United States Environmental Protection Agency	Office of Research and Development

National Exposure Research Laboratory
Research Abstract

Government Performance Results Act (GPRA) Goal # 1-Clean Air
Annual Performance Measure #214

Significant Research Findings:

The Contribution of Outdoor Fine Particle Concentrations to the Exposure of

High-Risk Sub-populations

Scientific	Significant associations have been found in many areas between fine particulate

Problem and	matter (PM) concentrations measured at ambient monitoring sites and increased

Policy Issues	mortality and morbidity. The persons most at risk include those with respiratory

or cardiovascular problems. The National Academy of Sciences (NAS) placed
studying the relationship between the ambient PM concentrations measured at a
central outdoor site and the personal exposures of these at-risk persons as the first
goal in their 13-year research portfolio for EPA PM research. (Cf.. Research
Priorities for Airborne Particulate Matter: IV. Continuing Research Progress,
National Academies Press (2004)) One difficulty determining this relationship is
in differentiating between particles from outdoor- and indoor-generated sources.

One approach for differentiating between particles from outdoor- and indoor-
generated sources is to identify and use a marker which is present in outdoor-
generated particles but not indoor-generated particles. Several studies have found
that sulfur might be a suitable marker. The EPA's National Exposure Research
Laboratory collected personal, indoor, and outdoor samples in an exposure study
conducted in the Research Triangle Park area of North Carolina. In this study, 29
adults with hypertension and 8 adults with implanted defibrillators were monitored
for 7 days each season, for up to four seasons. About 800 sets of personal, indoor,
and outdoor filters were analyzed for sulfur content. The hypothesis that sulfur is
not generated indoors was tested by graphically comparing indoor and outdoor
concentrations.

The sulfur marker method for estimating exposure to outdoor fine PM was
successfully demonstrated in this study. The hypothesis that sulfur is not
generated indoors was confirmed for all but one participant, who used tap water
containing sulfide in his room humidifier. The portion of fine particle exposure
due to outside ambient PM ranged between 33% and 77% using the sulfur marker
method. On average, indoor sources contributed more than half of the personal
PM exposure.

The research summarized here is contained in an upcoming EPA research report
(APM214):

Wallace, L., Williams, R., Suggs, J. Use of Indoor-Outdoor Sulfur Concentrations to Estimate the
Infiltration Factor, Outdoor Exposure Factor, Penetration Coefficient, and Deposition Rate for
Individual Homes (APM-214). US EPA, National Exposure Research Laboratory, Research

Research
Approach

Results and
Impact

Research
Collaboration and
Research
Products


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Triangle Park, NC. EPA/600/R-xx/xxx. 2004.

A journal article has also been submitted for publication:

Wallace, L. and Williams, R. Use of Indoor-Outdoor Sulfur Concentrations to Estimate the
Infiltration Factor, Outdoor Exposure Factor, Penetration Coefficient, and Deposition Rate for
Individual Homes. Environmental Science & Technology'. American Chemical Society,

Washington, DC, 39(6): 1707-1714, (2005).

The two earlier EPA project reports (APM-1 and APM-21) are:

Wallace, L., Williams, R., Suggs, J. et al., Exposure of High-Risk Subpopulations to Particles: Final

Report—APM-21. US EPA, National Exposure Research Laboratory, Research Triangle Park, NC. EPA/600/R-

03/145. February, 2004.

Williams, R. et al., Preliminary Particulate Matter Mass Concentrations Associated with Longitudinal Panel
Studies: Assessing Human Exposures of High Risk Subpopulations to Particulate Matter. US EPA, National
Exposure Research Laboratory, Research Triangle Park, NC. EPA/600/R-01/086.

The main publications dealing with the Research Triangle Park study are:

Williams RW, Suggs, J, Rea A, Leovic K, Vette A, Croghan C, Sheldon L, Rodes C, Thomburg J,
Ejire A et al. (2003a). The Research Triangle Park particulate matter panel study: PM mass
concentration relationships, Atmospheric Environment 31(^y.5349-5363

Williams, RW, Suggs J, Rea A, Sheldon L, Rodes C, Thomburg J (2003b). The Research Triangle
Park particulate matter panel study: modeling ambient source contribution to personal and
residential PM mass concentrations, Atmospheric Environment 37(38): 5365-5378.

Future studies of the sulfur marker method for estimating personal exposure to
outdoor fine PM should investigate the validity of this method for particles such as
iron and crustal elements which are at the upper end of the fine fraction. Such
particles potentially have different penetration and deposition behavior than the
sulfur tracer. A 3-year particle exposure study in the Detroit was begun during the
summer of 2004. The study, which includes measurements of personal, indoor,
and outdoor exposure to particles, gases, and elements, will provide opportunities
for further investigating the sulfur marker method.

Questions can be directed to:

Ron Williams
US EPA
NERL

MD E-205-04

RTP, NC 27711

Phone 919-541-2957

Fax 919-541-0905

Email williams.ronald@epa.gov

Contacts for

Additional

Information

Federal funding for this research was administered under EPA contract number
68-D2-0134, 68-D2-0187, 68-D99-012, 68-D5-0040, CR-82-0076, and CR-82-
8186.


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