With the use of electric vehicles on the rise, there's a lot of buzz about how environmentally friendly they are. While operational impacts are low compared to vehicles powered by internal combustion engines (ICEs), a closer look at all the production inputs, specifically the batteries, reveals a different side.
- LCA of Lithium-Ion Batteries: Key Facts at a Glance
- Possibilities and Constraints in Life Cycle Assessments of Lithium-Ion Batteries
- Lithium-Ion Batteries and the Rise of E-Vehicles
- Are Electric Vehicles Greener?
- Environmental Impacts of Lithium-Ion Batteries – A Major Factor in LCAs for E-Vehicles
- The EU Battery Regulation and LCA Requirements
- From Research to Reality: The Live LCA Approach
- Frequently Asked Questions
LCA of Lithium-Ion Batteries: Key Facts at a Glance
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Battery production accounts for 10–35% of an EV's total greenhouse gas emissions – the exact share depends heavily on the electricity mix used during manufacturing.
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BEVs generally outperform ICE vehicles in climate impact (GWP), but score worse in categories like ecological scarcity and eutrophication due to the demand for battery materials.
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The most critical life cycle phases for lithium-ion batteries are production (energy use) and end-of-life (recycling) – both carry significant environmental trade-offs.
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Recycling is not always the optimal solution: beyond a certain processing depth, the energy input may outweigh the environmental benefit – unless recovering rare materials is the priority.
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The EU Battery Regulation (2023/1542) mandates LCA-based carbon footprint declarations for EV batteries from February 2025, and digital battery passports from February 2027.
Possibilities and Constraints in Life Cycle Assessments of Lithium-Ion Batteries
This was the talk presented by Andreas Genest, sustainability consultant at IPOINT, at the Batterie Forum Deutschland in Berlin in January 2019. The 3-day conference with 350 attendees from politics, science, and economics focused on many aspects of lithium-ion batteries, from manufacturing and sourcing of raw materials, through the newest scientific insights, to the batteries' increasing use in logistics and e-mobility.
Attention was given mainly to the LCA of batteries in the field of electro-mobility, one of the fastest growing sectors for battery use. Genest presented various LCA studies of lithium-ion batteries and cast light on why their results often conflict.
Lithium-Ion Batteries and the Rise of E-Vehicles
Global EV adoption has accelerated dramatically since 2019. According to the International Energy Agency (IEA), over 17 million electric vehicles were sold worldwide in 2024 alone, and demand for lithium-ion batteries continues to grow in lockstep. So just how much impact does battery production have on the overall Life Cycle Assessment (LCA) of electric vehicles?
A commonly held belief is that while e-vehicles are greener to operate than vehicles with ICEs, their overall carbon emissions are simply shifted from the use-phase (less) to the production phase (more). According to LCA consultant Andreas Genest, that statement is mostly true – but also suggests a much more complex question.
"It is important to look closely at what exactly an LCA is focused on," Genest points out. "With so many different parameters to examine, you can end up with a wide range of results." When analyzing the life cycle of an e-vehicle, one should look at the entire process, from production of the vehicle, including all upstream chains, through its use phase, and, eventually, to its end-of-life processes.
Are Electric Vehicles Greener?
A commonly asked question is which vehicle type is more environmentally friendly: e-vehicles or those with "traditional" ICEs? When just taking the greenhouse warming potential (GWP) into account – a hot-button issue right now –, gas and diesel powered vehicles have the highest GHG emissions, followed by hybrid electric (HEV), plug-in hybrid electric (PHEV), and finally straight battery driven e-vehicles (BEV), which tend to have the lowest GWP.
But comparing only the GWP of the various vehicle types is not enough. As Genest shows, concentrating on GWP only takes climate impact into account while ignoring other potential environmental impacts, thus limiting the scope of the LCA. When including other environmental parameters a different picture emerges: while BEVs do better relative to GWP, they actually do worse in categories such as 'ecological scarcity' or 'eutrophication', due to demand for certain materials used in battery production.
A look at the bigger picture reveals that BEVs have a tendency to be more environmentally friendly than ICE-vehicles, but certainly do not have great scores in all impact categories across the board.
The electricity mix plays a particularly decisive role here. A BEV manufactured and charged in a country with a high share of renewable energy – such as Norway – can have a lifetime carbon footprint several times lower than the same vehicle operated on a coal-heavy grid. This is why geography and energy policy are inseparable from any meaningful lithium-ion battery LCA.
This also explains why we see a fairly wide range of results from various LCA studies of lithium-ion batteries: outcomes depend on the assumptions underlying each LCA and which impact categories the analysis chose to emphasize. "That's why comparison among LCAs is still extremely difficult – each study depends on too many variables," Andreas Genest sums up. Studies even show large discrepancies when estimating the share of battery production in the overall GHG emissions of e-vehicles, ranging from 10% to 35%.
Environmental Impacts of Lithium-Ion Batteries – A Major Factor in LCAs for E-Vehicles
It's worthwhile to take a closer look at what exactly the environmental impacts of batteries are. By far the most critical phases in a battery's life cycle are production (especially energy use) and recycling, an increasingly important issue.
The Sankey diagram below illustrates material and energy flows during the battery recycling process, showing the energy needed for various separation steps as well as the recovered material streams. The first recycling phase alone – disassembly – yields a large quantity of copper, steel, and aluminum, recouping nearly 50% of all materials. Every additional step yields additional material, but also calls for an increasing energy input per unit.
The question is: at which point does the energy input overwhelm the additional gains? Analysis of the recycling process should take a variety of impact categories into consideration, including the "avoided impact" of using recovered versus raw material.
So recycling may not always be the best solution. At some point, depending on your goals, you cross the cost-benefit threshold and the decision may no longer be cut and dry. If taken from a strict climate impact point of view, further recycling may not make any sense, but it may well do so if you're focused on reclaiming certain rare materials.
In the end, it's difficult to use LCAs to reach general conclusions: each particular study's underlying assumptions and choice of impact categories make a difference. However, LCA is a great tool to look at a specific set of parameters and provide specific recommendations for the most favorable options among those parameters. As Andreas Genest sees it, you should always keep the big picture in mind.
The EU Battery Regulation and LCA Requirements
Since the Batterie Forum Deutschland talk in 2019, the regulatory landscape for lithium-ion batteries has changed fundamentally. The EU Battery Regulation (Regulation (EU) 2023/1542) entered into force on 17 August 2023 and introduces binding lifecycle requirements across the entire battery value chain.
For manufacturers and supply chain managers, three LCA-related obligations stand out:
First, from February 2025, manufacturers must calculate and declare the carbon footprint for each EV battery model per manufacturing plant. This declaration must cover all relevant life cycle stages – from raw material extraction and cell production to assembly, distribution, and end-of-life – and must be independently verified by a third party.
Second, from August 2026, batteries must be classified into carbon footprint performance classes, creating market incentives to reduce lifecycle emissions.
Third, from February 2027, all EV and industrial batteries above 2 kWh placed on the EU market must carry a digital battery passport, accessible via QR code. This passport centralizes lifecycle data – including carbon footprint, recycled content, material composition, and durability metrics – in a standardized, machine-readable format.
These requirements make LCA no longer a voluntary sustainability tool for battery manufacturers, but a legal compliance obligation. Companies that have not yet established structured LCA processes and data collection systems face growing market access risk.
From Research to Reality: The Live LCA Approach
After being confronted with the difficulty of comparing the varying results of different LCAs on lithium-ion batteries, the University of Graz and IPOINT teamed up to investigate the matter and conduct their own studies.
In parallel, IPOINT developed the Live LCA approach in collaboration with TU Braunschweig's Battery Lab (BLB). The project combined Life Cycle Assessment (LCA) with Material Flow Cost Accounting (MFCA), using real-time production data – energy consumption, material use, and waste volumes – to calculate environmental impacts and costs dynamically, for every product and every process step.
The project has since been completed. Its core methodology – real-time, automated LCA powered by live production data and the LCA Software Umberto – now informs IPOINT's broader approach to automated life cycle assessment.
The results of this research feed directly into IPOINT Product Sustainability, which allows companies to automate LCA creation across entire product families, integrate environmental data into procurement and product development, and meet the lifecycle reporting requirements of the EU Battery Regulation and beyond.
For anyone interested in the full project documentation, details are available on the Live LCA project page.
Frequently Asked Questions
What is the carbon footprint of a lithium-ion battery?
Studies show GWP values ranging from roughly 60 to 200 kg CO₂-eq per kWh of battery capacity. Battery production accounts for 10–35% of an EV's total lifetime greenhouse gas emissions, with the electricity mix used in manufacturing being the single biggest variable.
What are the main environmental impacts of lithium-ion battery production?
The most significant environmental hotspots are manufacturing (driven by energy-intensive processes and the extraction of lithium, cobalt, and nickel) and end-of-life processing. Beyond GWP, batteries also score poorly in categories such as eutrophication and ecological scarcity.
How does the electricity mix affect the LCA results of a lithium-ion battery?
The carbon intensity of the grid used in both manufacturing and the vehicle's use phase has a decisive effect on overall GWP results. A BEV operated on renewables-heavy electricity can have a lifetime footprint several times lower than one running on coal-generated power.
What is the difference between a cradle-to-gate and a cradle-to-grave LCA for batteries?
A cradle-to-gate LCA covers environmental impacts from raw material extraction through manufacturing only. A cradle-to-grave LCA extends the scope to include the use phase and end-of-life processing, delivering a complete picture of a battery's total environmental footprint.
How does recycling reduce the environmental impact of lithium-ion batteries?
Recycling recovers valuable materials such as lithium, cobalt, copper, and aluminum, reducing the need for virgin resource extraction. However, each additional processing step requires more energy input, so the net environmental benefit depends on which impact categories are prioritized.
What does the EU Battery Regulation require for LCA?
Under Regulation (EU) 2023/1542, manufacturers must calculate and declare a carbon footprint per EV battery model and manufacturing batch using an approved LCA methodology – mandatory from February 2025. From February 2027, this and other lifecycle data must be stored in a digital battery passport linked to each battery via QR code.
