Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2011 Jul;17(4):923-965.
doi: 10.1080/10807039.2011.588157. Epub 2011 Jul 26.

Modeling Human Exposure to Phthalate Esters: A Comparison of Indirect and Biomonitoring Estimation Methods

Affiliations
Free PMC article

Modeling Human Exposure to Phthalate Esters: A Comparison of Indirect and Biomonitoring Estimation Methods

Kathryn E Clark et al. Hum Ecol Risk Assess. 2011 Jul.
Free PMC article

Abstract

Humans are potentially exposed to phthalate esters (PEs) through ingestion, inhalation, and dermal contact. Studies quantifying exposure to PEs include "biomarker studies" and "indirect studies." Biomarker studies use measurements of PE metabolites in urine to back-calculate exposure to the parent diester, while indirect studies use the concentration of the PE in each medium of exposure and the rate of intake of that medium to quantify intake of the PE. In this review, exposure estimates from biomarker and indirect studies are compiled and compared for seven PEs to determine if there are regional differences and if there is a preferred approach. The indirect and biomarker methods generally agree with each other within an order of magnitude and discrepancies are explained by difficulties in accounting for use of consumer products, uncertainty concerning absorption, regional differences, and temporal changes. No single method is preferred for estimating intake of all PEs; it is suggested that biomarker estimates be used for low molecular weight PEs for which it is difficult to quantify all sources of exposure and either indirect or biomarker methods be used for higher molecular weight PEs. The indirect methods are useful in identifying sources of exposure while the biomarker methods quantify exposure.

PubMed Disclaimer

Figures

Figure 1.
Figure 1.
Estimates of median DEP intake to adults.
Figure 2.
Figure 2.
Estimates of median BBP intake to adults.
Figure 3.
Figure 3.
Estimates of median DEHP intake to adults.

Similar articles

Cited by

References

    1. Anderson WAC. Castle L. Scotter MJ, et al. A biomarker approach to measuring human dietary exposure to certain phthalate diesters. Food Addit Contam. 2001;18:1068–74. - PubMed
    1. Barr DB. Silva MJ. Kato K, et al. Assessing human exposure to phthalates using monoesters and their oxidized metabolites as biomarkers. Environ Health Perspect. 2003;111:1164–9. - PMC - PubMed
    1. Barr DB. Wilder LC. Caudill SP, et al. Urinary creatinine concentrations in the U.S. population: Implications for urinary biologic monitoring measurements. Environ Health Perspect. 2005;113:192–200. - PMC - PubMed
    1. Bauer MJ. Estimation of the environmental contamination by phthalic acid esters leaching from household wastes. Sci Total Environ. 1997;208:49–57. - PubMed
    1. Becker K. Seiwert M. Angerer J, et al. DEHP metabolites in urine of children and DEHP in house dust. Int J Hyg Environ Health. 2004;207:409–17. - PubMed

LinkOut - more resources