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Exposure to Polycyclic Aromatic Hydrocarbons and adverse reproductive outcomes in women: current status and future perspectives

  • Ata Rafiee ORCID logo , Mohammad Hoseini , Sadaf Akbari and E. Melinda Mahabee-Gittens EMAIL logo
Published/Copyright: January 2, 2023

Abstract

Objectives

Polycyclic Aromatic Hydrocarbons (PAHs) are ubiquitous, toxic environmental chemicals that can cause adverse reproductive health effects. The objectives of this mini-review are to highlight the adverse reproductive outcomes due to PAH exposure with the main focus on polycystic ovary syndrome (PCOS) and premature ovarian failure (POF) and to provide perspectives on future research needs.

Content

We reviewed studies that have reported the adverse reproductive outcomes associated with PAHs exposures in women through a comprehensive search of bibliographic databases and gray literature sources. In addition, potentially modifiable sources of exposure to PAHs and associated reproductive outcomes were also investigated.

Summary

A total of 232 papers were retrieved through a comprehensive search of bibliographic databases, out of which three studies met the eligibility criteria and were included in the review. Results showed that exposure to PAHs is associated with adverse reproductive outcomes defined as PCOS, POF, and reproductive hormone imbalance. Sources of PAH exposure associated with adverse reproductive outcomes include active and passive tobacco smoking, specific cooking methods, and pesticides.

Outlook

Future studies are warranted to examine the mechanisms by which PAHs result in adverse reproductive endpoints in women. Further, environmental exposures that are potentially modifiable such as exposure to tobacco smoke, may contribute to PAH exposure, and these exposures should be targeted in future policies and interventions.

Introduction

Polycyclic Aromatic Hydrocarbons (PAHs) are a ubiquitous class of toxic environmental chemicals [1] to which humans can be exposed via inhalation, ingestion, and dermal contact [2]. PAHs are predominantly emitted during incomplete combustion and pyrolysis of various anthropogenic and natural sources, such as coal, coke, petrol, wood, forest fires, vehicle exhausts, and tobacco smoke [3], [4], [5]. Once entering the body, PAHs are metabolized and excreted in the urine, mainly as hydroxylated metabolites, with the most common being 1-hydroxypyrene (1-OHP) [6, 7]. The Environmental Protection Agency (EPA) has listed multiple PAHs such as benzo(a)pyrene (BaP), benzo(k)fluoranthene (BkF), and benz(a)anthracene (BaA) as high-priority chemicals of concern based on their carcinogenicity, mutagenicity, and toxicity [8]. The relationship between exposure to PAHs and adverse human health consequences has been well-documented, as exposure results in cardiopulmonary, reproductive, and neurological toxicity, carcinogenic effects, and damage to body organs such as the kidney and liver [5, 7, 9].

Human biomonitoring has been widely used as a complementary approach to exposure science to assess humans’ exposure to various chemicals, including PAHs in the general population and occupational settings [10], [11], [12], [13]. Previous epidemiological studies indicate that exposure to PAHs is associated with adverse reproductive outcomes such as polycystic ovary syndrome (PCOS) among women [14, 15]. PCOS is a complex endocrine syndrome with multiple factors contributing to its development, such as imbalances of reproductive hormones, insulin resistance, low-grade chronic inflammation, and heredity. PCOS is the most common cause of ovulatory infertility in women, affecting 5–10% of reproductive-aged women globally [14, 16]. Because women’s fertility is sensitive to hormone imbalances, exposure to chemicals such as PAHs, which may irritate the ovaries during women’s peak reproductive years, can interrupt ovarian follicular development [14, 15]. Since it is important to understand the existing research on the endocrine-disrupting potential of PAHs to explore the gaps and highlight future research needs, the present mini-review provides insight into the adverse reproductive outcomes in women defined as PCOS, premature ovarian failure (POF), and abnormal levels of reproductive hormones due to PAH exposure as well as perspectives on future research needs.

Methods

We conducted a comprehensive search on bibliographic databases, including Scopus, Web of Science, Embase, Medline, and PubMed, in July 2022. In addition, we searched the gray literature on Google Scholar and ProQuest. The search strategy was formed based on the PECOS format (population, exposure, comparator, outcome, and studies) as follows: (P) pregnant women or expecting mothers or women of reproductive age, (E) exposure to PAHs, (C) pregnant women or women at reproductive age who were not exposed to PAHs, (O) PECOS or POF, and (S) epidemiological observational studies (Supplementary material).

The retrieved studies from the databases that met the study’s aim were then transferred to the Covidence platform, where two independent reviewers assessed them, considering the set inclusion and exclusion criteria. The inclusion criteria were as follows: Human-based studies, primary/original research, studies focused on pregnant women or women of reproductive age, field studies, and studies that investigated PCOS and POF in pregnant women or women of reproductive age. For the exclusion criteria, we excluded animal and lab-based studies, simulation and modeling studies, studies that did not include a comparator group (e.g., controls), studies that investigated other reproductive outcomes resulting from PAHs exposure among women, systematic reviews, mini-reviews, highlight papers, abstracts presented in conferences without full-text available, and studies that focused on exposure to non-PAH pollutants. Two independent reviewers conducted the screening and full-text review stages on the Covidence platform, and disagreements were resolved through discussions until consensus was reached.

Data extraction was performed using a data collection form that included information on each study, such as the number of participants, year of publication, details of PAHs exposures, outcomes of interest, methods used to characterize PAH exposures, and assessment of adverse reproductive outcomes.

Results and discussion

General characteristics of the studies

We retrieved 232 published papers through a comprehensive search on bibliographic databases and gray literature sources, out of which three studies [14, 17, 18] met the eligibility criteria and were included in the present study (Figure 1). Studies were conducted in China and Canada, and the number of participants in the case and control groups was 226 and 140, respectively. Outcomes of interest (PCOS and POF) were assessed by measuring anti-mullerian hormone (AMH), luteinizing hormone (LH), and follicle-stimulating hormone (FSH) among the studied populations using chemiluminescence immunoassay.

Figure 1: 
Preferred reporting items for systematic reviews and meta-analyses (PRISMA) flow diagram.
Figure 1:

Preferred reporting items for systematic reviews and meta-analyses (PRISMA) flow diagram.

PAHs exposure and adverse reproductive outcomes in women

Two studies included in this study examined the associations between exposure to PAHs and adverse reproductive outcomes in women. In the study by Ye et al. [18]; a biomonitoring approach was performed among reproductive-aged women in China to assess the relationship between exposure to PAHs and the risk of premature ovarian failure (POF) [18]. The serum levels of low and high-molecular-weight PAHs (H-PAHs) were measured using a gas chromatography-triple quadrupole mass spectrometer system. In addition, serum levels of AMH, LH, and FSH were measured using an immunoassay. Ye et al. [18] observed significantly higher total serum PAH levels in the case group compared to controls, with pyrene (PYR) and naphthalene (NAP) being the most prevalent PAH congeners in both groups. Further, they found that serum concentrations of ƩPAHs, BaP, benzo(b)fluoranthene (BbF), BkF, phenanthrene (PHE), acenaphthene (ACE), NAP, acenaphthylene (ACY), chrysene (CHR), anthracene (ANT), and fluoranthene (FLT) were significantly associated with the risk of POF in the case group (Table 1).

Table 1:

Summary of the information and findings of the included studies.

Study No. Age (mean ± SD) Measured PAHs Reproductive hormone levels (cases) (mean ± SD) Reproductive hormone levels (controls) (mean ± SD)
  • Remarks

Case Control Case Control FSH, IU/L LH, IU/L AMH, ng/mL FSH, IU/L LH, IU/L AMH, ng/mL
Ye et al. [18] 157 120 34 ± 6 33 ± 6 NAP, ACE, ACY, FLO, PHE, anthracene ANT, FLA, PYR, CHR, BbF, BkF, and BaP 67.50 ± 30.49 39.76 ± 20.04 0.12 ± 0.67 6.80 ± 2.61 4.78 ± 2.61 3.08 ± 2.35
  1. Significantly higher total serum PAH levels were observed in the case group compared to controls

  2. Exposure to H-PAHs was significantly correlated with higher POF risks and ovarian dysfunction than L-PAHs

  3. Serum levels of most PAHs were significantly correlated with FSH serum levels in the case group

  4. Serum levels of all H-PAHs and some L-PAHs were significantly correlated with LH levels in the case group

Yang et al. [14] 50 30 29.7 + 3.2 30.6 + 2.9 Nap, Biphenyl (BP), acenaphthylene (ACN), ACE, Dibenzofuran (DBF), FLU, PHE, ANT, FLT, PYR, BaA, CHR, 1-Methylphenanthrene (1-MePhe), 2-Methylphenanthrene (2-MePhe), 1-Methylpyrene (1-MePyr), 1-hydroxy naphthalene (1-HO-Nap) 6.37 + 1.62 7.14 + 3.38 6.96 + 1.73 3.73 + 1.86
  1. Significantly higher PAHs in the case group compared to controls

  2. PAHs were correlated with PCOS

Neal et al. [17] 19 10 33.24 ± 1.06 34.10 ± 1.13 ACE, PHE, PYR, CHR, and BaP 6.19 ± 0.60 5.42 ± 0.88
  1. Significantly higher B[a]P higher levels in the follicular fluid of smoker women than controls

Ye et al. [18] also found that exposure to H-PAHs was significantly correlated with higher risks of POF and ovarian dysfunction than L-PAHs. Although research on the toxicological effects of exposure to PAHs and PCOS is limited, these findings are in parallel with other studies that reported exposure to PAHs could disrupt estrogen synthesis in follicular granulosa cells [14, 19]. Similarly, other studies revealed that exposure to some H-PAHs, such as BaP, may destroy the follicles and result in early menopause, suggesting that PAHs have endocrine-disrupting potential [20, 21]. One possible reason for these observed results could be due to the effect of exposure to PAHs on the aryl hydrocarbon receptor (AhR), a transcription factor expressed in ovarian tissues, which contributes to women’s ovarian follicular growth regulation. PAH congeners act as ligands for AhR, and exposure to some H-PAHs such as BaP may stimulate follicle apoptosis through the AhR pathway, which could increase POF risk [22], [23], [24].

Regarding the effect of PAHs exposures on reproductive hormones, the findings of this same study indicate that serum levels of all H-PAHs and L-PAHs, except PYR and FLO, were significantly correlated with FSH serum levels of the case group [18]. Moreover, serum levels of all H-PAHs and some L-PAHs, including ACE, NAP, and ANT, were significantly correlated with LH levels. The authors also found significant positive correlations between total serum PAHs with FSH and LH levels in the case group, and BaP was the most significantly correlated PAH congener with measured reproductive hormones [18]. Another study reported increased FSH and LH levels in women with POF, and significant correlations between exposure to PHE, PYR, and NAP with FSH and LH have also been observed [25]. Animal studies have reported a correlation between exposure to PHE and inhibition of LH-stimulated progesterone secretion and increased POF risk in female rats [26]. In addition, the estrogenic activity of PAHs, especially PHE, through interaction with the estrogen receptor alpha, has been observed in previous studies [27, 28].

Concerning reproductive hormones, it is also important to examine the effects of PAHs on AMH concentrations as AMH is correlated with ovarian cycle development, and monitoring AMH levels can be used to assess follicular depletion [29], [30], [31]. Since AMH levels are associated with the size of the ovarian follicular reserve, decreases in the level of this reproductive hormone could be a clinical marker of women’s ovarian disorders, including PCOS and POF [32, 33]. A recent study among Chinese reproductive-age women found negative correlations between AMH levels with all H-PAHs and L-PAHs except for FLO and PYR. The PAH serum levels were also inversely correlated with AMH concentration in women with PCOS [18].

The second study included in this review was conducted by Yang et al. [14]. Yang’s team conducted a case-control study among 50 women with PCOS and 30 normal non-pregnant female control participants from Northern China. Serum levels of 15 species of PAHs were measured using gas chromatography-mass spectrometry. Their results indicated that compared to control participants, participants with PCOS had significantly higher serum concentrations of 6 individuals and the sum of 15 compounds (ƩPAHs). Further, there were significant associations between the NAP and CAN and PCOS and marginally significant associations between PHE, FLU, ACE, ƩPAHs, and PCOS. The authors concluded that the findings of this preliminary study suggest that PAHs could be an etiologic exposure that results in PCOS.

The role of smoking in adverse reproductive consequences

Regarding smoking, one of the included studies [17] reported that BaP is one of the main PAHs present in mainstream and side-stream cigarette smoke. BaP could inhibit follicle development in active smokers and in individuals exposed to second-hand tobacco smoke [17, 24]. However, Ye et al. [18]; did not report significant correlations between cigarette smoking and the risk of reproductive endpoints in the studied population. However, this unexpected finding may be because only two active smokers were identified out of the 157 women who participated in that study, which precluded the examination of the effect of smoking on reproductive endpoints.

Previous studies have recognized that pollutants from active smoking and tobacco smoke exposure (i.e., second-hand smoke and/or third-hand smoke exposure) are important sources of exposure to PAHs [10, 34] that have potential ovo-toxic effects on reproductive hormones in rodents [35]. In addition, some studies have revealed a significant correlation between smoking and earlier menopause and the risk of POF [36, 37]. Cigarette smoking may interfere with AMH circulation in women of late-reproductive age [38], and significant correlations have been reported between exposure to high levels of BaP and a decrease in follicle AMH levels in mice exposed to cigarette smoke [24]. Although the mechanism underlying how smoking and PAH exposure affects follicular development is not well understood, some studies have reported that exposure to smoking could induce ovarian follicle destruction by caspase-3 activation [24, 39]. Another study found that there was a decrease in the circulating levels of estradiol (E2) and/or progesterone (P) due to exposure to cigarette smoke, suggesting that these decreases could affect women’s reproductive potential [24]. Given these prior findings, future toxicological studies are warranted to examine how exposure to PAHs can lead to adverse reproductive outcomes and explore the contribution of active and passive smoking in developing PCOS, POF, and reproductive hormone imbalance in women.

Other PAHs intake sources and concluding remarks

Dietary exposure is another important source and predictor of internal exposure to PAHs, as consumption of grilled and smoked meats is correlated with increases in urinary metabolites of PAHs [40]. Thus, future studies should explore the contribution of dietary PAH exposures to the risk of reproductive outcomes, such as ovulatory status and PCOS in adolescent girls and women of late-reproductive age, in order to investigate how different dietary habits can affect women’s reproductive health. Similarly, future studies are warranted to investigate the effects of other predictors of exposure to PAHs, such as cooking, on disrupting reproductive hormones in women. For example, high PAH levels could be emitted during high-temperature cooking methods such as stir and deep-frying, and PAH can subsequently enter the body through inhalation [41]. Moreover, the correlation between urinary H-PAHs with cooking was reported [42], and PAH levels have been found to be significantly correlated with the risk of POF in women [18].

In summary, the extant literature indicates that exposure to PAHs is associated with adverse reproductive outcomes, including PCOS, POF, and abnormal levels of reproductive hormones. Future studies are warranted to examine the mechanisms by which PAHs result in these outcomes. Further, environmental exposures that are potentially modifiable such as exposure to tobacco smoke, may contribute to PAH exposure, and reductions in these involuntary exposures should be targeted in future policies and interventions.


Corresponding author: E. Melinda Mahabee-Gittens, MD, PhD, Professor of Pediatrics, Division of Emergency Medicine, Cincinnati Children’s Hospital Medical Center, and University of Cincinnati College of Medicine, Cincinnati, OH, USA, E-mail:

Funding source: National Institute of Environmental Health Sciences

Award Identifier / Grant number: R01 ES030743

Award Identifier / Grant number: R01 ES027815

  1. Research funding: This work was supported, in part, by the National Institute of Environmental Health Sciences (NIH Grant Number R01 ES030743 and R01 ES027815, to Dr. Mahabee-Gittens).

  2. Author contributions: Ata Rafiee: Conceptualization, Methodology, Project administration, Data curation, Formal analysis, Writing – original draft, Writing – review & editing. Mohammad Hoseini: Writing – review & editing. Sadaf Akbari: Screening of the studies. E. Melinda Mahabee-Gittens: Supervision, Writing – original draft, Writing – review & editing. All authors have accepted responsibility for the entire content of this manuscript and approved its submission.

  3. Competing interests: Authors state no conflict of interest.

  4. Informed consent: Not applicable.

  5. Ethical approval: Not applicable.

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Supplementary Material

The article contains supplementary material (https://doi.org/10.1515/reveh-2022-0182).


Received: 2022-09-08
Accepted: 2022-12-10
Published Online: 2023-01-02
Published in Print: 2024-06-25

© 2022 Walter de Gruyter GmbH, Berlin/Boston

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  5. Improving the purification of aqueous solutions by controlling the production of reactive oxygen species in non-thermal plasma; a systematic review
  6. Ochratoxin A in coffee and coffee-based products: a global systematic review, meta-analysis, and probabilistic risk assessment
  7. Green space in health research: an overview of common indicators of greenness
  8. The effects of fine particulate matter on the blood-testis barrier and its potential mechanisms
  9. Evaluation of chemicals leached from PET and recycled PET containers into beverages
  10. The association between bisphenol a exposure and attention deficit hyperactivity disorder in children: a meta-analysis of observational studies
  11. A review on arsenic pollution, toxicity, health risks, and management strategies using nanoremediation approaches
  12. The impact of air pollution and climate change on eye health: a global review
  13. Exposure to Polycyclic Aromatic Hydrocarbons and adverse reproductive outcomes in women: current status and future perspectives
  14. Mechanisms of cholera transmission via environment in India and Bangladesh: state of the science review
  15. Effects of sulfur dioxide inhalation on human health: a review
  16. Health effects of alkaline, oxygenated, and demineralized water compared to mineral water among healthy population: a systematic review
  17. Toxic effects due to exposure heavy metals and increased health risk assessment (leukemia)
  18. A systematic review on environmental perspectives of monkeypox virus
  19. How does formal and informal industry contribute to lead exposure? A narrative review from Vietnam, Uruguay, and Malaysia
  20. Letter to the Editor
  21. Comments on “Personal protective equipment (PPE) and plastic pollution during COVID-19: strategies for a sustainable environment”, by Fatima Ali Mazahir and Ali Mazahir Al Qamari
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