Open access
Review Article
1 September 2021

Systematic Review of Exposure to Polycyclic Aromatic Hydrocarbons and Obstructive Lung Disease

Publication: Journal of Health and Pollution
Volume 11, Issue 31
CID: 210903

Abstract

Background.

There is fast-growing epidemiologic evidence of the effects of environmental chemicals on respiratory health. Polycyclic aromatic hydrocarbons (PAHs) have been linked with airway obstruction common in asthma and/or asthma exacerbation, and chronic bronchitis and emphysema.

Objectives.

A systematic review of the association between exposure to PAHs and obstructive lung diseases is not yet available. The present systematic review aims to evaluate the evidence available in epidemiological studies that have associated PAHs with obstructive lung diseases such as asthma, chronic bronchitis, emphysema.

Methods.

We performed a systematic literature search on PubMed, Google Scholar, and Scopus databases using relevant keywords and guided by predesigned eligibility criteria.

Results.

From the total of 30 articles reviewed, 16 articles examined the link between PAHs and lung function in both adults and children. Twelve articles investigated the association between PAHs and asthma, asthma biomarkers, and/or asthma symptoms in children. Two articles studied the relationship between PAHs and fractional exhaled nitric oxide (FeNO), a biomarker of airway inflammation and the relationship between PAHs and obstructive lung diseases and infections, respectively. One study assessed exposure to daily ambient PAHs and cough occurrence.

Discussion.

Twenty-seven studies found an association between PAHs and asthma and reduced lung function. In children it is reinforced by studies on prenatal and postnatal exposure, whereas in adults, reductions in lung function tests marked by low forced expiratory volume in 1 second, (FEV1), forced vital capacity (FVC), and forced expiratory flow (FEF25–75%) were the major health outcomes. Some studies recorded contrasting results: insignificant and/or no association between the two variables of interest. The studies reviewed had limitations ranging from small sample size, to the use of cross-sectional rather than longitudinal study design.

Conclusions.

The literature reviewed in the present study largely suggest positive correlations between PAHs and obstructive lung diseases marked mainly by asthma and reduced respiratory function. This review was registered with PROSPERO (Registration no: CRD42020212894)

Competing Interests.

The authors declare no competing financial interests.

Introduction

Polycyclic aromatic hydrocarbons (PAHs) are a common group of environmental pollutants that usually occur as complex mixtures of over 300 organic compounds composed of multiple aromatic rings. Polycyclic aromatic hydrocarbons are compounds of interest due to their widespread presence as well as their carcinogenic, mutagenic and toxicologic potential.1
Globally, the negative impact of PAHs on health is a major public health concern. Apart from being linked to increasing risk of cancers,2 impaired neurodevelopment,3 genotoxicity,4 cardiovascular disease,5 metabolic syndromes,6 and recently onset of diabetes mellitus,7 PAH exposure may also lead to non-cancerous health effects, particularly respiratory diseases such asthma and chronic obstructive pulmonary disease (COPD).810
The World Health Organization (WHO) estimate indicates that more than 80% of deaths associated with chronic obstructive pulmonary disease (COPD) occurred in low- and middle income countries (LMIC) in 2019,11 although the burden of COPD attributable to PAHs remains unknown.
Human populations can encounter health risks from PAHs via a variety of exposure pathways, including inhalation of ambient air containing PAHs, e.g., tobacco smoke, contaminated air from incomplete burning of coal, consumption of charbroiled foods, and use of coal or wood stoves, fireplaces for cooking and residential heating, industrial processes, vehicle exhaust, fossil fuels, and dermal contacts with environmental media such as contaminated soil and water.1214 The use of biomass (solid fuel) for cooking, lighting, and heating residence generates PAHs.15 Studies conducted by Pruneda-Alvarez et al. reported that women in developing countries using biomass as fuel in their home for cooking have greater exposure to PAHs than those who cook outside their homes or those who do not use biomass as fuel.16
Exposure to PAHs in adults seems to be linked to respiratory function and symptoms demonstrated as spirometric lung function parameters such as reduced forced expiratory volume in 1 second, (FEV1), which is the volume of air exhaled at the end of the first second of forced expiration; forced vital capacity (FVC), the volume of air that can be forcibly breathed out after taking the deepest breath possible and forced expiratory flow at 25 and 75% (FEF25%–75%) of the pulmonary volume.1719 A comprehensive review by Lag et al. supports the notion that air-borne and particulate-bound PAH exposure may contribute to the development and/or exacerbation of respiratory disease and dysfunction.20 Jedrichowski et al. revealed a strong association between prenatal exposure to PAHs and particulate matter less than 2.5 micrometers in diameter (PM2.5) and asthma, wheezing, and cough in the first two years of life among children who were prenatally exposed.21 Huang et al. observed that an increase in concentration of urinary PAH metabolites was significantly associated with elevated risk of adult asthma.22

Abbreviations

COPD
Chronic obstructive pulmonary disease
FEF25–75%
Forced expiratory flow at 25–75%
FEV1
Forced expiratory volume in 1 second
FVC
Forced vital capacity
OR
Odds ratio
A cohort study by Zhou et al. reported negative associations between monohydroxy PAHs (OH-PAHs) and lung function. In this study, each unit increase in sum total of low molecular weight (LMW) and high molecular weight (HMW) – PAHs was associated with a decrease in FEV1 and FVC, respectively.23
Adverse respiratory health outcomes in children such as bronchitis have also been linked to PAH exposure.2425 as well as decrements in lung function parameters.2629 Reductions in the ratio of FEV1/FVC among adults in work settings was found to be linked with increased PAH exposures.30
Reviews exist on the association between PAHs in ambient air pollution and non-malignant respiratory diseases focusing on air pollution as the main source of exposure, but a comprehensive systematic review with a precise question about the link between obstructive lung diseases and PAHs exposure irrespective of the exposure route is non-existent. The purpose of this systematic review, therefore, was to evaluate the evidence available for an association between PAHs from all exposure routes (inhalation, ingestion, and dermal uptake) and obstructive lung diseases (asthma and COPD: chronic bronchitis and emphysema) as well as the strength of the association. The present study is expected to provide epidemiological evidence that could be useful in exploring the etiology of obstructive respiratory diseases.

Methods

First, a search was performed on existing systematic reviews available in suitable electronic databases to ensure similar study had not yet been previously published to avoid duplication. A review protocol was then developed for our review question and the protocol was registered with PROSPERO (International prospective register of systematic reviews, 2020, CRD42020212894).31

Study criteria and search strategy

The present study searched electronic databases of PubMed, Google Scholar, and Scopus in between August and September 2020. An advanced search builder was used to search in PubMed and Scopus. We considered studies with cohort, cross-sectional, case-control, and panel study designs, and articles written in the English language with no restrictions on publication date, and studies reporting both prenatal and post-natal exposure to PAHs, studies that examined exposure in children and adults with no age restrictions investigating the association between PAHs and obstructive lung diseases such as asthma and COPD. Studies were excluded if they were reviews, abstracts, editorials, commentaries, measured other pollutants aside from PAHs, or were published in languages other than English. The search strategy was modified when searching different databases. The following keywords were used to retrieve relevant articles:
“polycyclic aromatic hydrocarbons” OR “PAHs” OR “anthracene” OR “pyrene” OR “hydroxypyrene” OR “1-OHP” OR “benzo(a)pyrene” OR “BaP” OR “phenanthrene” OR “hydroxyphenanthrene” OR “fluorene” OR “hydroxyfluorene” OR “naphthalene” OR “hydroxynaphthalene” AND “obstructive lung disease” OR “asthma” OR “wheezing” OR “bronchitis” OR “emphysema” OR “COPD.”
In addition, the references of the retrieved articles were checked for additional studies. A reference manager (Endnote, version X9.2, Clarivate analytics, Philadelphia, USA) was used to manage the retrieved literature and to check for duplicates.

Data screening and extraction

To select relevant articles, two members of the review team first reviewed the articles independently based on title and abstract. Having examined the titles, name of author, year of publication, journal name and issue number, duplicates were removed. We carefully screened articles again by titles and abstract, and finally by full texts available. Articles that were relevant to our objective were selected for inclusion while the others were excluded. Data from all the included studies were extracted with the help of a form predesigned by the reviewers (Supplemental Material 1) The data can be found in the summary of epidemiological studies included (Supplemental Material 2). Data includes: first author and publication year, study design, study participants and age at exposure, country of study or setting, exposure assessment, exposure metrics/study period outcome indicators, and key findings. The eligibility criteria mentioned earlier guided the entire screening process. Disagreements on article screening and data extraction were resolved by consulting with the third reviewer. Two reviewers disagreed on the inclusion of articles whose titles showed joint effects of PAHs and other pollutants. This was resolved by the third review who felt that those studies should be excluded on the grounds that the presence of other pollutants might have confounding effects on reported outcomes.

Risk of bias assessment

Assessment of the quality of individual studies was done using the approach outlined by the Strengthening the Reporting of Observational Studies in Epidemiology (STROBE) checklist. The STROBE statement is a 22-item checklist used to effectively report observational studies. These items assessed the following sections of the articles: Title and abstract (item 1), Introduction (items 2 and 3), Methods (items 4–12), Results (items 13–17), Discussion (item 18–21), and other information (item 22 on funding).32
Using the 22-item checklist, two reviewers independently appraised the methodological quality of the included studies. For a study, each item was assigned “0,” “1” or a maximum score of “2,” depending on how they meet the requirements of each item. By assigning one score to each item, papers could get a total minimum score of 22 and a maximum score of 44. These ratings are provided in a Table (Supplemental Material 3). Articles that scored 22 points and above were included in our review.

Results

Study selection was done using an adapted PRISMA (Preferred Reporting Items for Systematic Reviews and Meta-analyses)33 diagram and shown in Figure 1. Studies included in our review are summarized in Supplemental Material 2, and the characteristics of included studies are summarized in Table 1.
Figure 1 —A Study Selection Flowchart
Table 1 —Characteristics of included epidemiological studies
Study designStudy populationSettingExposure assessmentOutcomeKey findings
Of all the study designs, cohort and cross-sectional studies were more frequent. There were 12 cross-sectional studies 1718,26,29,3441
11 cohort19,21,2728,30,4247
Four (4) case-controls8,22,4849, and three (3) panel Studies5052
The greatest number of participants is 15, 447 reported in a cross-sectional study by Liu et al., 201539 whereas the lowest number of participants was 64 reported by Barraza-Villarreal et al.26Ten (10) studies were conducted in China1719,22,30,3536,38,49,52 followed by nine (9) studies29,37,39,41,42,4447 performed in the United States while others were conducted in different regions of the world: Canada, India, Japan, Korea, Mexico, New Zealand, Poland, and Saudi ArabiaEighteen (18) studies1819,22,2627,30,3437,3941,46,49, 51 detected PAHs using the urinary metabolites. Five (5) studies17,29,42,50,52 assessed PAHs by ambient (residential) air monitoring using air particle/PAHs sampler. One (1) study38 jointly used both urinary PAHs metabolites and ambient air monitoring. Five (5) studies28,4347 measured both pre-natal and post-natal exposure by personal air monitoring of PAHs during the second or trimester of pregnancy and residential (indoor and outdoor) air monitoring during childhood up to 5–6 years of age respectively. Two studies8,20 by measuring serum PAHs levels and PAH-DNA adducts in umbilical cord blood respectively. Only one study measured blood PAHs level.Twelve (12) studies1719,2630,3436,52 reported health outcomes as lung functions assessed by their spirometric values. Eleven (11) studies8,2122,37,39,42,4445,4749 reported health outcome as asthma. Two (2) studies43,50 reported chronic cough and number of wheezing days while two studies 38,50 reported increased exhaled nitric oxide, FeNO as the outcome. One (1) study41 reported asthma, chronic bronchitis and emphysema, wheezing, coughing, ear infection collectively. One (1) study26 also reported that decreased pH of EBC, a biomarker of airway inflammation as the health outcome.Fourteen (14) studies 8,21,22,37,39,4245,4750 revealed positive associations between PAHs and diagnosed asthma, asthma biomarkers: IgE, IL-4, resistin anti-mouse IgE and asthma symptoms e.g chronic cough, wheezing, and shortness of breath. Thirteen (13) studies 1719,2630,3437,52 reported inverse associations between PAHs and lung function parameters (FEV1, FVC, FEV1/FVC, FEF25–75%) as seen by reductions in spirometry test values performed. One (1) study41 showed a relationship between PAHs (2-hydroxyfluorene) and prevalent cases of chronic bronchitis and emphysema. Two (2) studies38,50 reported an association between PAHs and an increase in exhaled nitric oxide (NO) and (FeNO). One (1) study [26] found an association between PAH and PH of EBC, which is a biomarker of airway inflammation and increase in 2-hydroxyfluorene.

Quality assessment of included studies

Supplemental Material 3 shows the quality assessment of studies included in this review. Of the 22 items in the STROBE checklist,32 all studies reported study designs, settings, and locations, exposure, diagnostic criteria, details of methods of assessment, and sources of data. All the cohort studies19,21,2728,30,4247 reported the sources of data, method of selection of participants, inclusion and exclusion criteria, method of follow-up, and follow-up period. Of the four case-control studies, only two48,49 gave eligibility criteria for case and control, sources of data and method of case ascertainment, and control selection. All twelve cross-sectional studies1718,26,29,3441 reported inclusion and exclusion criteria, source of data, and method of selection of participants. Seven studies8,3940,45,47,48,50 did not explain how to control for confounding factors. It is not clear how studies dealt with readings of PAHs below the limit of detection except in Epton et al.51

Discussion

Polycyclic aromatic hydrocarbons are widely distributed in the environment through various anthropogenic sources. Knowing the effects of PAHs on respiratory function is of particular interest due to their toxicological characteristics, especially carcinogenic, mutagenic, and teratogenic tendencies. Although PAHs are generally associated with obstructive respiratory diseases, there has been no systematic review assessing the strength of evidence behind this association. To the best of our knowledge, this is the first systematic review to evaluate the evidence of the association.
The conclusions from the array of included studies with regards to the association between exposure to PAHs and respiratory disease in humans were varied.
First, this present review found that many of the studies conducted at different times have the same positive relationships between PAHs and respiratory symptoms among different populations, using similar study designs, and that asthma was studied more than other obstructive lung diseases. The outcome of most studies showed greater odds of association between PAHs exposure and asthma as well as with development of asthma symptoms such as wheezing in individuals with and without preexisting asthma.2122,39,4345,4750 For example, this is shown in the case-control studies by Huang et al.22 and Suresh et al.48
Huang et al. reported that PAHs: 2-hydroxyfluorene, 4-hydroxyphenanthrene, 1-hydroxyphenanthrene, and 1-hydroxypyrene were associated with elevated risks of asthma (odds ratio (OR) 2.04, 2.38, 2.04, and 2.35, respectively). Studies by Suresh et al. showed a high blood level of phenanthrene associated with bronchial asthma. (adjusted OR = 13.3, 95% confidence interval (Cl) 1.9–88.5) when compared with matched controls.
Another interesting finding is that prenatal exposure to PAHs can lead to respiratory symptoms during the early childhood in children exposed during pregnancy. Jedrichowski et al. reported that prenatal level of PAH-DNA (deoxyribonucleic) adducts correlated with wheezing days during the first two years of life (incident rate ratio: 1.69, 95% CI, 1.52 – 1.88).21 Polycyclic aromatic hydrocarbons also correlated with biomarkers of respiratory symptoms. Studies by Al-daghri et al., Li et al., and Anyenda et al. showed correlations with PAHs and immunoglobulin E IgE, interleukin 4 IL-4 and resistin, increased nitric oxide (NO) and fractional exhaled nitric oxide (FENO) which are biomarkers of childhood asthma and airway inflammation, respectively.8,38,50 However, Shiue et al. reported an inverse association between PAHs and asthma, although it showed a positive association between 2-hydroxyfluorene, 3-hydroxyfluorene and prevalent cases of emphysema. (OR: 1.60; 95% Cl: 1.26–2.03) and (OR: 1.42; CI, 1.15–1.77) respectively, and chronic bronchitis, (OR, 1.42, 95% CI, 1.04–1.94)
Secondly, the majority of the studies: (cross-sectional1718, 26,2934,37 and cohort studies19,27,28,30) found positive correlations between PAHs and reductions in lung function parameters: such as FEV1, FVC, and the ratio of both FEV/FVC, and FEF25–75% after adjusting for possible confounders such as age, gender, dust exposure, body mass index (BMI) z-score, serum cotinine (a biomarker of passive tobacco smoke exposure), and family history of asthma. This finding is particularly important given that most of the studies in this review were related to asthma and thus provides evidence of possible association between PAH exposure and other obstructive airway diseases.
Third, the present study found that the claims of some studies in this review contradicted the general results. Rodriguez et al. reported no association between urinary 1-hydroxypyrene (1-OHP) concentration and respiratory function as lung functions were categorized as normal.40 Padula et al. reported that no association was observed with the sum total of 4,- 5,- and 6 ringed PAH, ΣPAH456 and respiratory functions among asthmatic children.29 Findings by Miller et al indicated that PAH metabolite concentrations were not associated with asthma or any of the respiratory symptoms examined.46 Rosa et al. claimed that prenatal PAH exposure alone was not associated with asthma nor IgE at 5–6 years among children not exposed to environmental tobacco smoke (OR, 0.65; 95% CI, 0.41–1.01).47 IgE is an immunoglobulin which facilitates type 1 hypersensitivity reactions and plays a significant role in the pathogenesis of allergic asthma. Serum IgE associates closely with the risk of asthma.53
Epton et al. recorded no significant difference in FEV1 between asthmatics and non-asthmatics although the ratio of FEV1/FVC was significantly lower in the asthmatic participants who were exposed to PAHs.51 Han et al. reported that although an increase in total PAHs was associated with reduced FEV1 in children with pre-existing asthma, there was no significant association between urinary PAHs and lung function among non-asthmatic children.37
The studies in this review have a number of strengths. A significant proportion of the studies (twenty-two studies)1719,21,22,27,29,30,3437,39,41,4247,49,52 were conducted using a relatively large number of study participants ranging from 222 to 15 447. This has the statistical relevance of controlling for the risk of reporting false negative findings (type II error). It is well known that the generalizability of the results is limited by small sample size. In this review, small sample size (which ranged from 20 – 195) were found in eight studies.8,26,28,38,40,48,50,51
The power of a study is limited by small sample size which directly affects the statistical significance of some associations and the possible bias of study design. This can be said to be evident in studies by Li et al.38 and Rodriguez-Aguilar et al.40 Whereas Rodriguez et al. with a smaller sample size (134) found no association between 1-hydroxypyrene (1-OHP) and any respiratory symptoms, the study by Shen et al. with a larger sample size (505) found a strong association between 1-OHP and lower FEV1/FVC.17
Urinary assessment for PAHs is the most reoccurring means of exposure assessment in the studies reviewed. This is most likely due to its non-invasiveness and ease of collection which is convenient especially for studies involving a large number of participants. However, some studies18,30,35 opined that the use of single spot urine samples for exposure assessment has its limitations as it only reflects recent exposures but cannot indicate a past long-term level of PAH exposures. Repeated urine metabolite measurement and the use of 24-hour urine to measure past, chronic exposures were stated as preferable options to adequately describe this association.18,30 Theoretically, 24-hour void may be more reliable than spot urine, but it is not convenient to collect from study subjects and non-compliance can introduce bias in the sampling process. The use of first morning void as an alternative can be explained on the basis that it is often associated with 24-h void.5455 Large epidemiological studies involving a large number of participants, may encounter difficulties trying to collect first-morning voids, hence, spot urine has been used as a more practical, less cumbersome method. Although PAHs are varied in nature, this review has observed that both the LMW-PAHs: naphthalene, fluorene, phenanthrene and HMW PAHs: those with 4 or more fused rings such as pyrene were associated with obstructive lung diseases.
Finally, we observed that majority of the studies were conducted in higher income countries, mainly China and the United States. It is therefore recommended that more studies be carried out in sub-Saharan African and other LMIC where there are often weak environmental pollution controls and more than 60% of heating and cooking fuel is derived from solid fuel such as coal and firewood.15

Conclusions

Overall, the findings of the present review provide substantial evidence of the association between PAH exposure and obstructive lung diseases such as asthma, bronchitis, and emphysema, which is marked by reduced respiratory function. We therefore recommend that efforts be put in place to check future exposures, both prenatal/post and adult exposures, through policy making and other public health actions. Further research should focus on LMIC using longitudinal studies with long-term follow-up. This study can provide useful data in the evaluation of respiratory disease as patient exposures prior to disease onset is crucial to a fuller understanding of disease development.

Acknowledgments

The authors wish to acknowledge the technical support provided by Prof. Ogbonna Joel, leader, Center for Chemical and Oil Field Research, University of Port Harcourt for granting us access to their e-library. We are grateful to two anonymous editors for very good contributions to the manuscript prior to submission.

Article Notes

This study was funded as part of employment.

Supplementary Material

File (nwaozuzu_supplemental_material_1.docx)
File (nwaozuzu_supplemental_material_2.docx)
File (nwaozuzu_supplemental_material_3.docx)

References

1.
Lawal AT. Polycyclic aromatic hydrocarbons. A review. Cogent Env Sci, 2017 Jan 1; 3(1): 1339841 https://doi.org/10.1080/23311843.2017.1339841
2.
Mastrangelo G, Fadda E, Marzia V. Polycyclic aromatic hydrocarbons and cancer in man. Env Health Persp, 1996 Nov; 104(11): 1166–70. https://dx.doi.org/10.1289%2Fehp.961041166
3.
Perera F, Li TY, Zhou ZJ, Yuan T, Chen YH, Qu L, Rauh VA, Zhang Y, Tang D. Benefits of reducing prenatal exposure to coal-burning pollutants to children's neurodevelopment in China. Env Health Persp, 2008 Oct; 116(10): 1396–400. https://dx.doi.org/10.1289%2Fehp.11480
4.
Gamboa RT, Gamboa AR, Bravo AH, Ostrosky WP. Genotoxicity in child populations exposed to polycyclic aromatic hydrocarbons (PAHs) in the air from Tabasco, Mexico. Int J Env Res Pub He, 2008 Dec; 5(5): 349–55. https://doi.org/10.3390/ijerph5050349
5.
Feng Y, Sun H, Song Y, Bao J, Huang X, Ye J, Yuan J, Chen W, Christiani DC, Wu T, Zhang X. A community study of the effect of polycyclic aromatic hydrocarbon metabolites on heart rate variability based on the Framingham risk score. Occup Env Med, 2014 May 1; 71(5): 338–45. https://doi.org/10.11136/oemed-2013%E2%80%93101884
6.
Brocato J, Sun H, Shamy M, Kluz T, Alghamdi MA, Khoder MI, Chen LC, Costa M. Particulate matter from Saudi Arabia induces genes involved in inflammation, metabolic syndrome and atherosclerosis. J. Toxicol Env Health Part A, 2014 Jul 18; 77(13): 751–66. https://doi.org/10.1080/15287394.2014.892446
7.
Yang L, Zhou Y, Sun H, Lai H, Liu C, Yan K, Yuan J, Wu T, Chen W, Zhang X. Dose-response relationship between polycyclic aromatic hydrocarbon metabolites and risk of diabetes in the general Chinese population. Env Pollut, 2014 Dec 1; 195: 24–30. https://doi.org/10.1016/j.envpol.2014.08.012
8.
Al-Daghri NM, Alokail MS, Abd-Alrahman SH, Draz HM, Yakout SM, Clerici M. Polycyclic aromatic hydrocarbon exposure and pediatric asthma in children: a case–control study. Env Health, 2013 Dec; 12(1): 1–6. https://doi.org/10.1186/1476-069x-12-1
9.
Burstyn I, Boffetta P, Heederik D, Partanen T, Kromhout H, Svane O, Langård S, Frentzel-Beyme R, Kauppinen T, Stücker I, Shaham J. Mortality from obstructive lung diseases and exposure to polycyclic aromatic hydrocarbons among asphalt workers. Am J Epidemiol, 2003 Sep 1; 158(5): 468–78. https://doi.org/10.1093/aje/kwg180
10.
Armstrong B, Hutchinson E, Unwin J, Fletcher T. Lung cancer risk after exposure to polycyclic aromatic hydrocarbons: a review and meta-analysis. Env Health Persp, 2004 Jun; 112(9): 970–8. https://dx.doi.org/10.1289%2Fehp.6895
11.
World Health Organization. Chronic Obstructive pulmonary disease (COPD) [internet]; 2017. https://www.who.int/news-room/fact-sheets/detail/chronic-obstructive-pulmonary-disease-(copd)
12.
Abdel-Shafy HI, Mansour MS. A review on polycyclic aromatic hydrocarbons: source, environmental impact, effect on human health and remediation. Egypt J Pet, 2016 Mar 1; 25(1): 107–23. https://doi.org/10.1016/j.ejpe.2015.03.011
13.
Srogi K. Monitoring of environmental exposure to polycyclic aromatic hydrocarbons: a review. Env Chem Lett, 2007 Nov; 5(4): 169–95. https://doi.org/10.1007/s10311-007-0095-0
14.
Ramesh A, Walker SA, Hood DB, Guillén MD, Schneider K, Weyand EH. Bioavailability and risk assessment of orally ingested polycyclic aromatic hydrocarbons. Int J Toxicol, 2004 Sep; 23(5): 301–33. https://doi.org/10.1080/10915810490517063
15.
Gordon SB, Bruce NG, Grigg J, Hibberd PL, Kurmi OP, Lam KB, Mortimer K, Asante KP, Balakrishnan K, Balmes J, Bar-Zeev N. Respiratory risks from household air pollution in low- and middle-income countries. Lancet Respir Med, 2014 Oct 1; 2(10): 823–60. https://dx.doi.org/10.1016%2FS2213-2600(14)70168-7
16.
Pruneda-Álvarez LG, Pérez-Vázquez FJ, Salgado-Bustamante M, Martínez-Salinas RI, Pelallo-Martínez NA, Pérez-Maldonado IN. Exposure to indoor air pollutants (polycyclic aromatic hydrocarbons, toluene, benzene) in Mexican indigenous women. Indoor Air, 2012 Apr; 22(2): 140–7. https://doi.org/10.1111/j.1600-0668.2011.00750.x
17.
Shen M, Xing J, Ji Q, Li Z, Wang Y, Zhao H, Wang Q, Wang T, Yu L, Zhang X, Sun Y. Declining pulmonary function in populations with long-term exposure to polycyclic aromatic hydrocarbons-enriched PM2. 5. Env Sci Technol, 2018 Apr 19; 52(11): 6610–6. https://doi.org/10.1021/acs.est.8b00686
18.
Zhang LP, Zhang X, Duan HW, Meng T, Niu Y, Huang CF, Gao WM, Yu SF, Zheng YX. Long-term exposure to diesel engine exhaust induced lung function decline in a cross-sectional study. Ind Health, 2017 Jan 31; 55(1): 13–26. https://doi.org/10.2486/indhealth.2016-0031
19.
Zhou Y, Sun H, Xie J, Song Y, Liu Y, Huang X, Zhou T, Rong Y, Wu T, Yuan J, Chen W. Urinary polycyclic aromatic hydrocarbon metabolites and altered lung function in Wuhan, China. Am J Respir Crit Care Med, 2016 Apr 15; 193(8): 835–46. https://doi.org/10.1164/rccm.201412-2279oc
20.
Låg M, Øvrevik J, Refsnes M, Holme JA. Potential role of polycyclic aromatic hydrocarbons in air pollution-induced non-malignant respiratory diseases. Respir Res, 2020 Dec; 21(1): 1–22. https://doi.org/10.1186/s12931-020-01563-1
21.
Jedrychowski WA, Perera FP, Maugeri U, Mrozek-Budzyn D, Mroz E, Klimaszewska-Rembiasz M, Flak E, Edwards S, Spengler J, Jacek R, Sowa A. Intrauterine exposure to polycyclic aromatic hydrocarbons, fine particulate matter and early wheeze. Prospective birth cohort study in 4-year-olds. Pediatr Allergy Immunol, 2010 Jun; 21(4p2): e723–32. https://doi.org/10.1111/j.1399-3038.2010.01034.x
22.
Huang X, Zhou Y, Cui X, Wu X, Yuan J, Xie J, Chen W. Urinary polycyclic aromatic hydrocarbon metabolites and adult asthma: a case-control study. Sci Rep, 2018 May 16; 8(1): 1–8. https://doi.org/10.1038/s41598-018-26021-3
23.
Zhou Y, Mu G, Liu Y, Xiao L, Ma J, Wang B, Shi T, Tan A, Yuan J, Chen W. Urinary polycyclic aromatic hydrocarbon metabolites, Club cell secretory protein and lung function. Environment international. 2018 Feb 1; 111: 109–16. https://doi.org/10.1016/j.envint.2017.11.016
24.
Hertz-Picciotto I, Baker RJ, Yap PS, Dostál M, Joad JP, Lipsett M, Greenfield T, Herr CE, Beneš I, Shumway RH, Pinkerton KE. Early childhood lower respiratory illness and air pollution. Env Health Persp, 2007 Oct; 115(10): 1510–8. https://doi.org/10.1289/ehp.9617
25.
Jedrychowski W, Galas A, Pac A, Flak E, Camman D, Rauh V, Perera F. Prenatal ambient air exposure to polycyclic aromatic hydrocarbons and the occurrence of respiratory symptoms over the first year of life. Eur J Epidemiol, 2005 Sep; 20(9): 775–82. https://doi.org/10.1007/s10654-005-1048-1
26.
Barraza-Villarreal A, Escamilla-Nuñez MC, Schilmann A, Hernandez-Cadena L, Li Z, Romanoff L, Sjödin A, Del Río-Navarro BE, Díaz-Sanchez D, Díaz-Barriga F, Sly P. Lung function, airway inflammation, and polycyclic aromatic hydrocarbons exposure in Mexican schoolchildren: a pilot study. J Occup Env Med, 2014 Apr; 56(4): 415. https://doi.org/10.1097/jom.0000000000000111
27.
Choi YH, Kim JH, Hong YC. CYP1A1 genetic polymorphism and polycyclic aromatic hydrocarbons on pulmonary function in the elderly: haplotype-based approach for gene–environment interaction. Toxicol Lett, 2013 Aug 29; 221(3): 185–90. https://doi.org/10.1016/j.toxlet.2013.06.229
28.
Jedrychowski WA, Perera FP, Maugeri U, Majewska R, Mroz E, Flak E, Camann D, Sowa A, Jacek R. Long term effects of prenatal and postnatal airborne PAH exposures on ventilatory lung function of non-asthmatic preadolescent children. Prospective birth cohort study in Krakow. Sci Total Env, 2015 Jan 1; 502: 502–9. https://doi.org/10.1016/j.scitotenv.2014.09.051
29.
Padula AM, Balmes JR, Eisen EA, Mann J, Noth EM, Lurmann FW, Pratt B, Tager IB, Nadeau K, Hammond SK. Ambient polycyclic aromatic hydrocarbons and pulmonary function in children. J Expo Sci Env Epidemiol, 2015 May; 25(3): 295–302. https://doi.org/10.1038/jes.2014.42
30.
Wang S, Bai Y, Deng Q, Chen Z, Dai J, Li X, Zhang W, Zhang X, He M, Wu T, Guo H. Polycyclic aromatic hydrocarbons exposure and lung function decline among coke-oven workers: a four-year follow-up study. Env Res, 2016 Oct 1; 150: 14–22. https://doi.org/10.1016/j.envres.2016.05.025
31.
International Prospective Register of Systematic Reviews (PROSPERO) https://www.crd.york.ac.uk/prospero/
32.
Elm EV, Altman DG, Egger M, Pocock SJ, Gotzsche PC, Vandenbroucke JP. Policy and practice-the strengthening the reporting of observational studies in epidemiology (STROBE) statement: guidelines for reporting observational studies. Bulletin of the World Health Organization. 2007; 85(11): 867–72. https://doi.org/10.1371/journal.pmed.0040296
33.
Moher D, Shamseer L, Clarke M, Ghersi D, Liberati A, Petticrew M, Shekelle P, Stewart LA. Preferred reporting items for systematic review and meta-analysis protocols (PRISMA-P) 2015 statement. Systematic reviews, 2015 Dec; 4(1): 1–9. https://doi.org/10.1186/2046-4053-4-1
34.
Cakmak S, Hebbern C, Cakmak JD, Dales RE. The influence of polycyclic aromatic hydrocarbons on lung function in a representative sample of the Canadian population. Env Pollut, 2017 Sep 1; 228: 1–7. https://doi.org/10.1016/j.envpol.2017.05.013
35.
Cao L, Zhou Y, Tan A, Shi T, Zhu C, Xiao L, Zhang Z, Yang S, Mu G, Wang X, Wang D. Oxidative damage mediates the association between polycyclic aromatic hydrocarbon exposure and lung function. Env Health, 2020 Dec; 19(1): 1–0. https://doi.org/10.1186/s12940-020-00621-x
36.
Hou J, Sun H, Ma J, Zhou Y, Xiao L, Xu T, Cheng J, Chen W, Yuan J. Impacts of low socioeconomic status and polycyclic aromatic hydrocarbons exposure on lung function among a community-based Chinese population. Sci Total Env, 2017 Jan 1; 574: 1095–103. https://doi.org/10.1016/j.scitotenv.2016.09.034
37.
Han YY, Rosser F, Forno E, Celedón JC. Exposure to polycyclic aromatic hydrocarbons, vitamin D, and lung function in children with asthma. Pediatr Pulmonol, 2018 Oct; 53(10): 1362–8. https://dx.doi.org/10.1002%2Fppul.24084
38.
Li T, Wang Y, Hou J, Zheng D, Wang G, Hu C, Xu T, Cheng J, Yin W, Mao X, Wang L. Associations between inhaled doses of PM2. 5-bound polycyclic aromatic hydrocarbons and fractional exhaled nitric oxide. Chemosphere, 2019 Mar 1; 218: 992–1001. https://doi.org/10.1016/j.chemosphere.2018.11.196
39.
Liu H, Xu C, Jiang ZY, Gu A. Association of polycyclic aromatic hydrocarbons and asthma among children 6–19 years: NHANES 2001–2008 and NHANES 2011–2012. Respir Med, 2016 Jan 1; 110: 20–7. https://doi.org/10.1016/j.rmed.2015.11.003
40.
Rodríguez-Aguilar M, de León-Martínez LD, García-Luna S, Gómez-Gómez A, González-Palomo AK, Pérez-Vázquez FJ, Díaz-Barriga F, Trujillo J, Flores-Ramírez R. Respiratory health assessment and exposure to polycyclic aromatic hydrocarbons in Mexican indigenous population. Env Sci Pollut, 2019 Sep; 26(25): 25825–33. https://doi.org/10.1007/s11356-019-05687-w
41.
Shiue I. Urinary polyaromatic hydrocarbons are associated with adult emphysema, chronic bronchitis, asthma, and infections: US NHANES, 2011–2012. Env Sci Pollut Res, 2016 Dec; 23(24): 25494–500. https://doi.org/10.1007/s11356-016-7867-7
42.
Gale SL, Noth EM, Mann J, Balmes J, Hammond SK, Tager IB. Polycyclic aromatic hydrocarbon exposure and wheeze in a cohort of children with asthma in Fresno, CA. J. Expo Sci Env Epidemiol, 2012 Jul; 22(4): 386–92. https://doi.org/10.1038/jes.2012.29
43.
Jedrychowski WA, Perera FP, Majewska R, Camman D, Spengler JD, Mroz E, Stigter L, Flak E, Jacek R. Separate and joint effects of tranplacental and postnatal inhalatory exposure to polycyclic aromatic hydrocarbons: prospective birth cohort study on wheezing events. Pediatr Pulmonol, 2014 Feb; 49(2): 162–72. https://dx.doi.org/10.1002%2Fppul.22923
44.
Jung KH, Yan B, Moors K, Chillrud SN, Perzanowski MS, Whyatt RM, Hoepner L, Goldstein I, Zhang B, Camann D, Kinney PL. Repeated exposure to polycyclic aromatic hydrocarbons and asthma: effect of seroatopy. Ann Allergy Asthma Immunol, 2012 Oct 1; 109(4): 249–54. https://doi.org/10.1016/j.anai.2012.07.019
45.
Miller RL, Garfinkel R, Horton M, Camann D, Perera FP, Whyatt RM, Kinney PL. Polycyclic aromatic hydrocarbons, environmental tobacco smoke, and respiratory symptoms in an inner-city birth cohort. Chest, 2004 Oct 1; 126(4): 1071–8. https://doi.org/10.1378/chest.126.4.1071
46.
Miller RL, Garfinkel R, Lendor C, Hoepner L, Li Z, Romanoff L, Sjodin A, Needham L, Perera FP, Whyatt RM. Polycyclic aromatic hydrocarbon metabolite levels and pediatric allergy and asthma in an inner-city cohort. Pediatr Allergy Immunol, 2010 Mar; 21(2p1): 260–7. https://doi.org/10.1111/j.1399-3038.2009.00980.x
47.
Rosa MJ, Jung KH, Perzanowski MS, Kelvin EA, Darling KW, Camann DE, Chillrud SN, Whyatt RM, Kinney PL, Perera FP, Miller RL. Prenatal exposure to polycyclic aromatic hydrocarbons, environmental tobacco smoke and asthma. Respir Med, 2011 Jun 1; 105(6): 869–76. https://doi.org/10.1016/j.rmed.2010.11.022
48.
Suresh R, Shally A, Mahdi AA, Patel DK, Singh VK, Rita M. Assessment of association of exposure to polycyclic aromatic hydrocarbons with bronchial asthma and oxidative stress in children: A case control study. Indian J Occup Env Med, 2009 Apr; 13(1): 33. https://dx.doi.org/10.4103%2F0019-5278.50722
49.
Wang IJ, Karmaus WJ, Yang CC. Polycyclic aromatic hydrocarbons exposure, oxidative stress, and asthma in children. Int Arch Occup. Env Health, 2017 Apr 1; 90(3): 297–303. https://doi.org/10.1007/s00420-017-1198-y
50.
Anyenda EO, Higashi T, Kambayashi Y, Thao NT, Michigami Y, Fujimura M, Hara J, Tsujiguchi H, Kitaoka M, Asakura H, Hori D. Exposure to daily ambient particulate polycyclic aromatic hydrocarbons and cough occurrence in adult chronic cough patients: A longitudinal study. Atmos Env, 2016 Sep 1; 140: 34–41. https://doi.org/10.1016/j.atmosenv.2016.05.042
51.
Epton MJ, Dawson RD, Brooks WM, Kingham S, Aberkane T, Cavanagh JA, Frampton CM, Hewitt T, Cook JM, McLeod S, McCartin F. The effect of ambient air pollution on respiratory health of school children: a panel study. Env Health, 2008 Dec; 7(1): 1–1. https://doi.org/10.1186/1476-069x-7-16
52.
Mu G, Fan L, Zhou Y, Liu Y, Ma J, Yang S, Wang B, Xiao L, Ye Z, Shi T, Yuan J. Personal exposure to PM2. 5-bound polycyclic aromatic hydrocarbons and lung function alteration: Results of a panel study in China. Sci Total Env, 2019 Sep 20; 684: 458–65. https://doi.org/10.1016/j.scitotenv.2019.05.328
53.
Konradsen JR, Skantz E, Nordlund B, Lidegran M, James A, Ono J, Ohta S, Izuhara K, Dahlén SE, Alving K, Hedlin G. Predicting asthma morbidity in children using proposed markers of Th2-type inflammation. Pediatr Allergy Immunol, 2015 Dec; 26(8): 772–9. https://doi.org/10.1111/pai.12457
54.
Kissel JC, Curl CL, Kedan G, Lu C, Griffith W, Barr DB, Needham LL, Fenske RA. Comparison of organophosphorus pesticide metabolite levels in single and multiple daily urine samples collected from preschool children in Washington State. J Expo Sci Env Epidemiol, 2005 Mar; 15(2): 164–71. https://doi.org/10.1038/sj.jea.7500384
55.
Han IK, Duan X, Zhang L, Yang H, Rhoads GG, Wei F, Zhang J. 1-Hydroxypyrene concentrations in first morning voids and 24-h composite urine: intra-and inter-individual comparisons. J Expo Sci Env Epidemiol, 2008 Sep; 18(5): 477–85. https://doi.org/10.1038/sj.jes.7500639

Information & Authors

Information

Published In

Journal of Health and Pollution
Volume 11Issue 31September 2021

History

Received: 11 March 2021
Accepted: 14 June 2021
Published online: 1 September 2021

Keywords

  1. polycyclic aromatic hydrocarbons
  2. lung function
  3. asthma
  4. chronic obstructive pulmonary disease
  5. COPD
  6. FEV1 FVC
  7. FEF25–75%

Authors

Affiliations

Africa Center of Excellence in Public Health and Toxicological Research, University of Port Harcourt, Port Harcourt, Nigeria
Kingsley C. Partick-Iwuanyanwu https://orcid.org/0000-0002-0422-3880
Africa Center of Excellence in Public Health and Toxicological Research, University of Port Harcourt, Port Harcourt, Nigeria
Department of Biochemistry, University of Port Harcourt, Port Harcourt, Nigeria
Department of Community Medicine, Ambrose Ali University, Ekpoma, Edo State, Nigeria

Notes

Corresponding author: Chinemerem C. Nwaozuzu, [email protected]

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