Diesel Exhaust Emission Control Tim Johnson October 8, 2003 Diesel - - PowerPoint PPT Presentation

diesel exhaust emission control
SMART_READER_LITE
LIVE PREVIEW

Diesel Exhaust Emission Control Tim Johnson October 8, 2003 Diesel - - PowerPoint PPT Presentation

Diesel Exhaust Emission Control Tim Johnson October 8, 2003 Diesel emission control technology is making significant progress General technology approaches to hitting the regulations Filter technology NOx solutions Integrated


slide-1
SLIDE 1

Diesel Exhaust Emission Control

Tim Johnson October 8, 2003

slide-2
SLIDE 2

Diesel emission control technology is making significant progress

  • General technology approaches to hitting the

regulations

  • Filter technology
  • NOx solutions
  • Integrated solutions

2

slide-3
SLIDE 3

Regulations and Approaches

slide-4
SLIDE 4

Euro IV and Japan 2005 are coming next, with significant PM and NOx tightening; US2007 goes further; US2010 very low;

0.02 0.04 0.06 0.08 0.1 0.12 0.14

Euro V

US2004 Euro III

US2010

US2007

Japan 2005 Japan 2008

PM, g/kW-hr; ESC test

Euro IV

1 2 3 4 5 6

NOx, g/kW-hr; ESC test

New: German/French Euro VI (2010) proposal is 0.5 g/kW­hr NOx and 0.002 g/kW­hr PM

4

slide-5
SLIDE 5

In 2005, filters, DOCs, and SCR will be used

0.02 0.04 0.06 0.08 0.1 0.12 0.14

PM, g/kW-hr; ESC test

Euro V

US2004 Euro III

Euro IV

Japan 2005

Japan will use DPFs and advanced combustion

Some European HDD will use DOCs

The rest of Europe HDD will use 70% SCR

1 2 3 4 5 6

NOx, g/kW-hr; ESC test

5

slide-6
SLIDE 6

By 2007+, engine technologies are expected to make significant advances

Japan 2005

0.02 0.04 0.06 0.08 0.1 0.12 0.14

PM, g/kW-hr; ESC test

Euro V

US2004 Euro III

Euro IV US2010 US2007

1 2 3 4 5 6

NOx, g/kW-hr; ESC test

6

slide-7
SLIDE 7

By 2007+, engine technologies are expected to make significant advances

0.02 0.04 0.06 0.08 0.1 0.12 0.14

PM, g/kW-hr; ESC test

Euro V

US2004 Euro III

Euro IV US2010 US2007

Japan 2005

US HDD will use 80% eff. filters US MHDD will need 50% NOx and 70% PM Euro MHDD will need nominal PM Euro long haul will use 70% SCR

1 2 3 4 5 6

NOx, g/kW-hr; ESC test

7

slide-8
SLIDE 8

Recent developments in filters

slide-9
SLIDE 9

Diesel particulate filters use porous ceramics and catalyst to collect and burn the soot

Exhaust (CO2, H2O) Trapped soot on inlet wall surface Cell Plugs Exhaust (Soot, CO, HC) Enter Out

Ceramic Honeycomb Wall with Supported Catalyst Place a catalyst in front of or within filter to oxidize NO to NO2

9

slide-10
SLIDE 10

Regeneration strategies are being refined for better reliability

Bosch, Vienna Motorsymposium 4/02

10

slide-11
SLIDE 11

Low temperature combustion is being used in LDD to regenerate DPFs

Low load combustion strategy uses high EGR to burn slightly lean to generate CO&HC with low NOx and PM Catalyst inlet temperatures of 200 to 320C are reported that will heat CDPF (DPNR) to >600C under low load

  • This strategy, HCCI, and VVT offer attractive LT DPF

Toyota, JSAE 5/03 regeneration options.

  • They will not be implemented widely until 2007 or

beyond in HDD

11 •LTC is being used in LDD this year.

slide-12
SLIDE 12

Safe regeneration characteristics of catalyzed SiC filter systems are characterized

4 g/liter

50º

NGK 2003­01­0383

12

slide-13
SLIDE 13

Progress is being made in dropping back pressure and increasing thermal durability

Code: 50­11B means 50% porosity, 11 µm avg. Soot capacity is increased 75% by increasing pore size, broad (vs. narrow) pore size distribution thermal mass by 60%. A narrow pore size distribution of small pores gives the lowest pressure drop with or without catalyst. Corning DEER 8­03

13

slide-14
SLIDE 14

DPNR: high porosity

Pore structure can be engineered for the application

Uncatalyzed: narrow pore size, low porosity Catalyzed: broad size distribution and porosity Ibiden SAE 2003­01­0377

14

slide-15
SLIDE 15

New filter designs are increasing the ash storage capacity of filters

in

  • ut

in

  • ut

in in in

  • ut
  • ut

Ash storage capacity increases 2X with larger inlet:outlet ratio in DPF

(PSA, ETH Particulate Conf. 8­03)

15

slide-16
SLIDE 16

Filters are very effective in removing carbon ultrafines; under high load conditions, DPF can form nanoparticles

Fuel Sulfur Tests: Cummins CVS, ISM Engine, 1200/1927 N-m, Specially Formulated Lube Oil, 26 ppm S Fuel With and Without CDPF, TD

1.0E+04 1.0E+05 1.0E+06 1.0E+07 1.0E+08 1.0E+09 1.0E+10 dN/dlogDp, part/cm3 No CDPF, No TD CDPF No TD CDPF With TD

Corrected for DR Not corrected for particle losses

1 10 100 1000 Dp (nm)

With TD (thermal deneuder), carbon ultrafines are removed 2.5 orders

  • f magnitude. However, emissions of aerosol nanoparticles goes up.
  • Univ. of MN, CTA Monterey 3/03

16

slide-17
SLIDE 17

45 45 40 40 35 35 30 30

ent en OBD Curr OBD Curr

2 2 2 2 1 1 1 1 5 5

t (pA) (pA)

50 50 00 00 50 50 00 00 50 100 150 200

ELPI ELPI Cur Curr rent ent ( (pA) pA)

Dekati OBD vs. ELPI

50 100 200 150

PM OBD sensor is in early stages of development

ECU Emitted PM OBD Sensor Operation: Electrical potential across flow charges particles.

Good correlation between OBD device and

Difference betw een input current

ELPI, even at very low PM levels

and ground is indicative of PM

Dekati 8­03

17

slide-18
SLIDE 18

NOx Control

18

slide-19
SLIDE 19

NOx control is difficult in lean conditions

  • In stoichiometric conditions (like typical gasoline engines),

the three way catalysts takes our 98%+ of the NOx: CO + NOx = CO2 + N2

  • In lean conditions, the CO prefers to react with oxygen:

CO + 1/2O2 = CO2

  • Emission control systems need to accommodate

19

slide-20
SLIDE 20

State-of-the Art SCR system has NO2 generation and

  • xidation catalyst to eliminate ammonia slip

SCR Catalyst (S) 4NH3 + 4NO + O2 → 4N2 + 6H2O Urea 2NH3 + NO + NO2 → 2N2 + 3H2O (NH2)2CO 8NH3 + 6NO2 → 7N2 + 12H2O

H S V

Exhaust Gas Oxidation Catalyst (V)

O

2NO + O2 → 2NO2 Oxidation Catalyst (O) 4HC + 3O2 → 2CO2 + 2H2O 4NH3 + 3O2 → 2N2 + 6H2O 2CO + O2 → 2CO2 Hydrolysis Catalyst (H) Degussa, 9­99 (NH2)2CO + H2O → 2NH3 + CO2

20

slide-21
SLIDE 21

Reference: MECA

Pt Pt

Rh Rh

NO NO + + ½O O2

2

The NOx adsorber in storage mode during lean conditions; NOx stored as a nitrate

Lean Conditions CO CO2

2

Al Al2

2O

O3

3

Ba Ba(NO (NO3

3)

)2

2

BaCO BaCO3

3

NO NO2

2

Pt

Rh

2NO2 + BaO + 1/2O2 = Ba(NO3)2

21

slide-22
SLIDE 22

Reference: MECA

In rich mode, the nitrate dissociates to NO2, which is converted to nitrogen using the HCs or CO Rich Conditions

Al Al2

2O

O3

3

CO + HC + H CO + HC + H2

2

Pt Pt BaCO BaCO3

3

Rh Rh

Ba Ba(NO (NO3

3)

)2

2

N N2

2 +

+ CO O2

2

NOx NOx

O2 CO CO

22

slide-23
SLIDE 23

LNT and SCR lead the field on effective NOx control, but LNC showing improvement

System Transient Cycle NOx Efficiency Effective Fuel Penalty Swept Volume Ratio Notes

SCR, 400-csi 85-90% 3-4% urea or about 2% penalty in US 1.7 emerging Being applied and specs being finalized; low temp. performance issues; LNT 80-95% 1.5 – 4% total

  • regen. +

desulf. 1.3 to 2 Desulfation strategy and durability issues; integrated DPF/LNT components emerging; PGM cost issues DeNOx catalyst 20-60% 2 to 6% 0.85 to 4 Generally not sensitive to sulfur; HC slip issues; durability needs proving

23

slide-24
SLIDE 24

SCR

slide-25
SLIDE 25

77% of diesel is pumped at 2200 stations

2200 stations pump 77% of fuel; additional 3500 bring total to 97% Urea could cost $0.70/gal at the largest 65%

  • f truck stops

Estimates are that about 50% of 2007 trucks would need SCR to make infrastructure viable

EMA study by Tiax 6­03

25

slide-26
SLIDE 26

NO2/NO ratio is important in achieving good low temperature SCR performance

Johnson Matthey DEER 8­03

26

slide-27
SLIDE 27

Ammonia sensor is in development

Ford DEER 8­03

27

slide-28
SLIDE 28

Lean NOx Traps

slide-29
SLIDE 29

LNT aging studies are expanded to 1,000,000 effective miles; step deterioration observed at 600,000 miles

Aging generally follows loss in active surface area, but phosphorous and zinc contamination also evident

LNT formulation shows initial decline in capacity, and then stabilization out to 600 hours (est. 600,000 miles) before declining

  • SV = 21,000/hr ; standard lube oil
  • Accelerated Test Cycle:

again

  • A: 36 Minutes @ 350ºC with S Loading and Red­Ox Cycling
  • B: 63 Minutes @ 500ºC with Red­Ox Cycling
  • 6.3 Minutes of Rich Operation for deSulfation
  • A­B­A­B­A­B Sequence Repeated 1,000 Times

Emerachem DEER 8­03

29

slide-30
SLIDE 30

Top layer adsorbs SO2 for moderate storage capacity, but quick release.

A new double­layer LNT is developed that keeps SOx off the adsorbing material

Single layer formulations exhibit typical performance Double layer formulations exhibit superior` performance

Top layer adsorbs SO2 for moderate storage capacity, but quick release.

VTT, Mitsubishi SAE 2003­01­1158

30

slide-31
SLIDE 31

Hydrogen/CO reformate significantly improves LNT performance

Hydrogen facilitates the desulfation step and is very efficient in regenerating LNTs

MIT ArvinMeritor DEER 8­03

31

slide-32
SLIDE 32

Integrated systems

slide-33
SLIDE 33

DPF/SCR systems are on the road ­ 5 trucks in the US

SCR: extruded 200­csi, SVR=3.8

Combined FTP hit US2007 blended NOx and PM; 82% NOx efficiency, 89% PM efficiency

OICA hit US2007 transition NOx, but missed on PM due to sulfates

Ceramics LLT, SAE 2003­01­0774

  • 3 Mack highway

tractor/trailers

  • 2 refuse trucks
  • started mid­2002

33

slide-34
SLIDE 34

The large EPA 2­leg LNT/DPF system is replaced with a more “efficient” 4­leg system

NOx efficiencies are >95% at all S.S. modes and fuel penalties are 1.6 to 4.8%. In the EPA four­leg system, one leg is being regenerated while three legs are in collection

  • mode. The regeneration gas is throttled and

uses a fuel injector to minimize fuel penalty. SVR (LNT) = 2.8; SVR (filter) = 1.7 EPA Non­road NPRM 4­03

34

slide-35
SLIDE 35

35

LDT is hitting Bin 5 with LNT+CSF combination

SVR LNT = 1.2 SVR DPF = 2.0 all cordierite

Cummins, DEER 8­03

slide-36
SLIDE 36

A 4.0 liter light duty commercial truck is fit with the DPNR system

  • PM efficiency increases from 90% to

96% after 2000 hrs.

  • Ash back pressure increases 30%
  • In Japan Transient Cycle, temperatures

are too low, necessitating low temperature combustion at low load.

Toyota, Vienna Motorsymposium 5/03 Temperatures from 4l TSI­CR are sufficient to use only auxiliary injections to regenerate and desulfate. Other applications require low­temperature combustion control.

NOx emission more than doubles upon 2000 hrs of aging in 40 ppm sulfur fuel (200,000km); 65% NOx aged efficiency 36

slide-37
SLIDE 37

Exhaust emission control systems are part of the solution

  • DPFs, DOCs, SCR will be applied in 2005 in Japan and Europe

– DPF and SCR in 2007 in the US – LNT in LDD and MDD this year

  • Filters are in the optimization stage

– understanding improving regeneration – filter properties – ash management issues

  • NOx solutions are available at +70%

– SCR is being optimized – LNT is on dynos

  • Integrated solutions are making HDD the environmental benchmark

37

slide-38
SLIDE 38

THE END

Thank you.