Abstract
Objective: The extensive use of wet wipes for personal hygiene, household cleaning, and food service applications results in frequent dermal exposure to chemical preservatives such as 2-phenoxyethanol (PhE). Although PhE is permitted for use within established regulatory limits, data on its occurrence and concentration levels in consumer products remain limited, and recent systematic data are scarce. This study aimed to quantify PhE levels in commercially available wet wipes across different usage categories using a validated gas chromatography–mass spectrometry (GC-MS) method.
Methods: Due to substantial differences in wipe dimensions among products, a standardized subsampling approach (2×2 cm) was applied to enable comparable quantification and to characterize variability in preservative content. A total of 30 wet wipe products representing six usage categories were analyzed. The method demonstrated a linear range of 5–30 μg/mL (R² = 0.99), with a limit of detection (LOD) of 1.49 μg/mL and a limit of quantification (LOQ) of 5 μg/mL.
Results: In the study, PhE was detected in 17 of the 30 samples (56%), with concentrations ranging from 5.00 to 23.80 µg/mL in 2×2 cm wipe extracts and calculated full-size wipe concentrations ranging from 916.3 to 6246.4 µg/mL. The highest PhE levels were observed in products intended for sensitive use, such as baby wipes and feminine hygiene wipes, as well as in sachet wipes from small-scale food service venues.
Conclusion: The findings indicate considerable variability in PhE content among commercially available wet wipes, underscoring the importance of systematic analytical monitoring of preservative levels in frequently used skin-contact products.
References
Allison T, Ward BD, Harbottle M, Durance I. Do flushed biodegradable wet wipes really degrade? Sci Total Environ. 2023;894:164912. https://doi.org/10.1016/j.scitotenv.2023.164912
Lee J, Jeong S, Chae KJ. Discharge of microplastics fibres from wet wipes in aquatic and solid environments under different release conditions. Sci Total Environ. 2021;784:147144. https://doi.org/10.1016/j.scitotenv.2021.147144
Briain OÓ, Mendes ARM, McCarron S, Healy MG, Morrison L. The role of wet wipes and sanitary towels as a source of white microplastic fibres in the marine environment. Water Res. 2020;182:116021. https://doi.org/10.1016/j.watres.2020.116021
Gilbert P, McBain AJ. Potential impact of increased use of biocides in consumer products on prevalence of antibiotic resistance. Clin Microbiol Rev. 2003;16(2):189–208. https://doi.org/10.1128/cmr.16.2.189-208.2003
Hada JS. New trends in non-woven wet wipes. Int J Mod Trends Sci Technol. 2020;6(9S):89–96. https://doi.org/10.46501/IJMTST0609S15
Karlberg AT, Magnusson K, Nilsson U. Air oxidation of d-limonene (the citrus solvent) creates potent allergens. Contact Dermatitis. 1992;26(5):332–340. https://doi.org/10.1111/j.1600-0536.1992.tb00129.x
Lee I, Ji K. Identification of combinations of endocrine disrupting chemicals in household chemical products that require mixture toxicity testing. Ecotoxicol Environ Saf. 2022;240:113677. https://doi.org/10.1016/j.ecoenv.2022.113677
Boyce JM. A review of wipes used to disinfect hard surfaces in health care facilities. Am J Infect Control. 2021;49(1):104–14. https://doi.org/10.1016/j.ajic.2020.06.183
İslamoğlu A. Research of the awareness level on occupational health and safety of employees participating in biocidal applications in municipality: the case study of Mersin province [master’s thesis]. Mersin: University of Mersin; 2021. p.145.
Matura M, Sköld M, Börje A, Andersen KE, Bruze M, Frosch P, Karlberg AT. Selected oxidized fragrance terpenes are common contact allergens. Contact Dermatitis. 2005;52(6):320–328. https://doi.org/10.1111/j.0105-1873.2005.00605.x
Matura M, Sköld M, Börje A, Andersen KE, Bruze M, Frosch P, Karlberg AT. Not only oxidized R(+)- but also S(−)-limonene is a common cause of contact allergy in dermatitis patients in Europe. Contact Dermatitis. 2006;55(5):274–279. https://doi.org/10.1111/j.1600-0536.2006.00939.x
Orjales RN, Vazquez CC, Gonzalez FC, Paris MB. 2-Phenoxyethanol-induced contact urticaria and anaphylaxis. J Investig Allergol Clin Immunol. 2010;20(4):354–355.
Wieck S, Olsson O, Kümmerer K. Consumers’ perceptions of biocidal products in households. Int J Hyg Environ Health. 2018;221(2):260–268. https://doi.org/10.1016/j.ijheh.2017.11.005
Fan M, Liu Z, Dyer S, Federle T, Wang X. Development of environmental risk assessment framework and methodology for consumer product chemicals in China. Environ Toxicol Chem. 2019;38(1):250–261. https://doi.org/10.1002/etc.4300
Jolliet O, Huang L, Hou P, Fantke P. High throughput risk and impact screening of chemicals in consumer products. Risk Anal. 2021;41(4):627–644. https://doi.org/10.1111/risa.13604
Dréno B, Zuberbier T, Gelmetti C, Gontijo G, Marinovich M. Safety review of phenoxyethanol when used as a preservative in cosmetics. J Eur Acad Dermatol Venereol. 2019;33(Suppl 7):15–24. https://doi.org/10.1111/jdv.15944
Lee S, Pyo H, Chung BC, Kim H, Lee J. Simultaneous determination of alkoxyalcohols in wet wipes using static headspace gas chromatography and mass spectrometry. Bull Korean Chem Soc. 2014;35(11):3280–3288. https://doi.org/10.5012/bkcs.2014.35.11.3280
Pack EC, Lee HG, Jang DY, Sin HS, Kim TY, Kim HS, Choi DW. Probabilistic risk assessment of preservatives in dishwashing detergents and wet wipes for Korean consumers. Sci Total Environ. 2021;782:146829. https://doi.org/10.1016/j.scitotenv.2021.146829
Wang HY, Li B, Sun L. Uncertainty evaluation in determination of 2-phenoxyethanol in cosmetic by high performance liquid chromatography. J Food Saf Qual. 2020;11(1):128–133.
Akgündüz MÇ, Çavuşoğlu K, Yalçın E. The potential risk assessment of phenoxyethanol with a versatile model system. Sci Rep. 2020;10(1):1209. https://doi.org/10.1038/s41598-020-58170-9
Béranger R, Garlantézec R, Le Maner-Idrissi G, Lacroix A, Rouget F, Trowbridge J, Chevrier C. Prenatal exposure to glycol ethers and neurocognitive abilities in 6-year-old children: the PELAGIE cohort study. Environ Health Perspect. 2017;125(4):684–690. https://doi.org/10.1289/EHP39
Belsito D, Bickers D, Bruze M, Calow P, Greim H, Hanifin JM, Panel TRE. A toxicologic and dermatologic assessment of cyclic acetates when used as fragrance ingredients. Food Chem Toxicol. 2008;46(Suppl 12):S1–S27. https://doi.org/10.1016/j.fct.2008.09.039
Blume-Peytavi U, Lavender T, Jenerowicz D, Ryumina I, Stalder JF, Torrelo A, Cork MJ. Recommendations from a European roundtable meeting on best practice healthy infant skin care. Pediatr Dermatol. 2016;33(3):311–321. https://doi.org/10.1111/pde.12819
Lavender T, Furber C, Campbell M, Victor S, Roberts I, Bedwell C, Cork MJ. Effect on skin hydration of using baby wipes to clean the napkin area of newborn babies: assessor-blinded randomised controlled equivalence trial. BMC Pediatr. 2012;12:1–9. https://doi.org/10.1186/1471-2431-12-59
Rahma A, Lane ME. Skin barrier function in infants: update and outlook. Pharmaceutics. 2022;14(2):433. https://doi.org/10.3390/pharmaceutics14020433
Hernández B, Ortiz-Frutos FJ, García M, Palencia S, García MC, Iglesias L. Contact urticaria from 2-phenoxyethanol. Contact Dermatitis. 2002;47(1):54. https://doi.org/10.1034/j.1600-0536.2002.470116.x
Ehretsmann C, Schaefer P, Adam R. Cutaneous tolerance of baby wipes by infants with atopic dermatitis, and comparison of the mildness of baby wipe and water in infant skin. J Eur Acad Dermatol Venereol. 2001;15:16–21. https://doi.org/10.1046/j.0926-9959.2001.00004.x
Svoboda M, Kolarova J. A survey of anaesthetics used in the fish farming. Health Protection of Fish–Proceeding of Papers, Research Institute of Fish Culture and Hydrobiology. Vodnany (Czech Republic); 1999. p.49–72.

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