GSA Connects 2022 meeting in Denver, Colorado

Paper No. 81-9
Presentation Time: 10:25 AM

ESTIMATING HISTORICAL EXPOSURE TO PERFLUOROALKYL ACIDS IN SECURITY, FOUNTAIN, AND WIDEFIELD COLORADO: USE OF WATER-INFRASTRUCTURE BLENDING AND TOXICOKINETIC MODELS


MEEKS, Jessica1, MASS, Sara2, ADGATE, John3, BARTON, Kelsey4, SINGHA, Kamini5, MCCRAY, John E.6, STARLING, Anne7 and HIGGINS, Christopher2, (1)Golden, CO 80401; Hydrologic Science and Engineering, Colorado School of Mines, Golden, CO 80401, (2)CIVIL AND ENVIRONMENTAL ENGINEERING, Colorado School of Mines, Golden, ME 80401, (3)Department of Environmental & Occupational Health Center for Health, Work & Environment, Colorado School of Public Health, University of Colorado, Aurora, CO 80045; Denver, CO 80204, (4)Department of Environmental & Occupational Health Center for Health, Work & Environment, Colorado School of Public Health, University of Colorado, Aurora, ME 80045, (5)Hydrologic Science and Engineering, Colorado School of Mines, Golden, CO 80401, (6)Department of Civil and Environmental Engineering, Hydrologic Science and Engineering Program, Colorado School of Mines, Golden, CO 80401, (7)Department of Epidemiology, Colorado School of Public Health, University of Colorado, Aurora, ME 80045

Drinking water can be a major source of poly- and perfluoroalkyl substance (PFAS) exposure for humans. The lack of historic data on PFAS drinking-water concentrations and consumption patterns are a limiting factor for developing estimates of past exposure. Here, in contribution to a community-scale PFAS health effects study near fire training facilities that contaminated a local aquifer with PFAS, we present a novel water-infrastructure, mass-balance mixing model coupled to a non-steady state, single-compartment toxicokinetic model that used Monte Carlo simulations to estimate the start of PFAS exposure in drinking water for individuals within three PFAS-impacted communities in El Paso County, Colorado. Our modeling focused on perfluorohexane sulfonic acid (PFHxS) because median serum PFHxS concentrations in a sample of local residents (n=220) were twelve times the median observed in the U.S. National Health and Nutrition Examination Survey (2015-2016). Modeling results for study participants were grouped according to their community of residence, revealing a median start of exposure for the town of Fountain of 1997.0 (25-75% confidence interval 1991.0 - 2012.5), for Security of 2009.5 (25-75% confidence interval 1995.6 - 2014.0), and for Widefield of 2011.3 (25-75% confidence interval 2004.8 - 2015.0). Based on the towns’ locations relative to an identified hydraulically upgradient PFAS source, the modeled exposure sequencing does not completely align with this conceptual flow model, implying the presence of an additional PFAS source for the groundwater between Widefield and Fountain. This modeling effort complements the hydrologic model developed and evaluated in a companion study.