n-Heptane in Flame
Tflame(z) ≈ T (z) + (T (z) - T (z))
J. Phys. Chem. A, Vol. 103, No. 41, 1999 8225
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of fuel is consumed compared to other types of reactors.
Integration of a miniature flame reactor with an on-line GC/
MS provided detailed chemical information on n-heptane
combustion. The flame zone was narrow; the total flame height
to burnout was 1.25 mm. We detected about 30 different stable
organic intermediates. Figure 1 shows three chromatograms of
the oxidation at 100, 1000, and 1300 µm from the burner
surface. In the present experiment, taking place for 15 h,
spurious electronic and flow disturbances will produce some
outliers randomly. Table 3 shows examples of the reproducibility
for the final run presented in this study. Figure 2 shows the
resulting concentration profile of the n-heptane/air flame.
0.5
0.5
1.0
The cooling in the sample point due to the cooled quartz
microprobe was also investigated. A nude thermocouple,
protruding out of an alumina thermocouple shielding tube, was
positioned vertically in the microprobe holder. The temperature
profiles were measured for three configurations relating to the
cooling induced by the microprobe and its associated cooling
assembly. First, we measured with the thermocouple bead about
4
mm from cooling assembly. This corresponds to the distance
between the tip of the microprobe and the cooling assembly.
Second, we measured the temperature profile with the bead 10
mm away from the cooling assembly. Third, we measured
without the cooling assembly present. The measured temperature
difference is a first-order approximation of the cooling of the
sample introduced at the sampling point.
The species profiles of the C2-C7 alkenes formed; ethene,
propene, 1-butene, 1-pentene, 1-hexene, and 1-heptene share a
common form with broad peaks. Their concentration maxima
were found at a distance around 1000 µm. Figure 3 shows the
profiles for these compounds. Note that the ethene concentration
is divided by 8 and that the propene concentration is divided
by 2 in order to fit the profiles in the same plot. The species
profiles of methane, ethane and, propane have a similar form
with narrow peaks at around 1075 µm. Figure 4 shows the
species profiles of methane, ethane, and propane. Note that the
propane concentration is multiplied by 2. Alkynes and dienes
3. Numerical Modeling
The computations were performed using the Sandia flame
code PREMIX.14 The conditions inside the burner, at the burner
surface, and close to the burner are very difficult to model.
Therefore, the cold boundary conditions are simplified in the
PREMIX flame code and other similar flame codes. For
example, the burner is modeled as a cylinder with an open top
surface without any obstructions. In reality, our burner is a metal
disk with holes, with diameters of 150 µm, occupying about
(
ethyne, propyne, propadiene, and 1,3-butadiene) have their
maxima at around 1075 µm as the alkanes. Figure 5 shows
profiles for alkynes and dienes. Note that the ethyne and 1,3-
butadiene concentration is divided by 2 and that the propyne
concentration is multiplied by 4. Methanol, acetaldehyde,
4
0% of the area. Furthermore, in the flame code there are no
surface reactions included. Consequently, the modeling results
close to the burner are less reliable. This may result in a
distortion of the length scale of the computational profiles
compared to the experimental profiles.
2
-propanone, and propanal were also formed in the flame, and
their profiles are shown in Figure 6. Note that the acetaldehyde
concentration is divided by 2. The spatial averaging uncertainty
due to the probe is estimated to be (50 µm. During the final
experimental run the GC measurements were repeated at the
distances of 500, 700, and 900 µm from the burner. These
measurements illustrate the reproducibility during an experi-
mental series (15 h). Some of these measurements are presented
as double points in Figures 2-7 and also in Table 3.
The reaction mechanism of n-heptane oxidation and the
associated thermochemical and transport data were taken from
the work of Held et al. The mechanism used consists of 266
1
reactions and 41 species. The reaction mechanism has been
validated against flow reactor measurements, ignition delays,
1
and laminar flame speeds. However, it has not been used to
predict the species profiles in laminar premixed flames. Krypton
is present in only a minute inert amount in the combustible
mixture. To simplify the computations, the krypton was treated
as an extra addition of argon.
Table 4 shows the major (20) organic intermediates measured.
Dominating intermediate organic species were in decreasing
order: ethene, propene, ethyne, ethane, methane, 1-butene,
One major problem in the modeling of experimental flames
is the uncertainty of the temperature history experienced by the
sample. Molecules in a free adiabatic flame, a burner-stabilized
flame (without cooling probe), and a burner-stabilized flame
with a cooling probe represent the limiting cases. We have
modeled a burner-stabilized flame with corrections included for
the presence of a cooling probe. In the present study a
corresponding base temperature profile was used. However, as
discussed in many studies, the effect of the flame temperature
on the sampled molecules may be very complex. Therefore,
we also investigated the effect on species profiles of uncertain-
ties in the temperature profile. The computations were performed
using 10 different temperature profiles in the interval (200 K
around the base temperature profile. As a complement, we
modeled another heptane flame, also with φ ) 1 as in our
1
-pentene, propane, and 1,3-butadiene. For the concentration
maxima note the pattern ethene > propene > 1-butene >
-pentene > 1-hexene > 1-heptene. Alkene concentrations were
1
found to be a factor 5-10 or higher than those of the
corresponding alkanes. Significant amounts of propyne, propa-
diene, methanol, and acetaldehyde were also formed. The
concentration of formaldehyde was found to be about 2-3 times
higher than the acetaldehyde concentration. Traces of 2-pro-
panone and propanal were also detected. Below the level of 2
-
03
×
10
mol % traces of higher hydrocarbons in the C4-C7
range were found: 2-alkenes, 3-alkenes, higher alkadienes,
higher alkynes, and benzene. Most of these compounds showed
very distributed profiles and only an approximate identification
could be done for these. Figure 7 shows the species profiles of
8
experiment but burning at 0. 06 atm, using the same reaction
2
-butene, isobutene, and benzene, which are some of the minor
mechanism as above. During the final computations the values
on the GRAD and CURVE parameters were 0.1 and 0.2,
respectively. These values resulted in very dense grids of about
organic intermediates, identified in the flame. Note that the
benzene concentration is multiplied by 4.
1
10 grid points situated mainly in the flame zones.
4.2. Temperature Measurements. Figure 8 shows the
temperature profile of the flame. The temperature on the bottom
side of the burner disk was measured continuously during the
experiments; the temperature was 550 ( 50 K. We believe that
corrected flame temperatures at distances from 700 µm are
4
. Results
4
.1. GC/MS Measurements. The miniature flame reactor
provided very good stability and reproducibility. A minimum