Web Release Date: January 26,
Use of Personal-Indoor-Outdoor Sulfur Concentrations to Estimate the Infiltration Factor and Outdoor Exposure Factor for Individual Homes and Persons
National Exposure Research Laboratory, U.S. EPA, Research Triangle Park, North Carolina
Received for review March 24, 2004
Revised manuscript received October 14, 2004
Accepted December 3, 2004
Abstract:
A study of personal, indoor, and outdoor exposure to
PM2.5 and associated elements has been carried out for
37 residents of the Research Triangle Park area in North
Carolina. Participants were selected from persons expected
to be at elevated risk from exposure to particles, and
included 29 persons with hypertension and 8 cardiac patients
with implanted defibrillators. Participants were monitored
for 7 consecutive days in each of four seasons. One
goal of the study was to estimate the contribution of outdoor
PM2.5 to indoor concentrations. This depends on the
infiltration factor Finf, the fraction of outdoor PM2.5 remaining
airborne after penetrating indoors. After confirming with
our measurements the findings of previous studies that sulfur
has few indoor sources, we estimated an average Finf
for each house based on indoor/outdoor sulfur ratios. These
estimates ranged from 0.26 to 0.87, with a median value
of 0.55. Since these estimates apply only to particles of size
similar to that of sulfur particles (0.06-0.5
m diameter),
and since larger particles (0.5-2.5
m) have lower penetration
rates and higher deposition rates, these estimates are
likely to be higher than the true infiltration factors for PM2.5
as a whole. In summer when air conditioners were in
use, the sulfur-based infiltration factor was at its lowest
(averaging 0.50) for most homes, whereas the average Finf
for the other three seasons was 0.62-0.63. Using the
daily estimated infiltration factor for each house, we calculated
the contribution of outdoor PM2.5 to indoor air concentrations.
The indoor-generated contributions to indoor PM2.5 had
a wider range (0-33
g/m3) than the outdoor contributions
(5-22
g/m3). However, outdoor contributions exceeded
the indoor-generated contributions in 27 of 36 homes. A
second goal of the study was to determine the contribution
of outdoor particles to personal exposure. This is determined
by the "outdoor exposure factor" Fpex, the fraction of
outdoor PM2.5 contributing to personal exposure. As with
Finf, we estimated Fpex by the personal/outdoor sulfur ratios.
The estimates ranged from 0.33 to 0.77 with a median
value of 0.53. Outdoor air particles were less important
for personal exposures than for indoor concentrations, with
the median outdoor contribution to personal exposure
just 49%. We regressed the outdoor contributions to personal
exposures on measured outdoor PM2.5 at the central
site. The regressions had R2 values ranging from 0.19 to
0.88 (median = 0.73). These values provide an indication
of the extent of misclassification error in epidemiological
estimates of the effect of outdoor particles on health.
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