Deploy Enhanced Rock Weathering

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Basalt
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Summary

Enhanced rock weathering removes CO₂ from the air by accelerating the natural chemical and physical breakdown of certain rocks. This carbon removal practice can be effective and has been deployed in pilot and small-scale commercial projects. Advantages include its reliance on a natural process (geological weathering), its potential for large-scale deployment on land or in the ocean, and its potential to improve soil conditions and crop yields. Disadvantages of enhanced rock weathering include unpredictable effectiveness for carbon removal, complex monitoring and measurement requirements, and high costs. We will “Keep Watching” Enhanced Rock Weathering, but it is not yet ready for large-scale deployment as a climate solution.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

Based on our analysis, enhanced rock weathering is a promising carbon removal technique, but it is not ready for large-scale deployment. We will “Keep Watching” this potential climate solution.

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? Yes
Risk Is it risky or harmful? ?
Cost Is it cheap? No

What is it?

Enhanced rock weathering is a practice that removes CO from the atmosphere by accelerating the natural chemical and physical breakdown, or weathering, of rocks such as basalt, olivine, or limestone. This is typically achieved by crushing the rocks into dust or sand-sized particles to increase their surface area before applying them to croplands, beaches, or directly into the ocean, the latter of which is also a form of carbon removal known as Ocean Alkalinity Enhancement. During weathering, the rock surface chemically reacts with atmospheric CO that is dissolved in rain or ocean water. This reaction produces bicarbonate ions containing the carbon from the captured CO and positively charged cations, such as magnesium or calcium, depending on the type of rock. For land-based enhanced rock weathering, the bicarbonate needs to be flushed out to the ocean, where it is stable and can be securely stored for thousands of years.  

Does it work?

The basic idea of enhanced rock weathering is scientifically and geologically sound. Its effectiveness in converting atmospheric CO into bicarbonate has been demonstrated in laboratory and field trials for several rock types and application sites. There are currently numerous research and demonstration projects underway. More than a dozen companies are selling enhanced rock weathering-based carbon removal credits, with nearly 10,000 t of CO reported to have been removed as of early 2025.

Why are we excited?

Enhanced rock weathering has several features that improve the likelihood that it can be scaled up to remove and store globally meaningful amounts of atmospheric CO (i.e., >0.1 Gt CO₂/yr). Since enhanced rock weathering utilizes a natural process – mineralization – it does not need to be combined with other technologies to capture CO from the air or durably store it. Moreover, it does not require external energy for the carbon capture and storage process, although it does use energy and generate emissions from the mining, crushing, transport, and deployment of the crushed rock. Suitable rock types, such as basalt, which is widely used in construction, paving, and concrete, are common and often locally available. Globally, there are large areas of land and ocean surface on which enhanced rock weathering could be deployed, including on croplands where current agricultural practices often already include regular application of soil amendments. A recent study suggested that extensive deployment of enhanced rock weathering on U.S. agricultural lands could sequester 0.16–0.30 Gt CO₂/yr by 2050. Other studies have shown that the application of crushed rock to croplands for enhanced rock weathering can improve soil pH, provide essential soil nutrients, and improve crop yields.

Why are we concerned?

There are numerous challenges for enhanced rock weathering, as well as potential risks and adverse impacts from its large-scale deployment. Numerous studies on both land- and ocean-based enhanced rock weathering have shown that the amounts of atmospheric CO converted into bicarbonate are highly variable, dependent on rock type, soil type, application rates, and other variables, and are therefore difficult to accurately predict and model. This makes measurement, reporting, and verification of the amount of CO captured and stored, which is essential for the carbon market, reliant on extensive and expensive field measurements and customized models. There are also concerns about the harmful impacts of heavy metals, like nickel or chromium, that can be released during weathering, as well as other ecological impacts and environmental justice concerns, particularly for crushed rock deployed on beaches or in the ocean. Finally, costs for deployment and the purchase of enhanced rock weathering-based carbon credits are relatively high (>US$200–US$500 per t CO removed) and will likely remain high if verification continues to depend on large numbers of field measurements and carbon removal cannot be easily modelled. There is a general consensus in the scientific community that the current knowledge base is not sufficient to reliably or accurately quantify the CO captured and stored by most land- or ocean-based enhanced rock weathering deployments.

References

Bach, L. T., Gill, S. J., Rickaby, R. A., Gore, S., & Renforth, P. (2019). CO₂ removal with enhanced weathering and ocean alkalinity enhancement: potential risks and co-benefits for marine pelagic ecosystems. Frontiers in Climate 1(7). https://doi.org/10.3389/fclim.2019.00007 

Beerling, D. J. et al. (2025). Transforming US agriculture for carbon removal with enhanced weathering. Nature 638, 425–434. https://doi.org/10.1038/s41586-024-08429-2 

CDR.fyi. Leaderboards. (2025). Leaderboards. Retrieved from CDR.fyi website: https://www.cdr.fyi/leaderboards 

Cong, L., Lu, S., Jiang, P., Zheng, T., Yu, Z., & Lü, X. (2024). CO₂ sequestration and soil improvement in enhanced rock weathering: A review from an experimental perspective. Greenhouse. Gas. Sci. Technol., 14, 1122–1138. https://doi.org/10.1002/ghg.2313 

Geerts, L. J., Hylén, A., & Meysman, F. J. (2025). Review and syntheses: Ocean alkalinity enhancement and carbon dioxide removal through marine enhanced rock weathering using olivine. Biogeosciences 22(2), 355–384. https://doi.org/10.5194/bg-22-355-2025 

Höglund, R. (2025). Buyers of Enhanced Rock Weathering credits need to ask for the right type of MRV. Milkywire. https://www.milkywire.com/articles/buyers-of-enhanced-rock-weathering-credits-need-to-ask-for-the-right-type-of-mrv 

Jagoutz, O. & Krol, A. (2023). Enhanced Rock Weathering. MIT Climate Portal. https://climate.mit.edu/explainers/enhanced-rock-weathering 

Jeswani, H. K., Saharudin, D. M., & Azapagic, A. (2022). Environmental sustainability of negative emissions technologies: A review. Sustainable Production and Consumption 33, 608–635. https://doi.org/10.1016/j.spc.2022.06.028 

Jones, W., Bower, G., Pastorek, N., King, B., Larsen, J., Houser, T., Dasari, N., & McCusker, K. (2024). The landscape of carbon dioxide removal and US policies to scale solutions. https://rhg.com/wp-content/uploads/2024/04/The-Landscape-of-Carbon-Dioxide-Removal-and-US-Policies-to-Scale-Solutions.pdf 

Morris, A. (2024). Testing limestone’s ability to capture carbon from air. Northwestern Now. https://news.northwestern.edu/stories/2024/11/northwestern-scientists-test-limestones-ability-to-capture-carbon-from-air/ 

OPIS & CDR.fyi. (2025). Bridging the gap: Durable CDR market pricing survey. https://www.cdr.fyi/reports/pricing-survey-jan-2025.pdf 

Taylor, L. et al. (2016). Enhanced weathering strategies for stabilizing climate and averting ocean acidification. Nature Climate Change 6, 402–406. https://doi.org/10.1038/nclimate2882 

Credits

Lead Fellow

  • Christina Swanson, Ph.D.

Internal Reviewer

  • Sarah Gleeson, Ph.D.
Speed of Action
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Action Word
Deploy
Solution Title
Enhanced Rock Weathering
Classification
Keep Watching
Updated Date

Produce Bio-bricks / Bio‑oils

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Drop of oil
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Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Solution in Action
Speed of Action
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Caveats
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Additional Benefits
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Risks
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Consensus
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Action Word
Produce
Solution Title
Bio-bricks / Bio‑oils
Classification
Keep Watching
Updated Date

Advance Cultivated Meat

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Fried chicken sandwich
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Summary

Cultivated meat is produced from a sample of animal cells, rather than by slaughtering animals. This technology shows promise for reducing emissions from animal agriculture, but its climate impact depends on the energy source used during production. Research and development are still in early stages, and whether the products can scale depends on continued investments, consumer approval, technological growth, and regulatory acceptance. While cultivated meat shows potential, evidence about its emissions reduction potential is limited, and the high costs of production may restrain its scalability. Based on our assessment, we will “Keep Watching” this potential solution.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

Based on our analysis, cultivated meat is promising in its ability to reduce emissions from meat production, but the impact on a large scale remains unclear. 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? Limited
Effective Does it consistently work? Yes
Impact Is it big enough to matter? ?
Risk Is it risky or harmful? No
Cost Is it cheap? No

What is it?

Cultivated meat (also called lab-grown or cultured meat) is a cellular agriculture product that, when used to replace meat from livestock, can reduce emissions. Cultivated meat is developed through bioengineering. Its production uses sample cells from an animal, in addition to a medium that supports cell growth in a bioreactor. Energy is required to produce the ingredients for the growth medium and to run the bioreactor (e.g., for temperature control, the mixing processes, aeration).

Does it work? 

Since the development of cultivated meat is still in its infancy, there is limited evidence on its emissions savings potential from large-scale production. Preliminary estimates differ by an order of magnitude, depending on the energy source used in the lab environment. Using fossil energy sources, emissions generated from the production of one kilogram of cultivated meat could reach 25 kilograms CO₂‑eq. If renewable energy is used, emissions could be about two kilograms CO₂‑eq per kilogram of cultivated meat. By comparison, producing a kilogram of beef from livestock generates 80–100 kilograms CO₂‑eq, on average. Almost half of those emissions from livestock beef are in the form of methane. Producing pig meat and poultry meat generates about 12 kilograms and 10 kilograms of CO₂‑eq, respectively. Based on these estimates, cultivated meat could substantially reduce the emissions of beef. Compared to pork and chicken, however, its emissions depend on the source of energy used during production.

Why are we excited?

The cultivated meat industry is fairly new but growing rapidly. The first cell-cultivated meat product was developed in 2013. In 2024, there were 155 companies involved in the industry, located across six continents, mostly based in the United States, Israel, the United Kingdom, and Singapore. Agriculture is responsible for about 22% of global GHG emissions, and raising livestock, especially beef, is particularly emissions-intensive. Therefore, cultivated meat has great potential to reduce related emissions as demand for meat continues to grow across the world. Cultivated meat enables the production of a large amount of meat from a single stem cell. This means that far fewer animals will be needed for meat production. Cultivated meat is also more efficient at converting feed into meat than chickens, which reduces emissions associated with feed production and demand for land.

Why are we concerned?

Concerns about cultivated meat include scalability, cost, and consumer acceptance. Because cultivated meat is still an emerging area of food science, the cost of production may be prohibitive at a large scale. Although cell culture is routinely performed in industrial and academic labs, creating the culture medium for mass-market production at competitive prices will require innovations and significant cost reductions. There are still many unknowns about the commercial potential of cultivated meat and whether consumers will accept the products. In 2024, companies began to move from research labs to larger facilities to start producing meat for consumers. There are only two countries that allow the sale of cultivated meat: Singapore and the United States. Within the United States, about one-third of adults find the concept of cultivated meat appealing, and only about 17% would be likely to purchase it, according to a poll conducted on behalf of the Good Food Institute. However, even substituting a fraction of the beef consumed in the United States with cultivated meat could have an important impact on reducing emissions. Cultivated meat is a novel food and may require consumer education and producer transparency on production methods and safeguards in order to become more widely accepted.

Solution in Action
References

Congressional Research Service of the United States (2023). Cell-Cultivated Meat: An Overview https://www.congress.gov/crs-product/R47697

Garrison, G. L., et al. (2022). How much will large-scale production of cell-cultured meat cost?. Journal of Agriculture and Food Research, 10: 100358. https://doi.org/10.1016/j.jafr.2022.100358

Good Food Institute (2025). 2024 State of the Industry report: Cultivated meat, seafood, and ingredients. https://gfi.org/resource/cultivated-meat-seafood-and-ingredients-state-of-the-industry/

Good Food Institute (2024). Consumer snapshot: Cultivated meat in the U.S. https://gfi.org/wp-content/uploads/2025/01/Consumer-snapshot-cultivated-meat-in-the-US.pdf

Good Food Institute (2020). An analysis of culture medium costs and production volumes for cultivated meat https://gfi.org/resource/analyzing-cell-culture-medium-costs/

Gursel, I. et al. (2022). Review and analysis of studies on sustainability of cultured meat. Wageningen Food & Biobased Research. https://edepot.wur.nl/563404

Mendly-Zambo, Z., et al. (2021). Dairy 3.0: cellular agriculture and the future of milk. Food, Culture & Society, 24(5), 675–693. https://doi.org/10.1080/15528014.2021.1888411

MIT Technology Review (2023). Here’s what we know about lab-grown meat and climate change. https://www.technologyreview.com/2023/07/03/1075809/lab-grown-meat-climate-change/

J. Poore, & T. Nemecek (2018). Reducing food’s environmental impacts through producers and consumers. Science, 360, 987-992. https://doi.org/10.1126/science.aaq0216

Risner, D., et al. (2023) Environmental impacts of cultured meat: A cradle-to-gate life cycle assessment. bioRxiv, 2023.04.21.537778; doi: https://doi.org/10.1101/2023.04.21.537778

Sinke, P., et al. (2023). Ex-ante life cycle assessment of commercial-scale cultivated meat production in 2030. Int J Life Cycle Assess, 28, 234–254 https://doi.org/10.1007/s11367-022-02128-8

Treich, N. (2021). Cultured Meat: Promises and Challenges. Environ Resource Econ, 79, 33–61 https://doi.org/10.1007/s10640-021-00551-3

Tuomisto HL, et al. (2022) Prospective life cycle assessment of a bioprocess design for cultured meat production in hollow fiber bioreactors. Science of the Total Environment, 851:158051

World Bank (2024) Recipe for a Livable Planet: Achieving Net Zero Emissions in the Agrifood System https://openknowledge.worldbank.org/entities/publication/406c71a3-c13f-49cd-8f3f-a071715858fb

Xu X, Sharma P, Shu S et al (2021) Global greenhouse gas emissions from animal-based foods are twice those of plant-based foods. Nature Food, 2:724–732 https://doi.org/10.1038/s43016-021-00358-x 

Credits

Lead Fellow

  • Emily Cassidy

Internal Reviewers

  • Eric Toensmeier
  • Paul West, Ph.D.
  • Christina Swanson, Ph.D.
Speed of Action
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Action Word
Advance
Solution Title
Cultivated Meat
Classification
Keep Watching
Updated Date

Mobilize Green Hydrogen for Aviation and Trucking

Cluster
Fuel Switching
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A graphic of a clear bubble in the form of a molecule with a green background
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Summary

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.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

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

What is it?

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.

Does it work?

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.

Why are we excited?

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.

Why are we concerned?

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.

Solution in Action
References

Clean Hydrogen Partnership. (2020). Hydrogen-powered aviation. https://www.clean-hydrogen.europa.eu/media/publications/hydrogen-powered-aviation_en

Clean Hydrogen Partnership. (2020). Study on Fuel Cells Hydrogen Trucks. 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. https://doi.org/10.1016/j.apenergy.2023.121369

IEA. (2019). The Future of Hydrogen – Analysis. IEA. https://www.iea.org/reports/the-future-of-hydrogen

IPCC. (2022). IPCC Sixth Assessment Report Working Group III: Mitigation of Climate Change, Chapter 10: Transport. Retrieved May 28, 2025, from https://www.ipcc.ch/report/ar6/wg3/chapter/chapter-10/

IRENA. (2022). Green Hydrogen for Industry: A Guide to Policy Making. https://www.irena.org/publications/2022/Mar/Green-Hydrogen-for-Industry

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. https://doi.org/10.1016/j.enpol.2021.112703

McKinsey. (2023). Global Energy Perspective 2023: Hydrogen outlook. https://www.mckinsey.com/industries/oil-and-gas/our-insights/global-energy-perspective-2023-hydrogen-outlook 

Credits

Lead Fellow

  • Heather Jones, Ph.D.

Internal Reviewers

  • Heather McDiarmid, Ph.D.
  • Christina Swanson, Ph.D.
Speed of Action
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Caveats
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Additional Benefits
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Risks
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Consensus
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Trade-offs
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Action Word
Mobilize
Solution Title
Green Hydrogen for Aviation and Trucking
Classification
Keep Watching
Updated Date

Deploy Sustainable Aviation Fuel

Cluster
Fuel Switching
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Airline jet engine
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Summary

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.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

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

What is it?

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.

Does it work?

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.

Why are we excited?

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. 

Why are we concerned?

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.

Solution in Action
References

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. 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. https://transport.ec.europa.eu/transport-modes/air/environment/refueleu-aviation_en 

ICAO. (n.d.). LTAG Costs and Investments. ICAO. https://www.icao.int/environmental-protection/LTAG/Pages/LTAG-and-Fuels.aspx

ICAO. (n.d.). Sustainable Aviation Fuels. 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. 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

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 

Credits

Lead Fellow

  • Heather Jones, Ph.D.

Internal Reviewers

  • Christina Swanson, Ph.D.
  • Emily Cassidy
Speed of Action
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Caveats
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Additional Benefits
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Risks
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Consensus
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Trade-offs
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Action Word
Deploy
Solution Title
Sustainable Aviation Fuel
Classification
Keep Watching
Updated Date

Deploy Plastic Alternatives / Bioplastics

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Colorful smoothies in plastic cups with label 100% biodegradable
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Summary

Bioplastics are renewable, plant-based alternatives to conventional plastics that can reduce emissions by replacing fossil-based feedstocks with biogenic carbon feedstocks. These feedstocks are biomass materials that absorb atmospheric CO₂ during growth and serve as the carbon source for plastic production. The chemical and biological properties of bioplastics are well understood, commercially validated, and can reduce emissions when produced sustainably and managed properly at their end-of-life. Benefits include reducing fossil fuel reliance, alleviating plastic pollution, and, in targeted uses, supporting circularity. However, these are counterbalanced by their inconsistent emissions savings, high costs, and scalability constraints. We conclude that deploying bioplastics as plastic alternatives remains a climate solution to “Keep Watching”, but would require changes in feedstock and appropriate end-of-life infrastructure to achieve reliable emissions reductions.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

Based on our analysis, the widespread use of bioplastics is challenged by their potential ecological risks and currently high costs. While bioplastics offer some environmental benefits in niche applications, their climate impact is inconsistent and hinges on feedstock type, manufacturing practices, and waste management. Therefore, we conclude that Deploy Bioplastics is a 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? No
Risk Is it risky or harmful? ?
Cost Is it cheap? No

What is it?

Bioplastics (also called biopolymers) are plastic alternatives made from renewable biological sources, such as corn, sugarcane, crop residues, or other plants, instead of fossil fuels. Bioplastics are produced by extracting sugars or starches from plants and converting them through chemical or biological processes into chemical building blocks that form the basic structure of plastics. Because plants absorb atmospheric CO₂ through photosynthesis, the carbon stored in bioplastics is considered biogenic, as it is already part of the natural carbon cycle. In contrast, petrochemical plastics are made by extracting and refining oil or natural gas, which releases new (formerly buried) carbon into the atmosphere. Bioplastics cut emissions by replacing fossil carbon feedstocks with biomass-based feedstocks. Some bioplastics are durable, non-biodegradable, chemically identical to traditional plastics (i.e., “drop-in” bioplastics), and recyclable. Others are biodegradable and can be designed to break down in compost. Emissions from bioplastics come from growing and processing biomass (which requires energy and land use), manufacturing the plastics, and managing their end-of-life waste. Bioplastics can achieve climate benefits when the emissions from production and end-of-life are kept low enough to realize the advantages of biogenic carbon.

Does it work?

The basic idea of bioplastics is scientifically and chemically sound, with their development and commercialization ongoing since the 1990s. Numerous studies support the effectiveness of bioplastics in reducing atmospheric CO₂ emissions from feedstock production and manufacturing stages compared to fossil-based plastics, particularly when made from sustainably sourced biomass under energy-efficient conditions and properly composted or recycled. However, other studies show bioplastics have inconsistent emissions reduction performance. Global adoption also remains limited, representing only about 0.5% of total plastics production (approximately 2–2.5 million tons (Mt) out of 414 Mt, according to the organization European Bioplastics). 

Why are we excited?

Bioplastics, particularly biologically derived and biodegradable polymers, have functional advantages in reducing fossil fuel dependence and mitigating plastic pollution. By sourcing raw materials from renewable biomass instead of petroleum (e.g., oil, natural gas), bioplastics can lower CO₂ emissions in the production stage, especially when accounting for biogenic carbon uptake during plant cultivation. Some types of bioplastics are interchangeable with traditional plastics and can be produced with existing plastic manufacturing systems, easing the transition. Compostable plastics simplify disposal in applications where contamination with food or organic waste occurs, enabling organic recycling and returning carbon and other nutrients to soil. Biodegradable bioplastics are also advantageous for products that are often discarded and may leak into the environment. Studies show that two widely used commercial bioplastics, polylactic acid (PLA) and polyhydroxybutyrate (PHB), biodegrade 60–80% in composting conditions within 28–30 days, while cellulose-based and starch-based plastics can fully degrade in soil and marine environments in 180 days and 50 days, respectively. These functional benefits, combined with potential additional benefits, such as soil enrichment and waste stream simplification, make bioplastics appealing in specific, targeted use cases. More broadly, they can significantly contribute to emissions reduction efforts in materials production when designed for circularity and supported by infrastructure that facilitates appropriate end-of-life waste treatment. 

Why are we concerned?

Despite their promise, bioplastics have several limitations as a viable climate solution, including relatively low emissions reduction potential and possible risks and adverse impacts from their large-scale deployment. Current production is low. To reach a meaningful 20–30% marketplace share by 2040, bioplastics would need to expand manufacturing by approximately 30% per year, nearly double the current pace. This could put pressure on land and food systems, since current bioplastics rely on food-based crops for industrial-level production. This raises sustainability concerns around food security and could potentially drive unintended land-use changes such as deforestation or cropland conversion. Furthermore, the effectiveness of reducing emissions by replacing conventional plastics with bioplastics is low and inconsistent. Some bioplastics produce more life cycle emissions than conventional plastics. The likely climate impact of replacing 20–30% of traditional plastics with bioplastics is <0.1 Gt CO₂‑eq/yr. End-of-life treatment is also a major challenge. Many bioplastics are incompatible with home composting and current recycling streams, and improperly composted or landfilled biodegradable bioplastics can emit methane. Finally, bioplastics remain 2–3 times more expensive than conventional plastics.

Solution in Action
References

Barbu, B. (2024). Can biodegradable polymers make microplastics? C&EN Global Enterprise, 102(37), 21–22. https://doi.org/10.1021/cen-10237-cover4‌ 

Bauer, F., Nielsen, T. D., Nilsson, L. J., Palm, E., Ericsson, K., Fråne, A., & Cullen, J. (2022). Plastics and climate change—Breaking carbon lock-ins through three mitigation pathways. One Earth, 5(4), 361–376.‌ https://doi.org/10.1016/j.oneear.2022.03.007 

Benavides, P. T., Lee, U., & Zarè-Mehrjerdi, O. (2020). Life cycle greenhouse gas emissions and energy use of polylactic acid, bio-derived polyethylene, and fossil-derived polyethylene. Journal of Cleaner Production, 277(124010), 124010. https://doi.org/10.1016/j.jclepro.2020.124010 

Bishop, G., Styles, D., & Lens, P. N. L. (2022). Land-use change and valorisation of feedstock side-streams determine the climate mitigation potential of bioplastics. Resources, Conservation and Recycling, 180, 106185. https://doi.org/10.1016/j.resconrec.2022.106185‌ 

Chen, G., Li, J., Sun, Y., Wang, Z., Leeke, G. A., Moretti, C., Cheng, Z., Wang, Y., Li, N., Mu, L., Li, J., Tao, J., Yan, B., & Hou, L. (2024). Replacing traditional plastics with biodegradable plastics: Impact on carbon emissions. Engineering, 32, 152–162. https://doi.org/10.1016/j.eng.2023.10.002 

Cotterill, M. (2020, August 5). Bioplastics: Don’t let the label fool you. Canadian Geographic.
https://canadiangeographic.ca/articles/bioplastics-dont-let-the-label-fool-you/ 

Di Bartolo, A., Infurna, G., & Dintcheva, N. T. (2021). A review of bioplastics and their adoption in the circular economy. Polymers, 13(8), 1229. https://doi.org/10.3390/polym13081229 

Dokl, M., Copot, A., Krajnc, D., Fan, Y. V., Vujanović, A., Aviso, K. B., Tan, R. R., Kravanja, Z., & Čuček, L. (2024). Global projections of plastic use, end-of-life fate and potential changes in consumption, reduction, recycling and replacement with bioplastics to 2050. Sustainable Production and Consumption, 51, 498–518. https://doi.org/10.1016/j.spc.2024.09.025 

Escobar, N., & Britz, W. (2021). Metrics on the sustainability of region-specific bioplastics production, considering global land use change effects. Resources, Conservation and Recycling, 167, 105345. https://doi.org/10.1016/j.resconrec.2020.105345 

‌‌European Bioplastics. (2023). Bioplastics market development update 2023. European Bioplastics E.V. https://docs.european-bioplastics.org/publications/market_data/2023/EUBP_Market_Data_Report_2023.pdf 

‌‌European Bioplastics. (2024). Bioplastics market development update 2024. European Bioplastics E.V. https://www.european-bioplastics.org/market/ 

Ferreira-Filipe, D. A., Paço, A., Duarte, A. C., Rocha-Santos, T., & Patrício Silva, A. L. (2021). Are biobased plastics green alternatives?—A critical review. International Journal of Environmental Research and Public Health, 18(15), 7729. https://doi.org/10.3390/ijerph18157729 

Helm, L. T., Venier-Cambron, C., & Verburg, P. H. (2025). The potential land-use impacts of bio-based plastics and plastic alternatives. Nature Sustainability8, 190–201. https://doi.org/10.1038/s41893-024-01492-7 

Islam, M., Xayachak, T., Haque, N., Lau, D., Bhuiyan, M., & Pramanik, B. K. (2024). Impact of bioplastics on environment from its production to end-of-life. Process Safety and Environmental Protection, 188, 151–166. https://doi.org/10.1016/j.psep.2024.05.113‌ 

Ita-Nagy, D., Vázquez-Rowe, I., Kahhat, R., Chinga-Carrasco, G., & Quispe, I. (2020). Reviewing environmental life cycle impacts of biobased polymers: current trends and methodological challenges. The International Journal of Life Cycle Assessment, 25(11), 2169–2189. https://doi.org/10.1007/s11367-020-01829-2‌ 

Karali, N., Khanna, N., & Shah, N. (2024, April 12). Climate Impact of Primary Plastic Production [Review of Climate Impact of Primary Plastic Production]. Lawrence Berkeley National Laboratory. https://escholarship.org/uc/item/6cc1g99q‌ 

Meng, F., Brandão, M., & Cullen, J. M. (2024). Replacing plastics with alternatives is worse for greenhouse gas emissions in most cases. Environmental Science & Technology, 58(6), 2716–2727. https://doi.org/10.1021/acs.est.3c05191‌ 

Patria, R. D., Rehman, S., Yuen, C. W. M., Lee, D.-J., Vuppaladadiyam, A. K., & Leu, S. (2024). Energy-environment-economic (3E) hub for sustainable plastic management – Upgraded recycling, chemical valorization, and bioplastics. Applied Energy, 357, 122543. https://doi.org/10.1016/j.apenergy.2023.122543‌ 

Piemonte, V., & Gironi, F. (2010). Land-use change emissions: How green are the bioplastics? Environmental Progress & Sustainable Energy, 30(4), 685–691. https://doi.org/10.1002/ep.10518 

Plastics Europe. (2024, November 18). Plastics – the fast Facts 2024 • Plastics Europe. Plastics Europe. https://plasticseurope.org/knowledge-hub/plastics-the-fast-facts-2024/ 

Rosenboom, J.-G., Langer, R., & Traverso, G. (2022). Bioplastics for a circular economy. Nature Reviews Materials, 7, 117–137. https://doi.org/10.1038/s41578-021-00407-8 

‌The multifaceted challenges of bioplastics. (2024). Nature Reviews Bioengineering, 2(4), 279–279. https://doi.org/10.1038/s44222-024-00181-6 

Vanderreydt, I., Rommens, T., Tenhunen, A., Mortensen, L. F., & Tange, I. (2021, May). Greenhouse gas emissions and natural capital implications of plastics (including biobased plastics). Eionet Portal; European Environment Agency (EEA) European Topic Centre on Waste and Materials in a Green Economy. 
https://www.eionet.europa.eu/etcs/etc-wmge/products/etc-wmge-reports/greenhouse-gas-emissions-and-natural-capital-implications-of-plastics-including-biobased-plastics 

‌Walker, S., & Rothman, R. (2020). Life cycle assessment of bio-based and fossil-based plastic: A review. Journal of Cleaner Production, 261, 121158. https://doi.org/10.1016/j.jclepro.2020.121158 

Zhao, X., Cornish, K., & Vodovotz, Y. (2020). Narrowing the gap for bioplastic use in food packaging: An update. Environmental Science & Technology, 54(8), 4712–4732. https://doi.org/10.1021/acs.est.9b03755 

‌Zhao, X., Wang, Y., Chen, X., Yu, X., Li, W., Zhang, S., Meng, X., Zhao, Z.-M., Dong, T., Anderson, A., Aiyedun, A., Li, Y., Webb, E., Wu, Z., Kunc, V., Ragauskas, A., Ozcan, S., & Zhu, H. (2023). Sustainable bioplastics derived from renewable natural resources for food packaging. Matter, 6(1), 97–127. https://doi.org/10.1016/j.matt.2022.11.006 

Credits

Lead Fellow

  • Nina-Francesca Farac, Ph.D.

Contributors

  • Amanda Smith, Ph.D.
  • Sarah Gleeson, Ph.D.

Internal Reviewer

  • Christina Swanson, Ph.D.
Speed of Action
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Caveats
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Additional Benefits
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Risks
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Consensus
left_text_column_width
Trade-offs
left_text_column_width
Action Word
Deploy
Solution Title
Plastic Alternatives / Bioplastics
Classification
Keep Watching
Updated Date

Deploy Small Modular Nuclear Reactors

Sector
Electricity
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Exterior of a small modular nuclear facility
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Summary

Small modular nuclear reactors (SMRs) are advanced reactors designed to produce low-carbon electricity using smaller units that are factory-fabricated. SMRs aim to overcome the safety, cost, and scalability challenges of traditional large-scale nuclear power. They offer benefits such as passive safety systems, lower capital investment, and the potential to be deployed flexibly in remote or underserved regions. However, commercial deployment is limited, the costs remain uncertain, and long-term nuclear waste and proliferation concerns persist. We “Keep Watching” SMRs as a promising climate solution still in development that has not yet proven its readiness for large-scale implementation.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

Based on our analysis, SMRs are a plausible and potentially impactful climate solution, but they are not yet ready for widespread deployment. The core technology is credible and carries significant potential for reducing GHG emissions. However, readiness, cost certainty, and deployment evidence are still lacking. For now, we will “Keep Watching” SMRs.

Plausible Could it work? Yes
Ready Is it ready? No
Evidence Are there data to evaluate it? No
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

What is it?

Small modular nuclear reactors (SMRs) are advanced reactors that produce low-carbon electricity by harnessing the heat from nuclear fission, an established and well-understood physical process. The innovation of SMRs lies primarily in their design. Typically smaller than traditional reactors, with a capacity of less than 300 megawatts (MW), SMRs are factory-built for enhanced quality control. This design allows them to be delivered to installation sites more quickly and potentially at a lower cost compared to conventional reactors, which typically range in capacity from about 700 MW to over 1,600 MW. While SMRs are generally considered "utility-scale" in their capacity, their smaller size makes them a viable option for smaller-scale applications, such as large micro-grids. These reactors can be assembled in a modular fashion, allowing incremental capacity additions. Additionally, some SMR designs boast enhanced safety features, including passive cooling systems that can function without external power sources, reducing the risks associated with reactor overheating or meltdowns. Currently, several countries are planning the deployment of SMRs, particularly China and the United States. Given their modular nature, several African countries, such as Ghana, are also looking toward SMRs to address their energy access deficits. Based on current plans, the International Energy Agency expects several countries to have multiple SMRs installed and operational by around 2030.

Does it work?

The physics behind SMRs is sound, and their potential as low-carbon energy sources is also scientifically valid, as they do not emit GHG emissions during operation. Several pilot SMR projects have also been launched. SMRs have yet to move beyond the demonstration phase to widespread commercial adoption. No SMR is currently deployed at the scale necessary to reduce global emissions measurably. Furthermore, independent, peer-reviewed empirical data on long-term operational performance, scalability, and cost remain sparse. While several countries, including the United States, Hungary, China, and Ghana, have announced plans or are discussing deploying SMRs within the next decade, those plans are still in the preparatory stages.

Why are we excited?

SMRs have several features that make them appealing as a potential climate solution. If scaled appropriately, they could displace fossil-fuel-based power generation and reduce carbon emissions significantly. Projected deployment scenarios by the Nuclear Energy Agency suggest that by 2050, the global SMR market could reach 375 gigawatts of installed capacity, avoiding up to 15 Gt of cumulative CO₂ emissions. Their smaller size and modular nature reduce financial risk, making them potentially more accessible to developing countries or smaller utilities. They are also flexible in siting and can complement variable renewable energy sources like solar and wind by providing reliable baseload or backup power. Additionally, SMRs could help decarbonize hard-to-electrify sectors like process heat in industry or remote energy systems. These attributes have prompted excitement among proponents who see SMRs as a scalable, flexible, and resilient solution for emissions-free power. 

Why are we concerned?

Despite their promise, SMRs face several challenges that limit their readiness for large-scale deployment. Safety remains a concern – not necessarily because of design flaws, but because any nuclear reactor carries inherent risks. Waste disposal and the potential for proliferation of nuclear materials remain persistent issues. Regulatory hurdles are also significant, as existing frameworks are often geared toward conventional reactors and may slow the licensing of newer designs. The cost of SMRs is another outstanding question. Recent analyses by Wood Mackenzie suggest that SMRs could cost US$6,000 to US$8,000 per kilowatt of capacity, which is well above the costs of utility-scale solar (US$1,448) or onshore wind (US$2,098). Deployment timelines also pose a challenge. Given the urgency of climate action, technologies that cannot be deployed at scale within the next 10–15 years may offer limited near-term benefits. A recent study by the Institute for Energy Economics and Financial Analysis opines that SMRs are still too costly, too time-consuming to construct, and too risky to significantly impact the transition away from fossil fuels in the next decade. While peer-reviewed academic studies have been conducted, a comprehensive, independent evaluation of large-scale deployment remains absent.

Solution in Action
References

Asuega, A., Limb, B. J., & Quinn, J. C. (2023). Techno-economic analysis of advanced small modular nuclear reactors. Applied Energy, 334, 120669. https://doi.org/10.1016/J.APENERGY.2023.120669

Hussein, E. M. A. (2020). Emerging small modular nuclear power reactors: A critical review. Physics Open, 5, 100038. https://doi.org/10.1016/J.PHYSO.2020.100038

IEA. (2025). The Path to a New Era for Nuclear Energy. https://www.iea.org/reports/the-path-to-a-new-era-for-nuclear-energy

Midgley, E. (2023). Decarbonizing Industries with the Help of Small and Micro Nuclear Reactors | IAEA. https://www.iaea.org/bulletin/decarbonizing-industries-with-the-help-of-small-and-micro-nuclear-reactors

Sam, R., Sainati, T., Hanson, B., & Kay, R. (2023). Licensing small modular reactors: A state-of-the-art review of the challenges and barriers. Progress in Nuclear Energy, 164, 104859. https://doi.org/10.1016/J.PNUCENE.2023.104859

Sovacool, B. K., Andersen, R., Sorensen, S., Sorensen, K., Tienda, V., Vainorius, A., Schirach, O. M., & Bjørn-Thygesen, F. (2016). Balancing safety with sustainability: assessing the risk of accidents for modern low-carbon energy systems. Journal of Cleaner Production, 112, 3952–3965. https://doi.org/10.1016/J.JCLEPRO.2015.07.059

Van Hee, N., Peremans, H., & Nimmegeers, P. (2024). Economic potential and barriers of small modular reactors in Europe. Renewable and Sustainable Energy Reviews, 203. https://doi.org/10.1016/j.rser.2024.114743

Vanatta, M., Patel, D., Allen, T., Cooper, D., & Craig, M. T. (2023). Technoeconomic analysis of small modular reactors decarbonizing industrial process heat. Joule, 7(4), 713–737. https://doi.org/10.1016/J.JOULE.2023.03.009

World Nuclear Association. (2024). Small Nuclear Power Reactors. https://world-nuclear.org/information-library/nuclear-fuel-cycle/nuclear-power-reactors/small-nuclear-power-reactors 

Credits

Lead Fellow 

  • Michael Dioha, Ph.D.

Internal Reviewer

  • Christina Swanson, Ph.D.
Speed of Action
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Caveats
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Additional Benefits
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Risks
left_text_column_width
Consensus
left_text_column_width
Trade-offs
left_text_column_width
Action Word
Deploy
Solution Title
Small Modular Nuclear Reactors
Classification
Keep Watching
Updated Date

Deploy Nuclear Fusion

Sector
Electricity
Image
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A graphic showing the inside of a nuclear fusion reactor
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Summary

Nuclear fusion combines two elements in a nuclear reaction to form a larger element and release energy that can be used to generate electricity. Nuclear fusion has been researched since the 1950s, but there have been no nuclear fusion plants built to date. Globally, electricity production mainly relies on fossil fuels, with an increasing portion being generated by renewable sources such as wind and solar. However, wind and solar alone are unable to provide baseload electricity (the minimum amount of electric power delivered to an electrical grid) due to their intermittent nature, and energy storage is required for grid reliability. Advantages of nuclear fusion include reducing reliance on fossil fuels for electricity generation, producing emission-free electricity during operation, being inherently safer than nuclear fission, generating minimal nuclear waste, and providing baseload power. Disadvantages include technical challenges, high costs, and uncertainty around regulations. We will “Keep Watching” nuclear fusion, but it is currently unproven and extremely expensive.

Page Description for Social
Our mission is to help the world reach “Drawdown" as quickly, safely, and equitably as possible.
Overview

What is our assessment?

Based on our analysis, nuclear fusion is a promising alternative form of electricity generation, but it is still at a theoretical stage and will not be ready for large-scale deployment within the next 10–15 years, when it could have the most impact on meeting global climate targets. We will “Keep Watching” this potential climate solution.

Plausible Could it work? Yes
Ready Is it ready? No
Evidence Are there data to evaluate it? Limited
Effective Does it consistently work? No
Impact Is it big enough to matter? Yes
Risk Is it risky or harmful? No
Cost Is it cheap? No

What is it?

Nuclear fusion is the process by which two individual elements are fused together into a single larger element using high pressure and temperature; this reaction releases large amounts of energy. This is the same reaction that happens in stars such as the Sun. The energy from the fusion reaction can then be harnessed to produce electricity without emitting any GHG emissions. Nuclear fusion power plants are best suited for centralized, large-scale generation (between 500 MW and 1.2 GW of electricity output).

Does it work?

Nuclear fusion experiments have been carried out that prove the scientific principle is sound. However, only in recent years have experiments succeeded in producing more energy than was needed to initiate and sustain the fusion reaction. There have been no nuclear fusion power plants built to date, and it is unlikely that nuclear fusion–powered electricity generation will be ready for deployment before 2050.

Why are we excited?

Nuclear fusion energy offers several advantages as a solution to climate change, including high power density, the ability to deliver “firm” power (i.e., power that can be relied upon to meet demand when needed), and no greenhouse gas emissions. In addition, the most commonly used fuel for nuclear fusion – hydrogen – is readily accessible, there is no risk of a nuclear meltdown, and the process produces relatively little nuclear waste, meaning the risk of nuclear proliferation is almost nonexistent. Some research suggests that nuclear fusion could provide up to 15% of total electricity production either by replacing existing centralized power plants (e.g., oil and gas, coal, nuclear fission) that have reached end-of-life or to satisfy growing demand for electricity as access and electrification increase.

Why are we concerned?

Nuclear fusion is not considered remotely close to being ready to deploy as a climate solution. It faces many technical challenges, including uncertainties related to fusion reactor design and optimal fuel types. The costs for nuclear fusion–produced electricity are highly uncertain and are expected to grow compared to existing estimates. Current estimates for nuclear fusion energy costs exceed US$150/MWh, nearly double the 2020 price per MWh for other energy sources. There are also large uncertainties about the policy environment for nuclear fusion plants, which could hinder both development and deployment. Currently, projections suggest that nuclear fusion reactors could be introduced between 2050 and 2060. This means that even under optimistic conditions, nuclear fusion is unlikely to make a significant contribution to meeting 2050 emissions reduction targets. 

Solution in Action
References

Barbarino, M. (2020). A brief history of nuclear fusion. Nature Physics, 16, 890–893. https://www.nature.com/articles/s41567-020-0940-7 

Barbarino, M. (2023, August 3). What is nuclear fusion?. IAEA. https://www.iaea.org/newscenter/news/what-is-nuclear-fusion 

Foster, J., Lux, H., Knight, S., Wolff, D., & Muldrew, S. I. (2024). Extrapolating costs to commercial fusion power plants. IEEE, 52(9), 3772-3777. https://doi.org/10.1109/TPS.2024.3362428 

Kembleton, R. (2019). Nuclear fusion: What of the future. Managing Global Warming, 199–220. https://www.sciencedirect.com/science/article/abs/pii/B9780128141045000053 

Lerede, D., Nicoli, M., Savoldi, L., & Trotta, A. (2023). Analysis of the possible contribution of different nuclear fusion technologies to the global energy transition. Energy Strategy Reviews, 49. https://www.sciencedirect.com/science/article/pii/S2211467X23000949 

Lindley, B. Roulstone, T., Locatelli, G., & Rooney, M. (2023). Can fusion energy be cost-competitive and commercially viable? An analysis of magnetically confined reactors. Energy Policy, 177. https://www.sciencedirect.com/science/article/abs/pii/S0301421523000964 

Lopes Cardozo, N. J., Lange, A. G. G., & Kramer, G. J. (2016). Fusion: Expensive and taking forever?. Journal of Fusion Energy, 35, 94-101. https://link.springer.com/article/10.1007/s10894-015-0012-7 

Meschini, S., Laviano, F., Ledda, F., Pettinari, D., Testoni, R., Torsello, D., & Panella, B. (2023). Frontiers, 11. https://www.frontiersin.org/journals/energy-research/articles/10.3389/fenrg.2023.1157394/full 

MIT Energy Initiative. (2024). The role of fusion energy in a decarbonized electricity system. Massachusetts Institute of Technology https://energy.mit.edu/wp-content/uploads/2024/09/MITEI_FusionReport_091124_final_COMPLETE-REPORT_fordistribution.pdf 

Tokimatsu, K., Fujino, J., Konishi, S., Ogawa, Y., & Yamaji, K. (2003). Role of nuclear fusion in future energy systems and the environment under future uncertainties. Energy Policy, 31(8), 775–797. https://www.sciencedirect.com/science/article/abs/pii/S0301421502001271 

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