7.6.4. Current Understanding of Chemical Changes in Turbine and Exhaust Nozzle
Approximately 99.5-99.9% of the molar content of typical commercial engine
exhaust consists of N2, O2, CO2, and H2O. The species that compose the remaining
0.1-0.5% exist in trace amounts. This trace exhaust component consists primarily
of NOx, CO, unburned HC (including soot), the hydroxy family (HOx, H2Ox), the
sulfur oxide family (SOxO), and elemental species such as O. Figure
7-26 provides a general categorization of chemical processes occurring in
the turbine and exhaust nozzle. These processes are discussed in greater detail
below.
Table 7-7: Summary of confidence attached to current modeling
and measurements of emissions emerging from engines.
|
|
Principal Effects of Post-Combustor Reactions |
Exhaust Products from Engines and Levels of Confidence
Associated with Modeling and Measurements |
Primary constituents
(e.g.,H2O,CO2N2,O2) |
Present combustors convert almost all of the kerosene to
the products of complete combustion. Further CO oxidation in the turbine
(a few tenths of a percent or less) slightly increases CO2 emitted. Prediction
capability is good, and levels are easy to derive from basic engine operating
conditions or measurements. |
Secondary products (e.g., NO, NO2, N2O, SO2, CO, stable HC) |
NOx is little changed by flow through turbine. Oxidation of NO and NO2
to HONO and HNO3, occurring mainly in the high-pressure turbine, is a few
percent or less. For civil engines, CO and HC are relatively unchanged in
the turbine, but significant reductions can occur there in advanced military
engines. Accurate NOx predictions and measurements are now routinely performed
for assessment purposes. |
Oxidation products of secondary combustion species (e.g.,
HNO2, HNO3, SO3, H2SO4, H2O2, HNO) |
Chemical mechanisms and reaction rates of trace species are not well known
over the range of post-combustor conditions. The impact of fluid mechanics
on chemical evolution is not yet fully evaluated by models or measurements. |
Reactive species (e.g., O, OH, HO2, SO, H2, H, N, CH) |
As above, but validation of trace species chemistry mechanisms, via measurements,
is also needed over the relevant temperature and pressure range for both
classes. Further modeling is required to make the connection with species
for which measurements are not available. |
|
7.6.4.1. Primary Exhaust Constituents (H2O, CO2, N2O2)
Apart from the small effect of reactions involving trace species, changes in
major species concentration in the turbine and nozzle flow path are caused by
the diluting effect of cooling air. CO2 changes less than a few tenths of a
percent as a result of oxidation of CO (increases in H2O from HOx recombination
are even smaller). This CO2 fractional increase may grow in the first stages
of the high-pressure turbine as more advanced cycles are implemented because
associated cycle changes may result in relatively more CO at the entrance to
the turbine (Godin et al., 1995, 1997; Leide and Stouffs, 1996). Current small
changes and likely future changes in primary exhaust constituents can be predicted
with sufficient accuracy (Dryer et al., 1993) for assessment needs, however,
and the levels are all relatively easy to derive from measurements.
Figure 7-28: The ICAO landing and take-off cycle (LTO).
|
7.6.4.2. Secondary Combustion Products (NO, NO2, N2O, SO2, CO, stable HC)
Secondary products-such as NO, NO2, and SO2, as well as their oxidative products
SO3, HONO, HNO3, and H2SO4-formed via reactions initiated with the reactive
radicals OH and O are the principal participants of interest in chemical and
microphysical processes occurring soon after emission. Although OH and O are
reduced considerably by the engine exit, they continue to play an important
role in global atmospheric processes (see Chapters 2 and
3). To understand the processes occurring through the
engine, relative and absolute levels of these secondary combustion products,
their oxidative products (the acid gases), and the reactive radicals need to
be accurately characterized. Emissions indices for NOx, CO, and HC, as measured
by ICAO procedures for stages in a standard LTO cycle, are documented (ICAO,
1995b) for most in-use engines as part of the engine certification process;
these emissions typically correspond to tens to hundreds of ppmv. SOxO emissions
are directly proportional to the level of sulfur in the fuel [a 400 ppmm fuel
S level corresponds to an EI(SOxO) of 0.8]. Emissions of metals, whether from
impurities in the fuel or engine wear, are much smaller than the emissions discussed
here but may be of interest in soot activation and condensation processes (Chen
et al., 1998; Twohy et al., 1998). NOx does not change significantly through
the turbine and nozzle other than through changes resulting from dilution, although
the NO2/NO ratio may shift as a result of increased oxidation. Oxidation of
NO and NO2 to HONO and HNO3, respectively, is predicted to be on the order of
a few percent or less, occurring largely in the high-pressure turbine (Fahey
et al., 1995a; Anderson et al., 1996; Lukachko et al., 1998). Although this
change in the NOx level is not significant, changes in HONO and HNO3 represent
important changes in trace species of NOy (see below). Ground-based and in-flight
measurements indicate that emissions of N2O are also small relative to NOx (Kleffmann
et al., 1994; Fahey et al., 1995b). Further validation of NOx chemistry is warranted,
but indications are that current models can predict NOx evolution in the turbine
and nozzle with sufficient accuracy for assessment needs (Dryer et al., 1993),
and measurements of NOx with a few percent accuracy are possible.
For typical civil engines, CO and HC are relatively unchanged through the
turbine and exhaust nozzle. However, they can be reduced by up to two orders
of magnitude in the turbine and exhaust nozzles (Godin et al., 1995, 1997; Leide
and Stouffs, 1996; Lukachko et al., 1998) of advanced cycle military engines,
where completion of oxidation in the high-temperature regions of the turbine
results in the modest increases of CO2 mentioned above. Measurements of these
species CO2 and total hydrocarbons) are routine, and it is possible to measure
them to several percentage points accuracy (Katzman and Libby, 1975; Spicer
et al., 1992, 1994; Dryer et al., 1993; Howard et al., 1996).
Table 7-8: LTO cycle measurements for a high bypass GE
(CF6-80) turbofan engine (ICAO, 1995b).
|
Time in Mode |
Rated Output
(F00) |
Fuel Flow
(kg s-1) |
HC |
CO |
NOx |
SN |
0.7 mins. take-off |
100% |
2.353 |
0.08 |
0.52 |
28.06 |
7.1 |
2.2 mins. climb out |
85% |
1.913 |
0.09 |
0.52 |
21.34 |
- |
4.0 mins. approach |
30% |
0.632 |
0.20 |
2.19 |
8.97 |
- |
26 mins. idle |
7% |
0.205 |
9.68 |
43.71 |
3.74 |
- |
Dp/F00 (g kN-1) LTO cycle miss./rated output measured avg |
12.43 |
57.09 |
42.17 |
|
Dp/F00 (g kN-1) characteristic value to be regulated |
16.2 |
65 |
46.4 |
8.3 |
Current regulatory level |
19.6 |
118 |
80.2 |
18.3 |
|
|