Site-specific data confirm arsenic exposure predicted by the U.S. Environmental Protection Agency
- PMID: 9452415
- PMCID: PMC1533040
- DOI: 10.1289/ehp.98106133
Site-specific data confirm arsenic exposure predicted by the U.S. Environmental Protection Agency
Abstract
The EPA uses an exposure assessment model to estimate daily intake to chemicals of potential concern. At the Anaconda Superfund site in Montana, the EPA exposure assessment model was used to predict total and speciated urinary arsenic concentrations. Predicted concentrations were then compared to concentrations measured in children living near the site. When site-specific information on concentrations of arsenic in soil, interior dust, and diet, site-specific ingestion rates, and arsenic absorption rates were used, measured and predicted urinary arsenic concentrations were in reasonable agreement. The central tendency exposure assessment model successfully described the measured urinary arsenic concentration for the majority of children at the site. The reasonable maximum exposure assessment model successfully identified the uppermost exposed population. While the agreement between measured and predicted urinary arsenic is good, it is not exact. The variables that were identified which influenced agreement included soil and dust sample collection methodology, daily urinary volume, soil ingestion rate, and the ability to define the exposure unit. The concentration of arsenic in food affected agreement between measured and predicted total urinary arsenic, but was not considered when comparing measured and predicted speciated urinary arsenic. Speciated urinary arsenic is the recommended biomarker for recent inorganic arsenic exposure. By using site-specific data in the exposure assessment model, predicted risks from exposure to arsenic were less than predicted risks would have been if the EPA's default values had been used in the exposure assessment model. This difference resulted in reduced magnitude and cost of remediation while still protecting human health.
Similar articles
-
Biological and behavioral factors modify biomarkers of arsenic exposure in a U.S. population.Environ Res. 2013 Oct;126:134-44. doi: 10.1016/j.envres.2013.04.004. Epub 2013 Jun 15. Environ Res. 2013. PMID: 23777639
-
Multimedia exposures to arsenic and lead for children near an inactive mine tailings and smelter site.Environ Res. 2016 Apr;146:331-9. doi: 10.1016/j.envres.2015.12.011. Epub 2016 Jan 21. Environ Res. 2016. PMID: 26803211 Free PMC article.
-
Estimating Children's Soil/Dust Ingestion Rates through Retrospective Analyses of Blood Lead Biomonitoring from the Bunker Hill Superfund Site in Idaho.Environ Health Perspect. 2016 Sep;124(9):1462-70. doi: 10.1289/ehp.1510144. Epub 2016 Jan 8. Environ Health Perspect. 2016. PMID: 26745545 Free PMC article.
-
Issues in setting health-based cleanup levels for arsenic in soil.Regul Toxicol Pharmacol. 1997 Oct;26(2):219-29. doi: 10.1006/rtph.1997.1148. Regul Toxicol Pharmacol. 1997. PMID: 9356285 Review.
-
Total allowable concentrations of monomeric inorganic aluminum and hydrated aluminum silicates in drinking water.Crit Rev Toxicol. 2012 May;42(5):358-442. doi: 10.3109/10408444.2012.674101. Crit Rev Toxicol. 2012. PMID: 22512666 Review.
Cited by
-
Biomarkers of exposure: a case study with inorganic arsenic.Environ Health Perspect. 2006 Nov;114(11):1790-6. doi: 10.1289/ehp.9058. Environ Health Perspect. 2006. PMID: 17107869 Free PMC article. Review.
References
MeSH terms
Substances
LinkOut - more resources
Full Text Sources
Medical
Research Materials