Elsevier

Journal of Cleaner Production

Volume 108, Part A, 1 December 2015, Pages 1168-1176
Journal of Cleaner Production

A coherent life cycle assessment of a range of lightweighting strategies for compact vehicles

https://doi.org/10.1016/j.jclepro.2015.05.100Get rights and content

Abstract

A complete and fully consistent LCA-based comparison of a range of lightweighting options for compact passenger vehicles is presented and discussed, using advanced lightweight materials (Al, Mg and carbon fibre composites), and including all life cycle stages and a number of alternative end-of-life scenarios. Results underline the importance of expanding the analysis beyond the use phase, and point to maximum achievable reductions of environmental impact of approximately 7% in most impact categories. In particular, lightweighting strategies based on the use of aluminium were found to be the most robust and consistent in terms of reducing the environmental impacts (with the notable exception of a relatively high potential toxicity). The benefits of using magnesium instead appear to be less clear-cut, and strongly depend on achieving the complete phase-out of SF6 in the metal production process, as well as the establishment of a separate closed-loop recycling scheme. Finally, the use of carbon fibre composites leads to similar environmental benefits to those achieved by using Al, albeit generally at a higher economic cost.

Introduction

The automotive industry's current position as a significant contributor to global environmental impact, and more specifically greenhouse gas emissions, is clearly unsustainable, and also less and less acceptable to modern environmentally aware societies. In the United Kingdom, for instance, transportation currently accounts for approximately a quarter of the total direct greenhouse gas emissions in the country (UK Government, 2014a). Cars have also been shown to be the most carbon-intensive means of personal transportation on land (Borken-Kleefeld et al., 2013). Besides turning to more efficient and environmentally friendly power train options, one of the most effective strategies to cut down on a whole range of environmental impacts associated to the use phase of a vehicle is, unquestionably, to reduce its kerb mass (US-DoE, 2015, Koffler and Rhode-Brandenburger, 2010), and indeed a range of lightweighting strategies are currently being considered and tested by many car manufacturers in Europe and elsewhere (e.g. Audi, 2013, BMW, 2015, Ford, 2014, JLR, 2015). However, the production and processing of lightweight material parts often entails higher specific environmental burdens compared to the predominantly steel parts that they replace (Liu and Müller, 2012, IMA, 2013, Das, 2011), and it is therefore essential to expand the scope of the analysis beyond the use phase and include all other stages of a vehicle's life cycle, lest the advantages afforded by vehicle lightweighting be overestimated. Life cycle assessment (LCA) is thus arguably the most appropriate approach for the evaluation of the overall environmental consequences of vehicle improvement strategies based on the use of advanced lightweight materials.

A large number of individual LCA studies are available in the literature in which specific lightweighting strategies have been discussed and analysed (EAA, 2013, Das, 2014, Tharumarajah and Koltum, 2007, Du et al., 2010, Duflou et al., 2009, Koffler, 2014, Schmidt et al., 2004, Mayyas et al., 2012, Kim et al., 2010). However, the lack of consistency in terms of scope, assumptions, boundary conditions and impact metrics render any comparison across different studies fraught with difficulty and potentially misleading. An ex-post harmonization effort is undoubtedly helpful in removing unnecessary inconsistencies and allowing some general inferences to be made (Kim and Wallington, 2013); yet, ultimately, complete and fully coherent comparisons of alternative lightweighting strategies are still few and far between. This paper aims to fill this void by discussing the results of a new comparative LCA of a range of vehicle lightweighting options using advanced lightweight materials (aluminium, magnesium and carbon fibre reinforced polymers), including all life cycle stages of the entire vehicle and considering alternative end-of-life (EoL) scenarios. All options and scenarios are based on the same fundamental model and share the same underlying assumptions and system boundary, thereby ensuring strict methodological consistency across the board and allowing robust and scientifically sound conclusions to be drawn.

Section snippets

Materials and methods

This section includes: a concise introduction to the adopted methodology; the illustration of the unified LCA model underlying the full range of analysed lightweighting strategies, including a discussion of all relevant assumptions and key parameters; and a detailed examination of the lightweighting strategies themselves.

Results and discussion

Detailed results for the full range of analysed strategies and scenarios, including three variations of driving cycle in the use phase by way of sensitivity analysis, are presented in Fig. 1, Fig. 2, Fig. 3, Fig. 4. These figures are all presented in a similar format whereby the environmental impacts are broken down along the horizontal axis into five life-cycle phases: materials (including extraction, processing and delivery), manufacturing, use, maintenance and end-of-life, followed by a

Conclusions

Overall, the use of Al parts in lightweighting strategy n. 2 has produced the most consistent set of results, not requiring any ad hoc optimistic assumptions in order to deliver them and showing the least dramatic dependence on the EoL scenarios. The only remarkable exception to this general trend is represented by the HTP results, which need careful consideration, and which indicate that a ‘simple’ clear-cut answer in terms of “which strategy is best” may actually not exist, when different

Acknowledgements

The authors wish to acknowledge the financial support provided by the UK Engineering and Physical Sciences Research Council, under research grant EP/I038616/1 “Towards Affordable, Closed-Loop Recyclable Future Low Carbon Vehicle Structures – TARF-LCV”. Thanks are also due to Charles Kingdom, formerly at Coventry University, for his collaboration in the definition of the body part masses for the benchmark vehicle.

References (67)

  • A. Bala Gala et al.

    Introducing a new method for calculating the environmental credits of end-of-life material recovery in attributional LCA

    Int. J. Life Cycle Assess.

    (2015)
  • BMW, 2015....
  • J. Borken-Kleefeld et al.

    Mode, load, and specific Climate impact from passenger trips

    Environ. Sci. Technol.

    (2013)
  • M. Classen et al.

    Life Cycle Inventories of Metals

    (2009)
  • CML

    CML Life Cycle Impact Assessment Method (CML-IA)

    (2013)
  • S. Das

    Life cycle assessment of carbon fiber-reinforced polymer composites

    Int. J. Life Cycle Assess.

    (2011)
  • S. Das

    Life cycle energy and environmental assessment of aluminum-intensive vehicle design

    SAE Int. J. Mat. Manuf.

    (2014)
  • DG Environment

    Service Contract to Assess the Feasibility of Options to Reduce Emissions of SF6 from the EU Non-ferrous Metal Industry and Analyse Their Potential Impacts

    (2009)
  • Directive 2000/53/EC of the European Parliament and of the Council, 2006;...
  • R. Dones et al.

    Life cycle inventories for the nuclear and natural gas energy systems, and examples of uncertainty analysis

    Int. J. Life Cycle Assess.

    (2005)
  • European Aluminium Association (EAA)

    Aluminium in Cars. Unlocking the Light-weighting Potential

    (2013)
  • L. Eckstein et al.

    Benchmarking of the electric vehicle Mitsubishi i-MiEV

    ATZ Autotech.

    (2011)
  • Ecoinvent Centre for Life Cycle inventories (Ecoinvent)

    Ecoinvent LCI Database Version 2.2

    (2010)
  • Ecometrica

    Consequential and Attributional Approaches to LCA: a Guide to Policy Makers with Specific Reference to Greenhouse Gas LCA of Biofuels

    (2008)
  • S. Ehrenberger et al.

    Life-cycle assessment of the recycling of magnesium vehicle components

    JOM

    (2013)
  • X. Fang et al.

    Sulfur hexafluoride (SF6) emission estimates for China: an inventory for 1990-2010 and a Projection to 2020

    Environ. Sci. Technol.

    (2013)
  • X. Fang et al.

    Sulfur hexafluoride (SF6) emissions in East Asia determined by inverse modelling

    Atmos. Chem. Phys. Discuss

    (2013)
  • Ford, 2014....
  • L. Gaines et al.

    Operation of an Aluminum-intensive Vehicle: Report on a Six Year Project

    (2002)
  • Gossan Resources

    Lowering of CO2 Emission for Magnesium Production by Gossan-Zuliani Process

    (2012)
  • R. Heijungs et al.

    A review of approaches to treat uncertainty in LCA

  • M.A.J. Huijberts

    Application of uncertainty and variability in LCA. Part I. A general framework for the analysis of uncertainty and variability in life cycle assessment

    Int. J. Life Cycle Assess.

    (1998)
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