Research List

The community group Local Environmental Action Demanded (L.E.A.D.) Agency asked for assistance from EPA’s Technical Assistance Services for Communities (TASC) program. The request was for TASC review and comment on Version 1.1 of the Technical Memorandum: Development of Human Health Risk-Based Preliminary Remediation Goals for Operable Unit 5. The Technical Memorandum discusses human health risk-based preliminary remediation goals (PRGs) and ecological PRGs.

This fact sheet explains the purpose of a BHHRA, how a BHHRA is performed and how the RAGS tables will be used, and presents exposure assumptions made by EPA. The TASC program prepared the fact sheet, and it is funded by TASC. Its contents do not necessarily reflect the policies, actions or positions of EPA.

Atmospheric dispersion of particles from mine waste is potentially an important route of human exposure to metals in communities close to active and abandoned mining areas. This study assessed sources of mass and metal concentrations in two size fractions of respirable particles using positive matrix factorization (U.S. Environmental Protection Agency [EPA] PMF 3.0). Weekly integrated samples of particulate matter (PM) 10 m in aerodynamic diameter or less (PM10) and fine PM (PM2.5, or PM 2.5 m in aerodynamic diameter) were collected at three monitoring sites, varying distances (0.5–20 km) from mine waste piles, for 58 consecutive weeks in a former lead (Pb) and zinc (Zn) mining region. Mean mass concentrations varied significantly across sites for coarse PM (PM10–PM2.5) but not PM2.5 particles. Concentrations of Pb and Zn significantly decreased with increasing distance from the mine waste piles in PM10–PM2.5 (P 0.0001) and PM2.5 (P 0.0005) fractions. Source apportionment analyses deduced five sources contributing to PM2.5 (mobile source combustion, secondary sulfates, mine waste, crustal/soil, and a source rich in calcium [Ca]) and three sources for the coarse fraction (mine waste, crustal/soil, and a Ca-rich source). In the PM2.5 fraction, mine waste contributed 1– 6% of the overall mass, 40% of Pb, and 63% of Zn. Mine waste impacts were more apparent in the PM10–PM2.5 fraction and contributed 4 –39% of total mass, 88% of Pb, and 97% of Zn. Percent contribution of mine waste varied significantly across sites (P 0.0001) for both size fractions, with highest contributions in the site closest to the mine waste piles. Seasonality, wind direction, and concentrations of the Ca-rich source were also associated with levels of ambient aerosols from the mine waste source. Scanning electron microscopy results indicated that the PMF-identified mine waste source is mainly composed of Zn-Pb agglomerates on crustal particles in the PM10–PM2.5 fraction. In conclusion, the differential impacts of mine waste on respirable particles by size fraction and location should be considered in future exposure evaluations.