Personal care product use predicts urinary concentrations of some phthalate monoesters

Susan M Duty, Robin M Ackerman, Antonia M Calafat, Russ Hauser, Susan M Duty, Robin M Ackerman, Antonia M Calafat, Russ Hauser

Abstract

Phthalates are multifunctional chemicals used in a variety of applications, including personal care products. The present study explored the relationship between patterns of personal care product use and urinary levels of several phthalate metabolites. Subjects include 406 men who participated in an ongoing semen quality study at the Massachusetts General Hospital Andrology Laboratory between January 2000 and February 2003. A nurse-administered questionnaire was used to determine use of personal care products, including cologne, aftershave, lotions, hair products, and deodorants. Phthalate monoester concentrations were measured in a single spot urine sample by isotope dilution-high-performance liquid chromatography coupled to tandem mass spectrometry. Men who used cologne or aftershave within 48 hr before urine collection had higher median levels of monoethyl phthalate (MEP) (265 and 266 ng/mL, respectively) than those who did not use cologne or aftershave (108 and 133 ng/mL, respectively). For each additional type of product used, MEP increased 33% (95% confidence interval, 14-53%). The use of lotion was associated with lower urinary levels of monobutyl phthalate (MBP) (14.9 ng/mL), monobenzyl phthalate (MBzP) (6.1 ng/mL), and mono(2-ethylhexyl) phthalate (MEHP) (4.4 ng/mL) compared with men who did not use lotion (MBP, 16.8 ng/mL; MBzP, 8.6 ng/mL; MEHP, 7.2 ng/mL). The identification of personal care products as contributors to phthalate body burden is an important step in exposure characterization. Further work in this area is needed to identify other predictors of phthalate exposure.

Figures

Figure 1
Figure 1
Specific-gravity–adjusted urinary MEP concentration according to combinations of product types used. Data points represent medians; error bars represent 25th and 75th percentiles.
Figure 2
Figure 2
Specific-gravity–adjusted urinary MEP concentrations according to number of product types used. Data points represent medians; error bars represent 25th and 75th percentiles.

References

    1. Api AM. Toxicological profile of diethyl phthalate: a vehicle for fragrance and cosmetic ingredients. Food Chem Toxicol. 2001;39:97–108.
    1. ATSDR 1995. Toxicological Profile for Diethyl Phthalate. Atlanta, GA:Agency for Toxic Substances and Disease Registry. Available: [accessed 23 May 2003].
    1. ATSDR 2001. Toxicological Profile for Di-n-butyl Phthalate. Atlanta, GA:Agency for Toxic Substances and Disease Registry. Available: [accessed 23 May 2003].
    1. ATSDR 2003. Toxicological Profile for Di(2-Ethylhexyl) Phthalate. Atlanta, GA:Agency for Toxic Substances and Disease Registry. Available: [accessed 23 May 2003].
    1. Barber ED, Teetsel NM, Kolberg KF, Guest D. A comparative study of the rates of in vitro percutaneous absorption of eight chemicals using rat and human skin. Fundam Appl Toxicol. 1992;19(4):493–497.
    1. Blount BC, Milgram KE, Silva NJ, Malek NA, Reidy JA, Needham LL, et al. Quantitative detection of eight phthalate metabolites in human urine using HPLC-APCI-MS/MS. Anal Chem. 2000;72(17):4127–4134.
    1. CDC 2003. Second National Report on Human Exposure to Environmental Chemicals. Atlanta, GA:Centers for Disease Control and Prevention. Available: [accessed 1 August 2003].
    1. Deisinger PJ, Perry LG, Guest D. In vivo percutaneous absorption of DEHP from DEHP-plasticized polyvinyl chloride film in male Fischer 344 rats. Food Chem Toxicol. 1998;36(6):521–527.
    1. Duty SM, Silva MJ, Barr DB, Brock JW, Ryan L, Chen Z, et al. Phthalate exposure and human semen parameters. Epidemiology. 2003b;14(3):269–276.
    1. Duty SM, Singh NP, Silva MJ, Barr DB, Brock JW, Ryan L, et al. The relationship between environmental exposures to phthalates and DNA damage in human sperm using the neutral comet assay. Environ Health Perspect. 2003a;111:1164–1169.
    1. Elsisi AE, Carter DE, Sipes IG. Dermal absorption of phthalate diesters in rats. Fundam Appl Toxicol. 1989;12:70–77.
    1. Hagedorn-Leweke U, Lippold BC. Absorption of sun-screens and other compounds through human skin in vivo: derivation of a method to predict maximum fluxes. Pharm Res. 1995;12(9):1354–1360.
    1. Hauser R, Meeker J, Park S, Silva M, Calafat A. Temporal Variability of urinary phthalate levels in men of reproductive age. Environ Health Perspect. 2004;112:1734–1740.
    1. Hoppin JA, Brock JW, Davis BJ, Baird DD. Reproducibility of urinary phthalate metabolites in first morning urine samples. Environ Health Perspect. 2002;110:515–518.
    1. Houlihan J, Brody C, Schwan B. 2002. Not Too Pretty: Phthalates, Beauty Products and the FDA. Environmental Working Group, Coming Clean, and Health Care Without Harm. Available: [accessed 3 September 2003].
    1. Howard J, Page N, Perkins M. 2001. Toxicology Tutor II: Toxicokinetics, Absorption: Dermal Route. Bethesda, MD:Division of Specialized Information Services, National Library of Medicine, National Institutes of Health. Available: [accessed 7 November 2003].
    1. Koo HJ, Lee BM. Estimated exposure to phthalates in cosmetics and risk assessment. J Toxicol Environ Health. 2004;67:1901–1914.
    1. Koo J-W, Parham F, Kohn MC, Masten SA, Brock JW, Needham LL, et al. The association between biomarker-based exposure estimates for phthalates and demographic factors in a human reference population. Environ Health Perspect. 2002;110:405–410.
    1. Li LH, Jester WF, Orth JM. Effects of relatively low levels of mono-(2-ethylhexyl) phthalate on cocultured Sertoli cells and gonocytes from neonatal rats. Toxicol Appl Pharmacol. 1998;153(2):258–265.
    1. Melnick RL, Morrissey RE, Tomaszewski KE. Studies by the National Toxicology Program on di(2-ethylhexyl)phthalate. Toxicol Ind Health. 1987;3(2):99–118.
    1. Mint A, Hotchkiss SAM, Caldwell J. Percutaneous absorption of diethyl phthalate through rat and human skin in vitro. Toxicol In Vitro. 1994;8:251–256.
    1. Ng KM, ChuI, Bronaugh RL, Franklin CA, Somers DA. Percutaneous absorption and metabolism of pyrene, benzo[a]pyrene, and di(2-ethylhexyl) phthalate: comparison of in vitro and in vivo results in the hairless guinea pig. Toxicol Appl Pharmacol. 1992;115(2):216–223.
    1. Parks LG, Ostby JS, Lambright CR, Abbott BD, Klinefelter GR, Barlow NJ, et al. The plasticizer diethylhexyl phthalate induces malformations by decreasing fetal testosterone synthesis during sexual differentiation in the male rat. Toxicol Sci. 2000;58(2):339–349.
    1. Phillip Morris. 2004. Ingredients in Cigarettes. Richmond, VA: Phillip Morris. Available: [accessed 23 November 2000].
    1. Scott RC, Dugard PH, Ramsey JD, Rhodes C. In vitro absorption of some o-phthalate diesters through human and rat skin. Environ Health Perspect. 1987;74:223–227.
    1. Silva MJ, Barr DB, Reidy JA, Malek NA, Hodge CC, Caudill SP, et al. Urinary levels of seven phthalate metabolites in the US population from the National Health and Nutrition Examination Survey (NHANES) 1999–2000. Environ Health Perspect. 2004;112:331–338.
    1. Silva MJ, Malek NA, Hodge CC, Reidy JA, Kato K, Barr DB, et al. Improved quantitative detection of 11 urinary phthalate metabolites in humans using liquid chromatography-atmospheric pressure chemical ionization tandem mass spectrometry. J Chromatogr B. 2003;789(2):393–404.
    1. Swan SH, Main KM, Liu F, Stewart SL, Kruse RL, Calafat AM, et al. 2005. Decrease in anogenital distance among male infants with prenatal phthalate exposure. Environ Health Perspect 10.1289/EHP.8100.
    1. Wester RC, Melendres J, Sedik L, Maibach H, Riviere JE. Percutaneous absorption of salicylic acid, theophylline, 2,4-dimethylamine, diethyl hexyl phthalic acid, and p-aminobenzoic acid in the isolated perfused porcine skin flap compared to man in vivo. Toxicol Appl Pharmacol. 1998;151(1):159–165.

Source: PubMed

3
Iratkozz fel