Use Corn-Based Ethanol

Green hydrogen is an emissions-free fuel produced by using renewable electricity to split water into hydrogen and oxygen. For aviation and long-haul trucking, green hydrogen can be used either directly in fuel cells or combusted in modified engines, offering a potential pathway to deep emissions reductions. It generates no CO₂ at the point of use, and when produced with clean power, life-cycle emissions can be near zero. However, green hydrogen faces major barriers in terms of energy intensity, infrastructure needs, cost, and vehicle redesign. We will “Keep Watching” Mobilize Green Hydrogen for Aviation and Trucking due to its high potential impact, even though it is not yet ready for widespread deployment.
Based on our analysis, green hydrogen holds long-term potential in sectors that are difficult to decarbonize, particularly long-haul aviation and freight trucking. It is technologically feasible, but currently hampered by high costs, severe infrastructure gaps, and limited commercial readiness. While it is unlikely to be deployed at scale this decade, we will “Keep Watching” green hydrogen as innovation and policy evolve
Plausible | Could it work? | Yes |
---|---|---|
Ready | Is it ready? | No |
Evidence | Are there data to evaluate it? | Yes |
Effective | Does it consistently work? | Yes |
Impact | Is it big enough to matter? | Yes |
Risk | Is it risky or harmful? | No |
Cost | Is it cheap? | No |
Green hydrogen is a clean, emissions-free liquid fuel produced through electrolysis powered by renewable energy that can replace fossil fuels in some transportation sectors. Unlike hydrogen from fossil fuels (gray or blue hydrogen), green hydrogen generates no CO₂ emissions during production. For transportation, green hydrogen can be used in two main ways: (1) in fuel cell electric vehicles (FCEVs) to generate electricity onboard and power electric motors, or (2) combusted in specially designed hydrogen combustion engines or turbines. For aviation, liquid hydrogen may fuel aircraft engines directly, be used to produce synthetic jet fuels, or power fuel cell airplanes. For long-haul trucking, hydrogen can replace diesel by powering fuel cell trucks, which offer long range and fast refueling.
Green hydrogen is being produced and used in pilot projects and select transportation initiatives globally. Hydrogen combustion engines and fuel cells are currently in use and have been shown to reduce emissions compared to fossil fuels. For aviation, aircraft manufacturers, such as Airbus, have hydrogen-powered planes in development, with test flights expected by 2030, but it could be several decades before they are put into commercial use. In heavy-duty trucking, several major automakers, including Toyota and Hyundai, have already commercialized hydrogen trucks in limited markets, such as China and Japan.
Green hydrogen is one of the few near-zero-emission fuels with the potential to decarbonize aviation and long-haul trucking, where battery-electric solutions currently face range and weight constraints. If produced using abundant, low-cost renewables, green hydrogen could significantly cut emissions in sectors responsible for nearly 15% of global transport emissions. In aviation, hydrogen-based fuels like e-kerosene could save around five million tons of CO₂ per year in Europe by 2030. In trucking, hydrogen fuel cell vehicles are beginning to roll out but remain a niche market. Looking ahead, hydrogen has strong potential: by 2050, it could meet up to 30% of energy demand in long-haul trucking and significantly reduce aviation emissions, particularly for short- and medium-haul flights, but it will have to compete with advances in battery-electric options. Hydrogen enables fast refueling and long range, making it a strong candidate for freight and intercity applications. Additionally, investment in green hydrogen infrastructure could unlock cross-sectoral benefits, supporting decarbonization of industry, power, and potentially heating. As electrolyzer costs fall and renewable power expands, the economics and emissions profile of green hydrogen are likely to improve.
Despite its promise, green hydrogen for transport faces significant technical, economic, and logistical hurdles. Electrolysis is energy-intensive, and green hydrogen production is still expensive (US$300–600/t CO₂ avoided for trucking and US$500–1500/t CO₂ for aviation), making it much more costly than diesel or jet fuel but comparable to sustainable aviation fuel today. It is also less energy-dense by volume than other fuels, requiring complex transportation and storage (especially for aviation, where cryogenic tanks are needed) and limiting payload capacity. In addition to producing contrails, hydrogen leakage, though not a GHG, can contribute to indirect global warming effects. There are also safety concerns related to flammability and explosiveness, and a complete overhaul of transportation and refueling infrastructure is needed for both aviation and trucking. Green hydrogen requires entirely new infrastructure for production, storage, and distribution, including refueling stations for trucks and specialized handling systems for liquid or compressed hydrogen at each airport the airplane uses. The absence of this infrastructure creates a major barrier to adoption in aviation and long-haul trucking, where fuel logistics, safety standards, and scale are critical for commercial viability. Hydrogen remains a niche fuel due to its low energy density per volume, the need for cryogenic storage in aviation, limited refueling infrastructure, and high cost. While technically viable, major deployment for aviation and trucking is still nascent. Without a clear business case or strong policy incentives, uptake will remain limited in the near term.
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Sustainable aviation fuel (SAF) is a low-carbon alternative to conventional jet fuel. It is made from renewable feedstocks, including waste oils, agricultural residues, and renewable electricity. SAF can substantially reduce life-cycle GHG emissions and is already in use in commercial flights at low blending levels. Advantages include its compatibility with existing aircraft and fueling infrastructure, its potential to reduce emissions for long-haul aviation, and its ability to reduce emissions from organic waste streams. Disadvantages include limited feedstock availability, high costs, variable climate benefits depending on production methods, and challenges in scaling up supply to meet global demand. Based on our assessment, we will “Keep Watching” this potential solution.
Based on our analysis, sustainable aviation fuel (SAF) is a promising climate mitigation solution for reducing emissions in the aviation sector, particularly for long-haul flights where few alternatives exist. However, it is not yet cost-effective and faces significant challenges to scaling production due to severe feedstock restraints, land use pressure, and the need to meet robust sustainability standards. Based on our assessment, we will “Keep Watching” this potential solution.
Plausible | Could it work? | Yes |
---|---|---|
Ready | Is it ready? | Yes |
Evidence | Are there data to evaluate it? | Yes |
Effective | Does it consistently work? | Yes |
Impact | Is it big enough to matter? | Yes |
Risk | Is it risky or harmful? | No |
Cost | Is it cheap? | No |
Sustainable aviation fuel (SAF) is a low-carbon alternative to conventional jet fuel that reduces life-cycle greenhouse gas emissions from fuel production by using only non-petroleum feedstocks such as waste oils, agricultural residues, and municipal solid waste. It is usually produced using renewable electricity and captured CO₂. SAF is produced through chemical processes that convert these feedstocks into fuels that meet the same technical standards as fossil-based jet fuel, allowing them to be blended and used in existing aircraft engines and fueling infrastructure without modification. All SAFs approved by ASTM International, the body that sets fuel standards for aviation, are certified only for use in blends. No SAF is yet certified for 100% use in commercial aircraft (also known as “neat SAF”) for passenger flights.
The basic idea of sustainable aviation fuel is technologically sound and supported by decades of research into low-carbon fuel alternatives for aviation. Multiple SAF production pathways – such as hydroprocessed esters and fatty acids (HEFA), Fischer-Tropsch synthesis (FT), and alcohol-to-jet (ATJ) – have been approved by international aviation standards bodies, and several have been demonstrated at commercial scale. Real-world use of SAF is already underway: over 450,000 commercial flights have flown using SAF blends as of early 2025. SAF is currently being supplied at major airports in Europe, the United States, and Asia, with dozens of airlines integrating SAF into operations or entering offtake agreements. While current production remains limited (less than 0.5% of global jet fuel supply), government mandates, tax credits, and airline demand are driving the need for rapid scale-up. SAF is considered one of the most evidence-backed and immediately deployable climate solutions for reducing aviation emissions.
Sustainable aviation fuel offers several compelling advantages that make it a potential pathway for reducing aviation emissions. By reducing emissions 60-70% per ton compared to jet fuel, SAF could potentially avoid 0.1–0.2 Gt CO₂/yr by 2050. It can also reduce contrails. SAF can be used in existing aircraft and fueling systems without requiring new infrastructure or major redesigns. This makes it one of the few ready-to-deploy solutions for long-haul and international flights, which are difficult to electrify or replace. SAF production from waste oils and residues can also deliver benefits such as reduced methane emissions from organic waste streams and improved waste management. SAF offers a potentially scalable, technically feasible route to emissions reductions in a sector with few alternatives. Growing policy support, rising carbon prices, and airline demand are accelerating development.
Despite its promise, sustainable aviation fuel faces significant limitations, risks, and challenges that could constrain its impact and scalability. First, supply is a critical constraint. Due to limited feedstock availability, SAF is highly unlikely to be able to meet the ambitious 2050 goals set by ICAO, ReFuelEU Aviation, and other industry organizations, associations, and governmental institutions. This means that SAF must be combined with other strategies, like demand reduction and new aircraft technologies, to achieve full decarbonization. There are also major ecological and social risks, including competition for land and feedstocks that could displace food production or degrade ecosystems, as well as unequal access to the benefits of SAF deployment. Scaling synthetic SAF (e-fuels) requires vast amounts of clean electricity, water, and CO₂ – raising concerns about resource use and trade-offs with other sectors. Another major concern is cost. Current SAF prices are substantially higher than fossil jet fuel, ranging from US$300 to over US$1,500 per t CO₂ avoided, depending on the pathway. Without strong policy support, this cost premium poses a barrier to widespread adoption. Additionally, life-cycle emissions reductions vary widely depending on the feedstock and production pathway. While some SAFs (e.g., e-fuels using renewable electricity) can achieve near-zero emissions, others, especially those using food crops or poorly regulated waste streams, may deliver modest or uncertain climate benefits. Measurement, reporting, and verification of actual emissions reductions can be complex, especially when land-use change, indirect emissions, or supply chain impacts are involved. SAF combustion still contributes to climate impacts from contrails (albeit reduced compared to jet fuel), nitrogen oxides, and soot.
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Electric cars are four-wheeled passenger cars that run on electricity, usually from the electricity grid and stored in onboard batteries (i.e., not including fuel cell electric cars). This definition includes electric pickup trucks, motorhomes, and other such vehicles. It does not include two-wheeled vehicles or hybrid cars (which combine an electric motor with a gasoline or diesel engine). It also does not include freight and commercial vehicles, such as electric heavy trucks, buses, and ambulances. We define Mobilizing Electric Cars as replacing fossil fuel–powered cars (i.e., those powered by internal combustion engines) with electric equivalents, as well as building out the necessary infrastructure (especially charging stations) to support them.
Electric cars provide the same functionality as fossil fuel–powered cars, but use electric motors rather than fuel-burning engines. The energy for the motors comes from an onboard battery, which is normally charged using electricity from the grid.
Electric cars have no direct tailpipe emissions, since electric motors do not burn fuel to function. The grid electricity used to charge their batteries may have come from fossil fuel-burning power plants, meaning electric cars are not entirely free of direct emissions. However, in most electrical grids, even those that mainly generate electricity from fossil fuels, electric cars usually still produce fewer emissions per pkm than fossil fuel–powered cars. This is for three reasons. First, large, fixed power plants and efficient electric grids can convert fossil fuels into useful energy more efficiently than smaller, mobile internal combustion engines in cars. In extreme cases, such as grids powered entirely by coal, this might not be the case, particularly if the grid has a lot of transmission and distribution losses. Second, the powertrain of an electric car delivers electricity from the battery to the wheels much more efficiently than the powertrain of a fossil fuel–powered car, which wastes much more energy as heat (International Transport Forum, 2020; Mofolasayo, 2023; Verma et al., 2022). Third, electric cars’ powertrains enable regenerative braking, where the kinetic energy of the car’s motion is put back into the battery when the driver brakes (Yang et al., 2024).
Electric cars reduce emissions of CO₂, methane, and nitrous oxide to the atmosphere by replacing fuel-powered cars, which emit these gases from their tailpipes.
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Yoder, K. (2023, June 14). The environmental disaster lurking beneath your neighborhood gas station. Grist. https://grist.org/accountability/gas-stations-underground-storage-tank-leaks-environmental-disaster/
Cameron Roberts, Ph.D.
Ruthie Burrows, Ph.D.
James Gerber, Ph.D.
Daniel Jasper
Heather Jones, Ph.D.
Heather McDiarmid, Ph.D.
Alex Sweeney
Aiyana Bodi
James Gerber, Ph.D.
Hannah Henkin
Jason Lam
Ted Otte
Every million pkm shifted from fossil fuel–powered cars to electric cars reduces 48.52 t CO₂‑eq on a 100-yr basis (Table 1), or 49.13 t CO₂‑eq on a 20-yr basis.
We found this by collecting data on electricity consumption for a range of electric car models (Electric Vehicle Database, 2024) and multiplying it by the global average emissions per kWh of electricity generation. Fossil fuel–powered cars emit 115.3 t CO₂‑eq/pkm on a 100-yr basis (116.4 t CO₂‑eq/pkm on a 20-yr basis). Electric cars already have lower emissions in countries with large shares of renewable, nuclear, or hydropower generation in their electricity grids (International Transport Forum, 2020; Verma et al., 2022).
These data come disproportionately from North America and Europe, and, notably, leave out China, which has made major progress on electric cars in recent years and has many of its own makes and models.
Electric cars today are disproportionately used in high- and upper-middle-income countries, whose electricity grids emit fewer GHG emissions than the global average per unit of electricity generated (IEA, 2024). Electric cars in use today reduce more emissions on average than the figure we have calculated.
Electric cars have higher embodied emissions than fossil fuel–powered cars, due to the GHG-intensive process of manufacturing batteries. This gives them a carbon payback period which ranges from zero to over 10 years (Dillman et al., 2020; Ren et al., 2023).
Table 1. Effectiveness at reducing emissions.
Unit: t CO₂‑eq/million pkm, 100-yr basis
25th percentile | 38.95 |
mean | 49.54 |
median (50th percentile) | 48.52 |
75th percentile | 62.82 |
Shifted from fossil fuel–powered cars to electric cars, 100-yr basis.
Including purchase price, financing, fuel and electricity costs, maintenance costs, and insurance, electric cars cost on average US$0.05 less per pkm (US$49,442.19/million pkm) than fuel-powered cars. This is based on a population-weighted average of the cost differential between electric and fossil fuel–powered cars in seven countries: Japan, South Korea, China, the United States, France, Germany, and the United Kingdom (Nickel Institute, 2021b, 2021c, 2021a).
While this analysis found that electric cars are less expensive than fossil fuel–powered cars almost everywhere, the margin is often quite small. The difference is less than US$0.01/pkm (US$10,000/million pkm) in South Korea, the United States, and Germany. In some markets, electric cars are more expensive per pkm than fossil fuel–powered cars (IEA, 2022).
This amounts to savings of US$1,019/t CO₂‑eq on a 100-yr basis (Table 2), or US$1,006/t CO₂‑eq avoided emissions on a 20-yr basis).
Our analysis does not include costs that are the same for both electric and fossil fuel–powered cars, including taxes, insurance costs, and public costs of building road infrastructure.
Table 2. Cost per unit climate impact.
Unit: 2023 US$/t CO₂‑eq, 100-yr basis
median | -1,019 |
For every doubling in electric car production, costs decline by approximately 23% (Table 3; Goetzel & Hasanuzzaman, 2022; Kittner et al., 2020; Weiss et al., 2015).
In addition to manufacturing improvements and economies of scale, this reflects rapid technological advancements in battery production, which is a significant cost component of an electric powertrain (Weiss et al., 2015).
Table 3. Learning rate: drop in cost per doubling of the installed solution base.
Unit: %
25th percentile | 23.00 |
mean | 22.84 |
median (50th percentile) | 23.00 |
75th percentile | 24.00 |
Speed of action refers to how quickly a climate solution physically affects the atmosphere after it is deployed. This is different from speed of deployment, which is the pace at which solutions are adopted.
At Project Drawdown, we define the speed of action for each climate solution as emergency brake, gradual, or delayed.
Mobilize Electric Cars is a GRADUAL climate solution. It has a steady, linear impact on the atmosphere. The cumulative effect over time builds as a straight line.
The effectiveness of electric cars in mitigating GHG emissions is critically dependent on the emissions associated with electricity production. In electricity grids dominated by fossil fuels, electric cars have far higher emissions than in jurisdictions with low-emission electricity generation (International Transport Forum, 2020; IPCC, 2022; Milovanoff et al., 2020).
Electric car adoption faces a major obstacle in the form of constraints on battery production. While electric car battery production is being aggressively upscaled (IEA, 2024), building enough batteries to replace a significant fraction of fossil fuel–powered cars is an enormous challenge and will likely slow down a transition to electric cars, even if there is very high consumer demand (Milovanoff et al., 2020).
Approximately 28 million electric cars are in use worldwide (IEA, 2024). This corresponds to about 819,000 million pkm traveled by electric car worldwide each year (Table 4). We assume that all of this travel would be undertaken by a fossil fuel–powered car if the car’s occupants did not use an electric car. Adoption is much higher in some countries, such as Norway, where the share of electric cars was 29% in 2023.
To convert the IEA’s electric car estimates into pkm traveled, we needed to determine the average passenger-distance that each passenger car travels per year. Using population-weighted data from several different countries, the average car carries 1.5 people and travels an average of 29,250 pkm/yr. Multiplying this number by the number of electric cars in use gives the total travel distance shift from fossil fuel–powered cars to electric cars.
Table 4. Current (2024) adoption level.
Unit: million pkm/yr
Population-weighted mean | 818,900 |
Implied travel shift from fossil fuel-powered cars to electric cars.
Globally, about 104 billion pkm are displaced from fossil fuel–powered cars by electric cars every year (Table 5). The number of new electric cars purchased each year is growing at an average rate of over 10% (Bloomberg New Energy Finance, 2024; IEA, 2024), although purchase rates have declined slightly from record highs between 2020–2022. Global purchases of electric cars are still increasing by around 3.6 million cars/yr. This is based on globally representative data (Bloomberg New Energy Finance, 2024; IEA, 2024).
Despite this impressive rate of growth, electric cars still have a long way to go before they replace a large percentage of the more than 2 billion cars currently driven (WHO, 2024).
Table 5. 2023-2024 adoption trend.
Unit: million pkm/yr
Median, or population-weighted mean | 104,000 |
Implied travel shift from fossil fuel-powered cars to electric cars.
The adoption ceiling for electric cars is equal to the total passenger-distance driven by the more than 2 billion cars worldwide (WHO, 2024). Using a population-weighted mean of the average distance (in pkm) traveled per car annually, this translates to about 59 trillion pkm (Table 6).
Replacing every single fossil fuel–powered car with an electric car would require an enormous upscaling of electric car production capacity, rapid development of charging infrastructure, cost reductions to increase affordability, and technological improvements to improve suitability for more kinds of drivers and trips. It would also face cultural obstacles from drivers who are attached to fossil fuel–powered cars (Roberts, 2022).
Table 6. Adoption ceiling.
Unit: million pkm/yr
Median, or population-weighted mean | 59,140,000 |
Implied travel shift from fossil fuel-powered cars to electric cars.
The achievable adoption of electric car travel ranges from about 26–47 trillion pkm displaced from fossil fuel–powered cars (Table 7).
Various organizations have produced forecasts for electric car adoption. These are not assessments of feasible adoption per se; they are instead trying to predict likely rates of adoption, given various assumptions about the future (Bloomberg New Energy Finance, 2024; IEA, 2024). However, they are useful in that they take a large number of different variables into account to make their estimates. To convert these estimates of future likely adoption into estimates of the achievable adoption range, we apply some assumptions to the numbers in the scenario projections.
To find a high rate of electric car adoption, we assume that every country could reach the highest rate of adoption projected to occur for any country. Bloomberg New Energy Finance’s (2024) Economic Transition scenario predicts that Norway will reach an 80% electric vehicle stock share by 2040. We therefore set our high adoption rate at 80% worldwide. This corresponds to 1,617 million total electric cars in use, or 47 trillion pkm traveled by electric car. An important caveat is that with a global supply constraint in the production of electric car batteries, per-country adoption rates are somewhat zero-sum. Every electric car purchased in Norway is one that cannot be purchased elsewhere. Therefore, for the whole world to achieve an 80% electric car stock share, global electric car and battery production would have to increase radically. While this might be possible due to technological improvements or radical increases in investment, it should not be taken for granted.
To identify a lower feasible rate of electric car adoption, we simply take the highest estimate for global electric car adoption. Bloomberg’s Economic Transition scenario predicts 44% global electric car adoption by 2050. This corresponds to 890 million electric cars, or 26 trillion pkm.
Table 7. Range of achievable adoption levels.
Unit: million pkm/yr.
Current Adoption | 818,900 |
Achievable – Low | 26020000 |
Achievable – High | 47310000 |
Adoption ceiling (physical limit) | 59140000 |
Electric cars are currently displacing 0.040 Gt CO₂‑eq of GHG emissions from the transportation system on a 20-yr basis (Table 8), or 0.040 Gt CO₂‑eq on a 100-yr basis.
If electric cars reach 44% of the global car stock share by 2040, as Bloomberg (2024) projects, without any change in the total number of cars on the road, they will displace 1.263 Gt CO₂‑eq GHG emissions on a 100-yr basis (1.279 Gt CO₂‑eq on a 20-yr basis).
If electric cars globally reach 80% of car stock share, as Bloomberg projects might happen in Norway by 2040, they will displace 2.296 Gt CO₂‑eq GHG emissions on a 100-yr basis (2.325 Gt CO₂‑eq on a 20-yr basis).
If electric cars replace 100% of the global car fleet, they will displace 2.870 Gt CO₂‑eq GHG emissions on a 100-yr basis (2.906 Gt CO₂‑eq on a 20-yr basis).
These numbers are based on the present-day average emissions intensity from electrical grids in countries with high rates of electric car adoption. If more clean energy is deployed on electricity grids, the total climate impact from electric cars will increase considerably.
Table 8. Climate impact at different levels of adoption.
Unit: Gt CO₂‑eq/yr, 100-yr basis
Current Adoption | 0.040 |
Achievable – Low | 1.263 |
Achievable – High | 2.296 |
Adoption ceiling (physical limit) | 2.870 |
Since electric cars do not have tailpipe emissions, they can mitigate traffic-related air pollution, which is associated with asthma, lung cancer, increased emergency department visits for respiratory disease, and increased mortality (Anenberg et al., 2019; Guarnieri & Balmes, 2014; Pan et al., 2023; Pennington et al., 2024; Requia et al., 2018; Szyszkowicz et al., 2018). Transitioning to electric cars can reduce exposure to air pollution, improve health, and prevent premature mortality (Garcia et al., 2023; Larson et al., 2021; Peters et al., 2020).
The health benefits of adopting electric cars vary spatially and partly depend upon how communities generate electricity (Choma et al., 2020), but there is evidence that they have improved health. A study in California found a reduction in emergency department visits in ZIP codes with an increase in zero-emissions cars (Garcia et al., 2023). By 2050, projections estimate that about 64,000–167,000 deaths could be avoided by adopting electric cars (Larson et al., 2021).
Communities rich in racial and ethnic minorities tend to be located near highways and major traffic corridors and so are disproportionately exposed to air pollution (Kerr et al., 2021). Transitioning to electric cars could improve health in marginalized urban neighborhoods that are located near highways, industry, or ports (Pennington et al., 2024). These benefits depend upon an equitable distribution of electric cars and infrastructure to support the adoption of electric cars (Garcia et al., 2023). Low-income households may not see the same savings from an electric car due to the cost and stability of electricity prices and distance to essential services (Vega-Perkins et al., 2023)
Adopting electric cars can reduce a household’s energy burden, or the proportion of income spent on residential energy (Vega-Perkins et al., 2023). About 90% of United States households that use a car could see a reduction in energy burden by transitioning to an electric car. Money spent to charge electric cars is more likely to stay closer to the local community where electricity is generated, whereas money spent on fossil fuels often benefits oil-producing regions. This benefits local and national economies by improving their trade balance (Melaina et al., 2016).
Substituting electric car charging points for gas stations can eliminate soil and water pollution from leaking underground gas tanks (Yoder, 2023).
The adoption of electric cars reduces emissions of air pollutants, including sulfur oxides, sulfur dioxide, and nitrous oxides, and especially carbon monoxide and volatile organic compounds. It has a smaller impact on particulate emissions (Requia et al., 2018). Some air pollution reductions are limited (particularly PM and ozone) due to heavier electric cars and pollution from brakes, tires, and wear on the batteries (Carey, 2023; Jones, 2019).
Mining minerals necessary to produce electric car batteries carries environmental and social risks. This has been associated with significant harms, particularly in lower-income countries that supply many of these minerals (Agusdinata et al., 2018; Sovacool, 2019).
Electric cars might also pose added safety risks due to their higher weight, which means they have longer stopping distances and can cause more significant damage in collisions and to pedestrians and cyclists (Jones, 2019). This risk includes dual-motor electric cars that incorporate two electric motors – one for the front axle and one for the rear – providing all-wheel drive (AWD) capabilities. The addition of a second motor increases the vehicle's weight and complexity, which can lead to higher energy consumption and reduced overall efficiency. Moreover, the increased manufacturing costs associated with dual-motor systems can result in higher purchase prices for consumers (Nguyen et al., 2023). However, this configuration enhances vehicle performance, offering improved acceleration, traction, and handling, particularly in adverse weather conditions, which are valued by some consumers.
Electric car batteries can potentially be used as stationary batteries for use as energy storage to balance electrical grids, either through vehicle-to-grid (V2G) technology or with degraded electric car batteries being installed in stationary battery farms as a form of reuse (Ravi & Aziz, 2022).
The effectiveness of electric cars in reducing GHG emissions increases as electricity grids become cleaner, since lower-carbon electricity further reduces the emissions associated with car charging.
Electric cars compete with heat pumps for electricity. Installing both heat pumps and electric cars could strain the electric grid’s capacity (Fakhrooeian et al., 2024).
Scaling up the production of electric cars requires more mining of critical minerals, which could affect ecosystems that are valuable carbon sinks (Agusdinata et al., 2018).
Getting travelers onto bicycles, sidewalks, public transit networks, or smaller electric vehicles (such as electric bicycles) provides a greater climate benefit than getting them into electric cars. There is an opportunity cost to deploying electric cars because those resources could otherwise be used to support these more effective solutions (APEC, 2024).
million passenger-kilometers (million pkm)
CO₂, CH₄, N₂O, BC
Electric car batteries are currently quite emissions-intensive to produce, resulting in high embodied emissions. While the embodied emissions are higher for electric cars than fossil fuel–powered cars, the results are mixed when coupling these with operating emissions. Dillman et al.’s (2020) review of the literature on this topic found that producing the average battery-electric car emits 63% more GHG emissions than the average gasoline-powered car, and 77% more GHG emissions than the average diesel-powered car. Taking their lower tailpipe emissions into account, this gives them a GHG payback period of zero to more than 10 years. In some cases, the emissions payback period is longer than the expected lifespan of the electric car, meaning it will have higher life cycle GHG emissions than a comparable gasoline or diesel-powered car. However, the ITF (2020) found that the lifetime emissions from manufacturing, operation, and infrastructure are lower for electric cars. All of these studies relied on assumptions, including the type of car, size of battery, electricity grid, km/yr, and lifetime.
There is some criticism against any solution that advocates for car ownership, contending that the focus should be on solutions such as Enhance Public Transit that reduce car ownership and usage. Jones (2019) noted “there is little evidence to suggest that EVs can offer the universal solution that global governments are seeking,” and that efforts to popularize electric cars “may be better directed at creating more efficient public transport systems, rather than supporting personal transportation, if the significant health disbenefits of car use during the past 150 years are to be in any way reduced.”
Milovanoff et al. (2020) offered similar criticism: “Closing the mitigation gap solely with EVs would require more than 350 million on-road EVs (90% of the fleet), half of national electricity demand, and excessive amounts of critical materials to be deployed in 2050. Improving [the] average fuel consumption of fossil fuel–powered vehicles, with stringent standards and weight control, would reduce the requirement for alternative technologies, but is unlikely to fully bridge the mitigation gap. There is therefore a need for a wide range of policies that include measures to reduce vehicle ownership and usage.”
Allocating the limited global battery supply to privately owned electric cars might undermine the deployment of other solutions that also require batteries, but are more effective at avoiding GHG emissions (Castelvecchi, 2021). These could include electric buses, electric rail, and electric bicycles.
Cars are the largest source of vehicle emissions, which are shown here for urban areas.
Kott, T., Foster, K., Villafane-Delgado, M., Loschen, W., Sicurello, P., Ghebreselassie, M., Reilly, E., and Hughes, M. (2024). Transportation sector - Global road emissions. [Data set]. The Johns Hopkins University Applied Physics Laboratory (JHU/APL), Climate TRACE Emissions Inventory. Retrieved March 12, 2025 from Link to source: https://climatetrace.org
Cars are the largest source of vehicle emissions, which are shown here for urban areas.
Kott, T., Foster, K., Villafane-Delgado, M., Loschen, W., Sicurello, P., Ghebreselassie, M., Reilly, E., and Hughes, M. (2024). Transportation sector - Global road emissions. [Data set]. The Johns Hopkins University Applied Physics Laboratory (JHU/APL), Climate TRACE Emissions Inventory. Retrieved March 12, 2025 from Link to source: https://climatetrace.org
Electric cars can effectively mitigate climate change in all geographic regions, although there is spatial variability that influences per-pkm effectiveness and potential solution uptake. Effectiveness heavily depends on the carbon intensity of the charging source, which varies greatly between and within countries. The effectiveness of electric cars decreases for larger vehicles, favored in some countries (Jones, 2019; Nguyen et al., 2023).
The uptake of electric cars can be significantly influenced by socioeconomic factors, including the relative costs of fuels and electricity, the capacity of civil society to provide adequate charging infrastructure, and the availability of subsidies for electric vehicles.
Extreme temperatures can negatively impact vehicle range, both by slowing battery chemistry and increasing energy demands for regulating passenger compartment temperature, which can adversely affect consumers’ perceptions of electric car suitability in locations with such climates (International Council on Clean Transportation, 2024).
Electric cars are most effective in regions with low-carbon electricity grids (International Transport Forum, 2020; Verma et al., 2022). This includes countries with high hydro power (including Iceland, Norway, Sweden, and parts of Canada such as British Columbia and Quebec), nuclear energy (such as France), and renewables (including Portugal, New Zealand, and parts of the United States, including California and some of the Northwest) (IEA, 2024). Electric car adoption is growing rapidly in a number of regions. For future scaling, targeting countries with supportive policies, renewable energy potential, and growing urban populations will deliver the greatest climate benefits.
There is a high level of consensus among major organizations and researchers working on climate solutions that electric cars offer a substantial reduction in GHG emissions compared to fossil fuel–powered cars. This advantage is strongest in places where electricity in the grid comes from sources with low GHG emissions, but it persists even if fossil fuels play a major role in energy production.
Major climate research organizations generally see electric cars as the primary means of reducing GHG emissions from passenger transportation. This perspective has received criticism from some scholars who argue that electric cars have been overstated as a climate solution, pointing to supply constraints, embodied emissions, and emissions from electricity generation (Jones, 2019; Milovanoff et al., 2020). Embodied emissions are outside the scope of this assessment.
The Intergovernmental Panel on Climate Change (IPCC) (2022) estimated well-to-wheel (upstream and downstream emissions) GHG emissions intensity from gasoline and diesel cars at 139 g CO₂‑eq/pkm and 107 g CO₂‑eq/pkm, respectively. They estimated that electric cars running on low-carbon electricity (solar, wind, and nuclear sourced) emit 9 g CO₂‑eq/pkm; electric cars running on natural gas electricity emit 104 g CO₂‑eq/pkm; and electric cars running entirely on coal electricity emit 187 g CO₂‑eq/pkm. These estimates include upstream emissions, such as those from oil refining and coal mining.
The International Energy Agency (IEA, 2024) noted that “[a] battery electric car sold in 2023 will emit half as much as fossil fuel–powered equivalents over its lifetime. This includes full life-cycle emissions, including those from producing the car.”
The International Transport Forum (ITF) (2020) estimated that fossil fuel–powered cars emit 162 g CO₂‑eq/pkm, while electric cars emit 125 g CO₂‑eq/pkm. This included embodied and upstream emissions, which are outside the scope of this assessment.
The results presented in this document summarize findings from 15 reviews and meta-analyses and 24 original studies reflecting current evidence from 52 countries, primarily the IEA’s Electric Vehicle Outlook 2024), the Electric Vehicle Database 2024), the International Transportation Forum’s life cycle analysis on sustainable transportation 2020), the Nickel Institute’s cost estimates on electric cars (Nickel Institute, 2021b, 2021c, 2021a). We recognize this limited geographic scope creates bias, and hope this work inspires research and data sharing on this topic in underrepresented regions.