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International Journal of Engineering Science Invention
ISSN (Online): 2319 – 6734, ISSN (Print): 2319 – 6726
www.ijesi.org Volume 2 Issue 9ǁ September 2013 ǁ PP.45-53

Experimentation on Exhaust System Using TWC Converter For
Diesel Engine Emissions
D S Jaheer Basha M.Tech1, M A Chakravarthy M.Tech2 ,
1,2,3

N Haranadh M.Tech.3
(Assistant Professor of Mechanical Engineering Department, sri venkateswara college of engineering &
technology (autonomous), chittoor, Andhra Pradesh, India--517127)

ABSTRACT : We prepared a new kind of exhaust after-treatment system having Diesel Particulate Filter,
Three Way Catalytic (TWC) converter (in substitution of SCR & Oxidation catalyst) to determine the scope for
enhancing the efficiency of a Three Way Catalytic (TWC) converter system. Our results show that there is a
~99% reduction in the CO and HC emissions after arranging the retrofit. We also found that on an average
there is a 72% reduction in the NOx.

KEYWORDS : Diesel engine, DPF, Emissions, SCR, TWC.
I.

INTRODUCTION

The introduction of exhaust gas after treatment systems for diesel engines is a measure to fulfill the
legislation requirements [1],[2]. Selective catalytic reduction (SCR) are considered to be promising for this
better performance[3]. Therefore, in Europe, on road demonstrations of the SCR systems are conducted[4].
However, there are problems yet to be solved for practical usage of SCR systems. The first one is the low
activation for NOx reduction under low exhaust gas temperatures and transient conditions encountered in real
operating conditions.The selective catalytic reduction (SCR) process is a well-established concept, but yet
commercially not proved technology for nitrogen oxide [NO x] emission control for automobiles. In particular,
ammonia [NH3]SCR featured by a reductant [NH3] added to the exhaust gas is recognized as a flexible remedy
for mobile diesel NOx emission[5],[6]. One of the major challenges in the automobile application of the NH 3
SCR process is the enhancement of the de-NOx performance at low exhaust gas temperatures below 300ÂșC. One
of the feasible methods to promote de-NOx activity at low temperatures is to lead the reaction to pass through
the fast SCR path.The present investigation concern with experiment on Diesel engine test-rig inorder to
determine the exhaust gas emissions at the end of tail pipe at different loads by arranging the setup proposed.
1.1.Diesel Particulate Filter
The catalyst commonly contains an alumina wash coat supported on a honeycomb shape ceramic brick
as shown in below Fig. 1.[7],[8],[9].

Figure 1: DPF

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Experimentation On Exhaust System Using

1.2. Three Way Catalytic (TWC) Converter
This catalyst takes its name from controlling the three major emissions in an engine that are NO X,
VOCs and carbon monoxide[10]. The catalyst commonly contains an alumina wash coat supported on a
honeycomb shape ceramic brick as shown in Fig. 2. Precious metals are coated onto the alumina[11]. The active
part of the catalyst is further divided into oxidation and the reduction catalyst sites[12].

Figure 2: Automotive Catalytic Converter (TWC)

The platinum/rhodium components act as the active sites to carry out reduction reactions, while
platinum/palladium acts as the active component for oxidation reactions[13],[14].
A: Reduction Catalyst
B: Oxidation Catalyst
C: Honeycomb Ceramic Structure
Reduction of nitrogen oxides to nitrogen and oxygen:
2NOx → xO2 + N2
Oxidation of carbon monoxide to carbon dioxide:
Figure 3: Section of TWC
2CO + O2 → 2CO2
Oxidation of unburnt hydrocarbons (HC) to carbon dioxide and water: CxH2x+2 + [(3x+1)/2]O2 → xCO2 +
(x+1)H2O.

II.

EXPERIMENTAL DETAILS

2.1. Experimental Systems and Description
The experimental set up consists of single cylinder 4-stroke DI Diesel engine with 80mm borediameter, 110mm stroke length, rated speed of 1500rpm, 5 BHP/3.7 KW rated power and water cooled engine.
2.2. Various parts of experimental setup {Refer : Fig.4}
1.
kirloskar engine
2.
alternator/dynamometer
3.
alternative fuel tank
4.
air filter
5.
three-way valve
6.
exhaust pipe

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Experimentation On Exhaust System Using

7.
8.
9.
10
11.
12.
13.

DPF
multigas analyzer
diesel tank
burrette
three way valve
control panel
TWC (SCR+DOC)

13

Figure 4: Line Diagram of Experimental Setup with Test-rig

DPF
TWC

Figure 5:DPF+TWC Converter Experimental Setup with Engine

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Experimentation On Exhaust System Using


Figure 6: Auto Exhaust Multigas Analyzer

Figure 7: DPF and TWC Converters

2.3 Experimental Procedure
As first said, pure diesel is allowed to run the engine for about 30 min, so that it gets warmed up and
steady running conditions are attained. Before starting the engine, the lubricating oil level in the engine is
checked and it is also ensured that all moving and rotating parts are lubricated.The various steps involved in the
setting of the experiments are explained below,

The tests were carried out after installation of the engine testrig with setup

Precautions are taken, before starting the experiment on selected engine.

The engine is started at no load condition.

After that engine is allowed to run at rated speed of 1500rpm atleast 10 minutes for stabilization.

The multigas analyser is prepared to take the required readings of engine emissions.

Then at 0 KW the probe of the multigas analyser is placed at the exhaust tail pipe and readings are
noted.

The above experimental procedure is repeated for different loads from no load to 2 KW load, for the
[1]
[2]
[3]
[4]

same Engine at rated speed of 1500rpm in Two modes as follows:
With-out connecting Diesel Exhaust Aftertreatment system at the end of exhaust tail pipe.
With catalytic converters (DPF + TWC) connected at the end of exhaust tail pipe.
After completion of the test, the load on the engine is completely relieved and then the engine is stopped.

III.

RESULTS AND DISCUSSIONS

Experiments were conducted when the engine was fuelled with pure diesel. The experiment covered a
range of loads. The emission characteristics of the engine were observed in terms of concentration of CO, HC,
O2, NOx and CO2. The results obtained for with DPF+TWC converter +DEF system connected at the end of
exhaust tail pipe were compared with DPF+TWC converter connected at the end of exhaust tail pipe and
without connecting catalytic converter at the end of exhaust tail pipe.

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Experimentation On Exhaust System Using

Table I: Emission test Results for Pure Diesel (Without connecting catalytic converters at the end
of exhaust tail pipe)
Load

Speed

CO

HC

CO2

NOX

O2

kW

rpm

(%)

ppm

(%)

ppm

(%)

1

0

1500

0.074

52

1.1

44

19.08

2

0.5

1500

0.09

56

2.09

173

17.43

3

1.0

1500

0.084

81

3.5

532

15.32

4

1.5

1500

0.102

126

5.1

830

13.15

5

2.0

1500

0.155

239

8.2

942

9.05

S.N0

Table II: Emission test Results for Pure Diesel (With DPF+TWC converter connected at the end of
exhaust tail pipe)
Load

Speed

CO

HC

CO2

NOX

O2

kW

rpm

(%)

ppm

(%)

ppm

(%)

1

0

1500

0

0

0.7

10

19.78

2

0.5

1500

0

0

1.4

60

18.65

3

1.0

1500

0

0

2.2

88

17.54

4

1.5

1500

0

0

2.6

231

16.7

5

2.0

1500

0

0

3.7

69

15.09

S.N0

As per the above results tabulated the following graphs are drawn.

Figure 8:Load against CO

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Experimentation On Exhaust System Using


Figure 9: Load against HC

Figure 10: Load against O2

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Experimentation On Exhaust System Using


Figure 11:Load against NOX

Figure 12: Load against CO2
As per the above results obtained the exhaust after treatment system with DPF+TWC converter is the best
suitable for selected diesel engine to meet the diesel engine emissions legislation.

IV.

CONCLUSIONS

Based on the values obtained for the tests conducted, the following conclusions are made
*

CO emission is zero for DPF+TWC converter system connected at the end of exhaust tail pipe when
compared without connecting catalytic converter at the end of exhaust tail pipe. The CO emission is lower

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Experimentation On Exhaust System Using

when compared to the Bharat stage IV Norms for selected engine at all operated loads with retrofit
arranged.
* HC emission is zero for DPF+TWC converter system connected at the end of exhaust tail pipe when
compared without connecting catalytic converter at the end of exhaust tail pipe. The HC emission is lower
when compared to the Bharat stage IV Norms for selected engine at all operated loads with retrofit
arranged.
* Carbon dioxide emission is less for DPF+TWC converter system connected at the end of exhaust tail pipe
when compared without connecting catalytic converter at the end of exhaust tail pipe.
* Oxygen concentration is more for DPF+TWC converter system when compared to without catalytic
converter system at the end of exhaust tail pipe.
* Nitrogen oxides / dioxides (NOx) emission is less for DPF+TWC converter system when compared without
connecting catalytic converter at the end of exhaust tail pipe. The NOx emission is lower when compared to
the Bharat stage IV Norms for selected engine at all operated loads with retrofit.
*
From the above analysis the main conclusion is DPF+TWC converter system is suitable substitute for
diesel engine exhaust after-treatment setup as this system produces lesser emission than existing at all loads.
Abbreviations
DI
Direct Injection
DOC
Diesel Oxidation Catalyst
DPF
Diesel Particulate Filter
SCR
Selective Catalytic Reduction
TWC Three Way Catalyst

V.

ACKNOWLEDGEMENTS

All praise to Almighty God (Allah) who is the only source of knowledge and without whose mercy
coming this far would only have remained a dream.
Our special thanks to Professor A.RAMESH (I.C.Engines Lab Incharge), IIT-Madras for his kindness
and encouragement through our study period. Worth mentioning is the help, cooperation and encouragement
received from all our friends and co-researchers especially in the Reaction Eng & Catalysis Research group. We
Thank Assistant Professor A. VEERESH BABU, NIT-Warangal for some great and informative conversations
we had over the past few months. We would like to thank Department of Chemical Engineering & Mechanical
Engineering for the opportunity and the necessary facilities to carry out this research. We would like to highlight
our gratitude to Professor V.PANDU RANGADU for his constructive feedback and for the hours he put in
reviewing this work.

REFERENCES
[1]
[2]
[3]
[4]
[5]
[6]
[7]
[8]
[9]
[10]
[11]
[12]
[13]
[14]

“www.bosch-diesel.de” Robert Bosch GmbH 2011.
“www.wikipedia.org” Wikipedia¼- trademark of the Wikimedia Foundation Inc- “Jan-2007”.
“www.epa.gov” U.S Environmental protection agency, website- “Jan-2007”.
“www.ec.gc.ca” The Green LaneTM, Environment Canada's World Wide Web site- “Jan- 2007”.
Heywood, J.B., “Internal Combustion Engine Fundamentals”, McGraw-Hill Book Co., Singapore, 1988.
Diesel Net website “www.dieselnet.com” copy right © 1997 - 2007 Ecopoint Inc “Jan-2007”.
Gallant, T.R. “Experimental Diesel Particulate Filter Capabilities at PNNL.” Diesel Exhaust Emissions Reduction Conference,
Detroit, MI, August 24, 2006.
Blackman PG. Emission Control Options to Achieve Euro IV and Euro V on Heavy Duty Diesel Engines. SAE Journal. 2008;
2008280021.
Saenz, N., H. Dillon, S. Carlson, and G. Maupin. “Advanced Metallographic Techniques Applied to Diesel Particulate Filters.”
Microscopy Today, 2007: 15(5): p. 44.
Abdulhamid et. al, Influence of the type of reducing agent (H2, CO, C3H6 and C3H8) on the reduction of stored NOX in a
Pt/BaO/Al2O3 model catalyst. (2004) Topics Catal. 30/31, p. 161.
Akira Obuchi et. al, Performance of platinum-group metal catalysts for the selective reduction of nitrogen oxides by hydrocarbons.
Applied Catalysis B: Environmental Vol.2, Issue 1, 15 March 1993, Pages 71-80.
Andrea Scotti et. al, Kinetic study of lean NOX storage over the Pt- Ba/ Al2O3 system. Ind. Eng. Chem. Res 2004, 43, 4522-4534.
Burch et. al, A review of the selective reduction of NOX with hydrocarbons under lean-burn conditions with non-zeolitic oxide and
platinum group metal catalysts. Applied Catalysis B: Environmental Volume 39, Issue 4, 20 December 2002, Pages 283-303.
Daniel Chatterjee, Olaf Deutschmann and Jurgen Warnatz(2001), Detailed surface reaction mechanism in a three way catalytic
converter, Interdisciplinary Centre of Scientific Computing (IWR), Heidelberg University, 2001.

www.ijesi.org

52 | Page
Experimentation On Exhaust System Using


D. S. Jaheer Basha M.Tech
Advanced Internal Combustion Engines,
Engines,
P.G., Research Scholar,
Mechanical Engineering Department,
Department,
SVCET, Chittoor,
Andhra Pradesh,
India-517127.

M A Chakravarthy M.Tech
Advanced Internal Combustion Engines,

N Haranadh M.Tech
Advanced Internal Combustion

P.G., Research Scholar,
Mechanical Engineering Department,

P.G., Research Scholar,
Mechanical
Engineering

SVCET, Chittoor,
Andhra Pradesh,
India-517127.

SVCET, Chittoor,
Andhra Pradesh,
India-517127.

www.ijesi.org

53 | Page

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International Journal of Engineering and Science Invention (IJESI)

  • 1. International Journal of Engineering Science Invention ISSN (Online): 2319 – 6734, ISSN (Print): 2319 – 6726 www.ijesi.org Volume 2 Issue 9ǁ September 2013 ǁ PP.45-53 Experimentation on Exhaust System Using TWC Converter For Diesel Engine Emissions D S Jaheer Basha M.Tech1, M A Chakravarthy M.Tech2 , 1,2,3 N Haranadh M.Tech.3 (Assistant Professor of Mechanical Engineering Department, sri venkateswara college of engineering & technology (autonomous), chittoor, Andhra Pradesh, India--517127) ABSTRACT : We prepared a new kind of exhaust after-treatment system having Diesel Particulate Filter, Three Way Catalytic (TWC) converter (in substitution of SCR & Oxidation catalyst) to determine the scope for enhancing the efficiency of a Three Way Catalytic (TWC) converter system. Our results show that there is a ~99% reduction in the CO and HC emissions after arranging the retrofit. We also found that on an average there is a 72% reduction in the NOx. KEYWORDS : Diesel engine, DPF, Emissions, SCR, TWC. I. INTRODUCTION The introduction of exhaust gas after treatment systems for diesel engines is a measure to fulfill the legislation requirements [1],[2]. Selective catalytic reduction (SCR) are considered to be promising for this better performance[3]. Therefore, in Europe, on road demonstrations of the SCR systems are conducted[4]. However, there are problems yet to be solved for practical usage of SCR systems. The first one is the low activation for NOx reduction under low exhaust gas temperatures and transient conditions encountered in real operating conditions.The selective catalytic reduction (SCR) process is a well-established concept, but yet commercially not proved technology for nitrogen oxide [NO x] emission control for automobiles. In particular, ammonia [NH3]SCR featured by a reductant [NH3] added to the exhaust gas is recognized as a flexible remedy for mobile diesel NOx emission[5],[6]. One of the major challenges in the automobile application of the NH 3 SCR process is the enhancement of the de-NOx performance at low exhaust gas temperatures below 300ÂșC. One of the feasible methods to promote de-NOx activity at low temperatures is to lead the reaction to pass through the fast SCR path.The present investigation concern with experiment on Diesel engine test-rig inorder to determine the exhaust gas emissions at the end of tail pipe at different loads by arranging the setup proposed. 1.1.Diesel Particulate Filter The catalyst commonly contains an alumina wash coat supported on a honeycomb shape ceramic brick as shown in below Fig. 1.[7],[8],[9]. Figure 1: DPF www.ijesi.org 45 | Page
  • 2. Experimentation On Exhaust System Using
 1.2. Three Way Catalytic (TWC) Converter This catalyst takes its name from controlling the three major emissions in an engine that are NO X, VOCs and carbon monoxide[10]. The catalyst commonly contains an alumina wash coat supported on a honeycomb shape ceramic brick as shown in Fig. 2. Precious metals are coated onto the alumina[11]. The active part of the catalyst is further divided into oxidation and the reduction catalyst sites[12]. Figure 2: Automotive Catalytic Converter (TWC) The platinum/rhodium components act as the active sites to carry out reduction reactions, while platinum/palladium acts as the active component for oxidation reactions[13],[14]. A: Reduction Catalyst B: Oxidation Catalyst C: Honeycomb Ceramic Structure Reduction of nitrogen oxides to nitrogen and oxygen: 2NOx → xO2 + N2 Oxidation of carbon monoxide to carbon dioxide: Figure 3: Section of TWC 2CO + O2 → 2CO2 Oxidation of unburnt hydrocarbons (HC) to carbon dioxide and water: CxH2x+2 + [(3x+1)/2]O2 → xCO2 + (x+1)H2O. II. EXPERIMENTAL DETAILS 2.1. Experimental Systems and Description The experimental set up consists of single cylinder 4-stroke DI Diesel engine with 80mm borediameter, 110mm stroke length, rated speed of 1500rpm, 5 BHP/3.7 KW rated power and water cooled engine. 2.2. Various parts of experimental setup {Refer : Fig.4} 1. kirloskar engine 2. alternator/dynamometer 3. alternative fuel tank 4. air filter 5. three-way valve 6. exhaust pipe www.ijesi.org 46 | Page
  • 3. Experimentation On Exhaust System Using
 7. 8. 9. 10 11. 12. 13. DPF multigas analyzer diesel tank burrette three way valve control panel TWC (SCR+DOC) 13 Figure 4: Line Diagram of Experimental Setup with Test-rig DPF TWC Figure 5:DPF+TWC Converter Experimental Setup with Engine www.ijesi.org 47 | Page
  • 4. Experimentation On Exhaust System Using
 Figure 6: Auto Exhaust Multigas Analyzer Figure 7: DPF and TWC Converters 2.3 Experimental Procedure As first said, pure diesel is allowed to run the engine for about 30 min, so that it gets warmed up and steady running conditions are attained. Before starting the engine, the lubricating oil level in the engine is checked and it is also ensured that all moving and rotating parts are lubricated.The various steps involved in the setting of the experiments are explained below,  The tests were carried out after installation of the engine testrig with setup  Precautions are taken, before starting the experiment on selected engine.  The engine is started at no load condition.  After that engine is allowed to run at rated speed of 1500rpm atleast 10 minutes for stabilization.  The multigas analyser is prepared to take the required readings of engine emissions.  Then at 0 KW the probe of the multigas analyser is placed at the exhaust tail pipe and readings are noted.  The above experimental procedure is repeated for different loads from no load to 2 KW load, for the [1] [2] [3] [4] same Engine at rated speed of 1500rpm in Two modes as follows: With-out connecting Diesel Exhaust Aftertreatment system at the end of exhaust tail pipe. With catalytic converters (DPF + TWC) connected at the end of exhaust tail pipe. After completion of the test, the load on the engine is completely relieved and then the engine is stopped. III. RESULTS AND DISCUSSIONS Experiments were conducted when the engine was fuelled with pure diesel. The experiment covered a range of loads. The emission characteristics of the engine were observed in terms of concentration of CO, HC, O2, NOx and CO2. The results obtained for with DPF+TWC converter +DEF system connected at the end of exhaust tail pipe were compared with DPF+TWC converter connected at the end of exhaust tail pipe and without connecting catalytic converter at the end of exhaust tail pipe. www.ijesi.org 48 | Page
  • 5. Experimentation On Exhaust System Using
 Table I: Emission test Results for Pure Diesel (Without connecting catalytic converters at the end of exhaust tail pipe) Load Speed CO HC CO2 NOX O2 kW rpm (%) ppm (%) ppm (%) 1 0 1500 0.074 52 1.1 44 19.08 2 0.5 1500 0.09 56 2.09 173 17.43 3 1.0 1500 0.084 81 3.5 532 15.32 4 1.5 1500 0.102 126 5.1 830 13.15 5 2.0 1500 0.155 239 8.2 942 9.05 S.N0 Table II: Emission test Results for Pure Diesel (With DPF+TWC converter connected at the end of exhaust tail pipe) Load Speed CO HC CO2 NOX O2 kW rpm (%) ppm (%) ppm (%) 1 0 1500 0 0 0.7 10 19.78 2 0.5 1500 0 0 1.4 60 18.65 3 1.0 1500 0 0 2.2 88 17.54 4 1.5 1500 0 0 2.6 231 16.7 5 2.0 1500 0 0 3.7 69 15.09 S.N0 As per the above results tabulated the following graphs are drawn. Figure 8:Load against CO www.ijesi.org 49 | Page
  • 6. Experimentation On Exhaust System Using
 Figure 9: Load against HC Figure 10: Load against O2 www.ijesi.org 50 | Page
  • 7. Experimentation On Exhaust System Using
 Figure 11:Load against NOX Figure 12: Load against CO2 As per the above results obtained the exhaust after treatment system with DPF+TWC converter is the best suitable for selected diesel engine to meet the diesel engine emissions legislation. IV. CONCLUSIONS Based on the values obtained for the tests conducted, the following conclusions are made * CO emission is zero for DPF+TWC converter system connected at the end of exhaust tail pipe when compared without connecting catalytic converter at the end of exhaust tail pipe. The CO emission is lower www.ijesi.org 51 | Page
  • 8. Experimentation On Exhaust System Using
 when compared to the Bharat stage IV Norms for selected engine at all operated loads with retrofit arranged. * HC emission is zero for DPF+TWC converter system connected at the end of exhaust tail pipe when compared without connecting catalytic converter at the end of exhaust tail pipe. The HC emission is lower when compared to the Bharat stage IV Norms for selected engine at all operated loads with retrofit arranged. * Carbon dioxide emission is less for DPF+TWC converter system connected at the end of exhaust tail pipe when compared without connecting catalytic converter at the end of exhaust tail pipe. * Oxygen concentration is more for DPF+TWC converter system when compared to without catalytic converter system at the end of exhaust tail pipe. * Nitrogen oxides / dioxides (NOx) emission is less for DPF+TWC converter system when compared without connecting catalytic converter at the end of exhaust tail pipe. The NOx emission is lower when compared to the Bharat stage IV Norms for selected engine at all operated loads with retrofit. * From the above analysis the main conclusion is DPF+TWC converter system is suitable substitute for diesel engine exhaust after-treatment setup as this system produces lesser emission than existing at all loads. Abbreviations DI Direct Injection DOC Diesel Oxidation Catalyst DPF Diesel Particulate Filter SCR Selective Catalytic Reduction TWC Three Way Catalyst V. ACKNOWLEDGEMENTS All praise to Almighty God (Allah) who is the only source of knowledge and without whose mercy coming this far would only have remained a dream. Our special thanks to Professor A.RAMESH (I.C.Engines Lab Incharge), IIT-Madras for his kindness and encouragement through our study period. Worth mentioning is the help, cooperation and encouragement received from all our friends and co-researchers especially in the Reaction Eng & Catalysis Research group. We Thank Assistant Professor A. VEERESH BABU, NIT-Warangal for some great and informative conversations we had over the past few months. We would like to thank Department of Chemical Engineering & Mechanical Engineering for the opportunity and the necessary facilities to carry out this research. We would like to highlight our gratitude to Professor V.PANDU RANGADU for his constructive feedback and for the hours he put in reviewing this work. REFERENCES [1] [2] [3] [4] [5] [6] [7] [8] [9] [10] [11] [12] [13] [14] “www.bosch-diesel.de” Robert Bosch GmbH 2011. “www.wikipedia.org” WikipediaÂź- trademark of the Wikimedia Foundation Inc- “Jan-2007”. “www.epa.gov” U.S Environmental protection agency, website- “Jan-2007”. “www.ec.gc.ca” The Green LaneTM, Environment Canada's World Wide Web site- “Jan- 2007”. Heywood, J.B., “Internal Combustion Engine Fundamentals”, McGraw-Hill Book Co., Singapore, 1988. Diesel Net website “www.dieselnet.com” copy right © 1997 - 2007 Ecopoint Inc “Jan-2007”. Gallant, T.R. “Experimental Diesel Particulate Filter Capabilities at PNNL.” Diesel Exhaust Emissions Reduction Conference, Detroit, MI, August 24, 2006. Blackman PG. Emission Control Options to Achieve Euro IV and Euro V on Heavy Duty Diesel Engines. SAE Journal. 2008; 2008280021. Saenz, N., H. Dillon, S. Carlson, and G. Maupin. “Advanced Metallographic Techniques Applied to Diesel Particulate Filters.” Microscopy Today, 2007: 15(5): p. 44. Abdulhamid et. al, Influence of the type of reducing agent (H2, CO, C3H6 and C3H8) on the reduction of stored NOX in a Pt/BaO/Al2O3 model catalyst. (2004) Topics Catal. 30/31, p. 161. Akira Obuchi et. al, Performance of platinum-group metal catalysts for the selective reduction of nitrogen oxides by hydrocarbons. Applied Catalysis B: Environmental Vol.2, Issue 1, 15 March 1993, Pages 71-80. Andrea Scotti et. al, Kinetic study of lean NOX storage over the Pt- Ba/ Al2O3 system. Ind. Eng. Chem. Res 2004, 43, 4522-4534. Burch et. al, A review of the selective reduction of NOX with hydrocarbons under lean-burn conditions with non-zeolitic oxide and platinum group metal catalysts. Applied Catalysis B: Environmental Volume 39, Issue 4, 20 December 2002, Pages 283-303. Daniel Chatterjee, Olaf Deutschmann and Jurgen Warnatz(2001), Detailed surface reaction mechanism in a three way catalytic converter, Interdisciplinary Centre of Scientific Computing (IWR), Heidelberg University, 2001. www.ijesi.org 52 | Page
  • 9. Experimentation On Exhaust System Using
 D. S. Jaheer Basha M.Tech Advanced Internal Combustion Engines, Engines, P.G., Research Scholar, Mechanical Engineering Department, Department, SVCET, Chittoor, Andhra Pradesh, India-517127. M A Chakravarthy M.Tech Advanced Internal Combustion Engines, N Haranadh M.Tech Advanced Internal Combustion P.G., Research Scholar, Mechanical Engineering Department, P.G., Research Scholar, Mechanical Engineering SVCET, Chittoor, Andhra Pradesh, India-517127. SVCET, Chittoor, Andhra Pradesh, India-517127. www.ijesi.org 53 | Page