Vehicle programs must balance performance, safety, fuel efficiency, affordability and the environment, while maintaining designs that are appealing to customers. Use of higher strength steels allows for a reduction in the sheet metal thickness and in turn vehicle mass. The increased ductility offered by Advanced High Strength Steels facilitates part consolidation also contributing to lower weight and manufacturing cost while providing an efficient way to increase component and vehicle stiffness.
Low-density materials like aluminium, magnesium and composites have widespread use in luxury class vehicles, where amenities, comfort, and speed are prioritized over affordability. Penalties for not meeting fuel economy and emissions mandates are easily absorbed in the sales price.
On mass-market vehicles, where per-unit emissions are multiplied over higher volumes, automakers target selecting the most efficient way to achieve the lowest total emissions.
Compared with the limited number of low-ductility steels available decades ago, the lower density materials would have offered an easy but costly path to lightweighting. Back then, since there were not that many high-strength options, vehicle crashworthiness was improved by increasing thickness.
However, increasing metal strength allows for a thickness reduction while maintaining crash performance. The substantially higher strength steels available today have sufficient ductility to form complex stampings from sheets thin enough to be weight-competitive with components formed from lower-density materials that must be made from higher thickness to have comparable stiffness.
The spectrum of steel grades commercially available today have:
- higher strength, greatly contributing to the crash-energy management approach.
- higher ductility that allows for additional shape to be formed into the component, also increasing stiffness and potentially allowing for part consolidation,
- higher modulus than aluminium or magnesium that inherently leads to a stiffer component.
Recent years have seen an increased global sensitivity to tailpipe emissions, with Figure 1 highlighting regulations for passenger cars in different countries and regions. Many major markets have committed to fleet average emissions below 100 g CO2/km, and we’re on a negotiated global journey to Net Zero Emissions by 2050.
Figure 1: Passenger car emissions and fuel consumption targets, normalized to New European Driving Cycle I-2
The problem with the current regulation of automotive greenhouse gas (GHG) emissions is their focus solely on tailpipe emissions, produced from fuel combustion during vehicle use. The regulations ignore other significant sources of GHG emissions in the vehicle’s life cycle including vehicle production (including the emissions from material production) and treatment of the vehicle at the end of its useful life. This omission comes with serious risks. An unintended effect of this approach is an over-emphasis on vehicle lightweighting. While lightweighting can be an effective tool to reduce vehicle emissions, it must be done with a holistic knowledge of the implications related to the total vehicle life cycle GHG emissions.
Reducing vehicle mass decreases fuel consumption, which also reduces tailpipe emissions. This may, or may not, offset the increased production emissions from material production of the lower density materials. One possibility is that the reduction of emissions in the use phase results in overall lower emissions, but because of the trade-off between the use phase and production emissions, the result is not as low as predicted by a tailpipe-only metric – some of the use-phase savings is offset by the increased production emissions. Also possible is where the use phase savings and the production phase increase are approximately equal, resulting in no net savings at all. In the other extreme, the production emissions outweigh the use phase savings, resulting in the unintended consequences of an increase in the overall emissions. This last scenario is the very opposite of what government policy intends, but happens regularly when vehicles constructed with low density materials don’t reach their intended vehicle life.
One of the perceived advantages to using materials of lower density is the expectation that they will result in lower GHG emissions. To illustrate why this is not true, consider the emissions from the material production stage of a typical automotive component. The mid-range GHG values for each material are taken from the above chart and then multiplied by the projected material weight that is required to make a hypothetical component. (The actual mass for an equivalent component varies based on the material used and the component design.)
Figure 2: Material average GHG emissions from primary production, in kg CO2e per kg of material.W-40
Furthermore, low-density materials create an offsetting emissions problem, as production of these materials is GHG-intensive, and therefore costly to the environment. The production of these alternative materials can produce 7 to 20 times more emissions than steel, as shown in Figure 2.
Figure 3: Material GHG emissions in kg CO2e for functionally equivalent generic components.W-40
Figure 3 shows that the use of lower density materials does not necessarily mean a reduction in greenhouse gas emissions. Although less weight is required for some alternative materials to achieve the same component functional performance, the emissions from the material production stage can still be many times higher than those of the baseline component. Therefore, the increase in material production emissions may outweigh the reduction in use phase emissions even after factoring in the mass savings benefit.
Vehicles are transitioning to alternative-energy powertrains and away from those based on fossil fuels. In these new-energy vehicles powered entirely by renewable electricity, emissions from the vehicle production stage, which includes material production, could account for as much as 95% of total emissions. In this scenario, the usage phase accounts for a mere 5% of the lifetime emissions. This is the opposite of what is found with vehicles having conventional Internal Combustion Engine (ICE) powertrains. For this reason, use of low GHG material such as steel becomes even more important as the world moves towards a renewable future.
Life Cycle Assessment
Life Cycle Assessment (LCA) is an environmental accounting methodology that considers a product’s entire life cycle, with cradle-to-grave assessments typically including impacts from raw material extraction and production (manufacturing phase), through its useful life (use phase), and to the end-of-life disposal or recycling of the product (end-of-life phase). It also takes into account the full life cycle of energy sources used across all lifecycle phases. This process illuminates any potential trade-offs between phases and highlights the true environmental impact, beyond the focus on tailpipe-only emissions.
Recent years have seen a greater adoption of using Life Cycle Assessment to assess a vehicle’s true environmental impact rather than solely focusing on what comes out of the tailpipe. LCA accounts for the total emissions including those coming from material production, vehicle use, and the chosen end-of-life path. The principles, framework, requirements and guidelines for Life Cycle Assessment are laid out in international standards ISO 14040I-3 and ISO 14044I-4.
Most major OEMs utilize some form of life cycle thinking or LCA, recognizing its importance and effectiveness in product and process design. Material producers also accept and use LCA. Together with many of their member companies, the trade associations of the steel, aluminium, and plastics industries are among the most active members of the global LCA community.
The European Union requires accounting for embedded lifecycle emissions. Following a phase-in period, there will be monetary penalties assessed against companies not providing this information. These requirements will drive OEMs to demand pertinent details from all of their material suppliers.
Environmental policies target achieving a total net reduction in emissions, including GHG (measured in carbon dioxide equivalents, or CO2e, that is a measure of all greenhouse gases attributable to a product that affect global warming potential. Thus, CO2e includes gases other than CO2.
Properly applied, LCA enables automakers to ensure that improvements in one phase are not offset by worse performance in another phase. This assessment of potential trade-offs is critical to environmental improvement. For example, if the increase in production emissions of a lightweight material is greater than the decrease in use phase emissions, vehicle light-weighting in this manner counter-productively increases total emissions.
LCA can be used to assess a broad array of environmental impacts beyond the global warming potential of greenhouse gases, including acidification, ecotoxicity, and ozone depletion.
The Path To Net Zero Emissions
Fully autonomous Mobility as a Service vehicles such as the Steel E-Motive concept have the potential to address the ongoing and future requirements for decarbonisation of passenger transportation. Figure 4 shows the emissions walk-down beginning with a present-day C-sized BEV operating as a taxi.
Near term, a 60% reduction in Life Cycle emissions can be realized by an increased use of reduced CO2 steel and decarbonized battery production, along with an increased use of ride-sharing. Through 2035, as all available emissions reduction strategies are deployed – including autonomous MaaS vehicles with increased occupancy and extended vehicle and battery lives – an 86% reduction in emissions from a 2022 baseline is feasible.
Achieving Net Zero post 2035 requires carbon capture technologies, 100% renewable grid supplies, and carbon offsets or credits.
Each of these steps are described in detail within the Steel E-Motive Engineering Report.
Figure 4: The Path to Net Zero Vehicle Emissions
Blog
Vehicle LCA encompasses all phases of the product cycle, from raw material extraction to end of life recycling and disposal.
Life Cycle Assessment (LCA) continues to gain traction as the preferred method for assessing the environmental impacts of a product, and we are seeing more and more automotive LCA studies, and claims or conclusions based on LCA, being published. Here are five things to look for in an automotive LCA study. This is not an exhaustive list – there are many more things that need to be considered when conducting an LCA (the international standard that lays out requirements and guidelines for LCA, ISO 14044, lists 14). For a detailed look at LCA, I recommend Environmental Life Cycle Assessment, an excellent textbook published by the American Center for Life Cycle Assessment (ACLCA).
1. Is the study comparing “apples to apples”?
This can sometimes be a bit of a challenge in an automotive LCA, as cars are complex products made up of many systems and sub-systems, with supply chains that reach around the world. It is easy to lose sight of apparently subtle differences.
One such difference arises in material comparisons of an existing product and one at the design stage. Before making choices about which material has the lower impact, it is important to decide if this is a fair comparison. Have both designs been fully optimized? Does the theoretical design meet all the requirements (e.g. crash, NVH) of an existing design that has gone through all the additional steps necessary to get to production?
Functional equivalence is another important factor to consider. For example, it would be inappropriate to compare the “body” of a vehicle with a body-on-frame design with the “body” of a vehicle with a unibody design. Though both systems are casually referred to as the “body”, their functional requirements are very different. Similarly, when comparing an assembly of stamped parts to a single casting, it is important to include all the stamped parts that are required to meet the same functional performance as the cast part.
2. Has the best and most appropriate data been used?
As with any assessment tool, data is key, and there are many factors that can help determine which is the most appropriate to be used in a particular study. There are ten of these factors listed in ISO 14044, but I will only talk about three of them here. If you want more detail, Guidance on Data Quality Assessment for Life Cycle Inventory Data, published by USEPA’s National Risk Management Research Laboratory is a great resource.
Temporal scope – the temporal scope of the data describes when the data was collected, as well as the time period to which the data applies. An often-used rule of thumb is that the data used for the study should be no more than five years old. The goal is to use either data that reflects the time period when the product under study was actually produced or the most recent data that captures the current state of the art (these may of course be the same thing).
Geographical scope – the geographical scope of the data describes the location to which the data applies. This is critical, as the same process may have a very different impact profile in different locations. For example, primary aluminium made largely using electricity from hydropower in Canada will have a much different impact from primary aluminium made in China, where the electricity used comes almost entirely from coal. With automakers increasingly developing global platforms (i.e. using the same parts all over the world, as often as possible), it is important to consider how the results of an LCA might change if a product is produced in a region other than the one studied. The same is true when considering where a product is used. For example, the differences in electricity generation in Canada and China will greatly affect the impact of charging an electric vehicle.
Technological scope – the technological scope of the data describes the technology to which the data applies. Often the same product can be made from a variety of production pathways. Much like production in different regions, production via different pathways can result in much different impacts. An example of this is primary magnesium production. Magnesium produced via the Pidgeon process (a declining, but still-used method) can have a global warming impact more than 1.5 times higher than magnesium produced via the electrolytic method.
3. How sensitive are the results to changes in the choices made?
Because LCA involves choices about things like data and functional requirements (as well as a host of other parameter choices), it is important to understand what happens to the results if different choices are made or underlying conditions change. Inclusion of a sensitivity analysis of this kind allows us to evaluate the results of an LCA and look for areas that might require further study, perhaps by looking for more precise data. It could also affect decisions we might make based on the results. If the results of a study are very sensitive to the location in which the materials are made, we want to evaluate this if we are considering making the product in many different places.
4. What is the fundamental approach taken?
ISO 14040, which lays out the principles and framework for LCA, describes two fundamental approaches to LCA:
- one which assigns elementary flows and potential environmental impacts to a specific product system typically as an account of the history of the product, and
- one which studies the environmental consequences of possible (future) changes between alternative product systems.
It is important to consider which approach was used, and what the chosen approach means in terms of interpreting the results. In a very basic sense, the key lies in the words “history” and “future”. A study that considers the historical impact of a product (i.e. the impact of any product that has already been made) tells us about the impact of that particular product, but may be of limited use in making decisions about what the impact of that same product may be in the future. Studies of the potential future impact of a product, while necessary for decision making, are fraught with all the perils of predicting the future. Both approaches are valuable, and it is important to understand which approach was taken in order to make decisions about how to use the results of the study. The ILCD Handbook: General guide for Life Cycle Assessment, published by the Joint Research Center of the European Commission, provides guidance on when to use each approach in assessing the technological representativeness of LCI data.
5. How broadly can I apply the results?
It is often tempting to apply the results of a study more broadly than is justified. Given all the factors listed above (as well as the many others not included), it is critical that careful consideration be given when making decisions based on the results of automotive LCA studies in order to make sure that the scope of the study is in alignment with the scope of the decision. It is clearly inappropriate to make global decisions based on local studies, or to make future decisions based solely on past conditions. LCA is a valuable, well-developed tool for assessing environmental impacts, but we must be careful to use it appropriately.
The UCSB Automotive Energy and GHG Model, developed on behalf of WorldAutoSteel, is a publicly available, peer-reviewed tool for the assessment of automotive emissions on a life cycle basis. Version 5 of the UCSB Model can be downloaded for free at www.worldautosteel.org. At the UCSB Model page, you’ll find a video workshop at the end featuring Russ Balzer explaining the contents of the Model. A user guide is also available for download.
Does the subject of Life Cycle Assessment confuse you or would you like to learn more? There is a great free online course at our sister organization steeluniversity, “Introduction to LCA”, taught by Dr. Matthias Finkbeiner, head of the department of Sustainability Engineering at Technical University of Berlin, who introduces LCA methodology to analyse the environmental burdens of product and service systems. The course is fun and interactive, and you can finish it at your own pace.
Russ Balzer, LCACP, Technical Director, WorldAutoSteel and Phoenix Group
Russ Balzer is the LCA Technical Director at WorldAutoSteel and Phoenix Group. As Technical Director, Russ manages a variety of engineering projects, and has tactical and strategic responsibilities in WorldAutoSteel’s efforts to use and promote Life Cycle Assessment (LCA). Russ recently achieved LCACP certification and was recognized for his work in the field of LCA with the ACLCA’s Rising Star Award.
Blog
Life Cycle Assessment (LCA), and particularly vehicle product life cycle assessment, is a topic we are very passionate about here at WorldAutoSteel. So much so that we focus on LCA intensively for the entire month of October across all of our communications channels. Though it’s not an AHSS forming or joining topic, it is one that is critical to truly reducing vehicle emissions for future generations. Russ Balzer, Technical Director at WorldAutoSteel and our resident LCA professional, in this blog and the next, will talk about LCA, its importance, and the tools WorldAutoSteel has developed to provide environmental insight to design decision tradeoffs.
All over the world there are continuing and growing efforts to address transportation greenhouse gas (GHG) emissions, which remain a major unresolved issue. These efforts are intended to help the transportation sector make its contribution to global emissions reduction goals. Unfortunately, much of this effort is focused on reducing emissions only from the vehicle tailpipe, with no consideration of the other sources of emissions in that vehicle’s life. This is not an effective way to meet these goals. In fact, this approach could lead to the unintended consequence of increasing GHG emissions in some cases. Fortunately, there is a better way – life cycle assessment (LCA), a tool for looking at the environmental impact of a product across its entire life cycle (Figure 1).
Figure 1: Vehicle LCA encompasses all phases of the product cycle, from raw material extraction to end of life recycling and disposal.
Focusing solely on the tailpipe emissions means ignoring other significant sources of GHG emissions, such as vehicle production and emissions generated (or avoided) at the end of the vehicle’s useful life (see Figure 2 on Page 2). An example of this is that tailpipe-only thinking can put too much emphasis on lightweighting. Don’t get me wrong, lightweighting can be an important part of the solution. Three of the four main drivers of fuel consumption (and therefore tailpipe emissions) – rolling resistance, acceleration and gravity (as in climbing a hill) – are dependent on the vehicle’s mass. So we can see why vehicle lightweighting is an obvious choice. It is a direct way to reduce these power demands and achieve better fuel consumption and fewer tailpipe emissions. The problem with lightweighting arises when we are so focused on reducing a vehicle’s mass that we fail to consider the consequences to the vehicle’s overall emissions.
One of the potential consequences arises from the use of lower-density materials like aluminium, magnesium and even carbon fibre to replace steel in a vehicle. From a tailpipe perspective, this can seem like a good (if expensive) solution. Vehicle mass may be reduced, resulting in improved fuel consumption and fewer tailpipe emissions. Sadly, it is not that simple. These low-density materials come with an environmental cost in addition to their higher financial cost. This cost comes in the form of higher GHG emissions in the production of the material itself. On a global average basis, GHG emissions from aluminium production can be as much as eight times as high per kilogram of material as the GHG emissions from steel production. For carbon fibre and magnesium the difference in production GHG emissions is even greater. This means that, even though you may save tailpipe emissions with some applications of these low-density materials, there is always a trade-off of higher production emissions.
Figure 2: The difference between a regulatory focus that includes LCA and current tailpipe emissions.
In the best case, the reduction of emissions in the use phase does result in overall lower emissions, though, because of the trade-off between the tailpipe and production emissions, not as low as predicted by a tailpipe-only metric. Also possible is an intermediate case in which the use phase savings and the production phase increase are approximately equal, resulting in no net savings at all. In the worst case, the production emissions outweigh the use phase savings, resulting in the unintended consequence—higher overall emissions, the very opposite of what the regulation intends.
All three of these cases have two things in common. First, under a tailpipe-only regulation, we don’t know what the actual emissions are, because production emissions impacts are not being monitored. Second, because the low-density materials we are talking about are more expensive, all three of these cases come at a higher cost. So, we must ask ourselves: do we want to force automakers and consumers to pay more money without knowing the outcome? It’s time to consider another route to reducing emissions, and we believe that taking a life cycle approach is the correct route.
LCA assesses all the stages of a product’s life, from raw material extraction through production, use, and end of life processing. Though awareness of LCA has grown rapidly over the last 10-15 years, LCA methodology and practice have been developing since the early 1970s. Today, it is a mature assessment tool with global standards. Many car manufacturers are already using life cycle thinking and LCA, recognizing its importance and effectiveness in product and process design. LCA is equally accepted and used by material producers. In fact, together with many of their member companies, the trade associations of the steel, aluminium, and plastic industries are among the most active members of the global LCA community.
WorldAutoSteel has been directly involved with LCA since 2007, when we partnered with Dr. Roland Geyer of the University of California at Santa Barbara to develop an LCA tool for the assessment of material choices in passenger vehicles. The UCSB Automotive Materials Energy and Green House Gas (GHG) Comparison Model that Dr. Geyer developed on behalf of WorldAutoSteel is now in its fifth version and continues to be one of the most comprehensive publicly available vehicle LCA tools in the world.
The UCSB model is a full vehicle model assessing both GHG and energy effects of automotive material substitution over the entire life cycle of the vehicle.
Computation and parameter values are kept separate for maximum transparency and flexibility. This allowed the computational structure to be peer reviewed by members of the LCA community. The model calculates 27 main result values: three environmental indicators x three life cycle stages x three vehicles, as shown in Figure 3.
Figure 3: UCSB Model calculates 27 main result values.
The model has the flexibility to allow a multitude of different scenario evaluations, offering 14 structural material categories, 24 total material categories, adjustable material recycling methodology, a variety of biofuel and electricity pathways, as well as the powertrains, driving cycles and vehicle classes noted in Figure 4.
Figure 4: UCSB Model analysis options.
To maximize flexibility and transparency, all calculations are shown, and no parameter values are locked or hidden. This makes the UCSB Model an excellent tool for teaching LCA, particularly automotive LCA.
GHG emissions in the transport sector must be reduced to meet global emissions reduction goals. Lightweighting of passenger vehicles can be an important part of the emissions reduction solution in the transport sector, but only if lightweighting scenarios are viewed in the context of the overall vehicle emissions. Many companies inside and outside of the transport sector use Life Cycle Assessment, which considers environmental impacts from the whole of a vehicle’s life cycle, as their primary method to develop this overall view. The UCSB Automotive Energy and GHG Model, developed on behalf of WorldAutoSteel, is a publicly available, peer-reviewed tool for the assessment of automotive emissions on a life cycle basis. Version 5 of the UCSB Model can be downloaded for free at the WorldAutoSteel website here.
At the UCSB Model download page, you’ll find a video workshop featuring Russ Balzer explaining the contents of the Model. A user guide is also available for download.
Russ Balzer, Technical Director, WorldAutoSteel
Russ Balzer is the LCA Technical Director at WorldAutoSteel and Phoenix Group. As Technical Director, Russ manages a variety of engineering projects, and has tactical and strategic responsibilities in WorldAutoSteel’s efforts to use and promote Life Cycle Assessment (LCA). Russ recently achieved ACLCA LCACP certification and was recognized for his work in the field of LCA with the ACLCA’s Rising Star Award.
