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Development of a new tank-to-wheels methodology for energy use and green house gas emissions analysis based on vehicle fleet modeling

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Abstract

Background, aim and scope

Tank-to-Wheels (TtW) makes the largest contribution to the total Well-to-Wheels (WtW) energy consumption and greenhouse gas (GHG) emissions from fossil-derived transportation fuels. The most commonly adopted TtW methodologies to obtain vehicle energy consumption, energy efficiency, and GHG emissions used to date all have significant limitations. A new TtW methodology, which combines micro-scale virtual vehicle simulation with macro-scale fleet modeling, is proposed in this paper. The models capabilities are demonstrated using a case study based on data from the passenger car sector in Great Britain.

Methods

A simplified internal combustion engine model was developed in-house to simulate engine behaviors across a wide range of engine capacities and technologies. Vehicle simulation was then carried out using the efficiency map output by the simplified engine model for any given gasoline or diesel engine; the simulation was validated for 37 vehicles available on the UK market in terms of their vehicle-certification fuel consumption, with a discrepancy generally within 3%. Real-world fleet and driving data from the Great Britain’s car fleet was extracted from the Transport Statistics Great Britain (TSGB) database between 2001 and 2007TSGB 2001–2007. A virtual fleet was constructed with the validated virtual vehicles to represent the real-world passenger car fleet in terms of its composition and operating characteristics. This fleet model was shown to match the real-world fleet-averaged fuel consumption within 3% for the gasoline fleet and within 6% for the diesel fleet. Finally, several scenarios were analyzed using the validated fleet model, covering a projection for 2008, driving pattern, lubrication, and fuel. The vehicle-to-vehicle variation was found to be significant in some scenarios, indicating that a fleet-based methodology would be more rigorous and flexible.

Discussion

Energy consumption and CO2 emission figures from previous, well-recognized Europe-oriented studies (e.g., the 2008 JRC/EUCAR/CONCAWE study) were significantly lower than the TSGB real-world results based on the new TtW methodology. It is apparent that using a single vehicle to represent the whole fleet could be misleading; in particular, the relative energy efficiency and CO2 emission of diesel over gasoline cars might follow a different trend with time for the real-world fleet from that shown in previous studies.

Conclusions

Future WtW studies can benefit from the modeling toolset and methodology reported herein in a number of ways:

  • TtW analysis can be carried out

  • thoroughly—on a fleet basis

  • independently—involving less proprietary information

  • impartially—not concentrating on a specific vehicle model

  • and flexibly—allowing detailed analysis of physics, chemistry, and vehicle component performance.

  • When comparing different WtW energy pathways, e.g., gasoline vs. diesel passenger cars or natural gas vs. bio-diesel fuelled busses, the absolute aggregate fleet impact can be investigated—conclusions based on a single vehicle may overlook vehicle-to-vehicle variations and potentially mislead policy making.

  • Using the virtual fleet database as a platform, a large number of scenarios can be analyzed and detailed impact of fuels properties, vehicle technologies and driving patterns on WtW results investigated. The models will evolve in time together with the researchers’ knowledge base and data base.

Recommendations and perspectives

The virtual engine/vehicle/fleet model developed in this work can readily be expanded and upgraded in the future, in terms of model details, coverage, and data quality. The methodology itself is generically applicable to any defined fleet (passenger cars, commercial vehicles, etc.) with any operating characteristics at any given timeframe from any geographic region. Various subjects and their implications for fleet energy consumption and GHG emissions could be studied including, but not restricted to, the following:

  • Fuels—injector/valve cleanliness, anti-knock properties, dieselization, bio-components, gaseous fuels etc.

  • Engine/vehicle technology—friction and weight reduction, advanced combustion, hybridization etc.

  • Driving pattern—vehicle loading, gear-shifting schedule, tire maintenance, cold start, etc.

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Notes

  1. Primarily in two areas: (1) when comparing different energy pathways, e.g., gasoline vs. diesel passenger cars or natural gas vs. bio-diesel fuelled busses and (2) when studying different vehicle fleets, the compositions of which are significantly different.

  2. Combustion phasing is typically denoted as CA50, the crank angle position during the engine cycle when 50% of the fuel energy is released. The optimum CA50 for a gasoline engine is around 7 degrees after top dead center (TDC), which corresponds to an optimum spark timing for a given engine operating condition, commonly known as the minimum spark advance for best torque (MBT).

  3. There are many other factors that would account for the performance difference between a cold and a hot engine, such as heat transfer, transmission losses, the control strategies of the engine management system (EMS) to light off the exhaust catalyst etc. Modeling these effects would require a much more thorough and detailed approach than the one adopted thus far, which is beyond the scope of this work.

  4. Advanced Vehicle Simulator (ADVISOR), originally developed by the National Renewable Energy Laboratory (NREL), is a vehicle simulation software tool. Versions of ADVISOR until 2002 were based on open-source MATLAB code and publicly available. This work used the latest publicly available version, ADVISOR 2002.

  5. Typically, the accessory load required to drive the coolant and oil pump would have been accounted for in the engine model.

  6. The combustion efficiency of a typical PFI gasoline engine is between 90% and 95% (Heywood 1988), i.e., 5–10% of the total energy available in the fuel would escape the engine primarily in the form of CO, unburned hydrocarbons (HC) and soot. These exhaust emissions also have carbon content which, if ignored, would distort the CO2 calculation based on the fuel consumption and the fuel’s carbon weight fraction, although under normal conditions, the after-treatment system of a modern vehicle would typically convert the bulk of the exhaust emissions to CO2.

  7. As of 2007, conventional gasoline and diesel cars accounted for 99.7% of the total passenger car fleet in Great Britain.

  8. The hybrid electric model, Toyota Prius, was excluded, because even with the fast growth of hybrid vehicles seen in recent years, the percentage of hybrid vehicles in the whole passenger car fleet in 2007 in Great Britain was still insignificant at only ~0.1%.

  9. The real-world average traffic speed would be a value between the peak and off-peak figures but not available, as the number of vehicles and kilometers traveled during peak and off-peak time were unknown.

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Acknowledgments

The authors wish to thank their colleagues from the Greenhouse Gas Intensity Analysis Team at Shell Global Solutions for their efforts and useful remarks in reviewing this paper.

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Correspondence to Hongrui Ma.

Additional information

The Tank-to-Wheels analysis referred to in this paper differs from a typical life cycle assessment in that this paper only attempts to address in-use vehicle fuel consumption and CO2 emission, i.e., the production, dismantling, and final disposal of vehicles is not taken into account.

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Ma, H., Riera-Palou, X. & Harrison, A. Development of a new tank-to-wheels methodology for energy use and green house gas emissions analysis based on vehicle fleet modeling. Int J Life Cycle Assess 16, 285–296 (2011). https://doi.org/10.1007/s11367-011-0268-8

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