Electrification
How Clean is the Nickel and Lithium in a Battery?
The following content is sponsored by Wood Mackenzie
How Clean is the Nickel and Lithium in a Battery?
The production of lithium (Li) and nickel (Ni), two key raw materials for batteries, can produce vastly different emissions profiles.
This graphic from Wood Mackenzie shows how nickel and lithium mining can significantly impact the environment, depending on the processes used for extraction.
Nickel Emissions Per Extraction Process
Nickel is a crucial metal in modern infrastructure and technology, with major uses in stainless steel and alloys. Nickel’s electrical conductivity also makes it ideal for facilitating current flow within battery cells.
Today, there are two major methods of nickel mining:
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From laterite deposits, which are predominantly found in tropical regions. This involves open-pit mining, where large amounts of soil and overburden need to be removed to access the nickel-rich ore.
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From sulphide ores, which involves underground or open-pit mining of ore deposits containing nickel sulphide minerals.
Although nickel laterites make up 70% of the world’s nickel reserves, magmatic sulphide deposits produced 60% of the world’s nickel over the last 60 years.
Compared to laterite extraction, sulphide mining typically emits fewer tonnes of CO2 per tonne of nickel equivalent as it involves less soil disturbance and has a smaller physical footprint:
Ore Type | Process | Product | Tonnes of CO2 per tonne of Ni equivalent |
---|---|---|---|
Sulphides | Electric / Flash Smelting | Refined Ni / Matte | 6 |
Laterite | High Pressure Acid Leach (HPAL) | Refined Ni / Mixed Sulpide Precipitate / Mixed Hydroxide Precipitate | 13.7 |
Laterite | Blast Furnace / RKEF | Nickel Pig Iron / Matte | 45.1 |
Nickel extraction from laterites can impose significant environmental impacts, such as deforestation, habitat destruction, and soil erosion.
Additionally, laterite ores often contain high levels of moisture, requiring energy-intensive drying processes to prepare them for further extraction. After extraction, the smelting of laterites requires a significant amount of energy, which is largely sourced from fossil fuels.
Although sulphide mining is cleaner, it poses other environmental challenges. The extraction and processing of sulphide ores can release sulphur compounds and heavy metals into the environment, potentially leading to acid mine drainage and contamination of water sources if not managed properly.
In addition, nickel sulphides are typically more expensive to mine due to their hard rock nature.
Lithium Emissions Per Extraction Process
Lithium is the major ingredient in rechargeable batteries found in phones, hybrid cars, electric bikes, and grid-scale storage systems.
Today, there are two major methods of lithium extraction:
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From brine, pumping lithium-rich brine from underground aquifers into evaporation ponds, where solar energy evaporates the water and concentrates the lithium content. The concentrated brine is then further processed to extract lithium carbonate or hydroxide.
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Hard rock mining, or extracting lithium from mineral ores (primarily spodumene) found in pegmatite deposits. Australia, the world’s leading producer of lithium (46.9%), extracts lithium directly from hard rock.
Brine extraction is typically employed in countries with salt flats, such as Chile, Argentina, and China. It is generally considered a lower-cost method, but it can have environmental impacts such as water usage, potential contamination of local water sources, and alteration of ecosystems.
The process, however, emits fewer tonnes of CO2 per tonne of lithium-carbonate-equivalent (LCE) than mining:
Source | Ore Type | Process | Tonnes of CO2 per tonne of LCE |
---|---|---|---|
Mineral | Spodumene | Mine | 9 |
Mineral | Petalite, lepidolite and others | Mine | 8 |
Brine | N/A | Extraction/Evaporation | 3 |
Mining involves drilling, blasting, and crushing the ore, followed by flotation to separate lithium-bearing minerals from other minerals. This type of extraction can have environmental impacts such as land disturbance, energy consumption, and the generation of waste rock and tailings.
Sustainable Production of Lithium and Nickel
Environmentally responsible practices in the extraction and processing of nickel and lithium are essential to ensure the sustainability of the battery supply chain.
This includes implementing stringent environmental regulations, promoting energy efficiency, reducing water consumption, and exploring cleaner technologies. Continued research and development efforts focused on improving extraction methods and minimizing environmental impacts are crucial.
Sign up to Wood Mackenzie’s Inside Track to learn more about the impact of an accelerated energy transition on mining and metals.
Electrification
Visualizing the Supply Deficit of Battery Minerals (2024-2034P)
A surplus of key metals is expected to shift to a major deficit within a decade.

Visualizing the Supply Deficit of Battery Minerals (2024-2034P)
The world currently produces a surplus of key battery minerals, but this is projected to shift to a significant deficit over the next 10 years.
This graphic illustrates this change, driven primarily by growing battery demand. The data comes exclusively from Benchmark Mineral Intelligence, as of November 2024.
Minerals in a Lithium-Ion Battery Cathode
Minerals make up the bulk of materials used to produce parts within the cell, ensuring the flow of electrical current:
- Lithium: Acts as the primary charge carrier, enabling energy storage and transfer within the battery.
- Cobalt: Stabilizes the cathode structure, improving battery lifespan and performance.
- Nickel: Boosts energy density, allowing batteries to store more energy.
- Manganese: Enhances thermal stability and safety, reducing overheating risks.
The cells in an average battery with a 60 kilowatt-hour (kWh) capacity—the same size used in a Chevy Bolt—contain roughly 185 kilograms of minerals.
Battery Demand Forecast
Due to the growing demand for these materials, their production and mining have increased exponentially in recent years, led by China. In this scenario, all the metals shown in the graphic currently experience a surplus.
In the long term, however, with the greater adoption of batteries and other renewable energy technologies, projections indicate that all these minerals will enter a deficit.
For example, lithium demand is expected to more than triple by 2034, resulting in a projected deficit of 572,000 tonnes of lithium carbonate equivalent (LCE). According to Benchmark analysis, the lithium industry would need over $40 billion in investment to meet demand by 2030.
Metric | Lithium (in tonnes LCE) | Nickel (in tonnes) | Cobalt (in tonnes) | Manganese (in tonnes) |
---|---|---|---|---|
2024 Demand | 1,103,000 | 3,440,000 | 230,000 | 119,000 |
2024 Surplus | 88,000 | 117,000 | 24,000 | 11,000 |
2034 Demand | 3,758,000 | 6,082,000 | 468,000 | 650,000 |
2034 Deficit | -572,000 | -839,000 | -91,000 | -307,000 |
Nickel demand, on the other hand, is expected to almost double, leading to a deficit of 839,000 tonnes by 2034. The surge in demand is attributed primarily to the rise of mid- and high-performance electric vehicles (EVs) in Western markets.
Electrification
Visualizing the EU’s Critical Minerals Gap by 2030
This graphic underscores the scale of the challenge the bloc faces in strengthening its critical mineral supply by 2030.

Visualizing EU’s Critical Minerals Gap by 2030
The European Union’s Critical Raw Material Act sets out several ambitious goals to enhance the resilience of its critical mineral supply chains.
The Act includes non-binding targets for the EU to build sufficient mining capacity so that mines within the bloc can meet 10% of its critical mineral demand.
Additionally, the Act establishes a goal for 40% of demand to be met by processing within the bloc, and 25% through recycling.
Several months after the Act’s passage in May 2024, this graphic highlights the scale of the challenge the EU aims to overcome. This data comes exclusively from Benchmark Mineral Intelligence, as of July 2024. The graphic excludes synthetic graphite.
Securing Europe’s Supply of Critical Materials
With the exception of nickel mining, none of the battery minerals deemed strategic by the EU are on track to meet these goals.
Graphite, the largest mineral component used in batteries, is of particular concern. There is no EU-mined supply of manganese ore or coke, the precursor to synthetic graphite.
By 2030, the European Union is expected to supply 16,000 tonnes of flake graphite locally, compared to the 45,000 tonnes it would need to meet the 10% mining target.
Metal | 2030 Demand (tonnes) | Mining (F) | Processing (F) | Recycling (F) | Mining Target | Processing Target | Recycling Target |
---|---|---|---|---|---|---|---|
Lithium | 459K | 29K | 46K | 25K | 46K | 184K | 115K |
Nickel | 403K | 42K | 123K | 25K | 40K | 161K | 101K |
Cobalt | 94K | 1K | 19K | 6K | 9K | 37K | 23K |
Manganese | 147K | 0K | 21K | 5K | 15K | 59K | 37K |
Flake Graphite | 453K | 16K | 17K | N/A | 45K | 86K | N/A |
The EU is also expected to mine 29,000 tonnes of LCE (lithium carbonate equivalent) compared to the 46,000 tonnes needed to meet the 10% target.
In terms of mineral processing, the bloc is expected to process 25% of its lithium requirements, 76% of nickel, 51% of cobalt, 36% of manganese, and 20% of flake graphite.
The EU is expected to recycle only 22% of its lithium needs, 25% of nickel, 26% of cobalt, and 14% of manganese. Graphite, meanwhile, is not widely recycled on a commercial scale.
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