Development of Current and Future Diesel After Treatment Systems
Pakorn Bovonsombat, Byung-Sun Kang, Paul Spurk, Harald Klein, Klaus Ostgathe
Degussa Metals Catalysts Cerdec AG Rodenbacher Chaussee 4, P.O.Box 1351
D-63403 Hanau-Wolfgang, Germany
Content:
1. Overview 1-1. Legislation
1-2. PM & NO x trade-off
1-3. Requirement of NO x conversion efficiency for EU-IV
2. Diesel Oxidation Catalyst 3. NO x adsorber
4. Diesel Particulate Filter 5. Urea-SCR
6. Summary
Content:
1. Overview 1-1. Legislation
1-2. PM & NO x trade-off
1-3. Requirement of NO x conversion efficiency for EU-IV
2. Diesel Oxidation Catalyst 3. NO x adsorber
4. Diesel Particulate Filter 5. Urea-SCR
6. Summary
Total cycle emissions in NEDC-cycle in [g/km]
Legislation
CO HC + NO
xHC NO
xPM
EURO III 0.64 0.56 0.06 0.50 0.05
EURO IV 0.50 0.30 0.05 0.25 0.025
Total cycle emissions in [g/kWh]
Legislation
CO NMHC HC NO
xPM
EURO III 2.10 0.66 5.00 0.10
ESC- Test
Cycle EURO IV 1.50 0.46 3.50 0.02
EURO III 5.45 0.78 5.00 0.16
ETC- Test
Cycle EURO IV 4.00 0.55 3.50 0.03
EURO III and EURO IV legislation for diesel passenger cars in NEDC - cycle.
EURO III and EURO IV legislation for heavy-duty trucks.
Diesel Legislation
Thailand Diesel Legislation
CO HC+NOx
PMLess than 6 passengers 1.0 0.70 (0.90) 0.08 (0.10) More than 6 passengers 1.0 - 1.5 0.7 - 1.2 (0.9 - 1.6) 0.17 - 0.8 (0.10 - 0.20) Less than 2,500 Kg GW
( ) = Values for Direct Injection
Legislation for Light Duty Diesel
Total Cycle Emissions in R-83 Cycle (g/km)
Vehicle Category
CO HC NOx PM
More than 9 passengers
4.0 1.1 7 0.15
GW greater than 3,500 Kg.
Total Cycle Emissions in R-49 Cycle (g/ kwh) Legislation for Heavy Duty Diesel (Euro II)
Vehicle Category
optimized combustion
EURO IV
engine measure NOx-reduction
engine measure particulate reduction
particulate aftertreatment
NOx-aftertreatment NOx [g/km]
optimized combustion + better fuel
PM [g/km]
0.05
0.025
EURO III
0.25 0.50
NO
x/PM trade-off-curve for passenger cars. Emission values refer to
.NEDC- cycle. Similar principle is valid for heavy-duty trucks.
NOx-PM Trade-off
Requirement of NOx Conversion Efficiency for EU-IV
0,125 0,225 0,325 0,425 0,525 0,625 0,725 0,825
500 1000 1500 2000 2500
inertia test weight [kg]
NOxemission [g/km]
-50 -30 -10 10 30 50 70 90
required NOxconversion [%]
NOx emission EU 4 legal limits required NOx conversion
passive DeNO
xurea SCR NO
xadsorber
Content:
1. Overview 1-1. Legislation
1-2. PM & NO x trade-off
1-3. Requirement of NO x conversion efficiency for EU-IV
2. Diesel Oxidation Catalyst 3. NO x adsorber
4. Diesel Particulate Filter 5. Urea-SCR
6. Summary
Function of Diesel Oxidation Catalyst
Catalytic Converter
Engine-out : CO Unburned HC
PM NO
xCO
2H
2O
Reduced emission of PM and NO
x*C
mH
n+ (m+0.25n) O
2= m CO
2+ 0.5n H
2O CO + 0.5 O
2= CO
2* Passive NO
xconversion rate: Max. 10 %
Performance
of Diesel Oxidation Catalyst
0 10 20 30 40 50 60 70 80 90 100
NOx CO HC PM
total cycle conversion [%]
70 g Pt/cuft, fresh
V
cat= 2.5 l 2.0 L DI CR ITW = 1,587 kg 406 wt. ppm S
Diesel oxidation catalyst for passenger car – performance in NEDC – cycle.
10
89
82
41
Content:
1. Overview 1-1. Legislation
1-2. PM & NO x trade-off
1-3. Requirement of NO x conversion efficiency for EU-IV
2. Diesel Oxidation Catalyst 3. NO x adsorber
4. Diesel Particulate Filter 5. Urea-SCR
6. Summary
Support
Pt NOx
adsorber
NO + ½ O
2NO
3-
NO
2Support
Pt NOx
adsorber N
2NO
3- NO
xRed
NO
x- Adsorption NO
x- Reduction
Chemical model of NOx storage catalyst Source: N. Miyoshiet et al, SAE 950809 (1995)
Basic Concept of NO x Adsorber
N OC O , H C . P M . . .
C l e a n e x h a u s t
I l e a n p h a s e ; s t o r a g e o f n i t r o g e n o x i d e s
I I r i c h p h a s e ; r e g e n e r a t i o n o f t h e a d s o r b e r T i m e
1
λ
Operation principle of diesel NO
x–storage catalyst.
Operation Concept of NO x Adsorber
0 10 20 30 40 50 60 70 80 90 100
100 150 200 250 300 350 400 450 500
NO
xconversion [%]
Temperature in front of catalyst [°C]
Conversion Efficiency of NO x Adsorber
Model Gas composition:
• Simulation of typical diesel exhaust gas composition
• Adjustment lean / rich sumulation:
60 s lean / 10 s rich setting; SV = 30,000
NOx conversion as function of temperature in front of diesel Nox-storage catalyst
Model gas test
Content:
1. Overview 1-1. Legislation
1-2. PM & NO x trade-off
1-3. Requirement of NO x conversion efficiency for EU-IV
2. Diesel Oxidation Catalyst 3. NO x adsorber
4. Diesel Particulate Filter 5. Urea-SCR
6. Summary
1.Diffusion 2,3. Inertia effects Fibre
exhaust
Surface filter Fibre filter
Particulate Filter System
896
89
376
213
0 200 400 600 800 1000 1200
Vehicle A (0.112 g/km) Vehicle B (0.047 g/km) Number of regenerations
Distance between regenerations [km]
PM raw emissions measured in NEDC-cycle
Calculation of required filter regeneration cycles during 80,000 km in NEDC- cycle. Particulates loading in the filter: 10 g.
Number of Regenerations vs. PM Raw Emission
Examples of filter regeneration methods.
Type of Filter Regeration
Content:
1. Overview 1-1. Legislation
1-2. PM & NO x trade-off
1-3. Requirement of NO x conversion efficiency for EU-IV
2. Diesel Oxidation Catalyst 3. NO x adsorber
4. Diesel Particulate Filter 5. Urea-SCR
6. Summary
Basic System of SCR
S O V
urea (NH
2)
2CO
exhaust
SCR catalyst (S)
4NH
3+ 4NO + O
24N
2+ 6H
2O 2NH
3+ NO + NO
22N
2+ 3H
2O 8NH
3+ 6NO
27N
2+ 12H
2O
Guard catalyst (O) 4NH
3+ 3O
22N
2+ 6H
2O Pre-catalyst (V)
2NO + O
22NO
2„4HC + 3O
22CO
2+ 2H
2O“
2CO + O
22CO
20 200 400 600 800 1000
0 200 400 600 800 1000 1200
time [s]
NOx concentration [vppm]
0 20 40 60 80 100
NH3 / N2O concentration [vppm]
NOx raw
NOx after SCR system NH3 after SCR system N2O after SCR system
ECE 22 %
EUDC 83 %
total 63 %
ECE 22 %
EUDC 83 %
total 63 %