Movatterモバイル変換


[0]ホーム

URL:


Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
Thehttps:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

NIH NLM Logo
Log inShow account info
Access keysNCBI HomepageMyNCBI HomepageMain ContentMain Navigation
pubmed logo
Advanced Clipboard
User Guide

Full text links

Elsevier Science full text link Elsevier Science Free PMC article
Full text links

Actions

Share

.2023 Aug 25:888:164196.
doi: 10.1016/j.scitotenv.2023.164196. Epub 2023 May 17.

Occurrence of and dermal exposure to benzene, toluene and styrene in sunscreen products marketed in the United States

Affiliations

Occurrence of and dermal exposure to benzene, toluene and styrene in sunscreen products marketed in the United States

Vineet Kumar Pal et al. Sci Total Environ..

Abstract

Occurrence of volatile organic compounds (VOCs) such as benzene in personal care products is a topic of public health concern. Sunscreen products are extensively used to protect skin and hair from UV radiation from sun light. Nevertheless, little is known about exposure doses and risks of VOCs present in sunscreens. In this study, we determined the concentrations of and exposure to three VOCs, namely benzene, toluene and styrene, in 50 sunscreen products marketed in the United States. Benzene, toluene and styrene were found in 80 %, 92 % and 58 %, respectively, of the samples analyzed at mean concentrations of 45.8 ng/g (range: 0.007-862), 89.0 ng/g (range: 0.006-470) and 161 ng/g (range: 0.006-1650), respectively. The mean dermal exposure doses (DEDs) to benzene, toluene and styrene of children/teenagers were 68.3, 133 and 441 ng/kg-bw/d, respectively, whereas those of adults were 48.7, 94.6 and 171 ng/kg-bw/d, respectively. The lifetime cancer risk from benzene concentrations present in 22 sunscreen products (44 % of the samples) for children/teenagers and 19 sunscreen products (38 %) for adults, exceeded the acceptable benchmark risk level (1.0 × 10-6). This is the first study to comprehensively assess the concentrations of and risks to benzene, toluene and styrene present in sunscreen products.

Keywords: Benzene; Cancer risk; Exposure assessment; Sunscreens; Volatile organic compounds.

Copyright © 2023 Elsevier B.V. All rights reserved.

PubMed Disclaimer

Conflict of interest statement

Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Figures

Figure 1.
Figure 1.
Details of sunscreen products analyzed in this study. Samples for which information is unavailable are categorized as “Others”.
Figure 2:
Figure 2:
Heat map showing Spearman correlations between benzene, toluene and styrene concentrations measured in sunscreen products.
Figure 3.
Figure 3.
Concentrations of benzene, toluene and styrene measured in sunscreen products according to the type of UV filters (organic or inorganic) and Sunscreen Protection Factor (SPF). Samples for which information is unavailable are categorized as “Others”.
Figure 4.
Figure 4.
Frequency distribution curves for hazard quotients calculated from dermal exposure to benzene, toluene and styrene measured in sunscreen products. HQ refers to hazard quotients for non-carcinogenic risk; CR stands for carcinogenic risk. The red line indicates the threshold value for HQ or CR.
Figure 4.
Figure 4.
Frequency distribution curves for hazard quotients calculated from dermal exposure to benzene, toluene and styrene measured in sunscreen products. HQ refers to hazard quotients for non-carcinogenic risk; CR stands for carcinogenic risk. The red line indicates the threshold value for HQ or CR.
See this image and copyright information in PMC

Similar articles

See all similar articles

Cited by

References

    1. AAD, 2022. American Academy of Dermatology (AAD). Sunscreen FAQs. Available at:https://www.aad.org/media/stats-sunscreen. Access date: 23 August 2022.
    1. Adami G, Larese F, Venier M, Barbieri P, Lo Coco F, Reisenhofer E, 2006. Penetration of benzene, toluene and xylenes contained in gasolines through human abdominal skin in vitro. Toxicology in Vitro 20, 1321–1330. 10.1016/j.tiv.2006.05.008. - DOI - PubMed
    1. Al-Eitan LN; Aljamal HA; Alkhatib RQ, 2018. Gas Chromatographic–Mass Spectrometric Analysis of Sunscreens and Their Effects on Mice Liver and Kidney Enzyme Function. CCID, Volume 12, 11–21. 10.2147/CCID.S190359. - DOI - PMC - PubMed
    1. ATSDR, 2007. Agency for Toxic Substances and Diseases Registry (ATSDR), Public Health Statement for Benzene,https://www.atsdr.cdc.gov/ToxProfiles/tp3-c1-b.pdf. Access date: 20 December 2021.
    1. ATSDR, 2010. Agency for Toxic Substances and Disease Registry (ATSDR). Toxicological Profile for Styrene.https://www.atsdr.cdc.gov/toxprofiles/tp53.pdf. Access date: 20 December 2021. - PubMed

MeSH terms

Substances

Related information

Grants and funding

LinkOut - more resources

Full text links
Elsevier Science full text link Elsevier Science Free PMC article
Cite
Send To

NCBI Literature Resources

MeSHPMCBookshelfDisclaimer

The PubMed wordmark and PubMed logo are registered trademarks of the U.S. Department of Health and Human Services (HHS). Unauthorized use of these marks is strictly prohibited.


[8]ページ先頭

©2009-2025 Movatter.jp