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Güvenli Güneş Koruması: Oksibenzon ve Hormon Dengesi İlişkisi - ya da multicosmetics

Safe Sun Protection: The Relationship Between Oxybenzone and Hormone Balance

What is Oxybenzone (Benzophenone-3)?

Oxybenzone ((Benzophenone-3) is a filter used in sunscreens that protects the skin against both UV-B and UV-A radiation.

Effects of Oxybenzone on the Endocrine System

The endocrine system is a term used for the system of organs and glands that produce and secrete hormones into the blood. (14) The endocrine system consists of the hypothalamus, pineal gland, pituitary gland, thyroid gland, parathyroid gland, thymus gland, adrenal glands, and pancreas; the testes in men, the ovaries in women, and the placenta during pregnancy. (14) According to scientific studies, the most concerning sunscreen active ingredient is oxybenzone. It is easily absorbed by the skin and has hormonal imbalance-disrupting effects. (1)

Estrogen-like Activity

Increasing evidence regarding endocrine disrupting chemicals indicates adverse effects on the endocrine system, including the reproductive system and prostate, due to their estrogenic or antiandrogenic effects. (2)

According to in vivo and in vitro studies, oxybenzone can bind to the estrogen receptor and act like a natural estrogen in the body. This may increase cell proliferation, particularly in breast cancer cells, and negatively impact reproductive health. (3)

Effects on Thyroid Functions

Various studies have demonstrated the potential disruptive effects of oxybenzone (benzophenone-3) on thyroid function. These effects are related to its ability to alter the synthesis, secretion, and receptor interactions of thyroid hormones (especially T3 and T4).

Studies in mice have shown that oxybenzone can reduce levels of the thyroid hormones T3 (triiodothyronine) and T4 (thyroxine). This can lead to hypothyroidism-like results. A decrease in thyroid hormone levels can, through a feedback mechanism, lead to an increase in thyroid-stimulating hormone (TSH) levels. This can lead to long-term thyroid dysfunction. (4)

Some epidemiological studies suggest that hormone disruptors such as oxybenzone may be associated with the development of autoimmune thyroid diseases. (3)

Thyroid hormones play a critical role in brain development and metabolism. Oxybenzone has attracted attention because its use in pregnant women can cause neurodevelopmental disorders in the fetus. (4)

Effects on Reproductive Health

The effects of oxybenzone on reproductive health and its potential negative consequences for both male and female reproductive systems have been investigated in various scientific studies. Oxybenzone exposure has been shown to be associated with decreased sperm quality and decreased sperm motility. Animal studies have reported that oxybenzone can reduce testicular weight and lower testosterone levels. (4)

An epidemiological study by Buck Louis and colleagues indicates that oxybenzone can cause a decrease in sperm count and DNA damage in humans. (5) It is thought that oxybenzone, due to its estrogen-like effects, can disrupt hormonal cycles and lead to problems such as early menopause. (3) Women exposed to oxybenzone during pregnancy are at increased risk of low birth weight and premature birth. (6)

How Oxybenzone Enters the Body

The routes through which oxybenzone enters the body are related to environmental exposure and exposure through personal care products. It generally appears to enter the human body through these two primary routes.

Dermal Absorption

The most common route of oxybenzone absorption is through the skin via personal care products such as hormone-disrupting sunscreens. (7) Because oxybenzone is a lipophilic (oil-soluble) compound, it readily penetrates the epidermal lipid layer. (8) The rate of absorption varies depending on the integrity of the skin barrier, frequency of application, oxybenzone concentration, and the extent of skin surface area to which it is applied. (8) Exposure to UV light may increase oxybenzone absorption. This is due to the weakening of the skin barrier and an increased likelihood of reaching deeper layers. (9)

Participation in Systemic Circulation

Oxybenzone, absorbed through the skin (transdermal transfer), passes through the epidermal barrier, reaches the dermis layer and enters the blood circulation.

In a study published in the journal JAMA in 2019, Matta and colleagues measured plasma concentrations after skin application of oxybenzone-containing sunscreens. (7) Oxybenzone-containing sunscreen was applied to 24 participants four times a day for four days, and plasma samples were collected at regular intervals after each application. (7) After the first application, oxybenzone plasma concentration started at a low level of 0.5 ng/ml and increased rapidly as the number of applications increased. (7) By the end of the fourth day, plasma oxybenzone levels reached 210.1 ng/ml. (7) The duration of oxybenzone in plasma after the application was terminated was calculated to be approximately 24-48 hours. (7) However, in some participants, it was detected in plasma for up to 4 days after the application was terminated. (7) These findings suggest that oxybenzone crosses the skin barrier and enters the bloodstream, accumulates with repeated applications, is metabolized and slowly eliminated from the body, and varies in plasma residence time depending on individual differences. Once in the systemic circulation, oxybenzone binds to plasma proteins and is transported to various tissues throughout the body. Biotransformation occurs in the liver, where it is converted to more polar metabolites via glucuronidation and excreted. (10)

Risk Groups

Since oxybenzone came to the fore with its harmful effects, the affected populations have gained importance. The groups most at risk from oxybenzone's harmful effects include pregnant women, fetuses, infants, young children, individuals with hormonal imbalances, individuals prone to allergic reactions, individuals with a history of cancer, and individuals at high risk of cancer.

Pregnant and Nursing Mothers

Many studies have shown that oxybenzone can cross the placental barrier and pass to the fetus. This passage can have adverse effects on fetal development.

A study conducted in pregnant women in China sought to evaluate the effects of prenatal exposure to phenol derivatives (specifically chemicals such as oxybenzone and bisphenol A) on birth weight, gestational age, and neonatal health. Urine samples were collected from 450 women during pregnancy, and phenol and oxybenzone metabolite levels were measured. Parameters such as birth weight, time of birth, head circumference, and health status of the newborns were recorded. Benzophenone-3 (BP-3) metabolites were analyzed in the urine samples, and the resulting data were used to assess chemical exposure levels during pregnancy. The measured levels were compared with those of pregnant women without phenol exposure.

Babies born to mothers with high levels of oxybenzone exposure during pregnancy were found to have an average birth weight of 120-150 grams lower than babies born to women with low exposure. Babies born to mothers in the highest quartile of oxybenzone exposure had a 22% increased risk of low birth weight.

Women with high levels of oxybenzone metabolites have a significantly increased risk of premature birth (delivery before 37 weeks' gestation). The rate of premature birth was 18% in the group with high oxybenzone levels and 8% in the group with low levels. (11)

High oxybenzone exposure resulted in infants with a head circumference that was measured to be 0.5 cm smaller on average. Prenatal oxybenzone exposure increased the risk of fetal growth restriction (FGR). FGR cases were more common in the high-exposure group. (11) Specific and comprehensive scientific studies on the effects on breastfeeding mothers are limited.

Several studies have found varying amounts of oxybenzone and octinoxate in the breast milk of sunscreen users. It is not yet known whether these chemicals are transferred in high enough amounts to cause adverse effects in breastfed infants. (12,13) ​​To protect the health of both mother and baby, oxybenzone-free sunscreens should be preferred, and it is important to consult a healthcare professional if necessary. Sunscreens containing non-nanoparticle zinc oxide are a good alternative for breastfeeding mothers. (17)

Children and Adolescents

Because hormonal changes are more sensitive during childhood and adolescence, exposure to oxybenzone can have more serious consequences in this age group. Furthermore, children's skin is more sensitive and permeable, so the risk of accumulation is higher.

Many endocrine-disrupting chemicals have been observed to cause early puberty. Precocious puberty refers to a pathological condition involving the earlier-than-normal emergence of secondary sex characteristics. Because it causes increased hormone secretion in children, it can threaten both their physical and psychological health. While a cause is generally unidentifiable in girls, a specific cause is more likely to be found in boys. (14)

Precocious puberty causes the pineal glands to fuse prematurely, leading to premature completion of development. Hematomas in the hypothalamus, adenomas in the pituitary gland, tumors in the nervous system, short stature in adulthood, and cancers of the breast or reproductive system have been associated with precocious puberty. (14)

Safe Alternatives

When choosing skin care products and sunscreen, the ingredients of the sunscreens should be carefully examined.

According to the latest statements from the United States Food and Drug Administration (FDA), 16 compounds were studied and only two, zinc oxide and titanium dioxide, were reported as “generally recognized as safe and effective,” or GRASE, based on available information. (15,16)

Data indicating safety issues suggest that two rarely used sunscreen ingredients, aminobenzoic acid and trolamine salicylate, are not GRASE. (15,16) The FDA states that 12 other ingredients are not GRASE due to insufficient data: oxybenzone avobenzone, cinoxate, dioxybenzone, ensulizole, homosalate, meradimate, octinoxate, octisalate, octocrylene, padimate O, and sulisobenzone. (15,16)

Mineral-Based Sunscreens

Mineral sunscreens, such as zinc oxide, an FDA-approved sunscreen ingredient, create a physical barrier to block and reflect both UVA and UVB rays. Titanium dioxide is often found in cosmetics as a sunscreen, but it is not as effective at blocking some UVA rays and is therefore not preferred (alone) for sun protection. (17)

When safer sunscreens are desired, sunscreens containing non-nanoparticles of zinc oxide can be preferred. This form remains on the skin (it doesn't absorb into the bloodstream) and provides protection by scattering, absorbing, and reflecting UV rays. (17) Disadvantages include the ability to leave a white residue on the skin surface. (17) Because it doesn't enter the systemic circulation, it doesn't pass into breast milk, making it a good alternative for breastfeeding mothers. (17)

Nanoparticle zinc oxide formulations are also available and have been designed to reduce the appearance of a white residue. (17) However, small nanoparticles have the ability to penetrate the skin and be absorbed systemically to a small degree. (17) However, nanoparticle zinc oxide appears to have lower absorption than chemical sunscreens and therefore a lower risk of potential side effects. (17) However, there is one report suggesting that it is possible for breast-fed infants to consume enough nanoparticle zinc oxide to cause diarrhea. (18)

Natural UV Filters

A systematic database search investigated the effects of UV radiation on human keratinocyte cells (HaCaT) in vitro and UVB exposure in mouse models in vivo. Examples of natural UV filters include plant sources such as Hibiscus roseus, Moringa oleifera, Coffea arabica, and Vinis vinifera (19).

Natural UV filters are generally composed of plant compounds such as flavonoids, polyphenols, phenolic acids, and carotenoids. Flavonoids and phenolic compounds absorb UV rays with wavelengths between 200 and 400 nm thanks to the double bonds in their molecular structures. Plant polyphenols reduce oxidative stress by inhibiting free radical production, thus protecting skin cells from DNA damage caused by UV rays. (19)

Additionally, some ingredients increase the inhibition of matrix metalloproteinases (MMPs), thus reducing collagen destruction in the skin and thus reducing wrinkle formation. (19)

Legal Regulations and Restrictions

Oxybenzone is subject to various regulations and restrictions due to both its human health and environmental effects.

According to the EU Cosmetics Regulation and the US Food and Drug Administration (FDA), oxybenzone is approved for use in sunscreens at a maximum of 6%. However, a report from the European Commission has stated that current human exposure levels are unsafe and therefore recommended limiting the oxybenzone concentration to 2.2%. (16)

In 2021, the FDA stated that there was insufficient data on the safety of oxybenzone and requested that safety tests be completed. (16)

The sale of sunscreens containing oxybenzone has been banned in Hawaii, USA, effective January 1, 2021. (20) Additionally, scientific studies have shown that oxybenzone damages coral reefs and negatively impacts marine life. (21)

Conscious Consumer Guide

In light of studies on the accumulation of oxybenzone in the human body and its intergenerational transmission, the use of safe alternative products is key to avoiding potential risks and protecting environmental health. (22)

When choosing a sunscreen, carefully examine the ingredient list, and choose sunscreens free of chemicals like oxybenzone, natural mineral-based sunscreens, or natural and plant-based UV protectors. Alternatively, HelioVita has created a sunscreen line for you, paying attention to all these details for your safe use.

Pregnant women, fetuses, infants, young children, people with hormonal imbalances, individuals prone to allergic reactions, individuals with a history of cancer, and individuals at high risk of cancer should be more meticulous in choosing sunscreen.

If you don't want to use sunscreen, take physical precautions like a hat, sunglasses, and long-sleeved clothing. Remedium Body Lotion will replace the moisture your skin loses after exposure to sun, sand, hot weather, and wind.

References

1) Ghazipura M, McGowan R, Arslan A, Hossain T. Exposure to benzophenone-3 and reproductive toxicity: A systematic review of human and animal studies. Reprod Toxicol. 2017 Oct;73:175-183. doi: 10.1016/j.reprotox.2017.08.015. Epub 2017 Aug 24. PMID: 28844799.

2) Vitku J, Skodova T, Varausova A, Gadus L, Michnova L, Horackova L, Kolatorova L, Simkova M, Heracek J. Endocrine Disruptors and Estrogens in Human Prostatic Tissue. Physiol Res. 2023 Dec 17;72(S4):S411-S422. doi: 10.33549/physiolres.935246. PMID: 38116777.

3) Krause, M., Klit, A., Blomberg Jensen, M., Søeborg, T., Frederiksen, H., Schlumpf, M., Lichtensteiger, W., Skakkebaek, NE and Drzewiecki, KT (2012), Sunscreens: are they beneficial for health? An overview of endocrine disrupting properties of UV-filters. International Journal of Andrology, 35: 424-436. https://doi.org/10.1111/j.1365-2605.2012.01280.x

4) Amira M. Aker, Lauren Johns, Thomas F. McElrath, David E. Cantonwine, Bhramar Mukherjee, John D. Meeker, Associations between maternal phenol and paraben urinary biomarkers and maternal hormones during pregnancy: A repeated measures study,Environment International,Volume 113,2018,Pages 341-349, ISSN 0160-4120, https://doi.org/10.1016/j.envint.2018.01.006.

5) Buck Louis GM, Sundaram R, Schisterman EF, Sweeney AM, Lynch CD, Gore-Langton RE, Maisog J, Kim S, Chen Z, Barr DB. Persistent environmental pollutants and couple fecundity: the LIFE study. Environ Health Perspect. 2013 Feb;121(2):231-6. doi: 10.1289/ehp.1205301. Epub 2012 Nov 14. PMID: 23151773; PMCID: PMC3569685.

6) Wolff MS, Engel SM, Berkowitz GS, Ye X, Silva MJ, Zhu C, Wetmur J, Calafat AM. Prenatal phenol and phthalate exposures and birth outcomes. Environ Health Perspect. 2008 Aug;116(8):1092-7. doi: 10.1289/ehp.11007. PMID: 18709157; PMCID: PMC2516577.

7) Matta MK, Florian J, Zusterzeel R, Pilli NR, Patel V, Volpe DA, Yang Y, Oh L, Bashaw E, Zineh I, Sanabria C, Kemp S, Godfrey A, Adah S, Coelho S, Wang J, Furlong LA, Ganley C, Michele T, Strauss DG. Effect of Sunscreen Application on Plasma Concentration of Sunscreen Active Ingredients: A Randomized Clinical Trial. JAMA. 2020 Jan 21;323(3):256-267. doi: 10.1001/jama.2019.20747. Erratum in: JAMA. 2020 Mar 17;323(11):1098. doi: 10.1001/jama.2020.1950. PMID: 31961417; PMCID: PMC6990686.

8) Nadeem Rezaq Janjua, Brian Mogensen, Anna-Maria Andersson, Jørgen Holm Petersen, Mette Henriksen, Niels E. Skakkebæk, Hans Christian Wulf,Systemic Absorption of the Sunscreens Benzophenone-3, Octyl-Methoxycinnamate, and 3-(4-Methyl-Benzylidene) Camphor After Whole-Body Topical Application and Reproductive Hormone Levels in Humans,Journal of Investigative Dermatology,Volume 123, Issue 1,2004,Pages 57-61,ISSN 0022-202X,https://doi.org/10.1111/j.0022-202X.2004.22725.x.

9) Gonzalez H, Farbrot A, Larkö O, Wennberg AM. Percutaneous absorption of the sunscreen benzophenone-3 after repeated whole-body applications, with and without ultraviolet irradiation. BrJ Dermatol. 2006 Feb;154(2):337-40. doi: 10.1111/j.1365-2133.2005.07007.x. PMID: 16433806.

10) Janjua NR, Mogensen B, Andersson AM, Petersen JH, Henriksen M, Skakkebaek NE, Wulf HC. Systemic absorption of the sunscreens benzophenone-3, octyl-methoxycinnamate, and 3-(4-methyl-benzylidene) camphor after whole-body topical application and reproductive hormone levels in humans. J Invest Dermatol. 2004 Jul;123(1):57-61. doi: 10.1111/j.0022-202X.2004.22725.x. PMID: 15191542.

11) Tang R, Chen MJ, Ding GD, Chen XJ, Han XM, Zhou K, Chen LM, Xia YK, Tian Y, Wang XR. Associations of prenatal exposure to phenols with birth outcomes. Environ Pollut. 2013 Jul;178:115-20. doi: 10.1016/j.envpol.2013.03.023. Epub 2013 Apr 3. PMID: 23562958.

12) Anderson P.O. Summer Topics on Breastfeeding. Breastfeed Med. 2020 Jun;15(6):354-356. doi: 10.1089/bfm.2020.0053. Epub 2020 Mar 20. PMID: 32196354.

13) Lin H. Chen, Caroline Zeind, Sheila Mackell, Trisha LaPointe, Margot Mutsch, Mary E. Wilson, Breastfeeding Travelers: Precautions and Recommendations, Journal of Travel Medicine, Volume 17, Issue 1, 1 January 2010, Pages 32–47, https://doi.org/10.1111/j.1708-8305.2009.00362.x

14) https://yadacosmetics.com/blogs/uzman-gozuyle/endokrin-hormon-sistemi-bozucu- Kimyasal-maddeler-ve-erken-ergenlik-i%CC%87liskisi

15) https://www.fda.gov/drugs/cder-conversations/update-sunscreen-requirements-deemed-final-order-and-proposed-order

16) https://www.ewg.org/sunscreen/report/the-trouble-with-sunscreen-chemicals/

17) https://www.infantrisk.com/content/sunscreen-smarts-breastfeeding-families

18) Ceballos-Rasgado M, Lowe NM, Mallard S, Clegg A, Moran VH, Harris C, Montez J, Xipsiti M. Adverse Effects of Excessive Zinc Intake in Infants and Children Aged 0-3 Years: A Systematic Review and Meta-Analysis. Adv Nutr. 2022 Dec 22;13(6):2488-2518. doi: 10.1093/advances/nmac088. PMID: 36055780; PMCID: PMC9776731.

19) Li L, Chong L, Huang T, Ma Y, Li Y, Ding H. Natural products and extracts from plants as natural UV filters for sunscreens: A review. Animal Model Exp Med. 2023 Jun;6(3):183-195. doi: 10.1002/ame2.12295. Epub 2022 Dec 19. PMID: 36536536; PMCID: PMC10272908.

20) https://www.personalcarecouncil.org/sunscreen/

21) https://www.surfrider.org/news/your-guide-to-reef-friendly-sunscreens

22) Çetinkaya S. Endocrine environmental disruptors and their effects on adolescence. diclemedj. March 2009;36(1):59-66.

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