146
MTERNAL COMBUSnON ENGME FUNDAMENTALS
PROPERTIES
OF
WORKING
FLUIDS
147
or volume fraction in parts per million @pm) as C,. Sometimes results are
expressed as ppm propane (C3H,) or ppm hexane (C,H,,); to convert these to
ppm C, multiply by
3
or
6,
respectively. Older measurements of unburned hydro-
carbons were often made with a nondispersive infrared (NDIR) analyzer, where
the infrared absorption by the hydrocarbons in a sample cell was used to deter-
mine their
~oncentration.'~ Values of HC concehtrations in engine exhaust gases
measured by an FID are about two times the equivalent values measured by an
NDIR analyzer (on the same carbon number basis, e.g., C,). NDIR-obtained
concentrations are usually multiplied by 2 to obtain an estimate of actual HC
concentrations. Substantial concentrations of oxygen in the exhaust gas affect the
FID measurements. Analysis of
unburned
fuel-air mixtures should be done with
special care." To prevent condensation of hydrocarbons in the sample line
(especially important in diesel exhaust gas), the sample line is often heated.
NDIR analyzers are used for
CO, and CO concentration measurements.
Infrared absorption in a sample cell containing exhaust gas is compared to
absorption in a reference cell. The detector contains the gas being measured in
two compartments
separa~ed by a diaphragm. Radiation not absorbed in the
sample cell is absorbed by the gas in the detector on one side of the diaphragm.
Radiation not absorbed in the reference cell is absorbed by the gas in the other
half of the detector. Different amounts of absorption in the two halves of the
detector result in a pressure difference being built up which is measured in terms
of diaphragm distention. NDIR detectors are calibrated with sample gases of
known composition. Since water vapor IR absorption overlaps
CO, and CO
absorption bands, the exhaust gas sample is dried with an ice bath and chemical
dryer before it enters the NDIR instrument.
Oxygen concentrations are usually measured with paramagnetic analyzers.
Oxides of nitrogen, either the amount of nitric oxide (NO) or total oxides of
nitrogen (NO
+
NO,, NOJ, are measured with a chemiluminescent analyzer.
The NO in the exhaust
gas
sample stream is reacted with ozone in a flow reactor.
The reaction produces electronically excited NO, molecules which emit radiation
as
they decay to the ground state. The amount of radiation is measured with a
photomultiplier and is proportional to the amount of NO. The instrument can
also convert any NO, in the sample stream to NO by decomposition in a heated
stainless steel tube so that the total NO, (NO
+
NO,) concentration can be
determined.23 Gas chromatography can be used to determine all the inorganic
species
(N,
,
CO,, 0,, CO,
Hz)
or can be used to measure the individual hydro-
carbon compounds in the total unburned hydrocarbon mixture. Particulate emis-
siom are measured by filtering the particles from the exhaust gas stream onto
a
previously weighed filter, drying the filter plus particulate, and reweighing.
SPARK-IGNITION
ENGINE DATA. Dry exhaust gas composition data, as a func-
tion of the fuel/air equivalence ratio, for several different multi- and single-
cylinder automotive spark-ignition engines over a range of engine speeds and
loads are shown in Fig. 4-20. The fuel compositions (gasolines and isooctane) had
H/C ratios ranging from 2.0 to 2.25. Exhaust gas composition is
subs tan ti all^
Exhaust equivalence
ratio
FIGURE
4-20
Spark-ignition engine exhaust
gas
composition data in mole fractions as a function of fuelfair equiva-
lence
ratio. Fuels: gasoline and isooctane,
H/C
2
to
2.25.
(From D'Alleva and Lo~ell?~
StiCendm?'
Harrington and Shish~,'~ S~indt,~' and data from the author's laboratory at
MIT,)
different on the lean and the rich side of the stoichiometric airlfuel or fuellair
ratios; thus, the fuellair equivalence ratio
4
(or its inverse, the relative airjfuel
ratio
1)
is the appropriate correlating parameter. On the lean side of stoichiornet-
ric, as
4
decreases, CO, concentrations fall, oxygen concentrations increase, and
CO levels are low but not zero (-0.2 percent). On the rich side of stoichiometric,
CO and H, concentrations rise steadily as
4
increases and CO, concentrations
fall.
0,
levels are low (-0.2 to 0.3 percent) but are not zero. At stoichiometric
operation, there is typically half a percent
0,
and three-quarters of a percent CO.
Fuel composition has only a modest effect on the magnitude of the species
concentrations shown. Measurements with a wide range of liquid fuels show that
CO concentrations depend only on the equivalence ratio or relative fuellair ratio
(see Fig. 11-20).26
A
comparison of exhaust CO concentrations with gasoline,
Propane (C3H8), and natural gas (predominantly methane, CH,) show that only
with the high H/C ratio of methane, and then only for CO
2
4
percent, is fuel
composition significant." The values of CO, concentration at a given
4
are
slightly affected by the fuel H/C ratio. For example, for stoichiometric mixtures
with 0.5 percent
0,
and 0.75 percent CO, as the H/C ratio decreases CO,
concentrations increase from 13.7 percent for isooctane (H/C
=
2.25). to 14.2
to 14.5 percent for typical gasolines (H/C in range 2-1.8), to 16 for toluene
(H/C
=
1.14).29