Comparison of PM exhaust emissions measured at a chassis dynamometer and on-road chasing Rainer Vogt, Volker Scheer, Roberto Casati Ford Forschungszentrum.

Slides:



Advertisements
Similar presentations
Effect of Fuel Quality and Engine Technology on Particle Emissions
Advertisements

WLTP-06-31e WLTP correction algorithms progress report from TUG (chassis dynamometer corrections) and TNO (coast down corrections) preliminary results.
MASS EMISSION RATES AND CHEMICAL CHARACTERIZATION OF PM 2.5 EMISSIONS FROM TWO MOTORCYCLES Deniz Karman and Colin Welburn Department of Civil and Environmental.
27/06/02 Reproduction permitted with due acknowledgement DG TREN Particulates Consortium Lemnos, September 2003 Neville Thompson, Technical Coordinator,
12th U.S./North American MVS, Reno, Nevada, June 9-11, 2008 Effects of Sintered Metal Diesel Particulate Filter System on Diesel Aerosols and Nitric Oxides.
Ashish Shah, Per Tunestål and Bengt Johansson Lund University, Sweden
Soot Particle Aerosol Mass Spectrometer: Development, Validation, and Initial Application T. B. Onasch,A. Trimborn,E. C. Fortner,J. T. Jayne,G. L. Kok,L.
Experimental Evaluation of Various Biofuel-Diesel Blends as Diesel Engine Fuels Georgios Fontaras and Zissis Samaras Laboratory of Applied Thermodynamics.
The DG Tren ” Particulates „ project Zissis Samaras Lab of Applied Thermodynamics Aristotle University Greece.
Heavy-duty vehicle test facility at VTT Excellent tool to determine the effect of traffic environment on emissions and energy use Juhani Laurikko 10 June.
VII. How might current analysis methods be enhanced or combined to obtain more information about the nature of OC, EC, and other carbon fractions in filter.
Impact of Cold Climates on Vehicle Emissions: The Cold Start Air Toxics Pulse Tom Jobson, Yibo Huangfu, Graham VanderSchelden, Serena Chung Laboratory.
1 Influence of dilution and particle fractal dimension of diesel exhaust on measured SOA formation in a smog chamber Shunsuke Nakao (1,
Instrumented Vehicle BAQ Instrumented In-Use-Vehicles, a Versatile Tool to Measure Emissions BAQ 2004 Agra, India Dec 2004 Instrumented In-Use-Vehicles,
Homogeneous Charge Compression Ignition (HCCI) Engines Gajendra Singh.
WORKSHOP ON VEHICLE EXHAUST PARTICULATE EMISSION MEASUREMENT METHODOLOGY San Diego, 21 Oct 2002 Zissis Samaras Lab of Applied Thermodynamics Aristotle.
Real-world emissions in the EU: An overview of recent evidence and policy implications Peter Mock, Anup Bandivadekar APEC VFEL Workshop Singapore March.
Specialty Vehicle and Engine Testing Section (SVETS) Mobile Source Operations Division Pablo Cicero April 12, th Information Session.
Repeatability and Reproducibility Analysis of the Round Robin Results.
REGENERATION ISSUES Institute for Energy and Transport Joint Research Centre B. Giechaskiel, J. Andersson, G. Martini 3 April 2014.
Surface Measurements of PM, VOCs, and Photochemically Relevant Gases in Support of DISCOVER-AQ. J. Flynn, R. J. Griffin, B. Lefer, H. W. Wallace, Y. Leong,
WLTP DTP PM-PN Subgroup Activities, Progress & Future Plans 7 th DTP Meeting Bern 12 th – 14 th September 2011 Chris Parkin.
Laboratories included in the database  AVL  EMPA  MTC  TUG  Volvo  VTT  LAT  Shell  IFP  FFA.
Vehicle generated nanoparticles are not an artifact! D. B. Kittelson, W.F. Watts, and J.P. Johnson Center for Diesel Research University of Minnesota 8th.
Aeronet Workshop Berlin, Sep 2002 Leonidas Ntziachristos Mech. Eng, PhD Post-Doc Research Fellow Sampling & Instrumentation Techniques for Automotive.
Measurement of aerosol and VOC turbulent fluxes and in-canopy particle characterization at a pristine forest in Amazonia Luciana Rizzo.
3rd International Conference LUBRICANTS RUSSIA Diesel Particulate Filter Regeneration Strategy and its Influence on Engine Oil Characteristics Luca.
Drexel University Development of HCCI Technology at Drexel University Rodney Johnson Advisors: Dr. Miller and Dr. Cernansky Combustion Fuels and Fluids.
Concawe Nanoparticles from road vehicle exhaust: an artefact or a reality? Diane Hall BP/CONCAWE Lemnos Meeting: Round Table Discussion 11 th September.
Volvo Technology Corporation Dept / AMR / 01/11/2015 / page 1 Particulates.
Martin Mohr, PARTICULATES WP 500 EMPA contribution –WP 550 Investigation of sub-zero cold start effects.
Volvo Technology AB / Volvo Technology Corporation Dept / UW / 03/11/2015 / page 1 Particulates, Lemnos, 2003 Deliverable 13 Effects on particulate.
7th International ETH Conference on Combustion Generated Particles Zurich Zissis Samaras Laboratory of Applied Thermodynamics Aristotle University.
1 Ultrafine Particles and Freeways Yifang Zhu, Ph.D. Assistant Professor Department of Environmental Engineering Texas A&M University –Kingsville
ACEA PM-3 programme Caroline Hosier, Pilot, ACEA Task-Force Particulates (TF-PM) Ford Motor Company Draft presentation to GRPE Informal document No. GRPE-52-9.
Geneva, June 2011 Effect of ambient temperature (15 °C÷28 °C) on CO2 emissions from LDV over NEDC
EGA Technical World Leaders in Combustion Management Solutions Mk7 EGA.
EGA Technical World Leaders in Combustion Management Solutions Mk7 EGA.
Testing a Rear Wheel Drive xEV on a 2 Wheel and 4 Wheel Dynamometer Aaron Loiselle-Lapointe Emissions Research and.
Deliverable 10 Contents  Vehicles/engines  Diesel passenger cars  Gasoline (PFI-DISI) passenger cars  Diesel heavy duty vehicles  Diesel heavy duty.
Aerosol Size Distribution Performance Based on Changes to Particle Emissions and Nucleation Robert A. Elleman & David S. Covert Department of Atmospheric.
Jorma Keskinen Tampere University of Technology (TUT) Occurrence and fate of traffic generated nanoparticles in (urban) atmosphere.
Timetable  Submission of draft Reports to LAT  The reports must be simple and straightforward (see proposal of contents)  We do not deal.
25 January 2016 European Commission - Joint Research Centre (JRC)
29/02/2016 Reproduction permitted with due acknowledgement DG TREN – WP500 CONCAWE LD Vehicle Testing.
TUG Roadside Measurements of Particulate Matter (PM) size distribution P.J. Sturm, S. Hausberger Graz University of Technology: Michael Bacher, Bernhard.
© 2009, TSI Incorporated PMP PNC Calibration Recent Experiences Hans-Georg Horn TSI GmbH, Particle Instruments PMP Meeting, London, 30 March 2009.
RDE PN-PEMS programme Progress Update F. Riccobono, B. Giechaskiel, P. Bonnel STU, IET, JRC, European Commission.
© 2005 Northeast States for Coordinated Air Use Management (NESCAUM) Advanced Mobile Source Training Course MS Diesel III. Emission Testing and Diagnostics.
Date of download: 6/25/2016 Copyright © ASME. All rights reserved. From: Roles of Organic Emissions in the Formation of Near Field Aircraft-Emitted Volatile.
10 mm is the same as... 1 cm. 20 mm is the same as... 2 cm.
PN-Calibration Issues
India’s Comments on EPPR (Part-B2)
Laboratories included in the database
Mobile Air-conditioning (MAC):
D. Foster, T. Root, T. Kawai, E. Wirojsakunchai, E. Schroeder, N
PARTICULATES PROGRAM WP500
RDE Regulation Commission Meeting
BRAKE PARTICLE EMISSIONS
WLTP DTP PM-PN Subgroup Activities, Progress & Future Plans
Pems route and parameters
Lemnos 11/9/03 Comparison of PM exhaust emissions measured at a chassis dynamometer and on-road chasing on a test track.
Test Fuel Properties FT Diesel fuel Diesel fuel Properties (8/19)
Emissions testing in the laboratory and on the road: Preliminary results for one Euro 6 diesel vehicle Pierre Bonnel Martin Weiss Joint Research Centre.
Francesco Riccobono, Barouch Giechaskiel, Pierre Bonnel
PN-PEMS Progress update
Pilot project: Analysis of the relevance of influencing factors when determining CO2 emissions and fuel consumption during type approval of passenger cars.
Emissions testing with PEMS versus random laboratory driving cycles
Particle Size and Size Distributions
DTP Lab Process ICE: Open Issues
Presentation transcript:

Comparison of PM exhaust emissions measured at a chassis dynamometer and on-road chasing Rainer Vogt, Volker Scheer, Roberto Casati Ford Forschungszentrum Aachen GmbH Barouch Giechaskiel, Zissis Samaras LAT, Aristotle University Thessaloniki

2 Overview Objectives of the study On-road chasing method Results of on-road chasing Laboratory experimental setup Results of chassis dyno work, comparison of instruments Comparison of lab and chasing Conclusions

3 Objectives To measure the PM emissions of the VW TDI by chasing the exhaust plume with the Ford Mobile Laboratory (FML) at three constant speeds and fixed distance on a test trace To measure the PM emissions of the VW TDI with the PARTICULATES dilution system at the FFA chassis dynamometer at the same constant speeds and during the NEDC To compare the results obtained with the PARTICULATES dilution system with real-world dilution measured during chasing the exhaust plume with a special focus on nucleation particles

4 On-road chasing of exhaust plume Test vehicle: VW Golf TDI 1.9 l speed, fuel consumption EN590 diesel (280 ppm S) Ford Mobile Lab: SMPS, CPC, NOx, CO 2 T and RH Test track: high speed oval, 4 km/lap 14 m distance: 0.4 s (120 km h -1 ) 1 s (50 km h -1 )

5 In-let for on-road sampling inlet: 4 mm (15 cm) transfer line: 10.3 mm (420 cm) total residence: 1.4 s

6 Constant speed tests T= 3-6 °C, RH= % (February 2003) 10 min warm-up at 120 km h -1 8 min at 120, 100, 50 km h -1

7 Geometric Mean diameter

8 Speed ramp tests

9

10 Comparison: Lab & On-road chasing 50km h -1 PFSS: PDR: 12.5 DT: 32°C LR

11 Laboratory experimental setup Results of chassis dyno work comparison of instruments - Makis part -

12 Comparison: Lab & On-road chasing 100km h -1

13 Comparison: Lab & On-road chasing 120km h -1

14 Conclusions (1) The PARTICULATES system is suitable to study the influence of the dilution parameters on nucleation Longer residence time favours the growth of the nucleation particles and shifts the nucleation mode to larger diameters Lower dilution air temperature enhances the formation of nucleation particles, with increased number and a distinct mode is formed at lower speed. Chasing and lab experiments show that nucleation is not stable in a time scale of several minutes; dependent on vehicle history as shown in speed ramp tests

15 Conclusions (2) The particle size distributions (only soot mode present) measured during chasing at 50 km/h were in very good agreement with dynamometer measurements At about 100 km/h nucleation particles occur during the chasing experiment. The occurrence and in general the emission rate of these particles can be reproduced with the PARTICULATES system, if the dilution parameters are chosen in order to match the ambient conditions. At 120 km/h a strong nucleation mode is observed in the exhaust plume. While the PARTICULATES system is capable to reproduce the soot mode very well, it shows a nucleation mode, which is somewhat lower in particle number, but larger in diameter.

16 - Back-up -

km h -1 simulated % grade Effect of chassis load

18 Effect of chassis load 120 km h -1 simulated % grade