Validation of the COPERT road emission inventory model with real-use data



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1 Validation of the COPERT road emission inventory model with real-use data P. Dilara (P), V. Franco European Commission Joint Research Centre -Transport and Air Quality Unit M. Kousoulidou, L. Ntziachristos, S. Geivanidis, Z. Samaras Laboratory of Applied Thermodynamics - Aristotle University of Thessaloniki

2 INDEX Introduction Experimental setup Data analysis Results Discussion Conclusions

INTRODUCTION. Key Research Questions 3 How much does a modern vehicle emit under realistic driving conditions (i.e. outside regulated test cycles)? Portable Emissions Measurement System (PEMS) campaign to gather in-use, real-world data Can real-world measurement data be used for emission factor development / validation? Development of engine pollutant and FC maps from PEMS data Feed them into Vehicle Simulation tools Simulation of experimental routes and production of new EFs Direct comparison of PEMS data to EFs from model used in p national inventory compilations (COPERT)

4 EXPERIMENTAL SETUP PEMS measurement campaign Stock Euro 5 Diesel PC Three predefined routes Rural + Highway (135 km length, 65 kph average speed) Rural + Urban (61 km, 35 kph) Rural + Uphill (65 km, 4 kph) Second-by-second log Tailpipe concentration of exhaust gasses : O 2, HC, CO, CO 2 (NDIR) and NOx (electrochemical cell) Exhaust flowmeter GPS and vehicle-mounted weather station data ECU data: vehicle speed, engine rpm, intake air mass flow, coolant temperature

5 EXPERIMENTAL SETUP Stock Fiat Bravo 1.6 JTD (DPF Diesel) 88 kw, 3 N m @ 15 rpm Semtech-DS mobile emission analyzer (manufactured by Sensors, Inc.)

6 DATA ANALYSIS. Models COPERT (LAT Thessaloniki) Calculates emissions from all major pollutants, incl. exhaust and diffuse sources (evaporation, tyre and break wear), based on meanspeed emission factors Covers all major vehicle cats. (241 individual types/technologies) Applied for national-scale l inventories i throughout h t Europe ADVISOR (US Dpt. of Energy) http://lat.eng.auth.gr/copert/ Matlab/Simulink Analysis package for advanced vehicle modeling. Used to predict the fuel consumption and emissions of test vehicle

7 DATA ANALYSIS 1. Overview 15 1 PEMS data cyc_kph_r kpha Matlab tool for the creation of engine maps using synchronized data km /h 5 1 2 3 4 5 6 7 8 1 Synchronization of raw data 1.4 1.2 km/h 15 1 5 cyc_kph_r kpha System Response [-] 1.8 O 2 analyzer.6 NO analyzer.4 CO analyzer.2 Measured CO 2 analyzer Simulated 2 4 6 8 1 Time [s] Vehicle Simulation in ADVISOR emissions overall ratio.5 1 2 3 4 5 6 7 8 1.1.2.3.4.5.6.7.8.9 1.1 hc co/1 nox.5 pm 1 2 3 4 5 6 7 8 15 overall ratio 1 5 1 2 3 4 5 6 7 8

8 DATA ANALYSIS 1. Preprocessing Synchronization of raw PEMS data Model to perform a back correction of the analyzer s signal to correct for time lag and response Highly transient modes are filtered out Geivanidis & Samaras, Meas. Sci. Technol. 19, 28

9 DATA ANALYSIS 1. Engine pollutant and FC maps CEMOD (Creation of engine maps using optimized data) Matlab tool develops engine pollutant maps based on available data points of engine speed, torque and PEMS measurements using a neural network approach km/h 15 1 5 cyc_kph_r kpha 1 2 3 4 5 6 7 8 1.5 emissions 1.1 2.2 3.3 4.4 5.5 6.6 7.7 8.8 9.9 1.1 hc co/1 nox.5 pm overall ratio 1 2 3 4 5 6 7 8 15 overall ratio 1 5 1 2 3 4 5 6 7 8

1 RESULTS 1. PEMS vs. ADVISOR simulation EFs calculated directly from PEMS data vs. simulation of the PEMS routes in ADVISOR PEMS ADVISOR Deviation FC [l/1km] 5.37 5.4 1% CO [g/km].169.129 24% HC [g/km].3333.33 9% NOx [g/km].74.81 9% Results from Ispra Milano route (Rural + Highway)

11 DATA ANALYSIS 2. Direct Comparison INCERT (Interface for the Comparison of Emissions i from Road Transport) Graphical interface for the comparison between the emission factors derived within COPERT and those from PEMS Results for 1, 5 and 1-km data splits for average speed calculations

12 RESULTS. PEMS vs. COPERT EFS EFs calculated from PEMS data vs. corresponding mean-speed COPERT values HC emissions [g/km] Fuel consumption [g/km].6.5.44.3.2.1 1 km split 5 km split 1 km split 49 48 47 46 45 44 43 42 41 1 km split 5 km split 1 km split Mean deviation 34% PEMS Mean deviation -6% COPERT Results from Ispra Milano route (Rural + Highway)

13 RESULTS. PEMS vs. COPERT EFS EFs calculated from PEMS data vs. corresponding mean-speed COPERT values CO emissions [g/km] NO X emissions [g/km].18.16.14 12.12.1.8.6.4.2 1 km split 5 km split 1 km split.8.7.6.5.4.3.2.1 1 km split 5 km split 1 km split LIMIT Mean deviation 229% PEMS Mean deviation 71% COPERT Results from Ispra Milano route (Rural + Highway)

14 RESULTS. PEMS vs. COPERT EFS Plots generated by INCERT for easy comparison of results g/k km NOx 3 PEMS 2.5 2 15 1.5 1 COPERT ES Poly. (PEMS).5 2 4 6 8 1 12 14 Speed [km] NOx emissions (1-km split)

15 DISCUSSION. PEMS vs. COPERT EFs Distance splits have little influence upon results CO emissions: COPERT and PEMS EFs present similar trends. PEMS values up to 2% higher than COPERT, yet well below emission limits HC emissions remain generally low. Fuel consumption lower compared to the COPERT values. Modern low engine capacity Diesel vehicles not fully covered by model. NO X emissions approx. 6% higher than COPERT values. This increase may be attributed to real-world (higher load) operation. Both COPERT and PEMS values lie above current emission limits

16 CONCLUSIONS 1 Good agreement between PEMS data and ADVISOR results (esp. FC). Vehicle simulation with the use of real-life data is a promising approach for the production of Emission Factors, by simulating any cycle/condition needed Other more advanced and updated vehicle simulation models should be tested in the future like CRUISE, AUTONOMIE (ex-psat)

17 CONCLUSIONS 2 Good agreement between PEMS derived and COPERT EF values. In the case of NO X, both values are well above the applicable emission limit (up to 3.8 times higher; PEMS results are worse than corresponding Euro 1 EF!) PEMS flags the issue of excessive NO X emissions of modern diesel vehicles when driven outside regulated test cycles

18 GENERAL CONCLUSIONS PEMS can characterize the emissions of regulated pollutants of light duty vehicles over a full range of real-world driving states: idling, cruising, uphill & downhill roads. Still not as accurate or comprehensive as testing in permanent labs PEMS measurement campaigns in Europe to date cover only a small number of vehicles; insufficient for the derivation of technology specific EFs, best used for validating existing EFs or making relative comparisons

19 Thank you for your attention Contact: t panagiota.dilara@jrc.ec.europa.eu