Mobilize Electric Buses
Replacing fossil-fuel-powered irrigation pumps with electric pumps powered by the grid can reduce emissions in most regions of the world. Electric irrigation pumps, which can also be powered by on-site clean energy, are more efficient than fossil fuel pumps. They are already cost-competitive and widely used, and adoption is increasing. Their emissions benefits will continue to grow as irrigation expands and the emissions intensity of the electrical grid falls. However, based on current grid emissions intensity, the climate impact of using electric pumps for agricultural irrigation is not globally meaningful (<0.1 Gt CO₂‑eq/yr ). Despite its modest climate impact, our assessment finds that deploying electric irrigation pumps is “Worthwhile.”
Based on our analysis, deploying electric irrigation pumps will reduce emissions but will not provide a globally significant climate impact (>0.1 Gt CO₂‑eq/yr ), even under high adoption scenarios, until electrical grid emissions decline further. Therefore, this potential climate solution is “Worthwhile.”
| 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? | No |
| Risk | Is it risky or harmful? | No |
| Cost | Is it cheap? | Yes |
This solution reduces emissions from irrigation by replacing pumps powered by natural gas, diesel, propane, or gasoline with electric pumps. Irrigation is the practice of adding water to croplands or pastures to reduce crop water stress and increase productivity. Pumps are used on some irrigated croplands to extract groundwater, transport surface water, and pressurize water for application through sprinklers or drip irrigation systems. Electric pumps have much higher motor efficiencies (~88%) than fossil fuel pumps (~21–31%), so pump switching reduces the energy required to pump the same amount of water. The extent to which emissions are reduced depends on the emissions intensity of the electrical grid mix. Electric pumps reduce emissions when the emissions intensity of the grid is below ~0.75 kg CO₂‑eq /kWh, or when they are powered by on-site solar or wind energy. In some places, additional emissions reductions can be achieved through Improving Irrigation Water Use Efficiency.
The efficiency and emissions benefits of electric pumps over fossil fuel pumps are well established. On-farm pumping emissions, currently estimated at approximately 0.2 Gt CO₂‑eq/yr, could feasibly be eliminated if all fossil fuel pumps are replaced with electric pumps and electrical grid emissions reach net-zero, or if they are powered by on-farm solar or wind energy. However, the climate impact of electric pump adoption today would be much lower, as electricity generation still produces substantial emissions. Under current conditions, replacing a diesel pump with an electric pump will reduce emissions in most, but not all, places around the world.
Electric pumps can reliably reduce emissions, are already cost-competitive and widely used, and adoption is increasing. Irrigation is a major energy user, and its energy use is increasing as irrigated areas expand. These trends are expected to continue in the coming decades as climate change exacerbates heat and water stress and agricultural production intensifies in low- and middle-income countries. Coupled with ongoing reductions in electrical grid emissions intensity, the potential climate benefits of this solution are growing.
Electric pump adoption can also be geographically targeted, as just five countries (China, India, the United States, Pakistan, and Iran) account for almost 70% of irrigation energy use. Areas with high groundwater reliance can also be targeted, as groundwater pumping accounts for 89% of irrigation energy use.
Pump switching also provides additional benefits, such as lowering long-term energy costs for farmers and reducing air pollution from on-farm fossil fuel use. Access to the electrical grid is the primary technical barrier to electric pump adoption, but small-scale solar installations can be used where grid connectivity is limited. Powering pumps with on-site solar also eliminates operational emissions, reduces the load on the electrical grid, and insulates farmers from variability in energy costs.
The climate impacts of pump switching are highly dependent on the emissions factor of the electrical grid. A large share of the potential reduction in fossil fuel pumping is located in India and China, which currently have relatively high electrical grid emissions intensities. Under the current grid mix, we estimate that pump switching in these countries will result in only modest benefits or a small increase in emissions.
Anand, S. K., Rosa, L., Mohanty, B. P., Rajan, N., & Calabrese, S. (2025). Balancing productivity and climate impact: A framework to assess climate-smart irrigation. Earth’s Future, 13(11), Article e2025EF006116. Link to source: https://doi.org/10.1029/2025EF006116
Driscoll, A. W., Conant, R. T., Marston, L. T., Choi, E., & Mueller, N. D. (2024). Greenhouse gas emissions from US irrigation pumping and implications for climate-smart irrigation policy. Nature Communications, 15(1), Article 1. Link to source: https://doi.org/10.1038/s41467-024-44920-0
Hrozencik, R. A. & Aillery, Marcel. (2021). Trends in U.S. irrigated agriculture: Increasing resilience under water supply scarcity. United States Department of Agriculture Economic Research Service, Report No. EIB-229. Link to source: https://www.ssrn.com/abstract=3996325
Kebede, E. A., Oluoch, K. O., Siebert, S., Mehta, P., Hartman, S., Jägermeyr, J., Ray, D., Ali, T., Brauman, K. A., Deng, Q., Xie, W., & Davis, K. F. (2025). A global open-source dataset of monthly irrigated and rainfed cropped areas (MIRCA-OS) for the 21st century. Scientific Data, 12(1), Article 208. Link to source: https://doi.org/10.1038/s41597-024-04313-w
McCarthy, B., Anex, R., Wang, Y., Kendall, A. D., Anctil, A., Haacker, E. M. K., & Hyndman, D. W. (2020). Trends in water use, energy consumption, and carbon emissions from irrigation: Role of shifting technologies and energy sources. Environmental Science & Technology, 54(23), 15329–15337. Link to source: https://doi.org/10.1021/acs.est.0c02897
McDermid, S., Mahmood, R., Hayes, M. J., Bell, J. E., & Lieberman, Z. (2021). Minimizing trade-offs for sustainable irrigation. Nature Geoscience, 14(10), 706–709. Link to source: https://doi.org/10.1038/s41561-021-00830-0
McDermid, S., Nocco, M., Lawston-Parker, P., Keune, J., Pokhrel, Y., Jain, M., Jägermeyr, J., Brocca, L., Massari, C., Jones, A. D., Vahmani, P., Thiery, W., Yao, Y., Bell, A., Chen, L., Dorigo, W., Hanasaki, N., Jasechko, S., Lo, M.-H., … Yokohata, T. (2023). Irrigation in the Earth system. Nature Reviews Earth & Environment, 4, 435–453. Link to source: https://doi.org/10.1038/s43017-023-00438-5
McGill, B. M., Hamilton, S. K., Millar, N., & Robertson, G. P. (2018). The greenhouse gas cost of agricultural intensification with groundwater irrigation in a Midwest U.S. row cropping system. Global Change Biology, 24(12), 5948–5960. Link to source: https://doi.org/10.1111/gcb.14472
Qin, J., Duan, W., Zou, S., Chen, Y., Huang, W., & Rosa, L. (2024). Global energy use and carbon emissions from irrigated agriculture. Nature Communications, 15(1), Article 3084. Link to source: https://doi.org/10.1038/s41467-024-47383-5
Ren, C., & Rosa, L. (2025). Global energy and emissions of irrigation and fertilizers management for closing crop yield gaps. Environmental Research Letters. 20(10), Article 104026. Link to source: https://doi.org/10.1088/1748-9326/adfbfd
Rollason, E., Sinha, P., & Bracken, L. J. (2022). Interbasin water transfer in a changing world: A new conceptual model. Progress in Physical Geography: Earth and Environment, 46(3), 371–397. Link to source: https://doi.org/10.1177/03091333211065004
Rosa, L., Chiarelli, D. D., Sangiorgio, M., Beltran-Peña, A. A., Rulli, M. C., D’Odorico, P., & Fung, I. (2020). Potential for sustainable irrigation expansion in a 3 °C warmer climate. Proceedings of the National Academy of Sciences, 117(47), 29526–29534. Link to source: https://doi.org/10.1073/pnas.2017796117
Rosa, L., Rulli, M. C., Ali, S., Chiarelli, D. D., Dell’Angelo, J., Mueller, N. D., Scheidel, A., Siciliano, G., & D’Odorico, P. (2021). Energy implications of the 21st century agrarian transition. Nature Communications, 12(1), Article 2319. Link to source: https://doi.org/10.1038/s41467-021-22581-7
Sanders, K. T., & Webber, M. E. (2012). Evaluating the energy consumed for water use in the United States. Environmental Research Letters, 7(3), Article 034034. Link to source: https://doi.org/10.1088/1748-9326/7/3/034034
Schmitt, R. J. P., Rosa, L., & Daily, G. C. (2022). Global expansion of sustainable irrigation limited by water storage. Proceedings of the National Academy of Sciences, 119(47), Article e2214291119. Link to source: https://doi.org/10.1073/pnas.2214291119
Siddik, M. A. B., Dickson, K. E., Rising, J., Ruddell, B. L., & Marston, L. T. (2023). Interbasin water transfers in the United States and Canada. Scientific Data, 10(1), Article 1. Link to source: https://doi.org/10.1038/s41597-023-01935-4
Sowby, R. B., & Dicataldo, E. (2022). The energy footprint of U.S. irrigation: A first estimate from open data. Energy Nexus, 6, Article 100066. Link to source: https://doi.org/10.1016/j.nexus.2022.100066
Yang, Y., Jin, Z., Mueller, N. D., Driscoll, A. W., Hernandez, R. R., Grodsky, S. M., Sloat, L. L., Chester, M. V., Zhu, Y.-G., & Lobell, D. B. (2023). Sustainable irrigation and climate feedbacks. Nature Food, 4(8), Article 8. Link to source: https://doi.org/10.1038/s43016-023-00821-x
Avery Driscoll, Ph.D.
Christina Swanson, Ph.D.
Heather McDiarmid, Ph.D.
James Gerber, Ph.D.
Corn ethanol, an alcohol made by fermenting corn grain, is the most produced and used biofuel in the United States. The U.S. Renewable Fuel Standard requires that corn ethanol be blended with gasoline for the intended purpose of reducing transportation emissions. Ethanol is a useful vehicle fuel additive that improves engine performance and reduces air pollution. However, life cycle emissions analyses show that corn ethanol does not reduce GHG emissions as claimed and, more likely, increases emissions by 24% compared to gasoline alone. One-third of the corn grown in the U.S. is now used to produce more than 15 billion gallons of ethanol per year. This huge demand for corn has increased prices and driven the conversion of unfarmed land and natural ecosystems. The higher demand for corn also led to more fertilizer use on farms, resulting in increased pollution and nitrous oxide emissions. Based on these life cycle analyses, we conclude that using corn ethanol is "Not Recommended" as a climate solution.
The use of corn ethanol as a transportation biofuel, which has led to the expansion and intensification of corn production, does not reduce GHG emissions compared to gasoline. Based on this finding, using corn ethanol is not a plausible approach for reducing emissions and is “Not Recommended” as a climate solution.
| Plausible | Could it work? | No |
|---|---|---|
| Ready | Is it ready? | Yes |
| Evidence | Are there data to evaluate it? | Yes |
| Effective | Does it consistently work? | No |
| Impact | Is it big enough to matter? | No |
| Risk | Is it risky or harmful? | No |
| Cost | Is it cheap? | No |
Corn ethanol is a liquid biofuel that is blended with gasoline to displace a fraction of the petroleum-based fuel with a renewable fuel derived from plants. Proponents claim that blending corn ethanol with gasoline reduces emissions because the CO₂ produced from combusting the ethanol is offset, or balanced out, by the atmospheric CO₂ absorbed by the corn plant during growth. Corn ethanol is made from corn grain by breaking down the starch in the kernels into sugar and then fermenting it into a liquid. In the United States, the world leader in biofuel production, almost 90% of biofuel is corn ethanol. Most gasoline now sold in the U.S. contains about 10% corn ethanol, and, in 2025, the Renewable Fuel Standard (RFS) program requires production of more than 15 billion gallons of this biofuel. Currently, it is primarily made from corn kernels; the technology for producing biomass-derived ethanol from other, non-edible parts of the corn plant is not yet commercially viable. Brazil is the second-largest producer of ethanol, but uses sugarcane as a feedstock.
The Renewable Fuel Standard requires that the life cycle emissions from corn ethanol be at least 20% lower than those of conventional gasoline. However, based on comprehensive life cycle emissions analyses, using corn ethanol does not reduce emissions compared to gasoline. The main reasons for this are that the production of corn and processing it into ethanol generate large amounts of emissions, including from land conversion, fertilizer-related nitrous oxide emissions, and the industrial process of fermenting the corn into ethanol. The most prominent recent study reported that corn ethanol life cycle emissions were, at best, no less than gasoline and, more likely, were 24% higher. Corn ethanol is also more emissions-intensive than ethanol made from other plants, like sugar cane.
Ethanol has been used as a transportation fuel, including as a blend with gasoline, for more than a century. It boosts the octane number of fuel, improves engine performance and fuel economy, and reduces emissions of harmful pollutants like unburned hydrocarbons, nitrogen oxides, and particulates. Ethanol has also been used to replace other harmful and polluting gasoline additives, including lead and methyl tert-butyl ether (MTBE). Ethanol produced from non-edible biological feedstocks with lower production emissions, such as switchgrass or cellulose from crop residues, has the potential to reduce emissions.
The Renewable Fuel Standard (RFS) program requires that biofuels be blended into the transportation fuel supply at annually increasing increments. The United States now uses one-third of its corn to generate more than 15 billion gallons of ethanol per year. Not only does this mandated program not reduce emissions (it more likely increases emissions), but it also consumes corn that could otherwise be used for food or animal feed. The increased demand for corn for ethanol has increased corn prices, which in turn have contributed to the conversion of grasslands and semi-natural ecosystems to grow more corn. When grasslands, woodlands, or other natural ecosystems are plowed and converted to cropland, the carbon stored in the vegetation and soil is emitted to the atmosphere. Between 2008 and 2016, the conversion of 1.8 Mha of natural and semi-natural land in the U.S. released about 400 million metric tons of CO₂ from vegetation and soil. The increased corn production also increased the application of synthetic fertilizers, which has increased nitrate leaching, phosphorus runoff, and emissions of nitrous oxide, a powerful GHG (see Improve Nutrient Management). These problems are particularly severe in the U.S. Midwest and the Mississippi River drainage.
Broda, M., Yelle, D. J., & Serwańska, K. (2022). Bioethanol production from lignocellulosic biomass—challenges and solutions. Molecules, 27(24), 8717. Link to source: https://www.mdpi.com/1420-3049/27/24/8717
California Air Resources Board (CARB) (2003). Cleaner Burning Gasoline without MTBE. Link to source: https://ww2.arb.ca.gov/resources/fact-sheets/cleaner-burning-gasoline-without-mtbe
Cassidy, E. (2014). Ethanol’s Broken Promise. Environmental Working Group. Link to source: https://www.ewg.org/research/ethanols-broken-promise
Ciolkosz, D. (2024). Fuel Ethanol: Hero or Villain? Penn State Extension. Link to source: https://extension.psu.edu/fuel-ethanol-hero-or-villain
Douglas, L. (2022). U.S. corn-based ethanol worse for the climate than gasoline, study finds. Reuters. Link to source: https://www.reuters.com/business/environment/us-corn-based-ethanol-worse-climate-than-gasoline-study-finds-2022-02-14/
EPA (U.S. Environmental Protection Agency) (2023). Renewable Fuel Standard (RFS) Program: Standards for 2023–2025 and Other Changes Lifecycle Greenhouse Gas Results. Federal Register/Vol. 88, No. 132/Wednesday, July 12, 2023/Rules and Regulations. Link to source: https://www.govinfo.gov/content/pkg/FR-2023-07-12/pdf/2023-13462.pdf
EPA (U.S. Environmental Protection Agency) (2025a). Overview of the Renewable Fuel Standard Program. Link to source: https://www.epa.gov/renewable-fuel-standard/overview-renewable-fuel-standard-program
EPA (U.S. Environmental Protection Agency) (2025b). Lifecycle Greenhouse Gas Results. Link to source: https://www.epa.gov/fuels-registration-reporting-and-compliance-help/lifecycle-greenhouse-gas-results
Hill, J. (2022). The sobering truth about corn ethanol. Proceedings of the National Academy of Sciences, 119(11), e2200997119. Link to source: https://doi.org/10.1073/pnas.2200997119
Kramer, D. (2022). Whatever happened to cellulosic ethanol? Physics Today, 75(7), 22-24. Link to source: https://doi.org/10.1063/PT.3.5036
Lark, T. J., Hendricks, N. P., Smith, A., Pates, N., Spawn-Lee, S. A., Bougie, M., ... & Gibbs, H. K. (2022). Environmental outcomes of the US renewable fuel standard. Proceedings of the National Academy of Sciences, 119(9), e2101084119. Link to source: https://doi.org/10.1073/pnas.2101084119
Lark, T. J., Salmon, J. M., & Gibbs, H. K. (2015). Cropland expansion outpaces agricultural and biofuel policies in the United States. Environmental Research Letters, 10(4), 044003. Link to source: http://dx.doi.org/10.1088/1748-9326/10/4/044003
National Library of Medicine (2023). Toxicological Profile for Methyl tert-Butyl Ether (MTBE). Agency for Toxic Substances and Disease Registry (US); CHAPTER 1, RELEVANCE TO PUBLIC HEALTH. Link to source: https://www.ncbi.nlm.nih.gov/books/NBK601216/
Robertson, G. P., Dale, V. H., Doering, O. C., Hamburg, S. P., Melillo, J. M., Wander, M. M., ... & Wilhelm, W. W. (2008). Sustainable biofuels redux. Science, 322(5898), 49–50. Link to source: https://lter.kbs.msu.edu/docs/robertson/robertson_et_al._2008_science.pdf
Searchinger, T. et al. (2008) Use of U.S. Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land-Use Change. Science 319,1238-1240(2008). Link to source: https://doi.org/10.1126/science.1151861
Spawn, S. A., Lark, T. J., & Gibbs, H. K. (2019). Carbon emissions from cropland expansion in the United States. Environmental Research Letters, 14(4), 045009. Link to source: https://doi.org/10.1088/1748-9326/ab0399
Tilman, D., Socolow, R., Foley, J. A., Hill, J., Larson, E., Lynd, L., ... & Williams, R. (2009). Beneficial biofuels—the food, energy, and environment trilemma. Science, 325(5938), 270-271. Link to source: https://doi.org/10.1126/science.1177970
Wright, C. K., Larson, B., Lark, T. J., & Gibbs, H. K. (2017). Recent grassland losses are concentrated around US ethanol refineries. Environmental Research Letters, 12(4), 044001. Link to source: https://doi.org/10.1088/1748-9326/aa6446
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.
Clean Hydrogen Partnership. (2020). Hydrogen-powered aviation. Link to source: https://www.clean-hydrogen.europa.eu/media/publications/hydrogen-powered-aviation_en
Clean Hydrogen Partnership. (2020). Study on fuel cells hydrogen trucks. Link to source: https://www.clean-hydrogen.europa.eu/media/publications/study-fuel-cells-hydrogen-trucks_en
Galimova, T., Fasihi, M., Bogdanov, D., & Breyer, C. (2023). Impact of international transportation chains on cost of green e-hydrogen: Global cost of hydrogen and consequences for Germany and Finland. Applied Energy, 347, 121369. Link to source: https://doi.org/10.1016/j.apenergy.2023.121369
Gulli, C., Heid, B., Noffsinger, J., Waardenburg, M., & Wilthaner, M. Global energy perspective 2023: Hydrogen outlook. Link to source: https://www.mckinsey.com/industries/oil-and-gas/our-insights/global-energy-perspective-2023-hydrogen-outlook
International Energy Agency. (2019). The Future of hydrogen – analysis. IEA. Link to source: https://www.iea.org/reports/the-future-of-hydrogen
International Renewable Energy Agency. (2022). Green hydrogen for industry: A guide to policy making. Link to source: https://www.irena.org/publications/2022/Mar/Green-Hydrogen-for-Industry
Jaramillo, P., Ribeiro, S. K., Newman, P., Dhar, S., Diemuodeke, O. S., Kajino, T., Lee, D. S., Nugroho, S. B., Ou, X., Strømman, A. H., & Whitehead, J. (2022). Transport. In P.R. Shukla, J. Skea, R. Slade, A. Al Khourdajie, R. van Diemen, D. McCollum, M. Pathak, S. Some, P. Vyas, R. Fradera, M. Belkacemi, A. Hasija, G. Lisboa, S. Luz, & J. Malley, (Eds.), Climate change 2022: Mitigation of climate change. Contribution of working group III to the sixth assessment report of the intergovernmental panel on climate change (Chapter 10). Cambridge University Press. Link to source: https://10.1017/9781009157926.012
Li, Y., & Taghizadeh-Hesary, F. (2022). The economic feasibility of green hydrogen and fuel cell electric vehicles for road transport in China. Energy Policy, 160, 112703. Link to source: https://doi.org/10.1016/j.enpol.2021.112703
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. However, when combustion emissions are considered, SAF does not consistently reduce emissions when compared to conventional fuels. SAF is already in use in commercial flights at low blending levels. Advantages of SAF include its compatibility with existing aircraft and fueling infrastructure. Disadvantages include limited feedstock availability, high costs, variable climate benefits depending on production methods, and challenges in scaling up supply to meet global demand. We will “Keep Watching” SAF as part of a broader portfolio of aviation decarbonization strategies.
Based on our analysis, sustainable aviation fuel (SAF) has the potential to reduce emissions in the aviation sector, particularly for long-haul flights where few alternatives exist. However, pathways with the lowest emissions are not yet cost-effective and face significant challenges to scaling production due to feedstock constraints, land conversion pressure, and the need to meet robust sustainability standards. Based on our assessment, SAF is a climate solution to “Keep Watching.”
| Plausible | Could it work? | Yes |
|---|---|---|
| Ready | Is it ready? | Yes |
| Evidence | Are there data to evaluate it? | Yes |
| Effective | Does it consistently work? | No |
| Impact | Is it big enough to matter? | ? |
| 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 uses non-petroleum feedstocks such as waste oils, agricultural residues, and municipal solid waste. 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. As of 2025, existing SAFs are only approved for use in blends; no SAF is yet certified for 100% use in commercial aircraft (also known as “neat SAF”) for passenger flights.
Life-cycle emissions vary widely depending on the feedstock and production pathway. 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. However, as of 2025, the HEFA pathway (which uses vegetable oils, waste oils, or fats) is the only commercially deployed method to produce significant amounts of SAF.
While some SAFs could achieve low emissions, others, especially those using food crops or poorly regulated waste streams, deliver uncertain climate benefits or can even increase emissions compared to conventional fuels. (We include emissions from burning biomass and biofuels, using default Intergovernmental Panel on Climate Change [IPCC] stationary combustion emission factors for each feedstock. See the Drawdown Explorer primer on “Effectiveness” of solutions.) Others, such as FT pathways, which use municipal solid waste or agricultural waste and residues, have the greatest potential for emissions reduction.
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. However, SAF supplies less than 0.5% of global jet fuel use.
Sustainable aviation fuels may reduce contrails, potentially significantly reducing aviation’s climate impact. 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 deliver additional benefits, such as reduced methane emissions from organic waste streams and improved waste management. Growing policy support, rising carbon prices, and airline demand are accelerating development.
Despite its promise, SAF faces significant limitations and challenges that could constrain its impact and scalability. In the United States, soybean oil is one of the most commonly used feedstocks for HEFA SAF, and its production faces similar land use and ecological risks and constraints as corn ethanol. Whereas in Europe, waste oils and fats are more commonly used. Measurement, reporting, and verification of actual emissions reductions can be complex, especially when land-use change, indirect emissions, or supply chain impacts are involved.
Due to limited feedstock availability, SAF is highly unlikely to meet the ambitious 2050 goals set by industry organizations and government institutions. Effective SAFs must be combined with other strategies, like demand reduction and new aircraft technologies, to achieve substantial emissions reductions.
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 ton of CO₂ avoided, depending on the pathway. Without strong policy support, this cost premium poses a barrier to widespread adoption.
Alternative Fuels Data Center. (n.d.). Sustainable Aviation Fuel. https://afdc.energy.gov/fuels/sustainable-aviation-fuel
Bardon, P., & Massol, O. (2025). Decarbonizing aviation with sustainable aviation fuels: Myths and realities of the roadmaps to net zero by 2050. Renewable and Sustainable Energy Reviews, 211, 115279. https://doi.org/10.1016/j.rser.2024.115279
Boyles, H. (2022). Climate-Tech to Watch: Sustainable Aviation Fuel. https://itif.org/publications/2022/10/17/climate-tech-to-watch-sustainable-aviation-fuel
Buchholz, N., Fehrm, B., Kaestner, L., Uhrenbacher, S., & Vesco, M. (2023). Study: How To Accelerate Aviation’s CO2 Reduction | Aviation Week Network. Link to source: https://aviationweek.com/air-transport/aircraft-propulsion/study-how-accelerate-aviations-co2-reduction
Bullerdiek, N., Neuling, U., & Kaltschmitt, M. (2021). A GHG reduction obligation for sustainable aviation fuels (SAF) in the EU and in Germany. Journal of Air Transport Management, 92, 102020. https://doi.org/10.1016/j.jairtraman.2021.102020
EASA. (2025). Sustainable Aviation Fuels | EASA. https://www.easa.europa.eu/en/domains/environment/eaer/sustainable-aviation-fuels
European Commission. (n.d.). ReFuelEU Aviation. ReFuelEU Aviation - European Commission
ICAO. (n.d.). LTAG Costs and Investments. ICAO. Link to source: https://www.icao.int/environmental-protection/LTAG/Pages/LTAG-and-Fuels.aspx
ICAO. (n.d.). Sustainable Aviation Fuels. Link to source: https://www.icao.int/environmental-protection/pages/SAF.aspx
IEA. (2025). Aviation. IEA. https://www.iea.org/energy-system/transport/aviation
IATA. (2024). IATA - Disappointingly Slow Growth in SAF Production. Link to source: https://www.iata.org/en/pressroom/2024-releases/2024-12-10-03/
IATA. (2025). IATA Releases SAF Accounting and Reporting Methodology. https://www.iata.org/en/pressroom/2025-releases/2025-01-31-01/
Michaga, M. F. R., Michailos, S., Hughes, K. J., Ingham, D., & Pourkashanian, M. (2021). 10—Techno-economic and life cycle assessment review of sustainable aviation fuel produced via biomass gasification. In R. C. Ray (Ed.), Sustainable Biofuels (pp. 269–303). Academic Press. https://doi.org/10.1016/B978-0-12-820297-5.00012-8
O’Malley, J., & Baldino, C. (2024). Availability of biomass feedstocks in the European Union to meet the 2035 ReFuelEU Aviation SAF target. International Council on Clean Transportation. https://theicct.org/publication/low-risk-biomass-feedstocks-eu-refueleu-aug24/
Prussi, M., Lee, U., Wang, M., Malina, R., Valin, H., Taheripour, F., Velarde, C., Staples, M. D., Lonza, L., & Hileman, J. I. (2021). CORSIA: The first internationally adopted approach to calculate life-cycle GHG emissions for aviation fuels. Renewable and Sustainable Energy Reviews, 150, 111398. https://doi.org/10.1016/j.rser.2021.111398
Rojas-Michaga, M. F., Michailos, S., Cardozo, E., Akram, M., Hughes, K. J., Ingham, D., & Pourkashanian, M. (2023). Sustainable aviation fuel (SAF) production through power-to-liquid (PtL): A combined techno-economic and life cycle assessment. Energy Conversion and Management, 292, 117427. https://doi.org/10.1016/j.enconman.2023.117427
Rosales Calderon, O., Tao, L., Abdullah, Z., Talmadge, M., Milbrandt, A., Smolinski, S., Moriarty, K., et al. (2024). Sustainable Aviation Fuel State-of-Industry Report: Hydroprocessed Esters and Fatty Acids Pathway. Golden, CO: National Renewable Energy Laboratory. NREL/TP-5100-87803. Link to source: https://www.nrel.gov/docs/fy24osti/87803.pdf.
Shahriar, M. F., & Khanal, A. (2022). The current techno-economic, environmental, policy status and perspectives of sustainable aviation fuel (SAF). Fuel, 325, 124905. https://doi.org/10.1016/j.fuel.2022.124905
Voigt, C., Kleine, J., Sauer, D., Moore, R. H., Bräuer, T., Le Clercq, P., Kaufmann, S., Scheibe, M., Jurkat-Witschas, T., Aigner, M., Bauder, U., Boose, Y., Borrmann, S., Crosbie, E., Diskin, G. S., DiGangi, J., Hahn, V., Heckl, C., Huber, F., … Anderson, B. E. (2021). Cleaner burning aviation fuels can reduce contrail cloudiness. Communications Earth & Environment, 2(1), 1–10. https://doi.org/10.1038/s43247-021-00174-y
Watson, M. J., Machado, P. G., da Silva, A. V., Saltar, Y., Ribeiro, C. O., Nascimento, C. A. O., & Dowling, A. W. (2024). Sustainable aviation fuel technologies, costs, emissions, policies, and markets: A critical review. Journal of Cleaner Production, 449, 141472. https://doi.org/10.1016/j.jclepro.2024.141472
World Economic Forum. (2021). Clean Skies for Tomorrow: Sustainable Aviation Fuels as a Pathway to Net-Zero Aviation. World Economic Forum. https://www3.weforum.org/docs/WEF_Clean_Skies_Tomorrow_SAF_Analytics_2020.pdf
Yoo, E., Lee, U., & Wang, M. (2022). Life-Cycle Greenhouse Gas Emissions of Sustainable Aviation Fuel through a Net-Zero Carbon Biofuel Plant Design. ACS Sustainable Chemistry & Engineering, 10(27), 8725–8732. https://doi.org/10.1021/acssuschemeng.2c00977
Zahid, I., Nazir, M. H., Chiang, K., Christo, F., & Ameen, M. (2024). Current outlook on sustainable feedstocks and processes for sustainable aviation fuel production. Current Opinion in Green and Sustainable Chemistry, 49, 100959. https://doi.org/10.1016/j.cogsc.2024.100959
Electric scooters and motorcycles are battery-powered two- and three-wheeled vehicles that provide low-emissions mobility. This category of transport includes electric mopeds, motorbikes, seated motor scooters, motorcycles, and three-wheel vehicles, such as e-rickshaws and e-tuk-tuks. Electric scooters and motorcycles run on rechargeable batteries and are powered by electric motors rather than fossil fuel–powered ICEs, helping reduce transport-related GHG emissions. Throttle-controlled and pedal-assist (pedelecs) electric bicycles, as well as standing e-scooters/trotinettes, are excluded from the analysis of this climate solution.
Electric scooters and motorcycles use electricity stored in batteries to power an electric motor, providing mobility similar to conventional fossil fuel–powered two- and three-wheelers while generating significantly lower GHG emissions because they replace fossil-fuel combustion with electricity (Barreiros, 2020; Carranza et al., 2022; Cox & Mutel, 2018; International Transport Forum, 2020, 2023b; La Fleur et al., 2024; Mera & Bieker, 2023; Montoya-Torres et al., 2023; Schneider at al., 2023; Tuayharn et al., 2015).
Because of their efficiency, compact size, and affordability, electric scooters and motorcycles are particularly effective as transportation modes in urban and peri-urban areas. These vehicles’ relatively low energy use per pkm makes them an energy-efficient motorized transport mode, especially when powered with renewable electricity. Electric scooters and motorcycles are also increasingly used for delivery services, shared fleets, ride-hailing, and formal and informal shared rental systems, helping displace car or fossil fuel–powered motorcycle trips that typically result in high per-person GHG emissions.
Safety issues, informal charging infrastructure, and concerns surrounding equitable access are the principal challenges standing in the way of broader adoption of electric scooters and motorcycles, particularly in emerging economies where most electric two- and three-wheelers operate (La Fleur et al., 2024). Meanwhile, emissions benefits related to electric scooters and motorcycles are typically lower in regions with carbon-intensive electricity. These vehicles may also offer fewer GHG emissions reductions benefits in areas with strong pre-existing public transportation systems, especially if broader adoption of electric scooters and motorcycles triggers a decrease in public transit use. Finally, electric two- and three-wheelers generate higher GHG emissions and provide fewer health benefits than do pedal-assisted electric bicycles; nevertheless, electric scooters and motorcycles remain far more efficient than cars in terms of GHG emissions (International Transport Forum, 2020).
In addition to reducing emissions of GHGs such as CO₂, methane, and nitrous oxide, electric scooters and motorcycles eliminate tailpipe pollutants such as nitrogen oxides and particulate matter, lower fossil-fuel use, and reduce noise (International Transport Forum, 2023a). They also provide an immediate and practical pathway for creating cleaner, more equitable cities.
Anenberg, S., Miller, J., Henze, D., & Minjares, R. (2019). A global snapshot of the air pollution-related health impacts of transportation sector emissions in 2010 and 2015 [Report]. International Council on Clean Transportation. Link to source: https://theicct.org/publication/a-global-snapshot-of-the-air-pollution-related-health-impacts-of-transportation-sector-emissions-in-2010-and-2015/
Anup, S., Deo, A., & Bandivadekar, A. (2021). Impact of fuel consumption standard on electrification of two-wheelers in India [Technical paper 2021-26-0050]. SAE International. Link to source: https://doi.org/10.4271/2021-26-0050
Asia-Pacific Economic Cooperation. (2024). Connecting traveler choice with climate outcomes: Innovative greenhouse gas emissions reduction policies and practices in the APEC region through traveler behavioral change [Report]. Link to source: https://www.apec.org/publications/2024/09/connecting-traveler-choice-with-climate-outcomes--innovative-greenhouse-gas-emissions-reduction-policies-and-practices-in-the-apec-region-through-traveler-behavioral-change
Ayetor, G. K., Mbonigaba, I., & Mashele, J. (2023). Feasibility of electric two and three-wheelers in Africa. Green Energy and Intelligent Transportation, 2(4), Article 100106. Link to source: https://doi.org/10.1016/j.geits.2023.100106
Barreiros, T. V. (2020). Comparison of the life cycle of different scooters used in Berlin [Report 1.0]. GreenDelta GmbH. Link to source: https://www.openlca.org/wp-content/uploads/2025/01/Report_Scooters_in_Berlin.pdf
BloombergNEF. (2025, December 9). Lithium-ion battery pack prices fall to $108 per kilowatt-hour, despite rising metal prices: BloombergNEF [Press release]. Link to source: https://about.bnef.com/insights/clean-transport/lithium-ion-battery-pack-prices-fall-to-108-per-kilowatt-hour-despite-rising-metal-prices-bloombergnef
Carranza, G., Do Nascimiento, M., Fanals, J., Febrer, J., & Valderrama, C. (2022). Life cycle assessment and economic analysis of the electric motorcycle in the city of Barcelona and the impact on air pollution. Science of The Total Environment, 821, Article 153419. Link to source: https://doi.org/10.1016/j.scitotenv.2022.153419
Cox, B. L., & Mutel, C. L. (2018). The environmental and cost performance of current and future motorcycles. Applied Energy, 212, 1013–1024. Link to source: https://doi.org/10.1016/j.apenergy.2017.12.100
Guarnieri, M., & Balmes, J. R. (2014). Outdoor air pollution and asthma. The Lancet, 383(9928), 1581–1592. Link to source: https://www.thelancet.com/journals/lancet/article/PIIS0140-6736(14)60617-6/abstract
Gupta, R., Hertzke, P., Lath, V., & Vig, G. (2023). The real global EV buzz comes on two wheels. McKinsey & Company. Link to source: https://www.mckinsey.com/industries/automotive-and-assembly/our-insights/the-real-global-ev-buzz-comes-on-two-wheels
Hernandez, M., Kockelman, K. M., Lentz, J. O., & Lee, J. (2019). Emissions and noise mitigation through use of electric motorcycles. Transportation Safety and Environment, 1(2), 164–175. Link to source: https://doi.org/10.1093/tse/tdz013
International Energy Agency. (2020). Sustainable recovery [Report]. Link to source: https://www.iea.org/reports/sustainable-recovery
International Energy Agency. (2024). Global EV outlook 2024. Link to source: https://www.iea.org/reports/global-ev-outlook-2024/outlook-for-electric-mobility
International Energy Agency. (2025a). Global EV outlook 2025 [Report]. Link to source: https://www.iea.org/reports/global-ev-outlook-2025
International Energy Agency. (2025b). Breakthrough agenda report 2025 [Report]. Link to source: https://iea.blob.core.windows.net/assets/6f3b4ad7-b1aa-4791-b363-e4efe58cbb83/BreakthroughAgendaReport2025.pdf
International Transport Forum. (2020). Good to go? Assessing the environmental performance of new mobility [Corporate partnership board report]. Organisation for Economic Co-operation and Development/International Transport Forum. Link to source: https://www.itf-oecd.org/good-to-go-environmental-performance-new-mobility
International Transport Forum. (2023a). ITF transport outlook 2023 [Report]. Organisation for Economic Co-operation and Development. Link to source: https://doi.org/10.1787/b6cc9ad5-en
International Transport Forum. (2023b). Life-cycle assessment of passenger transport: An Indian case study [Policy paper]. Organisation for Economic Co-operation and Development. Link to source: https://doi.org/10.1787/2d11e416-en
Jaramillo, P., Ribeiro, S. K., Newman, P., Dhar, S., Diemuodeke, O. E., Kajino, T., Lee, D. S., Nugroho, S. B., Ou, X., Strømman, A. H., & Whitehead, J. (2022). Transport. In P. R. Shukla, J. Skea, R. Slade, A. Al Khourdajie, R. van Diemen, D. McCollum, M. Pathak, S. Some, P. Vyas, R. Fradera, M. Belkacemi, A. Hasija, G. Lisboa, S. Luz, & J. Malley (Eds.), Climate change 2022: Mitigation of climate change. Contribution of working group III to the sixth assessment report of the intergovernmental panel on climate change (pp. 1049–1160). Cambridge University Press. Link to source: https://doi.org/10.1017/9781009157926.012
Kamakaté, F., & Gordon, D. (2009). Managing motorcycles: Opportunities to reduce pollution and fuel use from two- and three-wheeled vehicles [Report]. International Council on Clean Transportation. Link to source: https://theicct.org/publication/managing-motorcycles-opportunities-to-reduce-pollution-and-fuel-use-from-two-and-three-wheeled-vehicles/
Kerr, G. H., Goldberg, D. L., & Anenberg, S. C. (2021). COVID-19 pandemic reveals persistent disparities in nitrogen dioxide pollution. Proceedings of the National Academy of Sciences, 118(30), Article e2022409118. Link to source: https://doi.org/10.1073/pnas.2022409118
Kumar, P. (2020, November 3). Busting the cost barrier: Why electric three-wheelers make business sense. World Resources Institute India. Link to source: https://wri-india.org/blogs/busting-cost-barrier-why-electric-three-wheelers-make-business-sense
Kumar, P., & Chakrabarty, S. (2020). Total cost of ownership analysis of the impact of vehicle usage on the economic viability of electric vehicles in India. Transportation Research Record: Journal of the Transportation Research Board, 2674(11), 563–572. Link to source: https://doi.org/10.1177/0361198120947089
Kumar, P., & Singh, A. (2024). Emerging opportunities for battery swapping in the electric two-wheeler segment in India. Transportation Research Record: Journal of the Transportation Research Board, 2678(1), 568–582. Link to source: https://doi.org/10.1177/03611981231171916
La Fleur, L., Lindkvist, E., Trångteg, R., Winter, S., & Thollander, P. (2024). Riding the future: Environmental, primary energy and economic analysis of an electric motorcycle - A Kenyan case study. Energy for Sustainable Development, 83, Article 101573. Link to source: https://doi.org/10.1016/j.esd.2024.101573
Mera, Z., & Bieker, G. (2023). Comparison of the life-cycle greenhouse gas emissions of combustion engine and electric passenger cars and two-wheelers in Indonesia [ICCT report]. International Council on Clean Transportation. Link to source: https://theicct.org/wp-content/uploads/2023/09/ID-17-%E2%80%93-LCA-Indonesia_report_final2.pdf
Montoya-Torres, J., Akizu-Gardoki, O., & Iturrondobeitia, M. (2023). Measuring life-cycle carbon emissions of private transportation in urban and rural settings. Sustainable Cities and Society, 96, Article 104658. Link to source: https://doi.org/10.1016/j.scs.2023.104658
Pan, S., Yu, W., Fulton, L. M., Jung, J., Choi, Y., & Gao, H. O. (2023). Impacts of the large-scale use of passenger electric vehicles on public health in 30 US. metropolitan areas. Renewable and Sustainable Energy Reviews, 173, Article 113100. Link to source: https://doi.org/10.1016/j.rser.2022.11310
Patil, M., Bandhu Majumdar, B., & Kumar Sahu, P. (2022). A comparative evaluation of the total cost of ownership between electric two-wheelers and motorized two-wheelers from an Indian perspective. Transportation Research Record: Journal of the Transportation Research Board, 2676(5), 526–550. Link to source: https://doi.org/10.1177/03611981221077087
Pennington, A. F., Cornwell, C. R., Sircar, K. D., & Mirabelli, M. C. (2024). Electric vehicles and health: A scoping review. Environmental Research, 251, Article 118697. Link to source: https://doi.org/10.1016/j.envres.2024.118697
Polanco Vásquez, L. O., Chavarría-Hernández, J. C., Arias Trinidad, A., Ordóñez-López, L. C., Forti Sosa, S., Contreras Pool, P. Y., & Barrera-Cabrera, J. N. (2025). Life cycle assessment of electric and gasoline moto-taxis in Yucatán, México: Impact of battery technology and social considerations. Energy for Sustainable Development, 85, Article 101614. Link to source: https://doi.org/10.1016/j.esd.2024.101614
Requia, W. J., Mohamed, M., Higgins, C. D., Arain, A., & Ferguson, M. (2018). How clean are electric vehicles? Evidence-based review of the effects of electric mobility on air pollutants, greenhouse gas emissions and human health. Atmospheric Environment, 185, 64–77. Link to source: https://doi.org/10.1016/j.atmosenv.2018.04.040
Schneider, F., Castillo Castro, D. S., Weng, K.-C., Shei, C.-H., & Lin, H.-T. (2023). Comparative life cycle assessment (LCA) on battery electric and combustion engine motorcycles in Taiwan. Journal of Cleaner Production, 406, Article 137060. Link to source: https://doi.org/10.1016/j.jclepro.2023.137060
Szyszkowicz, M., Kousha, T., Castner, J., & Dales, R. (2018). Air pollution and emergency department visits for respiratory diseases: A multi-city case crossover study. Environmental Research, 163, 263–269. Link to source: https://doi.org/10.1016/j.envres.2018.01.043
Tuayharn, K., Kaewtatip, P., Ruangjirakit, K., & Limthongkul, P. (2015). ICE motorcycle and electric motorcycle: Environmental and economic analysis [Technical paper 2015-01-0100]. SAE International. Link to source: https://doi.org/10.4271/2015-01-0100
United Nations Environment Programme. (2023). Electric two and three wheelers: Global emerging market overview [Report]. Link to source: https://www.unep.org/resources/report/global-emerging-market-overview-electric-two-and-three-wheelers
Wanyama, M. (2024). Africa’s automobile maintenance structure – How it can contribute to road crashes and increased emissions [Policy brief]. High Volume Transport Applied Research Programme. Link to source: https://transport-links.com/hvt-publications/africas-automobile-maintenance-structure-policy-brief
Weiss, M., Dekker, P., Moro, A., Scholz, H., & Patel, M. K. (2015). On the electrification of road transportation – A review of the environmental, economic, and social performance of electric two-wheelers. Transportation Research Part D: Transport and Environment, 41, 348–366. Link to source: https://doi.org/10.1016/j.trd.2015.09.007
World Health Organization. (2022). Powered two-and three-wheeler safety: A road safety manual for decision-makers and practitioners, second edition. Link to source: https://www.who.int/publications/i/item/9789240060562
Zia, S., Qureshi, S., Zulfiqar, M., & Ijaz, A. (2025). Assessing the feasibility of electric vehicle adoption in Pakistan affordability, preferences, and market readiness. Engineering Proceedings, 111(1), Article 42. Link to source: https://doi.org/10.3390/engproc2025111042
Ziegler, M. S., & Trancik, J. E. (2021). Re-examining rates of lithium-ion battery technology improvement and cost decline. Energy & Environmental Science, 14(4), 1635–1651. Link to source: https://doi.org/10.1039/d0ee02681f
Heather Jones, Ph.D.
Ruthie Burrows, Ph.D.
James Gerber, Ph.D.
Daniel Jasper
Alex Sweeney
Nina-Francesca Farac, Ph.D.
Heather McDiarmid, Ph.D.
Amanda D. Smith, Ph.D.
Electric scooters and motorcycles offer savings of up to 54.4 t CO₂‑eq /million pkm on a 100-year basis, compared with fossil fuel–powered models (Table 1) (Ayetor et al., 2023; Barreiros, 2020; Carranza et al., 2022; Cox & Mutel, 2018; International Transport Forum, 2020, 2023b; Mera & Bieker, 2023; Montoya-Torres et al., 2023; Polanco Vásquez et al., 2025; Schneider et al., 2023; Tuayharn et al., 2015). Every trip shifted from fossil fuel–powered models to electric models helps avoid GHG emissions by eliminating tailpipe emissions and replacing gasoline combustion with electricity use. Effectiveness is calculated by subtracting the per-pkm operating-phase emissions of electric models from the per-pkm operating-phase emissions of conventional fossil fuel–powered models. Furthermore, per-pkm emissions decrease as vehicle occupancy increases.
The extent of electric scooters and motorcycles’ long-term climate benefits across the vehicles’ life cycle depends on the local charging electricity mix. Widespread adoption of electric scooters and motorcycles supported by low-carbon grids delivers large GHG emissions reductions, for example, while electric scooter and motorcycle usage supported by fossil fuel–dominant grids narrows the emissions advantage over ICE models (Jaramillio et al., 2022). The effectiveness of electric scooters and motorcycles is likely an underestimate in many cities, particularly in Africa, where these vehicles are well positioned to replace old two-stroke motorcycles that generate high levels of pollution due to poor maintenance, counterfeit spare parts, and weak GHG emissions enforcement (Wanyama et al., 2024).
Table 1. Effectiveness at reducing emissions.
Unit: t CO₂‑eq (100-year basis)/million pkm
| 25th percentile | 29.9 |
| Mean | 48.2 |
| Median (50th percentile) | 54.4 |
| 75th percentile | 60.6 |
While it costs US$0.08/pkm to operate a fossil fuel–powered scooter or motorcycle, it costs only US$0.06/pkm for an electric model. This results in savings of US$0.02/pkm (US$20,800/million pkm) (Ayetor et al., 2023; Carranza et al., 2022; Cox & Mutel, 2018; Kumar, 2020; Kumar & Chakrabarty, 2020; La Fleur et al., 2024; Patil et al., 2022). These direct financial costs include vehicle purchase, maintenance expenses, and fuel. As a result, relying on electric models instead of their fossil fuel–powered counterparts generates a savings of US$382/t CO₂‑eq on a 100-year basis (Table 2).
Electric scooters and motorcycles also have a lower total operating cost than do fossil fuel–powered models, despite a higher initial purchase price. This is evident in a few African countries – including Ghana, Mauritius, Rwanda, Kenya, and South Africa – due to the high cost of gasoline compared withj electricity (Ayetor et al., 2023). In Ghana, gasoline cost US$7.13/gallon in 2023 while electricity cost US$0.04/kWh (Ayetor et al., 2023). However, the price difference between gasoline and electricity is much less in other countries, such as Egypt, India, and Spain (Ayetor et al., 2023; Carranza et al., 2022; Cox & Mutel, 2018; Kumar & Chakrabarty, 2020; La Fleur et al., 2024; Patil et al., 2022; United Nations Environment Programme [UNEP], 2023).
In most countries, the payback period for electric scooter and motorcycle users is about three to four years (IEA, 2020). Other countries, such as Pakistan, have reported a payback period as low as four to six months, while India reports a payback period ranging from one to eight years (Zia et al., 2025; Patil et al., 2022).
Table 2. Cost per unit of climate impact.
Unit: US$ (2023)/t CO₂‑eq (100-year basis)
| Median | -382 |
Very little literature exists exploring learning rates for electric scooters and motorcycles. In this analysis, we estimated a learning rate of just over 5% based on the median battery learning rate (13.5%) applied to the median battery portion (40%) of total cost (Table 3). Weiss et al. (2015) calculated a learning rate of 8% for all electric two-wheelers combined, including electric bicycles, scooters, and motorcycles.
Lithium-ion battery prices fell 97% during the past three decades, plummeting from US$7,500/kWh in 1991 to US$181/kWh in 2018. More importantly, lithium-ion battery costs halved between 2014–2018, while capacity increased by a factor of 50,000 over the same period.
Continuing the recent trend, battery prices declined another 8% from 2024 to 2025, dropping to US$108/kWh in 2025 (BloombergNEF, 2025). While the component of the learning rate linked to decreases in the price of lithium-ion batteries is expected to diminish in the coming years, advances in materials, design, technology, and the use of different battery types may contribute to future learning rate increases.
Table 3. Learning rate: Drop in cost per doubling of the installed solution base.
Unit: %
| 25th percentile | 4.2 |
| Mean | 5.4 |
| Median (50th percentile) | 5.4 |
| 75th percentile | 6.7 |
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 Scooters & Motorcycles 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 climate effectiveness of electric scooters and motorcycles depends strongly on the GHG emissions intensity of the electricity used for charging (IPCC, 2022). Additionally, it is important to consider that real-world performance and user acceptance of electric scooters and motorcycles can hinge on charging convenience and reliability. Even though many models can charge from standard sockets and some can use swapping, limited access to safe, affordable charging at home, work, or in public can constrain the degree to which electric scooters and motorcycles can be driven in practice (IEA, 2025b). Finally, in places where battery swapping is part of the charging strategy for electric scooters and motorcycles, the lack of common standards and interoperability (including battery form factors, connectors, communication protocols, and locking interfaces) can fragment markets and limit cross-brand usability, reducing the convenience benefits that swapping is meant to provide.
With approximately 79 million electric scooters and motorcycles in use worldwide – which corresponds to roughly 9% of the total global stock of nearly 859 million scooters and motorcycles (IEA, 2025a) – we estimated that electric scooters and motorcycles travel 865 billion pkm/yr (Table 4). We assumed this travel would occur on fossil fuel–powered scooters and motorcycles if electric scooters and motorcycles were not used. Adoption rates of electric scooters and motorcycles are much higher in countries such as China, where the global electric scooters and motorcycles stock share in 2024 was 39%.
To convert this number into pkm traveled via electric scooters and motorcycles, we needed to determine the median distance that each scooter and motorcycle travels per year. Using data from several different countries, the median scooter and motorcycle travels about 10,950 vehicle-kilometers (vkm)/yr. The vehicle occupancy was assumed to be one passenger per vehicle (International Transport Forum, 2020), making vkm equal to pkm. While occupancy is likely higher, reliable data are scarce; however, generally speaking increases in occupancy reduce GHG emissions and lower cost per pkm. Multiplying this number by the number of electric scooters and motorcycles in use (79 million) provides the total travel distance shifted (865 billion pkm/yr) from fossil fuel–powered scooters and motorcycles to their electric equivalents.
Table 4. Current (2024) adoption level.
Unit: million pkm/yr
| 25th percentile | 409,000 |
| Mean | 1,336,000 |
| Median (50th percentile) | 865,000 |
| 75th percentile | 1,580,000 |
Globally, the pkm driven via electric scooters and motorcycles rather than via fossil fuel–powered scooters and motorcycles increases by a median of about 110 billion pkm/yr (Table 5). Electric scooters and motorcycles purchases grew 22%/yr between 2019–2024 (IEA, 2025a). Global purchases of electric scooters and motorcycles are increasing by roughly 10 million vehicles/yr (IEA, 2025a).
Table 5. 2019–2024 adoption trend.
Unit: million pkm/yr
| 25th percentile | 41,000 |
| Mean | 166,000 |
| Median (50th percentile) | 110,000 |
| 75th percentile | 200,000 |
The total adoption ceiling for electric scooters and motorcycles is equal to the total passenger distance driven via scooters and motorcycles worldwide. Using the median distance traveled per vehicle annually, this translates to about 9.4 trillion pkm traveled per year (Table 6).
Replacing every fossil fuel–powered scooter and motorcycle with an electric scooter or motorcycle would require not only a major scale-up of electric scooter and motorcycle manufacturing (both vehicles and batteries), but also the rapid deployment of convenient charging options at homes, workplaces, and public locations, and cost reductions to make the purchase price of electric models affordable across income groups. While ambitious, this transition is technically possible. Electric scooters and motorcycles are already being produced at scale in several markets with new capacity being quickly added. Meanwhile, continued declines in battery cost – plus expanding charging and battery-swapping networks – can make widespread replacement both practical and cost-effective (IEA, 2025a).
Table 6. Adoption ceiling
Unit: million pkm/yr
| 25th percentile | 4,444,000 |
| Mean | 14,526,000 |
| Median (50th percentile) | 9,403,000 |
| 75th percentile | 17,174,000 |
The achievable adoption of electric scooter and motorcycle travel is roughly 6–8 trillion pkm/yr shifted from fossil fuel–powered ICE vehicles.
Various organizations and researchers have forecast future electric scooter and motorcycle adoption trends. These are not assessments of feasible adoption per se; rather, they are predictions of likely rates of adoption, given various assumptions about the future (Anup et el., 2021; Gupta et al., 2023; IEA, 2025a; Kumar & Singh, 2024; UNEP, 2023). Nevertheless, these forecasts are useful considering the sheer number of variables they take into account. To convert these estimates of future likely adoption into estimates of the achievable adoption range, we applied some optimistic assumptions to the numbers in the scenario projections.
To identify a lower feasible rate of adoption of electric scooters and motorcycles, we took the highest projected rate of electric scooters and motorcycles stock share by 2030, which was 60% in India according to Anup et al. (2021). This translates to 515 million electric scooters and motorcycles – or 5.6 trillion pkm/yr traveled via electric scooters and motorcycles.
To identify a high rate of adoption of electric scooters and motorcycles, we assumed that every country could reach the highest rate of adoption projected to occur for any country. Kumar and Singh (2024) predict that India could reach 80% electric scooters and motorcycles sales share by 2030; such a high share of sales would allow the stock share to quickly approach the rate of sales. We therefore set our high adoption rate at 80% adoption worldwide, which corresponds to 687 million electric scooters and motorcycles in use and 7.5 trillion pkm/yr traveled via electric scooters and motorcycles (Table 7).
Table 7. Range of achievable adoption levels.
Unit: million pkm/yr
| Current adoption | 865,000 |
| Achievable – low | 5,642,000 |
| Achievable – high | 7,522,000 |
| Adoption ceiling (physical limit) | 9,403,000 |
Electric scooters and motorcycles currently displace 0.05 Gt CO₂‑eq/yr of GHG emissions from the transportation system on a 100-yr basis (Table 8).
If electric scooters and motorcycles achieve 60% of the global scooters and motorcycles stock share – as Anup et al. (2021) projects will take place in India (our low achievable adoption estimate) – then with the current total number of scooters and motorcycles on the road, electric scooters and motorcycles will displace 0.31 Gt CO₂‑eq/yr of GHG emissions on a 100-yr basis.
If electric scooters and motorcycles reach 80% of global scooters and motorcycles stock share – our high achievable adoption estimate, as Kumar and Singh (2024) estimate might eventually happen in sales (that would lead to stock) in India – they will displace 0.41 Gt CO₂‑eq/yr of GHG emissions on a 100-yr basis.
And if electric scooters and motorcycles replace 100% of the global fleet of scooters and motorcycles – the adoption ceiling – they will displace 0.51 Gt CO₂‑eq/yr of GHG emissions on a 100-yr basis.
These estimates are based on the present-day emissions intensity from electrical grids; if grids become cleaner over time, the cumulative climate benefits of electric scooters and motorcycles would be even greater.
Table 8. Climate impact at different levels of adoption.
Unit: Gt CO₂‑eq/yr (100-yr basis)
| Current adoption | 0.05 |
| Achievable – low | 0.31 |
| Achievable – high | 0.41 |
| Adoption ceiling (physical limit) | 0.51 |
While the up-front cost of electric scooters and motorcycles is generally higher than that of fossil fuel–powered ICE scooters and motorcycles, electric scooter users and motorcyclists can save money on fuel costs once the initial costs are covered. Depending on mileage driven and fuel costs, the up-front cost can usually be recouped in about one year (UNEP, 2023).
Since electric scooters and motorcycles do not have tailpipe emissions, they can mitigate traffic-related air pollution, an environmental ill 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). Fossil fuel–powered motorcycles also emit toxic compounds such as benzene, formaldehyde, and polycyclic aromatic hydrocarbons, which are associated with increased cancer risk and short-term respiratory conditions (Kamakaté & Gordon, 2009).
Communities rich in racial and ethnic minorities tend to be located near highways and major traffic corridors, making those communities disproportionately exposed to air pollution compared to neighboring areas (Kerr et al., 2021). As a result, transitioning to electric scooters and motorcycles could improve community health in marginalized urban neighborhoods near highways (Pennington et al., 2024). These health benefits would prove particularly important for people in densely populated cities – especially in low- and middle-income countries where scooters and motorcycles are widely used and where air quality is often poor (La Fleur et al., 2024). It should be noted some of these benefits depend on the type of fuel used for electricity generation and could displace air pollution from urban centers to more rural areas near power plants.
Fossil fuel–powered ICE scooters and motorcycles can be very noisy, especially if they are not maintained regularly. In urban areas where motorcycles are a common choice for transportation, adopting electric motorcycles could improve noise pollution, which is a major chronic concern in cities across Asia and Africa (Kamakaté & Gordon, 2009; Hernandez et al., 2019; Sheng et al., 2016).
With the rapid growth of scooter use in urban areas of low- and middle-income countries, more widespread adoption of electric scooters could improve air pollution in densely populated areas where air quality is often a major concern. Increased adoption of electric scooters and motorcycles also reduces emissions of air pollutants associated with tailpipes, including particulate matter, sulfur oxides, sulfur dioxide, nitrogen oxides, carbon monoxide, and volatile organic compounds (Requia et al., 2018).
Electricity often costs less per pkm than gasoline, and electric scooter and motorcycle maintenance can be cheaper than maintenance for fossil fuel–powered ICE scooters and motorcycles. These factors lower marginal travel costs, which may increase pkm traveled for some users – partially offsetting GHG emissions benefits. This is a form of the rebound effect, where efficiency gains are offset by increased travel demand (Jaramillio et al., 2022).
If electric scooter and motorcycle fleets grow at a rate that outpaces the implementation of relevant safety measures, road safety could worsen given scooters and motorcycles already account for a large share of road traffic deaths worldwide. Rapid uptake of electric scooters and motorcycles in the absence of safer infrastructure, speed management, helmets, and enforcement could increase injuries and fatalities (World Health Organization [WHO], 2022).
Electric scooters and motorcycles reinforce non-car transportation modes by extending reach, offering first- and last-mile connections, and providing flexible options where fixed-route services are limited.
Electric scooters and motorcycles compete with alternatives to cars for the same traffic share. Once people have access to a scooter or motorcycle – electric or otherwise – they tend to use it frequently, to the detriment of other modes of transportation.
million passenger kilometers (million pkm)
CO₂ , CH₄, N₂O
Many electric scooters and motorcycles can charge from a standard household socket. Some areas also have battery swapping, meaning that infrastructure requirements for electric scooters and motorcycles are much lower than those for electric cars. However, there are still infrastructure requirements associated with electric scooter and motorcycle usage because riders need reliable, safe, and affordable access to charging or swapping, which can be a barrier for people who park on-street, live in multi-unit housing, or lack secure electricity access. For high-utilization commercial users such as delivery riders or motorcycle taxis, availability and uptime are critical, whereas downtime can lead to reduced earnings and weaken the business case for electrification (IEA, 2025b).
Consensus of effectiveness in decarbonizing the transport sector: High
A high level of consensus exists among major organizations working in the climate solutions arena that mobilizing electric scooters and motorcycles can offer a substantial reduction in GHG emissions. This segment of the transportation sector is already the most electrified in road transport globally, with roughly 79 million electric scooters and motorcycles on the road – or about 9% of the global fleet. IEA (2024) notes that full electrification of this segment is “within reach” with stronger policy support. Worldwide, road transport was responsible for more than 6 Gt CO₂ ‑eq emissions in 2024; more than 90% of those emissions came from cars and vans (60%) and trucks (33%), whereas only 7% of those emissions were generated by scooters and motorcycles (IEA, 2025a).
Electric scooters and motorcycles have been found to reduce external environmental costs as well, suggesting they can help accelerate the shift toward more sustainable transport systems (Carranza et al., 2022). Electric scooters and motorcycles generally outperform fossil fuel–powered scooter and motorcycle models in terms of environmental indicators (Montoya-Torres et al., 2023), and can retain advantages even when charged using electricity generated primarily from hard coal (Cox & Mutel, 2018).
The results presented in our analysis summarize findings from 14 original studies and seven reports reflecting current evidence from 23 countries. We recognize this limited geographic scope creates bias, and hope this work inspires research and data sharing on this topic in underrepresented regions.
Join the 80,000+ subscribers discovering how to drive meaningful climate action around the world! Every other week, you'll get expert insights, cutting-edge research, and inspiring stories.