Literature DB >> 14998748

Mono(2-ethyl-5-hydroxyhexyl) phthalate and mono-(2-ethyl-5-oxohexyl) phthalate as biomarkers for human exposure assessment to di-(2-ethylhexyl) phthalate.

Kayoko Kato1, Manori J Silva, John A Reidy, Donald Hurtz, Nicole A Malek, Larry L Needham, Hiroyuki Nakazawa, Dana B Barr, Antonia M Calafat.   

Abstract

Exposure to di-(2-ethylhexyl) phthalate (DEHP) is prevalent based on the measurement of its hydrolytic metabolite mono-(2-ethylhexyl) phthalate (MEHP) in the urine of 78% of the general U.S. population studied in the 1999-2000 National Health and Nutrition Examination Survey (NHANES). However, despite the high level of production and use of DEHP, the urinary MEHP levels in the NHANES samples were lower than the monoester metabolites of phthalates less commonly used than DEHP, suggesting metabolic differences between phthalates. We measured MEHP and two oxidative DEHP metabolites, mono-(2-ethyl-5-oxohexyl) phthalate (MEOHP) and mono (2-ethyl-5-hydroxyhexyl) phthalate (MEHHP) to verify whether these other metabolites account for a greater proportion of DEHP metabolic products in 127 paired human urine and serum samples. We found that the urinary levels of MEHHP and MEOHP were 10-fold higher than levels of MEHP; concentrations of urinary MEOHP and MEHHP were strongly correlated (r = 0.928). We also found that the serum levels of MEOHP and MEHHP were comparatively lower than those in urine. Furthermore, the glucuronide-bound conjugates of the oxidative metabolites were the predominant form in both urine and serum. MEOHP and MEHHP cannot be formed by serum enzymes from the hydrolysis of any contamination from DEHP potentially introduced during blood collection and storage. Therefore, concentrations of MEHHP and MEOHP in serum may be a more selective measure of DEHP exposure than is MEHP. However, additional data on the absorption, distribution, metabolism, and elimination of these oxidative metabolites are needed to completely understand the extent of DEHP exposure from the serum concentrations of oxidative DEHP metabolites.

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Year:  2004        PMID: 14998748      PMCID: PMC1241862          DOI: 10.1289/ehp.6663

Source DB:  PubMed          Journal:  Environ Health Perspect        ISSN: 0091-6765            Impact factor:   9.031


  23 in total

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Journal:  Toxicol Ind Health       Date:  1999 Jan-Mar       Impact factor: 2.273

3.  Quantitative detection of eight phthalate metabolites in human urine using HPLC-APCI-MS/MS.

Authors:  B C Blount; K E Milgram; M J Silva; N A Malek; J A Reidy; L L Needham; J W Brock
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4.  Absorption and metabolism of three phthalate diesters by the rat small intestine.

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Journal:  Food Cosmet Toxicol       Date:  1980-08

5.  Strategies for biological monitoring of exposure for contemporary-use pesticides.

Authors:  D B Barr; J R Barr; W J Driskell; R H Hill; D L Ashley; L L Needham; S L Head; E J Sampson
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6.  Exposure of hemodialysis patients to di-2-ethylhexyl phthalate.

Authors:  M A Faouzi; T Dine; B Gressier; K Kambia; M Luyckx; D Pagniez; C Brunet; M Cazin; A Belabed; J C Cazin
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9.  Effects of phthalic acid esters on the liver and thyroid.

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10.  Carcinogenicity testing of phthalate esters and related compounds by the National Toxicology Program and the National Cancer Institute.

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4.  Ovarian Toxicity and Epigenetic Mechanisms of Phthalates and Their Metabolites.

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5.  Mono(2-ethylhexyl) phthalate accelerates early folliculogenesis and inhibits steroidogenesis in cultured mouse whole ovaries and antral follicles.

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6.  Prenatal exposure to di-(2-ethylhexyl) phthalate (DEHP) affects reproductive outcomes in female mice.

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7.  Urinary metabolomic profiling in rats exposed to dietary di(2-ethylhexyl) phthalate (DEHP) using ultra-performance liquid chromatography quadrupole time-of-flight tandem mass spectrometry (UPLC/Q-TOF-MS).

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8.  Predicting residential exposure to phthalate plasticizer emitted from vinyl flooring: sensitivity, uncertainty, and implications for biomonitoring.

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9.  Association of exposure to phthalates with endometriosis and uterine leiomyomata: findings from NHANES, 1999-2004.

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10.  What additional factors beyond state-of-the-art analytical methods are needed for optimal generation and interpretation of biomonitoring data?

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Journal:  Environ Health Perspect       Date:  2009-06-24       Impact factor: 9.031

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