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Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Clean and Efficient Diesel Engine: Final Report DOE/ DE-
FC26-08NT06560
This is the final report for the Clean and Efficient Diesel Engine project, DOE Award
DE-FC26-08NT06560. It summarizes the activities of the two phases of the project.
This material is based upon work supported by the Department of Energy National
Energy Technology Center under Award Number(s) DE-FG26-08NT06560.
This report was prepared as an account of work sponsored by an agency of the United
States Government. Neither the United States Government nor any agency thereof, nor
any of their employees, makes any warranty, express or implied, or assumes any legal
liability or responsibility for the accuracy, completeness, or usefulness of any
information, apparatus, product, or process disclosed, or represents that its use would not
infringe privately owned rights. Reference herein to any specific commercial product,
process, or service by trade name, trademark, manufacturer, or otherwise does not
necessarily constitute or imply its endorsement, recommendation, or favoring by the
United States Government or any agency thereof. The views and opinions of authors
expressed herein do not necessarily state or reflect those of the United States Government
or any agency thereof.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Table of Contents Phase 1 ................................................................................................................................ 4
Task 1: Design Study for Fuel-Efficient System Configuration ......................................... 4
Task 2: Combustion System Studies ................................................................................ 12
GEVO Single Cylinder Experiments; Miller Cycle Tests for Improved Fuel Economy
....................................................................................................................................... 13
GEVO SCE Experiments with EGR; Effect of Injection Pressure and Multiple
Injections on an EGR-Equipped Engine ....................................................................... 15
GEVO SCE Experiments with EGR; Effect of Piston Bowl Geometry on an EGR-
Equipped Engine ........................................................................................................... 16
Summary ....................................................................................................................... 19
Task 3 ................................................................................................................................ 20
Phase 2 .............................................................................................................................. 53
Task 5 ................................................................................................................................ 53
Subtask 5A: Low Particulate Combustion Tests .......................................................... 53
Subtask 5B :Aggressive Valve Timing Studies. ........................................................... 53
Task 6: Advanced Air Handling. ...................................................................................... 53
Table of Figures Figure 1- Contour plot of normalized BSNOx with start of fuel injection and intake valve
closing for nominally sized turbine. Note that BSNOx values are normalized by
BSNOx at an IVC and SOI of 0. ................................................................................. 7
Figure 2- Contour plot of normalized BSFC with start of fuel injection and intake valve
closing for nominally sized turbine. The red squares superimposed on this plot are
of the normalized BSNOx equal to 1 from Figure 1. Note that BSFC values are
normalized by BSFC at an IVC and SOI of 0 from the nominal turbine case ............ 7
Figure 3- Contour plot of normalized BSNOx with start of fuel injection and intake valve
closing for the turbine with 20% reduced nozzle area. Note that BSNOx values are
normalized by BSNOx at an IVC and SOI of 0 from the nominal turbine case. ........ 8
Figure 4- Contour plot of normalized BSFC with start of fuel injection and intake valve
closing for the turbine with 20% reduced nozzle area. The red squares
superimposed on this plot are of the normalized BSNOx equal to 1 from Figure 3.
Note that BSFC values ................................................................................................ 8
Figure 5- Fuel injection timing trends of NOx and SFC for turbo-compounding engine
architecture ................................................................................................................ 10
Figure 6- Fuel injection timing trends of NOx and SFC for varying levels of EGR with
turbo-compounding. Results shown for EGR fractions of 10, 20, and 30% with an
intake valve closure 40° before the baseline. Baseline results are also shown for
comparison ................................................................................................................ 12
Figure 7: View of GE Global Research Single Cylinder Engine Lab .............................. 13
Figure 8- Comparison of engine performance for nominal and nominal-50 degree IVC
cams at (top) notch 8 and (bottom) notch 4. Triangles indicate NOx/SFC
improvement and asterisks indicate Smoke/SFC changes. ....................................... 15
Figure 9: Performance data for a notch 8 injection timing swing with 1800bar rail
pressure, notch 8 representative boost, and 25% EGR. ............................................ 17
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 10: Performance data for a notch 4 injection timing swing with 1800bar rail
pressure, notch 4 representative boost, and 25% EGR. ............................................ 19
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Phase 1
Task 1: Design Study for Fuel-Efficient System Configuration
The objective of this task was to perform a system design study of locomotive engine
configurations leading to a 5% improvement in fuel efficiency. Modeling studies were
conducted in GT-Power to perform this task. GT-Power is an engine simulation tool that
facilitates modeling of engine components and their system level interactions. It provides
the capability to evaluate a variety of engine technologies such as exhaust gas circulation
(EGR), variable valve timing, and advanced turbo charging. The setup of GT-Power
includes a flexible format that allows the effects of variations in available technologies
(i.e., varying EGR fractions or fuel injection timing) to be systematically evaluated.
Therefore, development can be driven by the simultaneous evaluation of several
technology configurations.
A variety of engine technologies were investigated within GT-Power to determine their
potential to reduce locomotive fuel consumption and emissions. These included high-
pressure fuel injection, variable fuel injection and intake valve timings, advanced
turbocharger configurations, and variable EGR fractions.
A base model was previously developed in GT-Power to simulate locomotive size
engines. The model consists of a 12 cylinder, turbocharged compression ignition engine.
This engine model is designed with the capability to operate at high horsepower (ranging
up to 5000 HP) and medium speeds (in the range of 1000 rpm). The model is equipped
with a turbocharger (turbine and compressor) and intercooler, consistent with locomotive
applications. The turbocharger increases the air to the engine, resulting in an increase in
specific power output. An intercooler, downstream of the compressor, is then necessary
to reduce the manifold air temperature, which can lead to lower NOx emissions and fuel
consumption.
Combustion within the cylinders is modeled with a direct injection diesel model. This
tool divides the injected fuel mass into zones and predicts burn rates and NOx emissions.
The parameters of the implemented model have been tuned to agree with available
experimental data.
The model is set up to operate with user defined fuel injection profiles (including
injection pressure) and intake valve profiles. This flexibility allows for evaluation of
injection profiles from those of a unit pump system or those consistent with a common
rail system. The intake valve closure timing can also be varied from a baseline case (a
conventional intake valve closure that maximizes engine volumetric efficiency) to earlier
closure events, affecting the air handling (i.e., Miller Cycle). These variations will
indicate the potential entitlement of each of these in a locomotive application.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
The model also allows for high-pressure EGR, with exhaust flow pumped from upstream
of the turbine to a location downstream of the compressor. An exhaust gas recirculation
pump and heat exchanger are in place to re-direct cooled exhaust gas back to the intake
manifold. EGR is a technology that can potentially reduce NOx emissions and overall
fuel consumption when incorporated with other engine technologies.
The current model is designed to be flexible and is equipped to rapidly investigate
different engine technology options. This format allows for evaluation of a relatively
large array of technology variations, providing significant data to guide single cylinder
experimental studies in subsequent tasks.
Intake valve timing profiles are an input to the model. Therefore, the user can define
intake valve profiles to vary the valve closure timing. Intake valve lift profiles have been
developed with intake valve closure events ranging from the baseline case to 120° earlier
than the baseline. These variations in valve closure will change the air handling of the
engine, potentially leading to a decrease in emissions and fuel consumption when
combined with other engine technologies such as fuel injection timing. The model
provides the flexibility to easily vary the start of fuel injection by changing the crank
angle to initiate the start of injection. Hence, a full parametric space of fuel injection
timing and valve lift closure timings can be evaluated.
The turbocharger is modeled as a simple turbine and simple compressor within GT-
Power. These tools simplify the turbine and compressor, as each element is not limited to
restrictions from their respective maps. The intention of these elements is for early
development purposes, so as not to restrict the turbocharger capabilities. Therefore,
various air handling techniques can be evaluated without being restricted to available
turbine and compressors.
The current model has been calibrated to experimental data providing confidence in the
model. The calibration was done with a fixed intake valve profile and a high-pressure
fuel injection profile consistent with a common rail system. GT-Power simulations of the
locomotive model were then conducted while varying intake valve lift profiles, fuel
injection timing, and turbine size. This parametric study consisted of the following range
of input parameters:
1. Variable intake valve lift profiles: Intake valve closure events from the baseline
to 70° earlier, in 10° increments.
2. Varying fuel injection timing: Fuel injection timing ranging from 2° after the
baseline to 8° before the baseline, in 2° increments.
3. Turbine size: Turbine size was varied by decreasing the nozzle area from its
nominal value by 10 and 20% (acting to effectively increase the turbine power
output).
Contour plots of brake specific NOx (BSNOx) and brake specific fuel consumption
(BSFC) over the entire operating space for the nominally sized turbine are shown in
Figure 1 and Figure 2, respectively. Note that each parameter is normalized by its
respective value at the nominal intake valve closing and nominal start of injection.
Figure 1 shows that, for a fixed start of injection, BSNOx can be reduced by earlier intake
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
valve closures. However, this decrease in BSNOx comes at the expense of increased fuel
consumption (see Figure 2). A second tradeoff between BSNOx and BSFC is seen with
injection timing. As the start of injection is advanced, BSFC is reduced while BSNOx
increases.
Figure 2 also has a constant BSNOx curve superimposed onto the contour plot. The red
line in Figure 2 correspond to the BSNOx = 1 contour from Figure 1. This superimposed
contour line shows that a 2% fuel benefit can be realized for the nominal turbine case by
injecting fuel 4° before the baseline and closing the intake valve approximately 50°
earlier than the nominal case.
GT-Power simulations were also performed with a turbine nozzle area reduced by 20%.
Contour plots of BSNOx and BSFC for the range of fuel injection timings and intake
valve closing for this turbine sizing are shown in Figure 3 and Figure 4, respectively.
Note that the BSNOx is normalized by the BSNOx value at nominal start of injection,
valve closing and turbine size. Similarly, BSFC is normalized by the BSFC at the
corresponding operating condition for the nominally sized turbine. Also, note that the red
line in Figure 4 correspond to the BSNOx = 1 contour from Figure 3.
The general trends of BSFC and BSNOx are similar for the smaller turbine as the nominal
turbine. However, it can be seen that the BSFC benefit of early injections is maintained
at the earliest intake valve closing (in contrast to the nominally sized turbine where BSFC
begins to drop off). Therefore, the emissions neutral point for the smaller turbine
corresponds to the earliest intake valve closing of –70° and a start of injection of -5°
(relative to nominal timing). At this operating point, there is an apparent 3.5% fuel
benefit from the baseline case with the nominal turbine (i.e., SOI = 0° and IVC = 0°) and
neutral emissions.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
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Figure 1- Contour plot of normalized BSNOx with start of fuel injection and intake valve closing for
nominally sized turbine. Note that BSNOx values are normalized by BSNOx at an IVC and SOI of 0.
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Figure 2- Contour plot of normalized BSFC with start of fuel injection and intake valve closing for
nominally sized turbine. The red squares superimposed on this plot are of the normalized BSNOx equal to
1 from Figure 1. Note that BSFC values are normalized by BSFC at an IVC and SOI of 0 from the nominal
turbine case
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0.7 0.75
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Figure 3- Contour plot of normalized BSNOx with start of fuel injection and intake valve closing for the
turbine with 20% reduced nozzle area. Note that BSNOx values are normalized by BSNOx at an IVC and
SOI of 0 from the nominal turbine case.
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Figure 4- Contour plot of normalized BSFC with start of fuel injection and intake valve closing for the
turbine with 20% reduced nozzle area. The red squares superimposed on this plot are of the normalized
BSNOx equal to 1 from Figure 3. Note that BSFC values
Next, an evaluation on the fuel consumption benefits of turbo-compounding was
conducted. As with the Miller cycle studies, the analyses were conducted in order to
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
assess the fuel consumption benefits while holding the emissions to currently regulated
NOx levels. The GT-Power model that was exercised included an auxiliary power turbine
downstream of the turbocharger. This turbine was modeled as a simple orifice of varying
diameter and fixed efficiency. The impact of intake valve closure timing on turbo-
compounding was also investigated by including earlier intake valve closure timings.
Figure 5 displays NOx and SFC trends with varying fuel injection timing for six engine
architectures. The curves are shown with NOx and SFC values normalized with respect
to a baseline cam configuration and fuel injection timing. In each instance, the turbine
orifice diameters were sized to best minimize NOx and SFC. The six NOx/SFC curves
displayed in the figure include:
1. Baseline intake valve closure with the nominal turbocharger turbine diameter without
turbo-compounding.
2. Intake valve closure forty degrees before the baseline.
3. Intake valve closure one hundred degrees before the baseline.
4. Baseline intake valve closure timing with added power turbine (turbo-compounding).
5. Intake valve closure forty degrees before the baseline with added power turbine
(turbo-compounding).
6. Intake valve closure one hundred degrees before the baseline with added power
turbine (turbo-compounding).
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
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SFC Delta [%]
NOx Delta [%]
Baseline Valve Closure
Early Closure: 40° before Baseline
Early Closure: 100° before Baseline
Baseline Valve Closure: Turbocompounding
Early Closure (40° before Baseline): Turbocompounding
Early Closure (100° before Baseline): Turbocompounding
Figure 5- Fuel injection timing trends of NOx and SFC for turbo-compounding engine architecture
A full range of power turbine and turbocharger turbine sizes were investigated in this
study. Results are only presented for the cases yielding the lowest SFC for each
configuration. It was already shown that SFC, at a constant NOx level, could be reduced
with an early intake valve closure when combined with a timing advance. This trend is
displayed again in Figure 5. Relative to the baseline, the early intake valve closure
(without turbo-compounding) shows a 3.5% reduction in SFC.
A further reduction in SFC, at a constant NOx level, is seen when a power turbine is
added downstream of the turbocharger turbine (i.e., turbo-compounding). Figure 5
displays this trend for three intake valve closure timings (the baseline, 40°, and 100°
before the baseline). In these instances, SFC is reduced by approximately 8% from the
baseline NOx level. These fuel consumption benefits were shown to occur due to the
combination of work extracted from the power turbine combined with a lower BSNOx
level allowing fuel injection timing to be advanced. It needs to be noted that the lower
BSNOx is due both to the increased residual gas content (internal EGR) as well as the
greater power output produced. The baseline intake valve closure (with turbo-
compounding) shows a greater fuel benefit than the early intake valve closure (with
turbo-compounding). The results displayed in Figure 5 show the potential benefit for
turbo-compounding to provide a fuel consumption benefit. However, the relative benefit
Nominal
Point
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
of turbo-compounding appears to diminish with earlier intake valve closure timings. At
the earliest intake valve closure timing, turbocompounding does not appear to reduce
SFC (compare yellow triangle solid curve with yellow triangle dashed curve). This
diminishing turbo-compounding benefit is due to two reasons. First, with the more
aggressive valve timing, turbine back pressures are already at high levels in order to
deliver sufficient airflow to the engine. The additional backpressure due to the
turbocompounding unit creates an additional pumping loss. Secondly, the more
aggressive valve timing enables a greater effective expansion to take place in the
cylinder. As such, the turbocompounding unit sees less energy available in the exhaust
stream to recover.
The study was further broadened to include an engine architecture for which turbo-
compounding is utilized as a means of circulating EGR. This architecture provides a
means to reduce emissions levels while also decreasing fuel consumption. In this
architecture, the power turbine downstream of the turbocharger turbine served to
backpressure the engine in order to circulate the EGR flow as well as extract energy from
the exhaust stream.
Figure 6 displays NOx and SFC trends with varying fuel injection timing for a single
intake valve closure timing (forty degrees before the baseline) as EGR fraction is
increased. Turbo-compounding has been implemented as a means to backpressure the
engine and, hence, circulate the EGR flow. Three distinct EGR fractions are displayed in
the figure (10, 20, and 30%) to provide an indication of the trends of NOx and SFC with
EGR flow. In each instance, the sizing of the turbine diameters (turbocharger and power
turbine) has been optimized to best minimize SFC and NOx. The NOx and SFC values in
this figure are normalized with respect to the baseline configuration and fuel injection
timing. Note that the baseline configuration is with a baseline valve timing and does not
have EGR or turbo-compounding.
The results in Figure 6 indicate that turbo-compounding can be an efficient method to
circulate EGR flow for this intake valve closure timing. The results show the potential to
significantly reduce NOx emissions while maintaining or improving fuel consumption.
For instance, the results show a 60% reduction in NOx with an SFC benefit of 3 to 4%
could be achieved with EGR fractions of 10 to 20%. A further reduction in NOx, up to
70% from the baseline, can be achieved at SFC parity with EGR levels from 20 to 30%.
These results indicate that, depending on emissions regulations, a system can be
optimized to meet NOx regulations while maintaining or improving fuel consumption
levels by means of waste heat recovery.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
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10% EGR: Valve closure 40° before baseline
20% EGR: Valve closure 40° before baseline
30% EGR: Valve closure 40° before baseline
Figure 6- Fuel injection timing trends of NOx and SFC for varying levels of EGR with turbo-compounding.
Results shown for EGR fractions of 10, 20, and 30% with an intake valve closure 40° before the baseline.
Baseline results are also shown for comparison
Task 2: Combustion System Studies
The EVO single-cylinder engine (SCE) has been used to explore engine configurations
more efficiently than a production multi-cylinder engine. The power assembly of the
SCE (i.e., combustion chamber, piston, connecting rod, cylinder liner strong back and
head) can be the same hardware as the current production engine, the GE Evolution, or
this hardware can be modified to investigate new technologies. For the data reported
here, a common rail fuel system was utilized, providing independent control of fuel
pressure, injection timing, and engine load. This technology is complimentary to the
miller-cycle testing, which requires some independent control of injection parameters to
control particulate matter (PM). Turbocharging is simulated through independent control
of intake and exhaust pressures. GT-power models and experimental data were used to
provide approximate air handling conditions for the SCE and post-processing calculations
were used to correct for minor pumping loop discrepancies.
The GRC Single cylinder facility is also equipped with a high-pressure cooled EGR
setup. The EGR is controlled via an electrically driven centrifugal pump. The EGR is
cooled with a standard shell and tube laboratory heat exchanger. The pump is a
necessary means of recirculating EGR as various points in the locomotive duty cycle
have the exhaust manifold pressure lower than the intake manifold pressure. While a
Nominal
Point
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
backpressure valve can raise the exhaust pressure to a level required to circulate EGR, it
also leads to an unfavorable gas exchange process and fuel economy penalty. As such, all
of the combustion experiments were conducted using a pump. All specific fuel
consumption numbers presented account for the power required to drive the pump.
GRC Single Cylinder Engine Lab
Figure 7: View of GE Global Research Single Cylinder Engine Lab
The SCE provided an avenue for evaluating a large amount of hardware including a high-
pressure common rail fuel system, miller cams with early intake valve closure, multiple
piston bowls and an EGR system. All of this hardware was tested with the goal of
reducing emissions while maintaining or improving fuel economy. Performance tests
focused on a high-load condition (notch 8) due to its substantial contribution to the
overall engine performance and also a moderate-load condition (notch 4) to provide a
more rounded survey of overall engine performance.
GEVO Single Cylinder Experiments; Miller Cycle Tests for Improved Fuel Economy
The first study performed under this contract was an investigation of miller cycle for
improved performance. In the so-called Miller cycle, the effective compression ratio is
reduced while expansion ratio is maintained. The benefit of this is that peak gas
temperatures are reduced, thereby lowering NOx emissions. If the NOx reduction is
significant, injection timing can be advanced and fuel economy can be gained as well.
Miller cycle was enabled in our experimental setup by using modified cams with early
intake valve closure.
Three cam configurations were compared in this study. The first configuration utilizes
the baseline cam with the nominal timing of valve closure and air-handling conditions
representative of a current production turbocharger. The second configuration utilizes a
miller cam where the intake valve closes 50 degrees earlier than nominal and air-handling
conditions representative of the current production turbocharger. The third configuration
utilizes a less aggressive miller cam with valve closure 40 degrees earlier than nominal
with air-handling conditions representative of a high-efficiency turbocharger. The data in
Figure 8 compares performance of the first two configurations.
Tests were performed at notches 4 and 8 for the baseline cam with nominal valve closing
and with a miller cam where the intake valve closed 50 degrees earlier than nominal. For
notch 8, the tests with the nominal cam were performed with low injection pressure and
tests with the -50deg cam were performed with both low and high injection pressure. The
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
data show that, for fixed rail pressure, fuel consumption improves by 5%, but smoke
increases by ~0.04 g/hp-hr. Increasing to high injection pressure was used to combat the
smoke penalty, resulting in no smoke increase and ~4.5% SFC improvement over the
nominal cam. Thus, for this high-load condition, the combination of increased injection
pressure and early intake valve closure has resulted in a significant fuel economy benefit
with no increase in emissions.
For notch 4, results are shown with low injection pressure for the nominal cam and
moderate and high with the –50 deg cam. These data show that the early valve closure
has a detrimental effect on the NOx/SFC performance at this moderate load condition.
The reason for this is that the air-fuel ratio at notch 4 is relatively low. These lower air-
fuel ratios result in poorer air utilization and slower combustion for the –50 cam.
Furthermore, even with an increase in rail pressure, the smoke is still ~0.02 to 0.04 g/hp-
hr higher for the –50deg cam. Thus, the performance benefit at notch 8 is somewhat
counterbalanced by some penalty at notch 4. Further investigations with rail pressure,
multiple injections, and turbocharger matching may help reduce the penalties at lower
loads while maintaining or improving the benefits at higher loads.
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Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
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Nominal-50deg, High Pressure
Figure 8- Comparison of engine performance for nominal and nominal-50 degree IVC cams at (top) notch
8 and (bottom) notch 4. Triangles indicate NOx/SFC improvement and asterisks indicate Smoke/SFC
changes.
For a locomotive engine targeting lower fuel consumption at NOx parity, miller cycle
using early intake valve closure is a potential pathway, but this may come at the expense
of particulate. Sample data were compared here and additional data are available in an
earlier report. It was shown that particulate can be reduced through higher rail pressure
and it is expected that further PM reductions are possible through the use of multiple
injections and careful specification of the fuel injector nozzle.
GEVO SCE Experiments with EGR; Effect of Injection Pressure and Multiple Injections
on an EGR-Equipped Engine
This section details a significant amount of combustion data that was collected using
exhaust gas recirculation (EGR) as a NOx reduction mechanism. The previous
combustion tests reported above sought to minimize specific fuel consumption at
constant NOx emissions levels. In other words, Miller cycle technology was being
evaluated to improve fuel economy without reducing NOx emissions. In contrast, EGR is
being assessed as a technology to drive down NOx emissions. While it is possible to
derive a fuel economy improvement from the use of EGR, this work aims at
understanding the benefits of using EGR as a fundamental mechanism to reduce NOx in a
large bore medium speed diesel engine. An unfortunate consequence of EGR is the
increase in particulate emissions. Therefore, tests conducted for this portion of the study
sought to understand the sensitivity of particulate emissions to injection pressure,
multiple injections and higher-pressure turbo-charging. The results of this study are
provided in a previous report, but some summary conclusions are listed below.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
The study performed to investigate injection pressure and multiple injections shows that
in an EGR-equipped engine, particulate can be reduced using increased boost pressure,
increased fuel injection pressure and multiple injections. Furthermore, it was shown that
fuel economy can improve or degrade as injection pressure is increased, depending on
how high the injection pressure is. The data shown here suggest that increasing boost
pressure results in a fuel economy penalty, which is true for this case, but it is likely that
there are some engine operating conditions where increased boost will improve engine
performance. This is true for cases where the air-fuel ratio is very low to begin with.
Finally, it was shown that multiple injections can be beneficial for emissions while
having an insignificant effect on fuel economy.
GEVO SCE Experiments with EGR; Effect of Piston Bowl Geometry on an EGR-
Equipped Engine
In this portion of the study, combustion tests were performed with 4 different piston
crowns in the presence of EGR. Geometric information of the crowns is listed in Table 1.
Bowl Shape CR
A Mexican hat 17
B Double-Rim 17
C Double-Rim 15
D Double-Rim 17
Table 1- Piston crown configurations and corresponding compression ratios
Three of the bowls investigated the effects of contouring at the bowl rim by incorporating
double-rim bowl designs. One such bowl was also used to understand the performance
tradeoffs of using a lower compression ratio piston. It is well known that reducing the
compression ratio and keeping all other parameters fixed will reduce NOx but increase
SFC. There is less information about what the effect will be on PM and also whether the
overall NOx/SFC performance tradeoff will be better or worse with the lower
compression ratio (i.e., if compression ratio is reduced and injection timing is advanced
until the NOx is unchanged, will the fuel economy be better or worse). Performance of
the 4 bowls is compared using a common rail fuel system with rail pressure of 1800bar.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
-60
-40
-20
0
20
40
60
80
-4 -2 0 2 4 6
SFC Change [%]
NOx Change [%]
Bow l A
Bow l B
Bow l C
Bow l D
-60
-40
-20
0
20
40
60
80
-50 0 50 100 150 200 250 300
Soot Change [%]
NOx Change [%]
Bow l A
Bow l B
Bow l C
Bow l D
Figure 9: Performance data for a notch 8 injection timing swing with 1800bar rail pressure, notch 8
representative boost, and 25% EGR.
Notch 8 performance data is shown in Figure 9. These data illustrate that Bowl C
exhibits a slightly inferior NOx/SFC tradeoff and that Bowl A shows the lowest overall
emissions. Furthermore, bowl B exhibits significantly higher soot emissions than the
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
other bowls. It is possible that the emissions from the other bowls may be improved
through further bowl/nozzle matching studies.
Figure 10 shows similar performance data for notch 4 operation. Bowl C clearly shows
worse NOx/SFC performance, resulting in almost 2% SFC penalty for NOx parity with
respect to bowl. However, in this case, the NOx/Soot characteristics of all 4 bowls are
about the same. It should again be noted that all bowls were tested with the same nozzle
and that further improvements may be recognized if the nozzles were optimized
individually for each bowl. However, these results suggest that the Mexican hat shape
with the higher compression ratio results in the best overall emissions and SFC
performance.
-40
-20
0
20
40
60
80
100
-4 -3 -2 -1 0 1 2 3
SFC Change [%]
NOx Change [%]
Bowl A
Bowl B
Bowl C
Bowl D
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
-40
-20
0
20
40
60
80
100
-80 -60 -40 -20 0 20 40 60
Soot Change [%]
NOx Change [%]
Bowl A
Bowl B
Bowl C
Bowl D
Figure 10: Performance data for a notch 4 injection timing swing with 1800bar rail pressure, notch 4
representative boost, and 25% EGR.
Summary
The work described in this section illustrates the impact of different hardware on engine
performance for locomotive applications. It was demonstrated that miller cycle can
reduce NOx at constant injection timing. This NOx reduction can be exploited either as a
direct emissions reduction strategy or as an enabler for injection timing advance for
improved fuel economy.
A high-pressure common rail system was shown to provide significant reductions in
particulate matter with modest fuel economy penalties for an EGR-equipped engine. The
prototype fuel system also enables multiple injections and it was shown that multiple
injections can further reduce the particulate with little or no penalty in NOx and fuel
consumption. Similar agile fuel injection systems will likely become a key tool for
meeting future particulate emission regulations.
Finally, engine performance was compared for 4 different piston crown geometries. It
was found that the simple Mexican hat design resulted in the best overall emissions and
fuel consumption. It was also found that the double-rim design resulted in worse engine
performance, however, it was noted that performance may be improved by matching the
injector nozzle to the crown.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Task 3
Subtask 3a: PM formation and characteristics Summary
The following is a summary of the key observations obtained under this task. A more
detailed description of the experiments that were performed is provided as an Appendix,
which includes the doctoral dissertation of Hee Je Seong, who performed much of the
work under this task.
Note that related to this task, three theses were completed in whole or in part with support
from this project:
Prabhakar, Bhaskar, “Effect of Common Rail Pressure on the Relationship Between
BSFC And BSPM at NOx Parity,” MS Thesis, Mechanical Engineering, Penn State
University, 2009.
Yehliu, Kuen, “Impacts of Fuel Formulation and Engine Operating Parameters on the
Nanostructure and Reactivity of Diesel Soot,” PhD Thesis, Energy & Mineral
Engineering, Penn State University, 2010. (three years of funding came from NSF Grant
#CTS-0553339).
Seong, Hee Je, “Impact of Oxygen Enrichment on Soot Properties and Soot Oxidative
Reactivity,” PhD Thesis, Energy and Geo-Environmental Engineering, Penn State
University, 2010.
Results
Fall 2007
The initial experiments performed with the SCE engine considered soot samples from
several operating conditions. Both oxidative reactivity and soot nanostructure were
analyzed for soot samples from the SCE and from the Cummins test engine at GE-GRC
for comparison. Figure 1 shows the variation in oxidative reactivity for the soot samples,
wherein the soot samples from the SCE and Cummins test engine are seen to be much
reactive than the light duty engine soot produced at PSU. All the soot samples from
different engines at GE fuel are very reactive and the SCE 20% EGR soot is more
reactive than SCE 30% EGR soot This raised questions about compatibility of the test
conditions, and experiments were begun at Penn State at higher intake oxygen
concentration to simulate the supercharged operation of the SCE.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0
10
20
30
40
50
60
70
80
90
100
0 10 20 30 40
We
igh
t lo
ss (
%)
Elapsed time (min)
DDC2.5L_1800rpm
Cummins_1050rpm
Cummins_1750rpm
SCE_20% EGR
SCE_30% EGR
Figure 1. Comparison of oxidative reactivity of soot samples from the SCE, the Cummins
test engine and the PSU 2.5L turbodiesel engine operating on a test fuel at GE GRC.
Thermophoretic samples were obtained from the SCE to compare the nanostructure of the
soot samples from 20% and 20% EGR conditions. Figure 2 shows HRTEM micrographs
comparison the nanostructure of the soots. Initial soot nanostructure is similar to that of
samples acquired from of DDC 2.5L turbodiesel engine at Penn State. Lamella length
(grapheme layers) in the 20% EGR soot appears longer than that in 30% EGR soot.
Raman spectrometry analyses of these soots show that the 30% EGR soot has greater
disorder, consistent with the HRTEM images: ID/IG(20%)=0.977, ID/IG(30%)=1.170.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
(a) (b)
Figure 2. HRTEM images of SCE soot samples, 1050 rpm (a) 20% EGR soot and (b)
30% EGR.
Thus, these initial measurements of some of the characteristics of the SCE soot provided
a motivation for more extensive examination of the soots from the SCE and to better
understand the impacts of having higher levels of O2 in the cylinder on soot
characteristics.
August 2009
In these experiments, the SCE was operated over a range of conditions to provide data on
the range of PM morphologies emitted by the SCE and the impact of varying engine
operating conditions. Soot samples were collected from the GE SCE in 2009 to provide
further characterization of locomotive engine soot. As shown in Table 1, EGR rate,
injection timing and rail pressure were varied at the same engine speed and engine torque
to generate these soot samples.
Table 1. SCE Engine conditions under which diesel particulates were collected in 2009
1
post injection was applied
The analytical tools used in this study are the same as those used for characterization of
soot samples from the PSU 2.5L engine. Measurements of soot oxidative reactivity were
carried out in a thermogravimetric analyzer at 500oC, and x-ray photoelectron
spectroscopy (XPS) was used to get compositional information of soot. Figure 3 shows
that the SCE soot reactivity varies in the order of 20%, 0%, 25.7%, 24.8% and 10.5%
EGR. For the 0% EGR soot and the 10% EGR soot from the same injection timing and
rail pressure, the former is shown to be significantly more reactive than the latter with
increasing EGR rate. This trend is also observed for the 20% EGR soot and the 25.7%
EGR soot from the same injection timing and rail pressure. Although it is difficult to
evaluate the effect of injection timing and rail pressure on soot oxidative reactivity at
different EGR ratio, it appears that soot from the advanced injection timing with higher
rail pressure is more reactive than from the retarded injection timing with lower rail
pressure in this study.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 3 TGA results at 500
oC for soot samples from GE SCE
Also, the 25.7% EGR soot is shown to be more reactive than the 24.8% EGR soot.
Although it is hard to determine the effect of 0.9% EGR difference, it seems that soot
from the post injection is less reactive. In order to better understand the TGA result,
surface oxygen content and other impurities of soot were investigated using XPS as
shown in Table 2. XPS result indicates that surface oxygen content increases with
increasing EGR ratio, and small amounts of Si are observed for the 0% EGR soot and
20% EGR soot. Consequently, the reason the 0% EGR soot and the 20% EGR soot being
more reactive than the other samples seems to be related to the catalytic effect by Si.
Although Si is the only inorganic component observed in these analyses, there is a
possibility that other inorganic components are also present in these soot samples because
XPS can detect elements down to only 15 nm depth in a material. The surface oxygen
content is also shown to be an important factor influencing soot oxidative reactivity when
no Si is present. Although XPS provides a general indication of factors affecting the
oxidative behaviors of different soot samples, further study is ongoing to get a better
understanding about the effect of soot crystalline structure on soot oxidative reactivity.
Table 2 Elemental analysis of soot samples from GE SCE using XPS
Sample Atomic concentration (%)
O Si
0% EGR soot
10.5% EGR soot
20.0% EGR soot
25.7% EGR soot
24.8% EGR soot
5.65
6.75
8.85
14.44
15.46
0.41
0
0.44
0
0
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
As indicated in a previous quarterly report, the elemental analysis by XPS showed that
soot samples from 0 and 20% EGR ratios contains Si as well as C and O in them, which
explains why they are more reactive in their soot oxidative reactivities than soot samples
from 10.5, 25.7 and 24.8% EGR ratios, where there are no metallic species present.
Although there might be a significant catalytic effect on these samples obtained from the
SCE by Si and other metals which may not be observed by XPS, it is also important to
investigate the effect of carbon crystalline structure on soot oxidative reactivity. Raman
spectroscopy and X-ray diffraction (XRD) have been popular instruments to examine this
property for various carbonaceous materials. In many studies, crystallite size represented
by crystallite height (Lc) and crystallite width (La) via XRD increases with increasing
degree in the crystalline order. In the case of Raman spectroscopy, many parameters from
first-order Raman spectrum have been investigated to study degree in the crystalline
order. From our extensive investigation, we found that this first-order Raman spectrum is
differently curve-fitted by different research groups and there has been no comparison
made for different curve-fitting methods. To better understand the relationship between
soot crystalline structure and soot oxidative reactivity, we compared many different
curve-fitting methods in order to find the best method to identify a good correlation.
Many carbonaceous materials show two characteristic peaks appearing at ~1360 cm-1
(D
peak) and ~1590 cm-1
(G peak) for first-order Raman spectra. The G peak is a stretching
mode at sp2 sites.
1 The D peak has been proven that it is from the existence of edge sites
and the relative position of the laser spot with respect to the edge.2 Some carbonaceous
materials like polycrystalline graphite show only sharp D and G peaks,3 but many
disordered and amorphous carbons also indicate additional peaks appearing at ~1180
(D4), ~1500 (D3) and ~1620 cm-1
(D2), which are related to sp3 or impurities,
3-5
amorphous carbon6 and disordered carbon,
3,7 respectively.
For this study, four different soot samples and a carbon black sample, which don’t
contain any metallic species, were used in this study in order to exclude their catalytic
effect. One diffusion flame soot (diffusion soot) was obtained from a laminar diffusion
burner with heptane fuel. DDC 30 and DDC 75 soots were collected at 30% and 75%
loads from the engine at Penn State, respectively. SCE soot was sampled from SCE at a
notch-8 condition with 10.5% EGR ratio. The carbon black investigated in this study is
obtained from Alfa Aesar. Among many curve-fitting methods, three, four and five
curve-fitting methods were employed for first-order Raman spectra, where 2 lorentzian
(L) (D1:1360cm-1
and G:1590cm-1
) and 1 gaussian (G) (D3:1500cm-1
), 3L (D1, D3 and
G), 3L (D1, D4:1180cm-1
and G) and 1G (D3), 4G (D1, D3, D4 and G), 4L (D1,
D2:1620cm-1
, D4 and G) and 1G (D3), and 5L (D1, D2, D3, D4 and G) were fitted as in
Figure 4.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
1.0
0.8
0.6
0.4
0.2
0.0
Normalized intensity
200018001600140012001000
Raman shift (cm-1)
original spectrum
D1 band (L)
D3 band (G)
G band (L)
(a)1.0
0.8
0.6
0.4
0.2
0.0
200018001600140012001000
D1 band (L)
D3 band (L)
G band (L)
(b)
1.0
0.8
0.6
0.4
0.2
0.0
200018001600140012001000
D4 band (L)
D1 band (L)
G band (L)
D3 band (G)
(c)1.0
0.8
0.6
0.4
0.2
0.0
200018001600140012001000
D4 band (L)
D1 band (L)
G band (L)
D3 band (L)
(d)
1.0
0.8
0.6
0.4
0.2
0.0
200018001600140012001000
D4 band (L)
D1 band (L)
G band (L)
D3 band (G)
D2 band (L)
(e)1.0
0.8
0.6
0.4
0.2
0.0
200018001600140012001000
D4 band (L)
D1 band (L)
G band (L)
D3 band (L)
D2 band (L)
(f)
Figure 4 Curve-fitted shape of SCE soot : (a) 2L (lorentzian) and 1G (gaussian) (2L1G),
(b) 3L, (c) 3L1G, (d) 4L, (e) 4L1G, (f) 5L
The oxidative trends of the 5 samples were compared at 500,550 and 600 oC. Diffusion
flame soot is the most reactive among the samples, and carbon black is the least reactive.
The time to be completely oxidized for SCE soot and DDC 30 soot is almost the same,
but DDC 30 soot is shown to exhibit a greater reactive rate. The oxidative trend in this
study is well represented by the time that the soot is half oxidized as indicated by t50% in
Table 3. The bigger 1/t50% is, the more reactive the soot becomes. Since the difference is
not significant at 600 oC, 1/t50% at 550
oC was introduced in this study as a parameter
representing the soot oxidative rate.
Table 3 Time to reach 50% oxidation at different temperatures
Operating
temperature
(oC)
1/t50% ( /min )
Diffusion
flame soot SCE soot
DDC 30
soot
DDC 75
soot
Carbon
black
500
550
600
650
7.31e-3
3.72e-2
1.02e-1
-
5.11e-3
2.11e-2
6.61e-2
-
5.94e-3
2.30e-2
7.11e-2
-
4.49e-3
1.92e-2
5.94e-2
-
01
1.93e-3
8.10e-3
2.80e-2
1: 1/∞ because there was no reaction at this temperature
Our results show that D1 full width at half maximum (D1 FWHM) reflects a good
oxidative trend for the 4 and 5 curve-fitting methods, and ID1/IG shows an excellent trend
for the 4 curve-fitting method. Accordingly, 3L1G and 4L fittings from the four curve-
fitting method seem to provide good Raman parameters in this study. Although D1
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
FWHM for the five curve-fitting methods is a good parameter, the same good trend can
be obtained from that for the four curve-fitting methods. Since the trends in both
intensity and area of D2 band from 3L1G fitting are also shown to be consistent with that
in the reactivity, 3L1G is found to be the best fitting among the examined fitting
methods. However, it is difficult to conclude that all the factors like: the portion of
amorphous carbon which is related to D2 band, the density of edge sites and the
distribution of crystallite sizes (which are represented by ID1/IG or D1/G and D1 FWHM,
respectively,) should be on the same order of effectiveness for determining soot oxidative
reactivity as we observed for D1/G, ID1/IG, D1 FWHM, and intensity and area in D2 band
from 3L1G fitting (Figure 5). In spite of this difficulty in selecting between the different
methods of interpreting Raman parameters, we can conclude that the relation between
soot oxidative reactivity and crystalline structure is interpreted more reliably and
consistently when all these parameters are analyzed. In this comparison, 3L1G fitting
provides a reasonable explanation about the effect of crystalline structure on soot
oxidative reactivity. Soot oxidative reactivity is closely related to the abundance of edge
sites and amorphous carbon. Correspondingly, more reactive soot shows a wider
distribution of crystallite sizes with an increase in the disorder.
1.6
1.4
1.2
1.0
0.8
D1/G
40x10-3302010
1/t50% ( /min )
(a)
Diffusion soot SCE soot DDC 30 soot DDC 75 soot Carbon black
4.0
3.5
3.0
2.5
2.0
1.5
1.0
I D1/IG
40x10-3302010
1/t50% ( /min )
(b)
Diffusion soot SCE soot DDC 30 soot DDC 75 soot Carbon black
200
160
120
80
D1 FWHM (cm-1)
40x10-3302010
1/t50% ( /min )
(c)
Diffusion soot SCE soot DDC 30 soot DDC 75 soot Carbon black
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 5. Comparison of Raman parameters from 3L1G fitting:
(a) height ratio of D1 to G, (b) area ratio of D1 to G, (c) D1 FWHM
During the 2009 particle sampling effort with the SCE, particle were also acquired via
thermophoretic sampling for transmissions electron microscopy. Figure 6 shows low
resolution images of particulate morphology, with two images from the 20% EGR case.
There are no clear trends in particulate morphology. This is not unexpected give that the
scope of the engine setting changes was fairly modest. Speed and load were fixed, while
EGR level and injection pressure varied.
(a)
(b)
(c)
(d)
Figure 6. TEM micrographs of diesel soot from the SCE at conditions as listed in
Table 1. (a) 0% EGR, (b) 10.5% EGR, (c) 20% EGR – image #1, and (d)
20% EGR – image #2.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
While there is no significant visible variation in morphology, and Figures 6c and 6d show
that there can be substantial variation in particle morphology at the same engine
operation condition, we have previously observed substantial variations in the oxidative
behavior of diesel soot and the mechanisms of oxidation when comparing 20% EGR and
0% EGR soots.1 Thus, it may be worthwhile to compare SCE or locomotive engine soots
from a broader range of operating conditions, such as from all 8 notch settings. From the
2009 SCE sampling, few high resolution TEM (HRTEM) images were produced. Figure
7 shows some of these images, from 0% and 10.5% EGR settings. Figure 7a shows signs
of long range order and the class shell-core nanostructure of mature diesel soot. Figure
7b lacks the fine resolution to draw any definitive comparisons with regard to
nanostructural characteristics, however, a qualitative (speculative) analysis of this image
shows a less ordered nanostructure than the 0% EGR case in Figure 7a. When
considering the differences in oxidative reactivity shown in Figure 3, it would be of great
interest to compare the nanostructures of the “as received” soots from 0% and 20% EGR,
since these showed the widest difference in reactivity. Also, it would be valuable to track
the changes in soot nanostructure at different extents of oxidation.
(a)
(b)
Figure 6. HRTEM micrographs of diesel soot from the SCE at conditions as listed in
Table 1. (a) 0% EGR, and (b) 10.5% EGR.
Conclusions
• Significant differences were observed in the oxidative reactivity for soots sampled
from the SCE at different test conditions. This significant variation in reactivity
warrants further study to assess what aspects of the soot structure or surface
chemistry are responsible for these variations in reactivity.
1 Al-Qurashi, K. and A.L. Boehman. Impact of Exhaust Gas Recirculation (EGR) on the Oxidative
Reactivity of Diesel Engine Soot. Combustion and Flame, 155, 675-695 (2008).
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
• Preliminary nanostructural analyses suggest differences in the degree of order in
the soot nanostructure is playing a role in variation in reactivity, but this needs
further measurements to confirm.
• There remain questions over whether oxidation behavior of the soot samples is
influenced by inorganic species present on the soot surface. Reactivity appears to
correlate with Si content for some of the soot samples. Again, this aspect of these
measurements warrants further study.
References
1. Ferrari. A. C.; Robertson, J. Interpretation of raman spectra of disordered and
amorphous carbon. Phys. Rev. B 2000, 61, 14095–14107
2. Casiraghi, C.; Hartschuh, A.; Qian, H.; Piscanec, S.; Georgi, C.; Fasoli, A.;
Novoselov, K. S.; Basko, D. M.; Ferrari, A. C. Raman spectroscopy of graphene
edges. Nano Letters 2009, 9, 1433–1441
3. Cuesta, A.; Dhamelincourt, P.; Laureyns, J.; Martínez-alonso, A. Tascón, J. M. D.
Raman microprobe studies on carbon materials. Carbon 1994, 32, 1523–1532
4. Sadezky, A.; Muckenhuber, H.; Grothe, H.; Niessner, R.; Pöschl, U. Raman
microspectroscopy of soot and related carbonaceous materials: spectral analysis
and structural information. Carbon 2005, 43, 1731–1742
5. Schwan, J.; Ulrich, S.: Batori, V.; Ehrhardt, H.; Silva, S. R. P. Raman
spectroscopy on amorphous carbon films, J. Appl. Phys. 1996, 80, 440–447
6. Nemanich, R. J.; Glass, J. T.; Lucovsky, G.; Shroder, R. E. Raman scattering
characterization of carbon bonding in diamond and diamondlike thin films. J.
Vac. Sci. Tech. A 1988, 1783–1787
7. Gruber, T.; Zerda, T. W.; Gerspacher, M. Raman studies of heat-treated carbon
blacks. Carbon 1994, 32, 1377–1382
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Subtask 3b: Examine EGR cooler fouling process and mitigation strategies
Summary
To meet Tier 4 emissions requirements for locomotive engines, use of exhaust gas
recirculation may be necessary
Experimental Design
This task involves understanding the mechanisms of EGR cooler fouling, focusing first
on the design of an experimental facility for studying the deposit formation process.
To perform the investigation of diesel EGR cooler fouling, surrogate heat exchanger
tubes have been designed which can be easily removed from the assembly and replaced
depending on the type of experiment. The tubes are made of 316L stainless steel and are
¼’ in diameter and a total of 6 tubes are inserted into a shell and tube type heat
exchanger. A 3-d model of the entire setup is completed. Components have to be
purchased and the setup has to be completed.
Figure 7. Overview of EGR cooling setup with closed loop cooling system
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
a)
b) c)
Figure 8. Initial Design of EGR Cooler Test Rig
a: Arrangement of tubes within the shell in isometric view.
b: A detailed view of tubes inside the shell in a wire-frame view.
c: Solid view of the shell and tube heat exchanger.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 9. Final design drawings of flanges for EGR cooler experiment
(a)
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
(b)
Figure 10. Final design drawings of the EGR Cooler, (a)View of EGR cooler without
shell and manifold and, (b) View of cooler with shell and manifold.
Once the EGR cooler design was finalized, components were ordered and given to the
machine shop for machining the model EGR cooler with surrogate tubes. A few final
modifications were made to the design during construction. The machined heat
exchanger with the components unassembled (Figure 11) and assembled (Figure 12) are
shown below.
Figure 11. Model EGR cooler: 2 flanges (with weld fittings and removable Swagelok
fittings), 2 headers, and 1 shell with 2 NPT fittings for coolant inlet and outlet. Tubes are
not shown.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 12. Assembled view of EGR cooler; O-rings (4 in number) create the seal between
the coolant and the exhaust gas on either side
After the construction phase was completed, baseline testing was conducted on the
existing EGR coolers (2 in number) on the Ford 6.4 L engine to get information on
typical temperatures (coolant in, coolant out, exhaust gas in, exhaust gas out from cooler
1, exhaust gas out from cooler 2) and EGR ratios at various engine speeds and loads.
Results from these tests will helped to identify a few standard operating conditions for the
model EGR cooler for fouling studies.
Then the model EGR cooler was installed along with the differential pressure gauge and
thermocouples. To complete the installation of the EGR cooler on the test engine a
closed-loop coolant circulator and a wedge-flow meter (capable of operating at high
temperatures) to measure the flow rate of exhaust gas through the EGR cooler were
installed on the test engine.
A baseline test was performed on the 6.4L Ford Engine to map out exhaust temperatures
upstream and downstream of the stock, twin-EGR coolers. Additionally, fuel
consumption and EGR % at the particular conditions was calculated. Results from these
tests can be seen in Table 1.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Table 4. Effect of engine operating conditions on exhaust temperature, cooler-out
temperatures, fuel consumption, and EGR percentage
Speed Load Power Fuel Cooler 1 Cooler 2 Coolant CO2 EGR %
Cons Inlet T Outlet T Outlet T Temp in out
rpm ft-lb kW g/min deg C deg C deg C deg C % % %
The tests below are performed at varying speeds and loads
750 32 3.40 NA 133.6 91.8 38.6 88.6 1.15 3.89 29.56
1000 23.5 3.33 36 144.7 94 48.5 89.4 1.07 3.23 33.13
1300 30 5.53 48 160.2 98.2 50.4 90.5 1.07 3.4 31.47
1600 46.2 10.48 83 196.5 110.2 51.6 91 1.4 4.52 30.97
1900 65.1 17.54 116 232.1 121.8 51.8 91.6 1.42 4.9 28.98
2300 85 27.73 191.1 294.2 148.5 46.7 93.5 1.45 5.01 28.94
2600 100.3 36.98 266.2 328.9 166.3 48.5 95 1.5 5.29 28.36
The tests below are performed at constant speed = 1500 rpm
1500 92.2 19.61 102.3 252.8 108.4 37.3 90.8 1.43 5.1 28.04
1500 150.2 31.95 137.7 261.2 99.8 38.2 91.2 0.96 5.42 17.71
1500 200 42.55 172.2 281.3 96 36.8 91.4 0.8 5.83 13.72
1500 250 53.18 201.1 312.3 98.5 33.2 92 0.85 6.53 13.02
1500 300 63.82 238.8 340.1 100.4 31.2 92.7 0.95 7.13 13.32
1500 350 74.46 272.8 360.2 105.5 27.6 93.4 0.87 7.39 11.77
The tests were conducted in 2 phases. The first phase varied both speed and load, as
represented by the pink color in the table. In the second phase, the engine was operated at
medium speed (1500 rpm) while the load was increased in steps of 50 lb-ft – denoted in
light green. From both the tests, it was observed that the gas outlet temperature from the
2nd
EGR cooler was lower than the coolant temperature. This result needs to be
reinvestigated. Corrections, if any, will be provided in the upcoming reports. These
results are helpful to select operating point(s) to perform EGR cooler experiments. EGR
percentage was calculated as below.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0
50
100
150
200
250
300
28
29
30
31
32
33
34
0 5 10 15 20 25 30 35 40
Fuel Consumption, g/minEGR Ratio
Fuel Consumption, g/min
EGR, %
Power, kW
Figure 13: Variation of EGR ratio and fuel consumption with power at varying speeds
and loads
From Figure 13, it is apparent that EGR percentage reduces with an increase in engine
power output. However, higher power also means greater fuel consumption. For extended
EGR cooler runs, an optimum value has to be selected so that fuel consumption is not
excessive.
We need to pick an
operating condition in
this regime. Points here
represent medium EGR
and moderate fuel
consumption
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0
5
10
15
20
25
30
100
150
200
250
300
50 100 150 200 250 300 350 400
CO2, intake, %
CO2, exhaust, %
EGR, %
Fuel Consumption, g/min
Various %
Fuel Consumption, g/min
Load, ft-lb
Speed = 1500 rpm
Figure 14. Variation of fuel consumption and EGR under conditions of fixed speed and
varying load
It can be observed from Figure 14 that when the speed was held constant, an increase in
load increased the CO2 content at the exhaust while the intake CO2 levels were reduced.
This indicates a decrease of EGR with load. These results have been obtained at the
baseline conditions – no modifications (such as rail pressure, injection timing, etc.) were
performed on the engine ECU.
Initial characterization of EGR cooler deposits
Soot deposits were collected from the EGR coolers of 2 engines - a 2.5L DDC VM
Motori engine and the 6.4L Ford power-stroke engine. These samples were subjected to a
non-isothermal test in TGA. The test involves pre-treating the soot sample under nitrogen
gas to drive away the volatiles and then subjecting it to oxidation in air, as the
temperature is ramped up to 800 °C. Results from these tests are shown in Figures 15 and
16.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0
20
40
60
80
100
0
200
400
600
800
1000
0 50 100 150 200 250
Weight, %
Temperature, deg C
Time, min
2.5L DDC Engine
Figure 15: Non-isothermal TGA analysis of EGR cooler deposit from the 2.5 L DDC-VM
Motori engine
0
20
40
60
80
100
0
200
400
600
800
1000
0 50 100 150 200 250
Weight, %
Temperature, deg C
Time, min
Figure 16: Non-isothermal TGA analysis of EGR cooler deposit from the 6.4L Ford
power-stroke engine
It can be observed that the EGR cooler soots contained significant amount of volatile
organic fraction (VOF). Typically, diesel engine exhaust soots have VOF in the range of
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
10-15%. However, EGR cooler soot deposits appeared to have VOF in the range of 35-
40% indicating a significant amount of condensed hydrocarbons. More investigation is
necessary to be confirm these initial results.
Preliminary investigation of the microstructure
EGR cooler soot deposits were investigated under a scanning electron microscope to
study the microstructure. Images from both the engines are shown in Figures 17 and 18.
Figure 17. Microstructure of carbon deposit from 2.5L engine EGR cooler
Figure 18. Microstructure of carbon deposit from 6.4L Ford engine EGR cooler
It can be inferred that the EGR cooler deposits from different engines have different
appearances, which could be either due to the conditions under which the engines were
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
operated, the time-temperature history of the EGR cooler temperature and the fuel used.
No direct conclusions can be drawn yet. Once we generate our own EGR cooler soot
samples under controlled and known conditions, analyses of the mechanism of EGR
cooler deposits will be possible.
Following the completion of the rig, several 5-6 hour tests were performed to check for
gas and coolant leaks - especially with the use of graphitic ferrules for gas-side sealing,
performance of the flow-meter and coolant circulator (coolant at 85°C), and the
sensitivity of the valve for flow adjustments, while the thermal effectiveness of the EGR
cooler was monitored.
Figure 19. EGR cooler test rig showing 1) EGR Cooler 2) High and low side pressure
taps 3) Coolant inlet and outlet
1
2
2
3
3
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 20. Test rig instrumented with 1) High temperature wedge-flow-meter with
pressure and temperature taps for corrections in gas density 2) Cooler downstream high
temperature valve.
Actual pressure of the exhaust gas entering the EGR cooler was monitored and was
observed to be in a range of 16-28 psia (ECU controlled), depending upon the engine
load. No data collection has been made so far, as the testing outline is still being
formulated. Additionally, the Ford 6.4L engine is currently being run on B40 biodiesel.
Experiments with ultra-low sulfur diesel (ULSD) will be performed once the current tests
conclude.
Current status research on EGR cooler fouling
Initial experiments were performed to monitor cooler effectiveness and pressure change
at two conditions of engine load, viz. 50 lb-ft and 100 lb-ft, while running the engine for
a total of 10 hours at 1500 rpm. The coolant temperature was maintained steady at 85° C
and the exhaust gas flow rate through the EGR cooler was held constant at 180 slpm. The
coolant flow rate was maintained sufficiently high to minimize coolant side temperature
gain.
After the completion of the initial tests, the tubes were removed from the EGR cooler and
evaluated for any deposits adhering to the inner surface. From a visual inspection, it
appeared as if the tubes were clean, but there was a significant amount of deposits glued
to the tube’s inner surface which appeared as a fine and undistinguishable layer. The
1
2
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
deposit layer was not affected by shaking the tube vigorously, which implied that they
were held by strong contact forces. A thin and long stainless steel tube was used to
remove the deposits by scraping them, ensuring that the underlying metal was not
scratched. Sufficient mass of sample (order of grams) was generated for particle
characterization purposes in just less than 10 hours of engine operation. Any remaining
particles were cleaned by running DCM through the tubes and thoroughly cleaning them
for the next experiment.
Condition 1: 1500 rpm, 50 lb-ft
0.45
0.5
0.55
0.6
0.65
0.7
0 100 200 300 400 500 600 700
Effectiveness
Effectiveness
Time, min
Stop of Run#1
Stop of Run#2
Stop of Run#3
Stop of Run#4
Figure 21. Change in EGR cooler effectiveness with time at 1500 rpm, 50 lb-ft and
180lpm flow through the EGR cooler
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
100
150
200
250
100
150
200
250
0 100 200 300 400 500 600 700
EGR inlet temp, deg C EGR outlet temp, deg C
EGR inlet temperature, deg C
EGR outlet te
mperature, deg C
Time, min
Steady EGR inlet temperature
Increasing EGR outlet temperature
Figure 22. EGR Inlet and outlet temperature as a function of time
From Figure 21, it can be observed that EGR effectiveness dropped from about 67%
when clean to about 46% in about 10-11 hours of operation. This is a significant loss
considering the model EGR cooler contains just 6 tubes to cool the exhaust gas. The
exhaust gas temperature at the inlet of the cooler remained a constant (~235°C), while the
gas temperature at the outlet increased from 130°C to 159°C, as observed in Figure 22.
Additionally, the pressure drop across the cooler increased as well as seen in Figure 4.
Interesting to note was that there was a slight improvement in the effectiveness after each
engine shutdown, which is termed as cooler recovery in the literature. Exact reasons for
this behavior are not understood yet. Researchers suspect that some condensation of
water during engine shutdown can have loosened the deposits, leading a blow-off of the
deposit layer during start-up.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
7.2
7.4
7.6
7.8
8
8.2
8.4
8.6
8.8
0 100 200 300 400 500 600 700
EGR del P, kPa
EGR del P, kPa
Time, min
Figure 23. EGR cooler delta P as a function of time.
Run 2: 1500 rpm, 100 lb-ft
In the second test, the engine load was increased to 100 lb-ft, while holding all other
conditions the same. The engine ECU commands a lower EGR% at higher loads, but the
reduction in flow rate through the EGR cooler was compensated by opening the valve to
allow a higher flow through the model cooler. A significant difference between the first
and the second test was that the effectiveness of the cooler when clean (start of the test)
was only 53% as against 67% in the first case. This is explainable in terms of higher gas
temperature at cooler inlet and a lower capacity of the cooler to cool the exhaust gas
down with just 6 tubes. The effectiveness at the end of the test dropped to as low as 39%.
The exhaust gas outlet temperature increased from 163°C to 189°C. Similar to the first
test, improvements in the effectiveness (cooler recovery) was seen during engine shut
down and start up conditions. All other trends were similar to condition 1.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0.38
0.4
0.42
0.44
0.46
0.48
0.5
0.52
0.54
0 100 200 300 400 500 600 700
Effectiveness
Effectiveness
Time, min
End of run 1
End of run 2
End of run 3
Figure 24. Change in EGR cooler effectiveness with time at 1500 rpm, 100 lb-ft and
180lpm flow through the EGR cooler
200
210
220
230
240
250
260
140
150
160
170
180
190
200
0 100 200 300 400 500 600 700
EGR Inlet Temp, deg C EGR Outlet Temp, deg C
EGR Inlet Temp, deg C
EGR Outlet Temp, deg C
Time, min
Increasing EGR outlet temp
Steady EGR Inlet temperature
Figure 25. EGR Inlet and outlet temperature as a function of time
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
5.8
6
6.2
6.4
6.6
6.8
7
0 100 200 300 400 500 600 700
EGR del P, kPa
EGR del P, kPA
Time, min
Figure 26. EGR cooler delta P as a function of time.
Pyrolysis GC-MS analysis of samples
The chemical signature of the samples collected from the EGR cooler was analyzed using
a pyrolysis GC coupled to a mass spectrometer. Conventional GC cannot be used until
the samples are extracted using DCM, because of the presence of high molecular weight
compounds in diesel engine soot. Pyrolysis GC has proven to be a useful technique to
provide unique fingerprinting of soot produced from diesel engines. Figures 27 and 28
show the chromatographs of the samples collected after 10-11 hours from the two engine
conditions. As it can be seen, the two different engine conditions produced different soots
with different chemical signature. An attempt was made to identify some of the major
peaks from the chromatographs and the details can be seen in Table 5. The relative
proportions (area ratios) are not calculated yet, and needs more understanding.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
0
500000
1000000
10 20 30 40 50 60 70
Arbitrary / Minutes Paged Z-Zoom CURSOR
File # 1 = 1500-50B 3/2/2011 2:18 PM Res=None
py:5/600/10 oven:40/1/4/300/10
Figure 27. Chromatograph of the sample from 1500 rpm, 50 lb-ft engine condition
0
50000
100000
150000
200000
250000
10 20 30 40 50 60 70
Arbitrary / Minutes Paged Z-Zoom CURSOR
File # 1 = 1500-100 3/2/2011 4:09 PM Res=None
py:5/600/10 oven:40/1/4/300/10
Figure 28. Chromatograph of the sample from 1500 rpm, 100 lb-ft engine condition
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Table 5. Probable compounds from Py-GC of the two EGR cooler samples
1500 rpm, 50 lb-ft 1500 rpm, 100 lb-ft
benzene benzene
methyl-benzene methyl-benzene
Ethyl-benzene styrene
styrene benzaldehyde
1,2 dimethyl benzene napthalene
benzaldehyde 2 methyl napthalene
methyl phenol tetradecane
napthalene 1,3 dimethyl napthalene
1-methyl napthalene heptadecane
1,3 dimethyl napthalene octadecane
heptadecane eicosane
octadecane
nonadecane
eicosane
Scanning electron microscopy
SEM technique was utilized to determine the microstructure of the sample surface, while
the EDS feature on the SEM was used to detect different elements other than hydrogen
on the surface of the sample. Results are available only for the condition at 50 lb-ft load.
Even though the microstructure images are presented in Figures 29 and 30, detailed
investigation is necessary as we believe that scraping the sample out of the EGR cooler
tubes and pressing the sample (to be held firmly on the sample holder for SEM) could
have changed the actual structure of the sample. In order to eliminate this for future
microscopy studies, the tubes need to be cut open carefully and mounted on the sample
holder, making sure the sample has not been disturbed.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 29. SEM image of EGR cooler soot at 1500 rpm, 50 lb-ft
Figure 30. SEM image of EGR cooler soot at 1500 rpm, 50 lb-ft
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Figure 31 shows a spectrum of different peaks from a spot on the sample surface. Some
of the major peaks observable are carbon, nickel, silicon, zinc, sulfur, calcium, and
nickel. The gold peak (Au) is shown due to gold sputtering on the sample to improve the
electrical conductivity. The copper peak is a result of using a copper tape to hold the soot
in place. Sulfur peak is observed even though ultra-low sulfur diesel is used for
experiments. Silicon, zinc, and calcium are typically constituents of a diesel lubricant.
Silicon is used as for foam control, while zinc is used for wear control and oxidation
protection, and calcium is used for protection against rust. Figure 32 shows that sample
also consists of iron, aluminum, and potassium. It is speculated that nickel and aluminum
originated from the engine manifold; however, the origin for potassium is still unclear.
Table 6 shows a distribution of normalized weight percentage of different elements
present in the sample.
Figure 31. Element scan at spot 1 from Figure 10
Figure 32. Elemental scan of the entire sample surface
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Table 6. Weight percentage of different elements from sample 1
Another feature of the SEM was explored, where the elemental distribution was observed
over a given area of the sample, and is shown in Figure 33. This feature is helpful to get
an idea of the relative concentration of a given element in a given region. The denser the
distribution, more dots are observed. For example, diesel soot which is mostly carbon has
the greatest distribution, as seen in Figure 33. Zinc, on the other hand is dense only in a
small region, which is also seen in the SEM image (bottom right corner of Figure 33),
which has a bright spot. Sulfur and silicon are distributed evenly over the entire area, but
are less dense than carbon.
Figure 33. Area scan to determine elemental distribution
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Conclusions
The current setup of the EGR cooler allows us to collect sufficient deposits within a short
period of time. Several characterization techniques have been applied to determine
physical and chemical properties of these deposits. A test matrix will be developed to
determine the changes to the deposit properties over time. Additional techniques will be
used as and when necessary.
This experimental apparatus represents a valuable tool for study the mechanisms of EGR
cooler fouling and can provide insights into mitigating such deposits in locomotive
applications.
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
Phase 2
Task 5 Subtask 5A: Low Particulate Combustion Tests
This task focused on the characterization of the impact of swirl on the formation of
particulate during combustion in large bore diesel engines. The cylinder head was
modified to realize higher levels of swirl than obtains in the current GEVO product. The
following observations were made in the course of these tests:
• For a given manifold air pressure, engine speed and load, a reduction in air-fuel
ratio was observed with the addition of swirl. This is attributed to higher port
losses and overall lower volumetric efficiency.
• Increasing the manifold air pressure increased the air fuel ratio back to baseline
levels. Correspondingly, the engine backpressure was increased to simulate actual
backpressure effects of a turbocharger.
• At notch 4, a small but measurable reduction in particulate matter was observed.
However, there was an adverse impact on BSFC.
• At notch 8, an increase in particulate matter was observed. In this case, there
appeared to be very little impact on BSFC.
Additional details of the results of the tests are available in the Phase 2 second quarter
report.
Subtask 5B :Aggressive Valve Timing Studies.
In this task, the effect of modified valve timing on engine performance was investigated.
Tests were performed at Notches 4 and 6 due to operating pressure limitations. The
following results were obtained:
• BSFC advantage was observed at both notches 4 and 6 at NOx parity.
• Particulate matter was the same for notch 6, but increased approximately 15% for
notch 4.
Additional details of the results of the tests are available in the Phase 2 second quarter
report.
Task 6: Advanced Air Handling. In this task, GT-Power modeling studies were performed to further our understanding of
advanced air-handling architectures. Two studies were performed; the first involved a
parametric analysis of fuel consumption tradeoffs with Miller cycle and cylinder
compression ratio variations. Results of this study showed that the efficiency improved
as the cylinder compression ratio was increased at the expense of increased cylinder
pressure and also delineated the efficiency response with Miller cycle.
The second study involved identifying turbocharger layouts that meet system
requirements over a broad operating range for selected intake valve closure timings. The
analysis entailed running the GT-Power model with turbocharger maps at selected
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
ambient conditions and engine loads. The model was exercised by scaling the
turbocharger maps to meet operational constraints (engine airflow levels and emissions
targets). Final scaling parameters were selected based on combinations that resulted in
minimum fuel consumption. Modeling results with these selected scaling parameters can
now be utilized to identify turbines and compressors to better match the engine
architecture.
Task 6 also included an experimental evaluation of Turbocompound technology. To this
end, a nominal 60 KWe subscale turbocompound system manufactured by Bowman
Power Group, Ltd, UK, was installed in the GRC turbocharger development cell and
evaluated over a range of operating conditions.
Testing was performed at generating speeds of 27,000, 33,000, and 35,000 rpm for inlet
temperatures of 650, 750, and 850F. In general, the Bowman TGS met performance
expectations over the operating ranges evaluated. Overall system efficiency exceeded
80% at design conditions, which is in line with estimates used for the modeling work
reported earlier. Application to the locomotive for power recovery would require
hardening of the components, both mechanical and electrical, to meet the harsh operating
environment found in rail service, as well as integration of the export power with the
locomotive electrical architecture. Cost and packaging are other important factors to be
addressed.
Further details of both the analysis and tests are available in the Phase 2 fourth and fifth
quarter reports.
APPENDIX
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011
IMPACT OF OXYGEN ENRICHMENT ON SOOT PROPERTIES AND SOOT
OXIDATIVE REACTIVITY, Hee Je Seong, PhD Thesis, Energy & Geo-Environmental
Engineering, Penn State University,
2010
Clean and Efficient Diesel Engine: Final Report Report Issue Date: April 2011