Reducing diesel particle emissions by particle oxidation catalyst

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Reducing diesel particle emissions by particle oxidation catalyst Lehtoranta Kati, Matilainen Pekka, Åsenbrygg Juha-Matti, Lievonen Ari & Kinnunen Toni Ecocat Oy, Vihtavuori, Finland

Contents Introduction - diesel particles, after-treatment Particle oxidation catalyst (POC) - structure Emission test set up Emission test results - NEDC - Steady state modes - Endurance test Summary

Introduction - What are diesel particulates - Soot is formed in the engine through the incomplete combustion process - VOF condensates on soot particles during exhaust gas cooling and dilution - In addition sulfates can be found in diesel particulate matter Soot Primary particle size ~20nm VOF (volatile organic fraction) Diesel particle mean size ~50-100nm

Introduction diesel PM reduction with after-treatment - Diesel oxidation catalyst (DOC) - effective reduction of HC and CO - some reduction of PM (reduction of VOF) - typical PM reduction 10-30% 100 90 80 DPF - Diesel particulate filter (DPF) - effective reduction of PM (soot) - typical PM reduction 80-95% - regeneration of filter needed (to avoid back pressure increase, blocking risk) PM reduction (%) 70 60 50 40 30 target with POC - Particle oxidation catalyst (POC) - first target: to increase particle deposition in catalyst without significant back pressure increase and to avoid blocking risk 20 10 0 DOC

POC substrates Structure of POC (EP 1230978, 2002) Substrate channels are produced with several corrugated screen layers subsequently welded together Exhaust gas follows the tortuous paths or goes through the screen Exhaust flow

POC substrates Structure of POC Selection of cell densities and corrugation angles. Novel POC coating on fine screen Screen holes are open or partly closed. Soot is collected on the surface of the wire or on the edges.

Trapping Principles 1. 2. 1. Impaction: coarse particles don t follow the flow curves 2. Diffusion and thermophoresis: in a temperature gradient small particles move from a hotter to a colder region 3. Particle Capture: small particles close to surface can be captured 3. -> Trapping methods of POC are studied in co-operation with Aerosol Physics Laboratory, Tampere University of Technology

LDD dynamometer emission tests

Emission test set-up DMM Mass concentration FPS CVS DOC (cc) + POC (uf) Test vehicle: VW Touran (1.9 dm 3, Euro 4) Test fuel: Futura Diesel (EN590) (S < 10ppm) Test-cycles: -NEDC - Steady modes: 60 km/h 80 km/h 120 km/h Gas analyzers, PM filter Regulated emissions -PM VOF Always minimum 3 test repetitions

Measurement equipments - Gaseous and particulate matter (PM) emissions are measured according to the European regulations (Directive 1999/96/EC), CVS tunnel is used to dilute the exhaust gas. - Volatile organic fraction (VOF) is analyzed from PM filters by weighing the PM samples before and after vacuum evaporation. - Dekati Mass Monitor (DMM) is used to measure mass concentration in real time. (In DMM this is done by compining aerodynamic and mobility size particle classification). Fine Particle Sampler (FPS) is used for sampling and diluting the sample for DMM. (Two stage dilution, primary with porous probe, secondary with ejector diluter). - In addition to emission tests e.g. exhaust temperatures and back pressures are measured.

Example of POC efficiency VW Touran, NEDC-test, emissions 0.800 0.700 RAW RAWDOC+POC 0.600 0.500 g/km 0.400 0.300 0.200 0.100 0.000 THC CO NOx THC+NOx PM*10 PM*10 61% DOC = 120 cpsi, d 90, L90, coated POC = 400 cpsi, d 118, L225, coated DOC+POC clearly reduces particle mass, in this case ~60%

Example of POC PM efficiency steady state driving 60km/h 80km/h 120km/h PM (g/km) 0.03 0.025 0.02 0.015 0.01 0.005 0 VOF non-vof 16% 63% RAW DOC DOC+POC PM (g/km) 0.05 0.045 0.04 0.035 0.03 0.025 0.02 0.015 0.01 0.005 0 VOF non-vof 25% 62% RAW DOC DOC+POC PM (g/km) 0.06 0.05 0.04 0.03 0.02 0.01 0 VOF non-vof 33% 71% RAW DOC DOC+POC DOC can reduce the volatile fraction (VOF) of PM POC reduces both VOF and non-vof emissions

Example of POC PM efficiency measured with DMM 3.0E+04 Mass concentration RAW DOC+POC 2.5E+04 60 km/h 80 km/h 120 km/h 2.0E+04 mass g/m 3 1.5E+04 1.0E+04 ~72% ~76% ~77% 5.0E+03 0.0E+00 0 500 1000 1500 2000 2500 3000 3500 time (s)

Example of POC PM efficiency 4000 km endurance test Target: average PM efficiency at least 30% Description of the 4000km Endurance Test Average speed between 25 and 35 km/h Maximum speed 70 km/h Speed between 50 and 70 km/h for maximum 10% of test time Minimum 7% of test time is idling Average temperature before and after particle reduction system always below 300 C Maximum engine speed < 60% of rated speed Initial state emission tests Emissions after 2000 km Emissions after 4000 km Worst case regeneration measurement Emissions after worst case regeneration

4000 km endurance test results 0.06 PM emissions (and reductions compared to orig.) LDD Vehicle (2.6 dm 3 ) 0.05 0.04 PM (g/km) 0.03 0.02 43% 39% 46% 50% 0.01 0 Initial state orig. DOC Initial state DOC+POC-X after 2000km DOC+POC-X after 4000km DOC+POC-X after regeneration DOC+POC-X after regeneration orig. DOC

Summary Comparative test results of the POC and DOC catalysts have proven that the POC has 30-60% PM conversion in addition to DOC (Note: Efficiency depends on application) Coating with precious metals is utilized in POC for regeneration purposes and to get the highest PM reduction possible (both VOF and non-vof reduction) 4000km worst case endurance test passed with POC further on road tests needed and are running at the moment, e.g. HDD truck over 100 000km More information e.g. heavy duty test results, see SAE 2007-24-0093 (to be published in SAE ICE 2007 in September)