Polycyclic aromatic hydrocarbons (PAHs) are persistent toxic pollutants of increasing concern in Gulf Cooperation Council (GCC) region due to rapid urbanization, industrialization and the dominance of oil and gas extraction activities. This review synthesizes evidence from eligible studies published between 2020 and 2025 that assessed PAH contamination in environmental dust from households, cars, mosques, and sporting walkways. Across these environments, total PAH concentrations ranged from several hundred to over 37,000 ng/g, frequently exceeding international safety benchmarks. While health risk assessments revealed benzo[a]pyrene-equivalent toxicity (BaP-TEQ) values reaching critical threshold of 700 ng/g in some scenarios, incremental lifetime cancer risks (ILCRs) in all the assessed studies spanned 10?? to 10?³, exceeding the U.S. Environmental Protection Agency’s acceptable limit of 10??. Dermal contact and ingestion were consistently the dominant exposure pathways, particularly for children and occupationally exposed groups such as taxi drivers. Smoking, incense burning, and proximity to high-traffic areas intensified PAH burdens. While non-carcinogenic risks were less frequently assessed, hazard index values(HI) occasionally exceeded the safety threshold of 1.0. These findings highlight substantial deficiency of research on chemical exposure-based health risk assessment across GCC countries beyond Kuwait and Kingdom of Saudi Arabia (KSA) and underscore the need for coordinated region-specific health risk frameworks to mitigate PAH exposure risks.
Introduction
Polycyclic Aromatic Hydrocarbons (PAHs) are toxic semi-volatile organic compounds (SVOCs) formed during incomplete combustion of fossil fuels and biomass.
They are environmental contaminants with serious health impacts: endocrine disruption, respiratory and neurological issues, hormonal imbalances, and cancer.
In the Gulf Cooperation Council (GCC) region, PAHs are widespread due to heavy fossil fuel use and frequent dust storms, which facilitate their distribution and accumulation in dust.
2. Research Gap & Objective
Existing studies in the MENA and GCC regions either:
Focused on contaminant distribution, or
Used biomonitoring without assessing environmental exposure routes.
Gap identified: No comprehensive regional health risk assessment using environmental data (especially dust).
Objective of the review: To assess human health risks from PAH-contaminated dust exposure in the GCC across multiple pathways:
Inhalation
Ingestion
Dermal contact
3. Methodology
Systematic review using Scopus with strict inclusion criteria:
Years: 2020–2025
Focus: Dust as the medium
Countries: Any GCC member state
Data: Environmental PAH concentrations
Outcome: Quantitative health risk metrics
Results: 15 studies found, 6 met criteria, all from Saudi Arabia (4) and Kuwait (2), indicating limited research in other GCC countries.
4. Key Health Risk Indicators
A. Carcinogenic Risk
Evaluated using:
Benzo[a]pyrene Toxic Equivalents (BaP-TEQ)
Benzo[a]pyrene Mutagenic Equivalents (BaP-MEQ)
Incremental Lifetime Cancer Risk (ILCR)
Total Cancer Risk (CR)
i. BaP-TEQ
Indicates the cancer-causing potential of PAH mixtures.
Two calculation methods:
Using Toxic Equivalency Factors (TEFs) for all PAHs
Using only highly potent PAHs (e.g., BaA, BbF, BaP, etc.)
Risk Interpretation (BaP-TEQ):
Level
BaP-TEQ (ng/g)
Interpretation
Low
< 70
No risk
Moderate
70–700
Low potential risk
High
700–7000
Critical
Very High
> 7000
High risk
ii. BaP-MEQ
Reflects mutagenic potential of PAHs using Mutagenic Equivalency Factors (MEFs).
Same calculation method as TEQ but with MEFs.
B. Incremental Lifetime Cancer Risk (ILCR)
Probability of developing cancer due to lifetime exposure.
ILCR = Daily Intake (DI) × Slope Factor (SF)
Total cancer risk (CR) is sum of ILCRs for:
Inhalation
Ingestion
Dermal contact
Risk Interpretation (US EPA):
ILCR / CR Value
Interpretation
≤ 10??
Safe / negligible
10?? to 10??
Potential cancer risk
≥ 10??
Significant cancer risk
5. Non-Carcinogenic Risk Indicators
A. Hazard Quotient (HQ)
Measures risk of non-cancer health effects for a single exposure route.
HQ = Daily Intake (DI) / Reference Dose (RFD)
B. Hazard Index (HI)
Sum of HQs across multiple exposure routes.
HI = ∑HQ
Risk Interpretation:
HQ / HI Value
Interpretation
≤ 1
No health risk
> 1
Possible adverse effects
6. Parameters for Risk Assessment
Parameters vary for adults, children, and occupational groups (e.g., drivers), including:
Ingestion rates
Skin surface area & adherence factors
Exposure duration & frequency
Body weight
Inhalation rates
Cancer slope factors (SFs) used:
Ingestion: 7.3
Inhalation: 3.85
Dermal: 25
7. Key Findings
Dust is a major carrier of PAHs in the GCC, making it a critical focus for monitoring.
BaP-TEQ and BaP-MEQ are useful for evaluating carcinogenic and mutagenic risks.
In most reviewed studies:
PAH levels exceeded safe thresholds.
Carcinogenic and non-carcinogenic risks were evident, especially for children and sensitive populations.
Kuwait and Saudi Arabia are better studied; other GCC countries lack data.
8. Conclusion & Policy Implications
This review fills a critical gap by assessing PAH-related health risks in the dust pathway across the GCC.
Results support:
Urgent need for broader environmental health monitoring.
Development of targeted mitigation strategies.
Informed policymaking for environmental safety in arid urban regions.
Conclusion
This review confirms that GCC populations are exposed to PAHs at levels exceeding international safety thresholds, particularly for carcinogenic risks. Children and workers with high exposure frequency are especially vulnerable. Based on the findings of this review , the following are recommended:
1) Establishing GCC-wide monitoring programs covering air, water, soil, food, and indoor environments.
2) Developing region-specific health risk guidelines that reflect unique environmental and cultural conditions.
3) Integrating environmental monitoring with biomonitoring and epidemiological studies.
4) Implementing stricter emission and waste management regulations while promoting public awareness of exposure risks.
By adopting coordinated monitoring and policy frameworks, GCC states can mitigate risks, protect public health, and enhance environmental resilience in the face of chemical exposure.
References
[1] Alamri, S. H., Ali, N., Albar, H. M. S. A., Rashid, M. I., Rajeh, N., Qutub, M. M. A., & Malarvannan, G. (2021). Polycyclic aromatic hydrocarbons in indoor dust collected during the covid-19 pandemic lockdown in saudi arabia: Status, sources and human health risks. International Journal of Environmental Research and Public Health, 18(5), 1–13. Scopus. https://doi.org/10.3390/ijerph18052743
[2] Alghamdi, M. A., Hassan, S. K., Al Sharif, M. Y., Khoder, M. I., & Harrison, R. M. (2021). On the nature of polycyclic aromatic hydrocarbons associated with sporting walkways dust: Concentrations, sources and relative health risk. Science of The Total Environment, 781, 146540. https://doi.org/10.1016/j.scitotenv.2021.146540
[3] Alghamdi, M. A., Hassan, S. K., Shetaya, W. H., Al Sharif, M. Y., Nawab, J., & Khoder, M. I. (2024). Polycyclic aromatic hydrocarbons in indoor mosques dust in Saudi Arabia: Levels, source apportionment, human health and carcinogenic risk assessment for congregators. Science of the Total Environment, 946. Scopus. https://doi.org/10.1016/j.scitotenv.2024.174331
[4] Al-Harbi, M., Al-Enzi, E., Al-Mutairi, H., & Whalen, J. K. (2021). Human health risks from brominated flame retardants and polycyclic aromatic hydrocarbons in indoor dust. Chemosphere, 282, 131005. https://doi.org/10.1016/j.chemosphere.2021.131005
[5] Al-Harbi, M., Alhajri, I., & Whalen, J. K. (2020). Health risks associated with the polycyclic aromatic hydrocarbons in indoor dust collected from houses in Kuwait. Environmental Pollution, 266, 115054. https://doi.org/10.1016/j.envpol.2020.115054
[6] Ali, N., Kadi, M. W., Ali Albar, H. M. S., Rashid, M. I., Chandrasekaran, S., Summan, A. S., de Wit, C. A., & Malarvannan, G. (2021). Semi-volatile organic compounds in car dust: A pilot study in jeddah, saudi arabia. International Journal of Environmental Research and Public Health, 18(9). Scopus. https://doi.org/10.3390/ijerph18094803
[7] Federal contaminated site risk assessment in Canada: Toxicological reference values (TRVs). (2021). Health Canada = Santé Canada.
[8] Khaled, R., Elabed, S., Masarani, A., Almulla, A., Almheiri, S., Koniyath, R., Semerjian, L., & Abass, K. (2023). Human biomonitoring of environmental contaminants in Gulf Countries – current status and future directions. Environmental Research, 236, 116650. https://doi.org/10.1016/j.envres.2023.116650
[9] Nisbet, I. C. T., & LaGoy, P. K. (1992). Toxic equivalency factors (TEFs) for polycyclic aromatic hydrocarbons (PAHs). Regulatory Toxicology and Pharmacology, 16(3), 290–300. https://doi.org/10.1016/0273-2300(92)90009-X
[10] Ouda, M., Kadadou, D., Swaidan, B., Al-Othman, A., Al-Asheh, S., Banat, F., & Hasan, S. W. (2021). Emerging contaminants in the water bodies of the Middle East and North Africa (MENA): A critical review. Science of The Total Environment, 754, 142177. https://doi.org/10.1016/j.scitotenv.2020.142177
[11] US EPA. (1989). Risk Assessment Guidance for Superfund Volume I Human Health Evaluation Manual (Part A). https://www.epa.gov/system/files/documents/2024-10/rags_a_508.pdf