Measurement of fine particulate matter nonvolatile and
semi-volatile organic material with the Sunset Laboratory Carbon Aerosol
Monitor.
by Grover, Brett D.^Kleinman, Michael^Eatough, Norman L.^Eatough,
Delbert J.^Cary, Robert A.^Hopke, Philip K.^Wilson, William E.
The combination of technology used in the High-Volume Brigham Young
University Organic Sampling System (BIG BOSS (18)) and the Harvard
particle concentrator (19) has resulted in the PC-BOSS. (4,18-20) The
configuration and operation of the PC-BOSS as used in the studies
reported here has been previously described. (11) The PC-BOSS was used
for sample collection to determine fine particulate mass, sulfate,
carbonaceous material (elemental and organic), nitrate, SVOM, and
semi-volatile nitrate. Samples for the chemical characterization of
[PM.sub.2.5] in the minor flow following a particle concentrator and a
BOSS diffusion denuder were collected in a filter pack containing a
pre-fired (800 [degrees]C) 47-mm quartz filter (Pallflex) followed by
47-mm CIG fiber filter to determine fine particulate carbonaceous
material and nitrate, including semi-volatile species lost from the
particles during sampling. A second parallel filter pack containing a
47-mm Teflon (Whatman) filter followed by a 47-mm Nylon (Gelman,
Nylasorb) filter was used to determine [PM.sub.2.5] filter retained
(nonvolatile) mass, sulfate and nitrate, including any nitrate lost from
the particles during sample collection. A side flow filter pack, before
the particle concentrator, containing a 47-mm polycarbonate (Corning,
Nuclepore, 0.4-[micro]m pore size) filter followed by a 47-mm CIG
filter, was used to collect particles (excluding semi-volatile species
lost during sampling) and gas-phase organic material after the
2.5-[micro]m outlet cut. These data were compared with data from the
minor flow filters to determine the particle concentrator and denuder
efficiencies. The quartz filter nonvolatile OC (NVOC) and EC, and CIG
filter SVOC, determined with the PC-BOSS, were used for comparison with
the results obtained with the two Sunset monitors.
Temperature Programmed Volatilization (4,21) was used in the
analysis of PC-BOSS collected samples for total carbonaceous material.
In this method, the various sample filters are heated from ambient
temperature at a predetermined ramp rate to a predetermined termination
temperature. The ramp rate and termination temperatures are dependent on
the type of filter being analyzed. Quartz filters are heated to 800
[degrees]C in an [N.sub.2]/[O.sub.2] atmosphere. Charcoal-impregnated
filters are heated to 400 [degrees]C in an [N.sub.2] atmosphere. Carbon
in compounds desorbed from the filters during the heating process is
catalytically converted to [CO.sub.2] and detected by NDIR absorption.
The PC-BOSS results provided a comparison for the data obtained
with the two Sunset monitors because total fine particulate carbonaceous
material, including the NVOC, SVOC, and EC, are also measured with this
instrument. A disadvantage of the PC-BOSS is that the limits of
detection of this sampler were higher than for the Sunset monitors.
Therefore, 3-hr integrated data were obtained with the PC-BOSS.
Sample Collection
Initial studies were conducted in February 2003 in Lindon, UT. The
Lindon sampling site has been previously described. (11) In these
experiments, results obtained with the modified Sunset monitor were
compared with fine particulate SVOC determined in 6-hr integrated
samples with the PC-BOSS. More extensive studies were conducted during
July 2003 at the South Coast Air Quality Management District (SCAQMD)
sampling site in Rubidoux, CA. In these experiments, both the
conventional and modified Sunset monitors were simultaneously used.
Results were compared with 3-hr integrated PC-BOSS sample results.
RESULTS AND DISCUSSION
Efficiency of the Sunset Monitor Denuder for Removal of Gas-Phase
Organic Material
The analysis of material collected by the CIG filter in the
modified Sunset instrument is illustrated in Figure 1B. On the basis of
data obtained in several studies with a charcoal-impregnated filter
using a parallel plate denuder (4,5,8,9,14,18,20) the initial peak in
the data is due to the small fraction of the gas-phase organic material
entering the denuder that is not removed by the denuder, and this
material is well separated from SVOC lost from particles. For the sample
given in Figure 1B, this initial peak is about half the size of the
larger peakin the 220-450 [degrees]C temperature step. The gas-phase
organic material collected on the side-flow filter of the PC-BOSS is a
measure of the total gas-phase organic material that enters the
diffusion denuder of the Sunset instrument. The initial peak in Figure
1B is the amount of this total that is not removed by the denuder.
Comparison of these two values gives the denuder efficiency. Initially
the efficiency of the denuder was better than 99.5%. However, as
observed in the data obtained over a 3-week period in Lindon, the size
of the first peak, relative to the SVOC peak, increases with time as the
efficiency of the denuder drops to approximately 98% over this time
period. The data illustrated in Figure 1B are after approximately 2
weeks of sampling with the denuder. To help maintain high denuder
efficiency, new charcoal-impregnated cellulose fiber filter strips
(Schleicher and Schuell) were placed in the denuder about every 10 days
during the Lindon study. These strips are cut to size for the denuder
box and used without further treatment as received from the
manufacturer. Denuder strips were not changed during the Rubidoux study
because the study duration of 4 weeks was not expected to result in a
significant degradation of denuder efficiency on the basis of previous
studies. (14)
Determination of Fine Particulate Carbonaceous Material with the
Sunset Monitors
The two Sunset monitors used at Rubidoux were intended to allow for
the semicontinuous measurement of total fine particulate carbonaceous
material, nonvolatile carbonaceous material (including both nonvolatile
OC and EC) being determined on the instrument with the quartz filter,
and fine particulate SVOC lost from the particles collected on the
quartz filter being determined on the instrument with the CIG filter.
The data obtained with the modified Sunset instrument using a CIG filter
are illustrated in Figure 1B and have been discussed in the proceeding
section. Typical data obtained with the conventional Sunset monitor are
illustrated in Figure 1A. As shown, the organic carbonaceous material is
initially evolved in four temperature steps in a He atmosphere. Any
pyrolyzed carbon and EC are then removed in an [O.sub.2]/He atmosphere,
with the amount of EC identified from the point at which the measured
absorbance returns to the original value for the sample. Although the
data obtained with the Sunset instrument will allow determination of the
amount of carbon evolved in each of the temperature steps and the
identification of the concentrations of EC, only total carbonaceous
material is used in the comparisons made in this paper.
[FIGURE 2 OMITTED]
[FIGURE 3 OMITTED]
The concentrations of nonvolatile and SVOC determined with the two
instruments are illustrated with concentrations determined over a 7-day
period in the Rubidoux study in Figure 2. As illustrated, the results
indicate that SVOC was a significant fraction of the total fine
particulate material during the study. Concentration of SVOC and
nonvolatile quartz filter carbon were both high and showed strong (but
different) diurnal patterns during the first 4 days of this period.
Concentrations were much lower during the last 2 days.
The accuracy in the measurement of SVOC, NVOC, and total
[PM.sub.2.5] C (calculated as the sum of NVOC, SVOC, and EC) as
illustrated by the data in Figure 2, can be evaluated by comparison of
the measurement obtained with the modified Sunset instrument and the
SVOC, NVOC, and total [PM.sub.2.5] C (also calculated as the sum of
NVOC, SVOC, and EC) measured using the PC-BOSS as described above. These
two measurements for each species are compared for the 3-hr integrated
time periods over which the PC-BOSS measurements were made in Figure 3
and the linear regression statistics are given in Table 1. The larger
number of data points in Figure 3 for SVOC as compared with NVOC results
from two time periods when the Sunset quartz data (NVOC) were not valid.
As illustrated, measurements for total [PM.sub.2.5] C made by the two
instruments agreed. Linear regression analysis of the data given in
Figure 3 (N = 21, [R.sup.2] = 0.92) gives a zero intercept slope of 0.99
[+ or -] 0.02. The slope obtained with a fit intercept is similar, 0.90
[+ or -] 0.06. The precision of the comparison is [sigma] = [+ or -]1.5
[micro]g C/[m.sup.3] (8%), and the average measured concentration of
[PM.sub.2.5] C is 18.8 [micro]g C/[m.sup.3], with no bias between the
two measurements. The precision of the comparison is similar to the
expected precision of the PC-BOSS 3-hr integrated measurement of [+ or
-]1-2 [micro]g [PM.sub.2.5] C/[m.sup.3], on the basis of the blank
filter reproducibility and the uncertainty in the flow data, and also on
the basis of results of past studies. (14,18,20) Thus, this comparison
indicates that the [PM.sub.2.5] C measurements by the two independent
techniques are equivalent. During the time period when SVOC was
measured, the SVOM (assuming SVOM was 61% C) (22) averaged 21% of the
total [PM.sub.2.5], as previously reported for measurements by an R
& P filter dynamics measurement system tapered element oscillating
microbalance. (23)
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