Journal List > Korean J Obstet Gynecol > v.54(3) > 1088254

Kim, Hong, Lee, Chung, Yang, Kim, Kho, and Kim: An estimate of phthalate exposure among term pregnant women living in Bucheon: The pilot study

Abstract

Objective

Phthalates are a group of phthalic acid esters and these are used as plasticizers. Several studies have described phthalate exposure in other countries, but there are no such reports from Korea. We assessed exposure to phthalic acid in the urine of full term pregnant women.

Methods

There were 32 full term deliveries in our hospital from August, 2009 to April, 2010. We received approval from the Institutional Review Board at our hospital and written informed concept from all the patients. We review the obstetrics history, the history of medical illness and other problems. To assess exposure to different phthalates, we measured the concentrations of nine phthalate metabolites in the spot urine samples collected 24 hours before delivery. The urinary concentrations of 10 phthalate ester metabolites (mono-methyl phthalate [MMP], mono-ethyl phthalate [MEP], mono-n-butyl phthalate [MnBP], mono benzyl phthalate [MBzP], mono-[2-ethylhexyl] phthalate [MEHP], mono-[2-ethyl-5-hydroxyhexyl] phthalate [MEHHP], mono-[2-ethyl-5-oxohexyl] phthalate [MEOHP], mono-isobutyl phthalate [MiBP], mono-[2-ethyl-5-carboxypentyl] phthalate [5cx-MEPP], and mono-[2-carboxymethylhexyl] phthalate [2cx-MMHP]) were analyzed in the spot urine samples collected from the pregnant women. The data is being used as a pilot study for a large multicenter study.

Results

The mean age was 31.1±3.2 years. The mean gestational age was 38.4±1.3 weeks. The creatinine-corrected concentration (geometric mean: µg/g Cr) was 1.754 (MMP), 3.443 (MEP), 3.839 (MnBP), 2.721 (MBzP), 2.437 (MEHP), 4.042 (MEHHP), 3.504 (MEOHP), 2.805 (MiBP), 3.765 (5cx-MEPP), and 3.775 (2cx-MMHP).

Conclusion

Our data reflects a preliminary description of pregnant women's exposure, before delivery, to phthalates. So, a prospective multicenter study is needed to evaluate phthalate exposure based on our data.

Figures and Tables

Table 1
Clinical characteristics of term pregnancy in study
kjog-54-140-i001

Values are presented as mean±standard deviation or number (%).

BMI, body mass index.

Table 2
Distribution of urinary phthalate metabolites (µg/L) concentration without creatinine-adjusted in 32 women who had term births
kjog-54-140-i002

GM, geometric mean; GSD, geometric standard deviation; Min, minumum; Max, maximum; MMP, mono-methyl phthalate; MEP, monoethyl phthalate; MiBP, mono-isobutyl phthalate; MnBP, mono-n-butyl phthalate; MEHP, mono-(2-ethylhexyl) phthalate; MEOHP, mono-(2-ethyl-5-oxohexyl) phthalate; MEHHP, mono-(2-ethyl-5-hydroxyhexyl) phthalate; 5cx-MEPP, mono-(2-ethyl-5-carboxypentyl) phthalate; 2cx-MMHP, mono-(2-carboxymethylhexyl) phthalate; MBzP, mono-benzyl phthalate.

Table 3
Distribution of urinary concentration of phthalate metabolites (creatinine-adjusted, µg/g Cr) among 32 women who had term births
kjog-54-140-i003

GM, geometric mean; GSD, geometric standard deviation; Min, minumum; Max, maximum; MMP, mono-methyl phthalate; MEP, monoethyl phthalate; MiBP, mono-isobutyl phthalate; MnBP, mono-n-butyl phthalate; MEHP, mono-(2-ethylhexyl) phthalate; MEOHP, mono-(2-ethyl-5-oxohexyl) phthalate; MEHHP, mono-(2-ethyl-5-hydroxyhexyl) phthalate; 5cx-MEPP, mono-(2-ethyl-5-carboxypentyl) phthalate; 2cx-MMHP, mono-(2-carboxymethylhexyl) phthalate; MBzP, mono-benzyl phthalate.

Table 4
Pearson's correlation coefficients with log-transformed urinary creatinine-adjusted phthalate's metabolite concentrations among 32 women who had term births
kjog-54-140-i004

( ), P-value.

MMP, mono-methyl phthalate; MEP, mono-ethyl phthalate; MiBP, mono-isobutyl phthalate; MnBP, mono-n-butyl phthalate; MEHP, mono-(2-ethylhexyl) phthalate; MEOHP, mono-(2-ethyl-5-oxohexyl) phthalate; MEHHP, mono-(2-ethyl-5-hydroxyhexyl) phthalate; 5cx-MEPP, mono-(2-ethyl-5-carboxypentyl) phthalate; 2cx-MMHP, mono-(2-carboxymethylhexyl) phthalate; MBzP, mono-benzyl phthalate.

*P<0.05.

Table 5
Comparison of geometric mono-(2-ethyl-5-carboxypentyl) phthalate (5cx-MEPP, creatinine-adjusted, µg/g Cr) according to exposure history (food and environmental) in 31 women who had term births by Student' t-test (one no-respondent is not included)
kjog-54-140-i005

References

1. Go YJ. Phthalate safety supervision countermeasure in child article. Proceedings of the 32th Korean Society of Health Promotion Conference. 2007. 2007 Nov 9; Seoul, Korea. Seoul: The Korean Society of Health Promotion;163–166.
2. Shin HS, Pyo HS. Behavior of Phthalate in environment and biology. Proceedings of the 32th Korean Society of Health Promotion Conference. 2007. 2007 Nov 9; Seoul, Korea. Seoul: The Korean Society of Health Promotion;168–194.
3. Kim TH, Hong YP. Endocrine disruptor and menopause. J Korean Soc Menopause. 2010. 16:1–5.
4. Lintelmann J, Katayama A, Kurihara N, Shore L, Wenzel A. Endocrine disruptors in the environment (IUPAC technical report). Pure Appl Chem. 2003. 75:631–681.
5. Caserta D, Maranghi L, Mantovani A, Marci R, Maranghi F, Moscarini M. Impact of endocrine disruptor chemicals in gynaecology. Hum Reprod Update. 2008. 14:59–72.
6. Nagel SC, vom Saal FS, Thayer KA, Dhar MG, Boechler M, Welshons WV. Relative binding affinity-serum modified access (RBA-SMA) assay predicts the relative in vivo bioactivity of the xenoestrogens bisphenol A and octylphenol. Environ Health Perspect. 1997. 105:70–76.
7. Sheehan DM, Willingham E, Gaylor D, Bergeron JM, Crews D. No threshold dose for estradiol-induced sex reversal of turtle embryos: how little is too much? Environ Health Perspect. 1999. 107:155–159.
8. Yang M, Park MS, Lee HS. Endocrine disrupting chemicals: human exposure and health risks. J Environ Sci Health C Environ Carcinog Ecotoxicol Rev. 2006. 24:183–224.
9. Stewart PW, Lonky E, Reihman J, Pagano J, Gump BB, Darvill T. The relationship between prenatal PCB exposure and intelligence (IQ) in 9-year-old children. Environ Health Perspect. 2008. 116:1416–1422.
10. Colon I, Caro D, Bourdony CJ, Rosario O. Identification of phthalate esters in the serum of young Puerto Rican girls with premature breast development. Environ Health Perspect. 2000. 108:895–900.
11. Wolff MS, Britton JA, Boguski L, Hochman S, Maloney N, Serra N, et al. Environmental exposures and puberty in inner-city girls. Environ Res. 2008. 107:393–400.
12. Yang CY, Yu ML, Guo HR, Lai TJ, Hsu CC, Lambert G, et al. The endocrine and reproductive function of the female Yucheng adolescents prenatally exposed to PCBs/PCDFs. Chemosphere. 2005. 61:355–360.
13. Crain DA, Janssen SJ, Edwards TM, Heindel J, Ho SM, Hunt P, et al. Female reproductive disorders: the roles of endocrine-disrupting compounds and developmental timing. Fertil Steril. 2008. 90:911–940.
14. Foster WG, Neal MS, Han MS, Dominguez MM. Environmental contaminants and human infertility: hypothesis or cause for concern? J Toxicol Environ Health B Crit Rev. 2008. 11:162–176.
15. Wigle DT, Arbuckle TE, Turner MC, Berube A, Yang Q, Liu S, et al. Epidemiologic evidence of relationships between reproductive and child health outcomes and environmental chemical contaminants. J Toxicol Environ Health B Crit Rev. 2008. 11:373–517.
16. Irvin EA, Calafat AM, Silva MJ, Aguilar-Villalobos M, Needham LL, Hall DB, et al. An estimate of phthalate exposure among pregnant women living in Trujillo, Peru. Chemosphere. 2010. 80:1301–1307.
17. Berman T, Hochner-Celnikier D, Calafat AM, Needham LL, Amitai Y, Wormser U, et al. Phthalate exposure among pregnant women in Jerusalem, Israel: results of a pilot study. Environ Int. 2009. 35:353–357.
18. Faouzi MA, Dine T, Gressier B, Kambia K, Luyckx M, Pagniez D, et al. Exposure of hemodialysis patients to di-2-ethylhexyl phthalate. Int J Pharm. 1999. 180:113–121.
19. Doull J, Cattley R, Elcombe C, Lake BG, Swenberg J, Wilkinson C, et al. A cancer risk assessment of di(2-ethylhexyl)phthalate: application of the new U.S. EPA risk assessment guidelines. Regul Toxicol Pharmacol. 1999. 29:327–357.
20. Takatori S, Kitagawa Y, Kitagawa M, Nakazawa H, Hori S. Determination of di(2-ethylhexyl)phthalate and mono(2-ethylhexyl) phthalate in human serum using liquid chromatography-tandem mass spectrometry. J Chromatogr B Analyt Technol Biomed Life Sci. 2004. 804:397–401.
21. Inoue K, Yamaguchi A, Wada M, Yoshimura Y, Makino T, Nakazaw H. Quantitative detection of bisphenol A and bisphenol A diglycidyl ether metabolites in human plasma by liquid chromatography-electrospray mass spectrometry. J Chromatogr B Biomed Sci Appl. 2001. 765:121–126.
22. Koo HJ, Lee BM. Estimated exposure to phthaiates in cosmetics and risk assessment. J Toxicol Environ Health A. 2004. 67:1901–1914.
23. Koch HM, Bolt HM, Angerer J. Di(2-ethylhexyl) phthalate (DEHP) metabolites in human urine and serum after a single oral dose of deuterium-labelled DEHP. Arch Toxicol. 2004. 78:123–130.
24. Park MS, Yang YJ, Hong YP, Kim SY, Lee YP. Assessment of di (2-ethylhexyl) phthalate exposure by urinary metabolites as a function of sampling time. J Prev Med Public Health. 2010. 43:301–308.
25. Clark MF, Reade MC, Boyd CA, Young JD. Effects of endotoxin exposure on cationic amino acid transporter function in ovine peripheral blood mononuclear cells. Exp Physiol. 2003. 88:201–208.
26. Weuve J, Hauser R, Calafat AM, Missmer SA, Wise LA. Association of exposure to phthalates with endometriosis and uterine leiomyomata: findings from NHANES, 1999-2004. Environ Health Perspect. 2010. 118:825–832.
27. Patisaul HB, Adewale HB. Long-term effects of environmental endocrine disruptors on reproductive physiology and behavior. Front Behav Neurosci. 2009. 3:10.
28. Adibi JJ, Hauser R, Williams PL, Whyatt RM, Calafat AM, Nelson H, et al. Maternal urinary metabolites of Di-(2-Ethylhexyl) phthalate in relation to the timing of labor in a US multicenter pregnancy cohort study. Am J Epidemiol. 2009. 169:1015–1024.
TOOLS
Similar articles