost linearly associated with the risk of childhood leukemia. No minimum exposure threshold emerged for benzene, while analyzes of traffic density and nitrogen dioxide NO2 showed such a limit. The disease subtype, exposure time, and age of the child appear to modify these associations [21,22].
Air pollution can contribute to a significant burden of childhood asthma cases. For other allergic diseases, e.g., conjunctivitis, eczema, and sensitization, there are substantially fewer studies, and the evidence is less strong [7]. Early life upper-respiratory tract infections are associated with an increased risk of school-age asthma. Early childhood lower-respiratory tract infections have a direct impact on lung development and subsequent chronic respiratory diseases [23].
The fetal oxidative balance achieved when protective prenatal factors neutralize sources of oxidative stress may be critical in the prevention of asthma and allergic diseases. Potentially protective prenatal exposures to nutrients such as vitamin D have been identified, as well as prenatal exposures to prooxidants, such as smoking and prenatal air pollutants, that may increase the risk of asthma and allergic outcomes in adolescence. Protective nutrients may offset the adverse effects of prooxidant exposure [24].
A growing body of research links traffic-related environmental factors to childhood obesity. Long-term traffic pollution shows a weak positive association with an increased BMI in children, and traffic flow, pollution, and noise could influence weight-related behaviors. The relationship between traffic environmental factors and obesity is receiving increasing attention in the fields of children’s health and life-course epidemiology [25].

4. Discussion

This systematic review analyzed twenty-one studies evaluating the association between particulate air pollution with some chronic diseases, and the increased morbidity and mortality due to air pollution worldwide, in adults and children.
The findings show that air pollution has several acute and long-term effects on human health, especially in urban areas with a high traffic density, from PM 2.5 and PM 10 particles, and their main components, such as organic carbon, elemental carbon, ammonium nitrate sulfate, nitrogen dioxide, and benzene [26]. A poor air quality also has significant economic implications, increasing medical care costs, and reducing worker productivity [27].
More prospective studies with large numbers of participants are needed in developing countries. The evidence gap map (EGM) is an emerging method of evidence synthesis that can provide a strategic approach to generating issue-based evidence, and support evidence-based environmental policy-making [11,28].
Systematic reviews of both short-term and long-term studies concerning air pollutants, morbidity, and mortality are needed to further support our findings [9,15].
The limitations of our study were the use of English-language literature only, the time limitation of the last five years, and the fact that we were limited to including articles only from the PubMed database.

5. Conclusions

Air pollution is a serious environmental problem and a major worldwide public health problem that poses serious risks to human health, especially in developing countries, accelerated by industrialization and urbanization. There is an urgent need for informed policy and decision-making to ensure that children and adults living in low- and middle-income countries (LMICs) will have clean air to breathe in their homes. The studies conducted in LMICs are still scarce. Strict environmental health policies are needed, to keep air pollution levels and, consequently, death rates from cancer and other chronic diseases, as low as possible. As new scientific evidence is generated, air quality guidelines should be reviewed periodically, and updated where necessary.

Author Contributions

P.P.: Interpretation of data and data curation, writing and drafting of the manuscript; P.P., O.G., I.K., I.A.: Editing the manuscript. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Krieger, N.J. Climate crisis, health equity, and democratic governance: The need to act together. Public Health Policy 2020, 41, 4–10. [Google Scholar] [CrossRef] [PubMed]
  2. Urrutia-Pereira, M.; Guidos-Fogelbach, G.; Solé, D. Climate changes, air pollution and allergic diseases in childhood and adolescence. J. De Pediatr. 2022, 98 (Suppl. 1), S47–S54. [Google Scholar] [CrossRef] [PubMed]
  3. Eckhardt, C.M.; Wu, H. Environmental Exposures and Lung Aging: Molecular Mechanisms and Implications for Improving Respiratory Health. Curr. Environ. Health Rep. 2021, 8, 281–293. [Google Scholar] [CrossRef]
  4. Yang, J.; Zhou, M.; Li, M.; Yin, P.; Hu, J.; Zhang, C.; Wang, H.; Liu, Q.; Wang, B. Fine particulate matter constituents and cause-specific mortality in China: A nationwide modelling study. Environ. Int. 2020, 143, 105927. [Google Scholar] [CrossRef]
  5. Ordóñez-Iriarte, J.M. Mental health and environmental health. A prospective view. SESPAS Report 2020. Gac. Sanit. 2020, 34 (Suppl. 1), 68–75. [Google Scholar] [CrossRef] [PubMed]
  6. Park, J.; Kim, H.J.; Lee, C.H.; Lee, C.H.; Lee, H.W. Impact of long-term exposure to ambient air pollution on the incidence of chronic obstructive pulmonary disease: A systematic review and meta-analysis. Environ. Res. 2021, 194, 110703. [Google Scholar] [CrossRef]
  7. Fuertes, E.; Sunyer, J.; Gehring, U.; Porta, D.; Forastiere, F.; Cesaroni, G.; Vrijheid, M.; Guxens, M.; Annesi-Maesano, I.; Slama, R.; et al. Associations between air pollution and pediatric eczema, rhinoconjunctivitis and asthma: A meta-analysis of European birth cohorts. Environ. Int. 2020, 136, 105474. [Google Scholar] [CrossRef]
  8. Chen, J.; Hoek, G. Long-term exposure to PM and all-cause and cause-specific mortality: A systematic review and meta-analysis. Environ. Int. 2020, 143, 105974. [Google Scholar] [CrossRef]
  9. Rodosthenous, R.S.; Kloog, I.; Colicino, E.; Zhong, J.; Herrera, L.A.; Vokonas, P.; Schwartz, J.; Baccarelli, A.A.; Prada, D. Extracellular vesicle-enriched microRNAs interact in the association between long-term particulate matter and blood pressure in elderly men. Environ. Res. 2018, 167, 640–649. [Google Scholar] [CrossRef]
  10. Huangfu, P.; Atkinson, R. Long-term exposure to NO2 and O3 and all-cause and respiratory mortality: A systematic review and meta-analysis. Environ. Int. 2020, 144, 105998. [Google Scholar] [CrossRef]
  11. Sun, Z.; Zhu, D. Exposure to outdoor air pollution and its human-related health outcomes: An evidence gap map. BMJ Open 2019, 9, e031312. [Google Scholar] [CrossRef] [PubMed]
  12. Kim, H.-B.; Shim, J.-Y.; Park, B.; Lee, Y.-J. Long-Term Exposure to Air Pollutants and Cancer Mortality: A Meta-Analysis of Cohort Studies. Int. J. Environ. Res. Public Health 2018, 15, 2608. [Google Scholar] [CrossRef] [PubMed]
  13. Sui, J.; Xia, H.; Zhao, Q.; Sun, G.; Cai, Y. Long-Term Exposure to Fine Particulate Matter and the Risk of Chronic Liver Diseases: A Meta-Analysis of Observational Studies. Int. J. Environ. Res. Public Health 2022, 19, 10305. [Google Scholar] [CrossRef] [PubMed]
  14. Gabet, S.; Lemarchand, C.; Guénel, P.; Slama, R. Breast Cancer Risk in Association with Atmospheric Pollution Exposure: A Meta-Analysis of Effect Estimates Followed by a Health Impact Assessment. Environ. Health Perspect. 2021, 129, 57012. [Google Scholar] [CrossRef]
  15. Kang, J.; Jung, J.Y.; Huh, J.Y.; Ji, H.W.; Kim, H.C.; Lee, S.W. Behavioral interventions to reduce particulate matter exposure in patients with COPD. Medicine 2021, 100, e28119. [Google Scholar] [CrossRef]
  16. Hansel, N.N.; Putcha, N.; Woo, H.; Peng, R.; Diette, G.B.; Fawzy, A.; Wise, R.A.; Romero, K.; Davis, M.F.; Rule, A.M.; et al. Randomized Clinical Trial of Air Cleaners to Improve Indoor Air Quality and Chronic Obstructive Pulmonary Disease Health: Results of the CLEAN AIR Study. Am. J. Respir. Crit. Care Med. 2022, 205, 421–430. [Google Scholar] [CrossRef]
  17. Sordillo, J.E.; Rifas-Shiman, S.L.; Switkowski, K.; Coull, B.; Gibson, H.; Rice, M.; Platts-Mills, T.A.E.; Kloog, I.; Litonjua, A.A.; Gold, D.R.; et al. Prenatal oxidative balance and risk of asthma and allergic disease in adolescence. J. Allergy Clin. Immunol. 2019, 144, 1534–1541.e5. [Google Scholar] [CrossRef]
  18. Nicolaou, L.; Checkley, W. Differences between cigarette smoking and biomass smoke exposure: An in silico comparative assessment of particulate deposition in the lungs. Environ. Res. 2021, 197, 111116. [Google Scholar] [CrossRef]
  19. Okello, S.; Akello, S.J.; Dwomoh, E.; Byaruhanga, E.; Opio, C.K.; Zhang, R.; Corey, K.E.; Muyindike, W.R.; Ocama, P.; Christiani, D.D. Biomass fuel as a risk factor for esophageal squamous cell carcinoma: A systematic review and meta-analysis. Environ. Health 2019, 18, 60. [Google Scholar] [CrossRef]
  20. Lee, K.K.; Bing, R.; Kiang, J.; Bashir, S.; Spath, N.; Stelzle, D.; Mortimer, K.; Bularga, A.; Doudesis, D.; Joshi, S.S.; et al. Adverse health effects associated with household air pollution: A systematic review, meta-analysis, and burden estimation study. Lancet Glob. Health 2020, 8, e1427–e1434. [Google Scholar] [CrossRef]
  21. Chen, J.G.; Johnson, J.; Egner, P.; Ng, D.; Zhu, J.; Wang, J.B.; Xue, X.F.; Sun, Y.; Zhang, Y.H.; Lu, L.L.; et al. Dose-dependent detoxication of the airborne pollutant benzene in a randomized trial of broccoli sprout beverage in Qidong, China. Am. J. Clin. Nutr. 2019, 110, 675–684. [Google Scholar] [CrossRef] [PubMed]
  22. Filippini, T.; Hatch, E.E.; Rothman, K.J.; Heck, J.E.; Park, A.S.; Crippa, A.; Orsini, N.; Vinceti, M. Association between Outdoor Air Pollution and Childhood Leukemia: A Systematic Review and Dose-Response Meta-Analysis. Environ. Health Perspect. 2019, 127, 46002. [Google Scholar] [CrossRef]
  23. van Meel, E.R.; Mensink-Bout, S.M.; Den Dekker, H.T.; Ahluwalia, T.S.; Annesi-Maesano, I.; Arshad, S.H.; Baïz, N.; Barros, H.; von Berg, A.; Bisgaard, H.; et al. Early-life respiratory tract infections and the risk of school-age lower lung function and asthma: A meta-analysis of 150,000 European children. Eur. Respir. J. 2022, 60, 2102395. [Google Scholar] [CrossRef] [PubMed]
  24. Guo, C.; Sun, X.; Diao, W.; Shen, N.; He, B. Correlation of Clinical Symptoms and Sputum Inflammatory Markers with Air Pollutants in Stable COPD Patients in Beijing Area. Int. J. Chronic Obstr. Pulm. Dis. 2020, 15, 1507–1517. [Google Scholar] [CrossRef]
  25. Wang, Z.; Zhao, L.; Huang, Q.; Hong, A.; Yu, C.; Xiao, Q.; Zou, B.; Ji, S.; Zhang, L.; Zou, K.; et al. Traffic-related environmental factors and childhood obesity: A systematic review and meta-analysis. Obes. Rev. 2021, 22 (Suppl. 1), e12995. [Google Scholar] [CrossRef]
  26. Fuller, R.; Landrigan, P.J.; Balakrishnan, K.; Bathan, G.; Bose-O’Reilly, S.; Brauer, M.; Caravanos, J.; Chiles, T.; Cohen, A.; Corra, L.; et al. Pollution and health: A progress update. Planet Health 2022, 6, e535–e547. [Google Scholar] [CrossRef] [PubMed]
  27. Del Moral, R.; Walker, L.R. Environment and Health; Parisianou S.A.: Athens, Greece, 2016; ISBN 9789605830700. (In Greek) [Google Scholar]
  28. Benavides, J.; Rowland, S.T.; Shearston, J.A.; Nunez, Y.; Jack, D.W.; Kioumourtzoglou, M.A. Methods of evaluating environmental health impact at different stages of the policy process in cities. Curr. Environ. Health Rep. 2022, 9, 183–195. [Google Scholar] [CrossRef]
Figure 1. Flow chart illustrating the process of searching and locating research articles.
Figure 1. Flow chart illustrating the process of searching and locating research articles.
Environsciproc 26 00118 g001
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MDPI and ACS Style

Petropoulou, P.; Artopoulou, I.; Kalemikerakis, I.; Govina, O. Environment and Public Health: Air Pollution and Chronic Diseases. Environ. Sci. Proc. 2023, 26, 118. https://doi.org/10.3390/environsciproc2023026118

AMA Style

Petropoulou P, Artopoulou I, Kalemikerakis I, Govina O. Environment and Public Health: Air Pollution and Chronic Diseases. Environmental Sciences Proceedings. 2023; 26(1):118. https://doi.org/10.3390/environsciproc2023026118

Chicago/Turabian Style

Petropoulou, Pinelopi, Ioli Artopoulou, Ioannis Kalemikerakis, and Ourania Govina. 2023. "Environment and Public Health: Air Pollution and Chronic Diseases" Environmental Sciences Proceedings 26, no. 1: 118. https://doi.org/10.3390/environsciproc2023026118

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