Deploy Leaf Protein Concentrates
This solution has potential but is not yet available in the real world – or the technology still lacks clear effectiveness, evidence, or a reasonable cost – and is not yet ready to be deployed.
In low- and middle-income countries, adopting cooking equipment that uses cleaner fuels or is more efficient has the potential to reduce GHG emissions from both cooking and deforestation due to unsustainable biomass use. Such equipment is readily available and inexpensive and provides significant social benefits. Barriers to adoption include cost and cultural practices, particularly in sub-Saharan Africa. Due to limited data to evaluate the emissions impact of improving fuel-burning equipment, we will “Keep Watching” this solution.
Based on our analysis, improving fuel-burning cooking equipment is an important strategy for reducing GHG emissions from stoves and unsustainable wood harvesting, especially in low-income countries where the additional social and health benefits are significant. However, the lack of quantitative data on the emissions impacts precludes a full analysis. 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? | 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? | Yes |
Improved fuel-burning cooking equipment reduces emissions from combustion and unsustainable biomass harvesting by switching to more efficient cooking equipment or cooking equipment that burn cleaner fuels. In many countries around the world, it is common to cook meals over open fires with solid fuels such as wood, charcoal, dung, and coal or over kerosene stoves Cooking using solid fuels occurs mainly in low-income countries and in rural areas, with one report estimating that 84% of people in sub-Saharan Africa lacked cleaner cooking solutions in 2020 (Stoner et al., 2021). Improved fuel-burning cooking equipment includes more efficient cookstoves and stoves that use cleaner fuels such as liquid petroleum gas, natural gas, biogas, and alcohol. Use of such equipment reduces emissions from combustion and unsustainable biomass harvesting (International Energy Agency [IEA], 2023). Improving fuel-burning cooking equipment is widely seen as a stepping stone toward cooking with electricity in regions lacking reliable and affordable access to electricity (Couture & Jacobs, 2019). Solar-powered cookstoves are not included here, and shifting to electric cooking is addressed in Deploy Electric Cooking Equipment.
Improved fuel-burning cooking equipment is widely available, is proven to reduce GHG emissions, and can reduce unsustainable biomass harvesting. This is because cleaner fuels are less carbon intensive and make the cooking equipment more energy efficient, resulting in less emissions per unit of heat delivered (Johnson, 2009; Khavari et al., 2023). Meanwhile, more efficient solid-fuel cookstoves can reduce fuel usage by 25-40% (MacCarty et al., 2010). Using less biomass for cooking also means less unsustainable wood harvesting that can lead to deforestation (Bailis et al., 2015). The IEA (2023) estimates that 0.8 Gt CO₂‑eq/yr could be avoided by 2030 if all households cooked with cleaner cooking fuels or electricity, and a similar amount of emissions could be prevented by avoiding deforestation.
Improving fuel-burning cooking equipment is a low-cost climate solution that has had high rates of adoption in some countries driven in part by the significant additional benefits. Most improved cooking equipment has up-front costs of less than $US100 (Modern Energy Cooking Services & Energy 4 Impact 2021), and there can be operational cost savings because the new equipment is more fuel efficient. China, India, and Indonesia saw 2–4% of their populations gain access to cleaner cooking technologies (including electric appliances) each year between 2010 and 2022 (IEA, 2023), highlighting how adoption can grow with supportive policies and funding.
Improved cooking equipment provides numerous social benefits. The World Health Organization (2024) estimated that 2.9 million premature deaths occur per year from household air pollution, and inefficient cooking contributes to that. The World Bank (2020) estimated that cooking with solid fuels and kerosene causes US$1.4 trillion/yr in negative health impacts, mainly to women and girls. Women and girls also may be vulnerable to violence and assault when collecting biomass fuel. The IEA (2023) estimates that an average of 5 hours a day are spent on collecting biomass and cooking in some regions when inefficient cooking methods are used, time that might otherwise be spent on schooling or additional employment. Finally, biodiversity loss and deforestation are reduced when less biomass is used for cooking (Pearson et al., 2017).
Adoption of improved fuel-burning cooking equipment is held back by cost and cultural barriers, while lack of data hinders emissions impact analyses. Despite being low cost, improved fuel-burning cooking equipment and their fuels are financially inaccessible to many households in low-income countries, including half of households in sub-Saharan Africa (World Bank, 2020). Households using improved cooking equipment may revert to old equipment if fuel becomes unaffordable or cookstoves do not support traditional cooking practices (Jewitt et al., 2020). Finally, the full potential of this solution to reduce emissions cannot be assessed due to a lack of studies specific to improvements to fuel-burning equipment and the types of GHGs involved.
Bailis, R., Drigo, R., Ghilardi, A., & Masera, O. (2015). The carbon footprint of traditional woodfuels. Nature Climate Change, 5(3), 266–272. Link to source: https://doi.org/10.1038/nclimate2491
Couture, T. D., & Jacobs, D. (2019). Beyond fire: How to achieve electric cooking [Report]. Hivos and World Future Council. Link to source: https://www.worldfuturecouncil.org/wp-content/uploads/2019/05/Beyond-Fire-How-to-achieve-electric-cooking.pdf
International Energy Agency. (2023). A vision for clean cooking access for all. Link to source: https://iea.blob.core.windows.net/assets/f63eebbc-a3df-4542-b2fb-364dd66a2199/AVisionforCleanCookingAccessforAll.pdf
Jewitt, S., Atagher, P., & Clifford, M. (2020). “We cannot stop cooking”: Stove stacking, seasonality and the risky practices of household cookstove transitions in Nigeria. Energy Research & Social Science, 61, Article 101340. Link to source: https://doi.org/10.1016/j.erss.2019.101340
Johnson, E. (2009). Charcoal versus LPG grilling: A carbon-footprint comparison. Environmental Impact Assessment Review, 29(6), 370–378. Link to source: http://dx.doi.org/10.1016/j.eiar.2009.02.004
Khavari, B., Ramirez, C., Jeuland, M., & Fuso Nerini, F. (2023). A geospatial approach to understanding clean cooking challenges in sub-Saharan Africa. Nature Sustainability, 6(4), 447–457. Link to source: https://doi.org/10.1038/s41893-022-01039-8
MacCarty, N., Still, D., & Ogle, D. (2010). Fuel use and emissions performance of fifty cooking stoves in the laboratory and related benchmarks of performance. Energy for Sustainable Development, 14(3), 161–171. Link to source: https://doi.org/10.1016/j.esd.2010.06.002
Modern Energy Cooking Services, & Energy 4 Impact. (2021). Clean cooking: Financing appliances for end users [Report]. Link to source: https://www.energy4impact.org/sites/default/files/2024-09/financing_appliances_report_0.pdf
Pearson, T. R. H., Brown, S., Murray, L., & Sidman, G. (2017). Greenhouse gas emissions from tropical forest degradation: An underestimated source. Carbon Balance and Management, 12(1), Article 3. Link to source: https://doi.org/10.1186/s13021-017-0072-2
Stoner, O., Lewis, J., Martínez, I. L., Gumy, S., Economou, T., & Adair-Rohani, H. (2021). Household cooking fuel estimates at global and country level for 1990 to 2030. Nature communications, 12(1), Article 5793. Link to source: https://doi.org/10.1038/s41467-021-26036-x
World Bank. (2020). The state of access to modern energy cooking services [Report]. Link to source: https://www.worldbank.org/en/topic/energy/publication/the-state-of-access-to-modern-energy-cooking-services
World Health Organization. (n.d.). Proportion of population with primary reliance on clean fuels and technologies. Retrieved May 29, 2026, from Link to source: https://www.who.int/data/gho/data/themes/air-pollution/household-air-pollution
Anenberg, S. C., Balakrishnan, K., Jetter, J., Masera, O., Mehta, S., Moss, J., & Ramanathan, V. (2013). Cleaner cooking solutions to achieve health, climate, and economic cobenefits. Environmental Science & Technology, 47(9), 3944–3952. Link to source: https://pubs.acs.org/doi/10.1021/es304942e
Clean Cooking Alliance. (2022). Accelerating clean cooking as a nature-based climate solution [Report]. Link to source: https://cleancooking.org/reports-and-tools/accelerating-clean-cooking-as-a-nature-based-climate-solution/
International Energy Agency. (2025). Universal access to clean cooking in Africa [Report]. Link to source: https://iea.blob.core.windows.net/assets/f0170390-a39b-407e-9ffe-b1cc865d0c5d/UniversalAccesstoCleanCookinginAfrica.pdf
International Renewable Energy Agency. (2024). Advancing renewables-based clean cooking solutions: Key messages and outcomes [Report]. Link to source: https://cop.impulsouth.org/wp-content/uploads/2025/01/IRENA_Renewables-based_clean_cooking_2024.pdf
Kaur-Sidhu, M., Ravindra, K., Mor, S., & John, S. (2020). Emission factors and global warming potential of various solid biomass fuel-cook stove combinations. Atmospheric Pollution Research, 11(2), 252–260. Link to source: https://doi.org/10.1016/j.apr.2019.10.009
Rosenthal, J., Quinn, A., Grieshop, A. P., Pillarisetti, A., & Glass, R. I. (2018). Clean cooking and the SDGs: Integrated analytical approaches to guide energy interventions for health and environment goals. Energy for Sustainable Development, 42, 152–159. Link to source: https://doi.org/10.1016/j.esd.2017.11.003
Sharma, D., Ravindra, K., Kaur, M., Prinja, S., & Mor, S. (2020). Cost evaluation of different household fuels and identification of the barriers for the choice of clean cooking fuels in India. Sustainable Cities and Society, 52, Article 101825. Link to source: https://doi.org/10.1016/j.scs.2019.101825
United Nations. (n.d.). Goal 7: Ensure access to affordable, reliable, sustainable and modern energy for all. Retrieved May 29, 2026, from Link to source: https://sdgs.un.org/goals/goal7#progress_and_info
World Health Organization. (2025). Household air pollution. Link to source: https://www.who.int/news-room/fact-sheets/detail/household-air-pollution-and-health
Heather McDiarmid, Ph.D.
Christina Swanson, Ph.D.
Amanda D. Smith, Ph.D.
Electric cooking equipment such as electric resistance stoves, induction stoves, and electric ovens can replace fuel-burning cooking equipment and reduce cooking-related GHG emissions, especially in regions with low-emission electricity grids. Cooking with electricity has significant health, safety, and energy efficiency benefits but cost, reliable access to electricity, and cultural compatibility are barriers to adoption. The climate impact varies regionally and data limitations hinder a deeper analysis, so we will “Keep Watching” this potential climate solution.
Based on our analysis, deploying electric cooking equipment can reduce emissions while providing significant additional benefits for health. However, the lack of quantitative data on emissions impacts precludes a full analysis. 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? | No |
| 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? | ? |
Using electricity for cooking instead of burning fuels such as liquid petroleum gas (LPG), natural gas, biogas, biomass, charcoal, coal, or kerosene reduces the emissions from burning fuels and can reduce emissions overall when powered by low-emissions electricity. The World Health Organization (WHO, n.d.) estimated that 60% of the global population cooked with gas and 26% cooked with biomass in 2023, while only 8.4% used electricity. Natural gas is the most common fuel for gas cooking in countries where gas distribution infrastructure exists, while liquid petroleum gas is common in low- and middle-income countries (Kojima, 2021). Cooking with electricity typically involves single or multi-element electric resistance or induction cookstoves and electric ovens. The Improve Fuel-Burning Cooking Equipment solution focuses on the adoption of more efficient fueled cookstoves and the switch to cleaner fuels such as LPG as a stepping stone toward eventual electric cooking in low-income communities where reliable and affordable access to electricity is currently lacking (Couture & Jacobs, 2019).
Cooking with electricity rather than fuels reduces emissions from cooking in areas with low grid emissions (Gould et al., 2023), and relies on well-established technologies. Burning fuels for cooking generates greenhouse gas emissions, and methane leaks from natural gas stoves also contribute to emissions (Lebel et al., 2022). Cooking with electricity can be two or more times more energy efficient than alternatives (Rao & Sagar, 2024). Furthermore, electric cooking equipment is widely available. However, the total emissions impact of shifting to electric cooking equipment will be limited because cooking is a minor contributor to total building energy use worldwide (IEA, 2025).
Electric cooking can have significant benefits for health, safety, and energy use, with modern electric appliances growing in popularity among chefs. Electric cooking equipment also supports all-electric new developments and provides benefits in communities with mini-grids. Burning fuels for cooking contributes to household air pollution (Lebel et al., 2022), which is responsible for an estimated 2.9 million premature deaths per year (WHO, n.d.), and also generates poisonous carbon monoxide. Explosions can also result when fuel leaks from fuel-burning cooking equipment (Lebel et al., 2022). Electric cooking reduces or eliminates these health and safety risks because fuels are not used. Furthermore, electric cooking is more energy efficient (Gould et al., 2023), and therefore releases less unwanted heat to the kitchen area which can improve comfort and the need for air conditioning (Li et al., 2024; Luo et al., 2023). Modern induction cookstoves are gaining in popularity among chefs because they can heat food faster with better temperature control than alternatives (Hawking, 2025) and have the added advantage of being easy to clean. In new developments, electric cooking enables all-electric developments that avoid locking in new fossil-fuel infrastructure (Tan et al., 2022). In some regions in Africa, electric pressure cookers are also a promising solution for some cooking tasks because their lower energy needs make them easier to integrate into mini-grids (Efficiency for Access et al., 2020; Kweka et al., 2021).
Electric cooking adoption can be hampered by costs, unreliable access to electricity, and cultural preferences. In addition, net emissions can increase when used in areas with high grid emissions, and data for analysis are limited. In high-income countries, switching to electric cooking can trigger additional electrical upgrade costs (Pergantis et al., 2025). In low-income countries, up-front costs are a major barrier, as is reliable, safe, and affordable access to electricity (Das et al, 2025; IEA, 2024). An estimated 750 million people lack access to electricity worldwide, with more than 80% living in Africa (IEA, 2024). Households may also continue to use traditional cooking methods alongside electric appliances due to cultural preferences (Crentsil et al., 2025). The effectiveness of this solution varies regionally, with grid emissions factors, electrical equipment efficiency, and the fuel being substituted all playing a role in whether electric cooking provides net emissions benefits and the magnitude of those benefits. The biggest factor is the emissions due to the grid mix providing electricity, which varies regionally. Finally, a lack of data on the relative proportions of fuels in use today for cooking is a barrier to deeper analysis.
Couture, T. D., & Jacobs, D. (2019). Beyond fire how to achieve electric cooking. [Report.] Hivos people unlimited, World Future Council. Link to source: https://www.worldfuturecouncil.org/wp-content/uploads/2019/05/Beyond-Fire_-How-to-achieve-electric-cooking.pdf
Crentsil, A. O., Danquah, S. K., Agbelie, I. S. K., & Bawakyillenuo, S. (2025). E-cooking growth in Ghana: Empirical examination of opportunities and challenges. Clean Energy, 9(6), 96–108. Link to source: https://doi.org/10.1093/ce/zkaf034
Das, I., Galeos, S. K. D., Xue, Y., Zong, J., Lewis, J. J., Fujita‐Conrads, R., Williams, K. N., Troncoso, K., Adair‐Rohani, H., & Jeuland, M. (2025). The costs and benefits of clean cooking policies in low‐ and middle‐income countries under real‐world conditions. Sustainable Development, 33(4), 6108–6123. Link to source: https://doi.org/10.1002/sd.3463
Efficiency for Access, PowerGen, & Modern Energy Cooking Services. (2020). Electric pressure cooking: Accelerating mocrogrid e-cooking through business and delivery model innovations [Report]. Link to source: https://efficiencyforaccess.org/wp-content/uploads/Accelerating-Microgrid-E-Cooking-Through-Business-and-Delivery-Model-Innovations.pdf
Gould, C. F., Bejarano, M. L., De La Cuesta, B., Jack, D. W., Schlesinger, S. B., Valarezo, A., & Burke, M. (2023). Climate and health benefits of a transition from gas to electric cooking. Proceedings of the National Academy of Sciences, 120(34), Article e2301061120. Link to source: https://doi.org/10.1073/pnas.2301061120
Hawking, T. (2025). Are induction stoves better? These chefs think so. Popular Science. Link to source: https://www.popsci.com/science/how-induction-stoves-work-better/
International Energy Agency. (2024). SDG7: Data and projections. Link to source: https://www.iea.org/reports/sdg7-data-and-projections/overview
International Energy Agency. (2025). Energy efficiency 2025. Link to source: https://iea.blob.core.windows.net/assets/23a80bb2-6985-4507-ab99-c1d700f6548b/EnergyEfficiency2025.pdf
Kojima, M. (2021). Primary household energy for cooking and heating in 52 developing economies. World Bank. Link to source: https://openknowledge.worldbank.org/server/api/core/bitstreams/2f5b11f1-170f-5c3b-a5f8-25057993f294/content
Kweka, A., Clements, A., Bomba, M., Schürhoff, N., Bundala, J., Mgonda, E., Nilsson, M., Avila, E., & Scott, N. (2021). Tracking the adoption of electric pressure cookers among mini-grid customers in Tanzania. Energies, 14(15), Article 4574. Link to source: https://doi.org/10.3390/en14154574
Lebel, E. D., Finnegan, C. J., Ouyang, Z., & Jackson, R. B. (2022). Methane and NO x emissions from natural gas stoves, cooktops, and ovens in residential homes. Environmental Science & Technology, 56(4), 2529–2539. Link to source: https://doi.org/10.1021/acs.est.1c04707
Li, J., Li, S., Zeng, Y., Zhou, X., Zeng, L., Liu, M., Cao, C., Xia, Y., & Gao, J. (2024). Cooking-related thermal comfort and carbon emissions assessment: Comparison between electric and gas cooking in air-conditioned kitchens. Building and Environment, 265, Article 111992. Link to source: https://doi.org/10.1016/j.buildenv.2024.111992
Luo, M., Guo, X., Feng, X., & Chen, W. (2023). Studying occupant’s heat exposure and thermal comfort in the kitchen through full-scale experiments and CFD simulations. Indoor and Built Environment, 32(5), 928–943. Link to source: https://doi.org/10.1177/1420326X221147161
Pergantis, E. N., Reyes Premer, L. D., Lee, A. H., Priyadarshan, Liu, H., Groll, E. A., Ziviani, D., & Kircher, K. J. (2025). Protecting residential electrical panels and service through model predictive control: A field study. Applied Energy, 386, 125528. Link to source: https://doi.org/10.1016/j.apenergy.2025.125528
Rao, N. D., & Sagar, A. D. (2024). Electric cooking as a clean and just energy solution. Nature Reviews Earth & Environment, 5(11), 751–752. Link to source: https://doi.org/10.1038/s43017-024-00608-z
Tan, L., Fahollahzadeh, M.H., Taylor, E. (2022). The economics of electrifying buildings: residential new construction. Rocky Mountain Institute. https://rmi.org/insight/economics-of-electrifying-residential new-construction/
World Health Organization. (2025). Household air pollution. World Health Organization. Link to source: https://www.who.int/news-room/fact-sheets/detail/household-air-pollution-and-health
World Health Organization. (n.d.). Cooking fuels: Population with primary reliance on fuels and technologies for cooking, by fuel type, proportions (%). World Health Organization. Link to source: https://www.who.int/data/gho/data/indicators/indicator-details/GHO/proportion-of-population-with-primary-reliance-on-fuels-and-technologies-for-cooking-by-fuel-type
Aemro, Y. B., Moura, P., & De Almeida, A. T. (2021). Experimental evaluation of electric clean cooking options for rural areas of developing countries. Sustainable Energy Technologies and Assessments, 43, Article 100954. Link to source: https://doi.org/10.1016/j.seta.2020.100954
Cozzi, L., Petrelli, M., & Roge, A. (2026, May 13). Energy crisis threatens world’s most vulnerable as cooking fuel shortages grow. International Energy Agency. International Energy Agency. Link to source: https://www.iea.org/commentaries/energy-crisis-threatens-world-s-most-vulnerable-as-cooking-fuel-shortages-grow
Floess, E., Grieshop, A., Puzzolo, E., Pope, D., Leach, N., Smith, C. J., Gill-Wiehl, A., Landesman, K., & Bailis, R. (2023). Scaling up gas and electric cooking in low- and middle-income countries: Climate threat or mitigation strategy with co-benefits? Environmental Research Letters, 18(3), Article 034010. Link to source: https://doi.org/10.1088/1748-9326/acb501
Im, H., & Kim, Y. (2020). The electrification of cooking methods in Korea—Impact on energy use and greenhouse gas emissions. Energies, 13(3), Article 680. Link to source: https://doi.org/10.3390/en13030680
Leach, M., Mullen, C., Lee, J., Soltowski, B., Wade, N., Galloway, S., Coley, W., Keddar, S., Scott, N., & Batchelor, S. (2021). Modelling the costs and benefits of modern energy cooking services—Methods and case studies. Energies, 14(12), Article 3371. Link to source: https://doi.org/10.3390/en14123371
Odoi-Yorke, F. (2024). A systematic review and bibliometric analysis of electric cooking: Evolution, emerging trends, and future research directions for sustainable development. Sustainable Energy Research, 11, Article 2024. Link to source: https://doi.org/10.1186/s40807
Heather McDiarmid, Ph.D.
Christina Swanson, Ph.D.
Amanda D. Smith, Ph.D.
Advanced geothermal energy is an emerging clean energy technology that harnesses the Earth’s subsurface heat to generate emissions-free baseload and dispatchable electricity and heat. Unlike traditional geothermal systems that tap naturally occurring hot water or steam reservoirs, advanced geothermal systems (AGS) use a range of technologies, including directional drilling and hydraulic fracturing, to access or create artificial geothermal reservoirs through which they circulate water or other fluids. Accessible geothermal resources suitable for AGS occur across the globe and, if technology improvements continue, advanced geothermal systems could supply around 15% of the world’s electricity by 2050. However, to progress from pilot stage to commercialization, the industry needs more demonstration projects to address high upfront costs, technical challenges, and environmental and safety concerns, and to generate greater policy support to facilitate deployment. Based on our assessment, advanced geothermal energy is a potentially high-impact climate solution that we will “Keep Watching.”
Advanced geothermal systems (AGS) are emerging as one of the most promising technologies for reliable, utility-scale, zero-carbon energy that can complement wind and solar, strengthening grid resilience, and providing heat for district heating and industrial uses. The technology, which is built on an existing base of technical and industrial expertise and capacity, is advancing rapidly through major R&D efforts, pilot projects and, just recently, small scale commercial operations. While large-scale deployment is still in its early stages and challenges remain around cost, execution, and social acceptance, we expect meaningful progress by the 2030s. For now, we will “Keep Watching” this solution.
| Plausible | Could it work? | Yes |
|---|---|---|
| Ready | Is it ready? | No |
| Evidence | Are there data to evaluate it? | Limited |
| 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 |
Advanced geothermal systems (AGS) are a suite of renewable energy technologies that extract heat from deep within the Earth’s crust to generate electricity, provide high-temperature heat for industrial processes or district heating, and enable geothermal energy storage by storing heat underground. Unlike traditional geothermal systems that tap naturally occurring hot water or steam reservoirs, such as geysers or volcanic areas, AGS access geothermal heat by drilling into the earth, injecting and circulating water (or other fluids) through hot, dry rock formations underground, and then recovering the heated fluid or steam to generate electricity before reinjecting it back underground. Circulation of the water between the surface and the geothermal reservoir can be a in closed loop system, where the water or other fluid is contained within pipes throughout the heat exchange circulation cycle, or in an open loop, enhanced geothermal system (EGS) where the subsurface rocks are hydraulically fractured, or “fracked,” to increase permeability and allow water to flow between an injection well and a production well.
Electricity and heat production by an advanced geothermal power plant emits virtually no greenhouse gases. Analysis by the National Renewable Energy Laboratory showed that the median life cycle emissions from enhanced geothermal power plants were 32 g CO₂‑eq/kWh, just 6% of the median life cycle emissions from a natural gas power plant, with most of the emissions generated during construction rather than operation. Geothermal energy has been used for more than a century, but AGS that use the directional and horizontal drilling and hydraulic fracturing techniques developed by the oil and gas industry to access previously inaccessible underground heat resources are relatively new. To date, several small-scale and experimental AGS projects have successfully produced electricity, and in December 2025, the first commercial plant for electricity and heat production delivered electricity to the grid in Germany.
Advanced geothermal energy systems are a potentially transformative climate solution for several reasons. First, they could massively expand clean energy availability. AGS can be deployed in almost any region with hot subsurface rocks. Experts estimate the Earth’s accessible geothermal resources are staggeringly large, and that tapping just 0.1% of the heat under our feet could meet global energy needs for millennia. If technology improvements continue, advanced geothermal could supply around 15% of the world’s electricity by 2050. Second, unlike solar and wind energy, advanced geothermal power plants produce steady baseload power, dispatchable power, and even energy storage. Currently, coal and gas power plants are commonly used to provide stability and backup power to electricity grids around the world. AGS can provide the same energy benefits, complementing wind and solar energy by providing firm capacity and grid stability services to a renewable-heavy electricity grid, without the harmful climate impacts. Third, AGS plants have a relatively small land footprint and can potentially be sited near demand centers (including repurposing old fossil plant sites), improving energy security for regions with limited solar or wind resources.
Recent technological breakthroughs have improved the prospects for AGS. The application of directional drilling and hydraulic fracturing techniques has produced higher fluid flow rates and extended reservoir life. This has dramatically increased the heat extraction per well, overcoming previous limitations and boosting the energy output and economics of AGS. Industry reports show drilling rates in hot rock have increased by 300–500% in the last few years, slashing upfront costs. A recent U.S. Department of Energy report projects that the cost of next-generation geothermal projects, including AGS, will fall below that of other baseload power sources such as nuclear and natural gas with carbon capture and storage (CCS) by 2035. Other projections suggest that geothermal electricity could drop to around US$50/MWh by the 2030s, competitive with other renewables and nuclear. Finally, AGS leverage a skilled workforce and supply chain from the oil and gas sector. The necessary drilling rigs, subsurface imaging, and engineering expertise already exist, which could help scale up AGS faster than entirely new industries.
Despite its promise, AGS face several challenges that temper its near-term prospects. To bridge the gap from pilot stage to commercialization, the industry needs more demonstration projects, case studies of success, and greater public trust. This is challenging because advanced geothermal projects today have high upfront capital costs, primarily due to deep drilling and, for EGS, hydraulic stimulation expenses, as well as high operational costs. Current AGS electricity is also far more expensive than conventional renewables, often hundreds of dollars per MWh. Until these costs decline, the industry may struggle to attract the investment financing needed to scale up. Moreover, the geological uncertainty in any given project is high because limited geophysical data in many regions makes it hard to pinpoint the best spots to drill. Developers must invest in exploration with no guarantee of finding an adequate resource, so early projects carry a significant risk of cost overruns.
Safety and environmental concerns also pose challenges. In some types of geologies, enhanced geothermal systems, which use hydraulic fracturing to create the heat exchange reservoirs and circulate fluid underground, can trigger small earthquakes. Some EGS have been halted after local earthquakes caused alarm and minor damage. Because they use water and circulate hot brines, AGS could pose risks for groundwater contamination or water consumption in arid regions, although geothermal system designs that use closed-loop systems or non-potable water can avoid these problems. Finally, geothermal projects often face regulatory and logistical hurdles and lengthy permitting processes. In many countries, regulatory regimes and incentives have focused on solar, wind, and even nuclear, while geothermal energy (and especially AGS) has received comparatively little support. This means AGS developers may struggle with financing and grid access due to policy gaps or obstacles.
Aghahosseini, A., & Breyer, C. (2020). From hot rock to useful energy: A global estimate of enhanced geothermal systems potential. Applied Energy, 279, Article 115769. Link to source: https://doi.org/10.1016/J.APENERGY.2020.115769
Akindipe, D. F., Smith, M., Witter, E., et al. (2026). 2025 U.S. Geothermal Market Report. (Technical Report No. NLR/TP-5700-91898). National Laboratory of the Rockies. https://docs.nrel.gov/docs/fy26osti/91898.pdf
Blankenship, D., Gertler, C., Kamaludeen, M., O’Connor, M., & Porse, S. (2024). Pathways to Commercial Liftoff: Next-Generation Geothermal Power. U.S. Department of Energy. Link to source: https://cdn.catf.us/wp-content/uploads/2025/06/09154348/doe-liftoff-nextgen-geothermal.pdf
Boretti, A. (2025). Enhanced geothermal systems: Potential, challenges, and a realistic path to integration in a sustainable energy future. Next Energy, 8, Article 100332. Link to source: https://doi.org/10.1016/J.NXENER.2025.100332
Eberle, A., Heath, G. A., Carpenter Petri, A. C., & Nicholson, S. R. (2017). Systematic review of life cycle greenhouse gas emissions from geothermal electricity. (Technical Report No. NREL/TP-6A20-68474). National Renewable Energy Laboratory. Link to source: https://docs.nrel.gov/docs/fy17osti/68474.pdf
EnergyNews247 (2025). Eavor’s Geothermal System to Come Online in Germany. Link to source: https://energynews247.com/eavors-geothermal-system-to-come-online-in-germany/
Heath, G., O'Donoughue, P., & Whitaker, M. (2012). Life cycle GHG emissions from conventional natural gas power generation: Systematic review and harmonization (Presentation No. NREL/PR-6A20-57229). National Renewable Energy Laboratory. Link to source: https://docs.nrel.gov/docs/fy13osti/57229.pdf
Horne, R., Genter, A., McClure, M., Ellsworth, W., Norbeck, J., & Schill, E. (2025). Enhanced geothermal systems for clean firm energy generation. Nature Reviews Clean Technology, 1(2), 148–160. Link to source: https://doi.org/10.1038/S44359-024-00019-9
International Energy Agency. (2024). The future of geothermal energy. Link to source: https://www.iea.org/reports/the-future-of-geothermal-energy
Kah, M. & Kleinberg, R. (2025, April 7). The potential contribution of enhanced geothermal systems to future power supply: Roundtable summary. Center on Global Energy Policy at Columbia Columbia University SIPA. Link to source: https://www.energypolicy.columbia.edu/publications/the-potential-contribution-of-enhanced-geothermal-systems-to-future-power-supply-roundtable-summary/
Lipton, J. & Seligman. A. (2025). Powering the future: What 50 years of enhanced geothermal teaches us today. Clean Air Task Force. Link to source: https://www.catf.us/wp-content/uploads/2025/08/CATF-EGS-Trend-Analysis-Report.pdf
Kassem, M. A., & Moscariello, A. (2025). Geothermal energy: A sustainable and cost-effective alternative for clean energy production and climate change mitigation. Sustainable Futures, 10, Article 101247. Link to source: https://www.sciencedirect.com/science/article/pii/S2666188825008081
McKasy, M., Yeo, S. K., Zhang, J. S., Cacciatore, M. A., Allen, H. W., & Su, L. Y. F. (2025). Support for regulation of enhanced geothermal systems research: examining the role of familiarity, credibility, and social endorsement. Geothermal Energy, 13(1), 1–21. Link to source: https://doi.org/10.1186/S40517-025-00346-5
Nath, F., Mahmood, M. N., Ofosu, E., & Khanal, A. (2024). Enhanced geothermal systems: A critical review of recent advancements and future potential for clean energy production. Geoenergy Science and Engineering, 243, Article 213370. Link to source: https://doi.org/10.1016/J.GEOEN.2024.213370
Ricks, W., & Jenkins, J. D. (2025). Pathways to national-scale adoption of enhanced geothermal power through experience-driven cost reductions. Joule, 9(7), Article 101971. Link to source: https://doi.org/10.1016/J.JOULE.2025.101971
U.S. Department of Energy. (n.d.). Enhanced Geothermal Systems. Retrieved October 20, 2025, from Link to source: https://www.energy.gov/eere/geothermal/enhanced-geothermal-systems
Zastrow, M. (2019, March 22). South Korea accepts geothermal plant probably caused destructive quake. Nature. Link to source: https://doi.org/10.1038/D41586-019-00959-4
Improve Steel Production involves replacing the use of fossil fuels in making steel from iron ore with electrolytic hydrogen and clean electricity. Doing so could reduce emissions from steel production by more than 90%. Although the necessary technologies exist, adoption has been very limited, with the major barriers being the cost of clean electricity and the availability of suitable iron ore. Other strategies for reducing the emissions from steel production typically rely on bioenergy sources or carbon capture and storage (CCS), which have limited potential to reduce emissions. As demand for steel grows globally, new policies are needed to increase market demand for low-emissions steel. Given the lack of improved steel facilities and supportive policies today, we will “Keep Watching” this solution.
Based on our analysis, Improve Steel Production using H2-DRI-EAF powered by clean electricity has the potential to significantly reduce emissions. However, while the individual technologies for H2-DRI-EAF are mature and their combined use has been piloted, the process has not yet been adopted in a meaningful way. We will “Keep Watching” this solution, but it is not ready for widespread adoption.
| 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 |
Currently, making steel from iron ore relies heavily on coal and other fossil fuels to provide heat and reducing agents (chemicals that remove oxygen from iron ore). Improve Steel Production refers to using electric heat and hydrogen produced by electrolysis to reduce the iron ore (H2-DRI) and electric arc furnaces (EAF) to melt the resulting iron and alloy it with carbon to make steel. The solution also requires the electricity used in these processes to include significant renewable energy or other low-carbon generation. The output is varying grades of steel with different degrees of hardness and brittleness determined by slight variations in carbon content. This solution does not include processes that rely on bioenergy or CCS, since the emissions from burning bioenergy contribute to climate change and CCS is not an effective climate solution.
Replacing fossil fuels in steelmaking with H2-DRI-EAF that uses electrolytic hydrogen and where all electricity comes from relatively clean sources results in significantly reduced emissions. Steel made today using fossil fuels for heat and as a reducing agent results in an estimated 1.8 t CO₂‑eq /t of steel. By contrast, steel made using H2-DRI-EAF and low-carbon electricity would generate an estimated 0.12 t CO₂‑eq /t of steel and is a more energy-efficient process. EAF furnaces are already very common in steelmaking and for recycling existing steel, but are rarely combined with H2-DRI. Although H2-DRI was first used on an industrial scale in 2001, that plant was shut down for economic and political reasons, and economics remain a barrier. Finally, technologies to make industrial hydrogen from electricity are mature, but most hydrogen produced today is made from fossil fuels and is carbon-intensive. Active research is exploring other technologies that could become important for improving steel production in the future, most notably aqueous or molten oxide electrolysis, both of which use electricity to directly remove oxygen from iron ore, and can be combined with EAF to make steel.
Steelmaking is classified as a hard-to-abate industry, and H2-DRI-EAF powered by clean electricity is considered one of the best strategies for cutting emissions in this sector. The Net Zero Industry project forecasts that under an emissions-neutral steel scenario by 2050, roughly 40% of global steel production could depend on H2-DRI-EAF, with the remainder consisting of recycled steel (47%), steelmaking with CCS (11%), or technologies not yet defined (2%). The impact is potentially significant, given that steelmaking accounted for an estimated 3.7 Gt of CO₂‑eq in 2019. Improved steelmaking has the additional benefit of reducing air and land pollution, as burning coal releases fine particulate matter, heavy metals, and other pollutants. In China, steel production is the largest industrial source of air pollution. As demand for steel is expected to increase up to 30% by 2050 due to demand from India and other low- and middle-income countries, it is critical that new and existing production shift to cleaner, lower-emission technologies, and that policies supporting this shift be implemented.
While proposed low-emission steel projects have attracted significant attention from the press, many have since been canceled or put on hold. As of 2025, we could find references to only a few pilot facilities producing improved steel as we have defined it here. The entire H2-DRI-EAF process is considered to be at the large-scale prototype demonstration stage. However, contributing technologies such as electrolytic hydrogen production and EAF are more mature, and H2-DRI was first used on an industrial scale in 2001. The higher cost of making low-emission steel is a significant barrier to industrial adoption and consumer demand. Electricity accounts for nearly half the cost of producing low-emission steel from iron ore. To increase adoption, improved steel facilities need to be located in areas that can readily supply both iron ore and abundant low-carbon, low-cost electricity. In areas such as China, where the electricity grid still relies heavily on fossil fuels, transitioning to H2-DRI-EAF risks increasing emissions unless dedicated renewables are integrated into the project. To move this solution forward, new policies are needed to create an international market for low-emission steel. Meanwhile, existing steelmaking facilities typically have lifetimes of 25–40 years, which increases the likelihood of stranded assets or continued reliance on fossil fuels by 2050. Under its Sustainable Development Scenario, the International Energy Agency (IEA) projects that, by 2050, only 12% of cumulative direct emissions reductions in steelmaking will be due to electrification and the use of hydrogen (the IEA considered emissions from electricity to be indirect). Reducing demand for steel, incremental efficiency gains, and CCS are expected to make up the bulk of cumulative direct emissions reductions, according to the IEA projections.
Bataille, C., Stiebert, S., Li, F. (2021). Global facility level net-zero steel pathways. Net Zero Steel. Link to source: https://netzeroindustry.org/wp-content/uploads/pdf/net_zero_steel_report.pdf
Devlin, A., Kossen, J., Goldie-Jones, H., & Yang, A. (2023). Global green hydrogen-based steel opportunities surrounding high quality renewable energy and iron ore deposits. Nature Communications, 14(1), 2578. Link to source: https://doi.org/10.1038/s41467-023-38123-2
Hubner Australia. (n.d.). Green steel manufacturing: Processes and comparisons. Hubner Australia. Link to source: https://hubner.au/green-steel-manufacturing/
IEA. (2020). Iron and steel technology roadmap. Link to source: https://iea.blob.core.windows.net/assets/eb0c8ec1-3665-4959-97d0-187ceca189a8/Iron_and_Steel_Technology_Roadmap.pdf
Kueppers, M., Hall, W., Levi, P., Simon, R., & Vass, T. (2023, July 11). Steel. IEA. Link to source: https://www.iea.org/energy-system/industry/steel
Lang, S., Kopf, M., & Valery, R. (2021, November 18). Cicored fine ore direct reduction—A proven process to decarbonize steelmaking. Metso. Link to source: https://www.metso.com/insights/blog/mining-and-metals/circored-fine-ore-direct-reduction-a-proven-process-to-decarbonize-steelmaking/
Leadit. (2025, May). Green steel tracker. Leadit Leadership Group for Industry Transition. Link to source: https://www.industrytransition.org/green-steel-tracker/
McKinsey & Company. (2024). Green-steel hubs: A pathway to decarbonize the steel industry. McKinsey & Company. Link to source: https://www.mckinsey.com/industries/metals-and-mining/our-insights/green-steel-hubs-a-pathway-to-decarbonize-the-steel-industry#/
Milne, R. (2025, October 13). Flagship green steel start-up in funding crisis as Europe’s low-carbon ambitions falter. Financial Times. Link to source: https://www.ft.com/content/ac619c2d-9c7a-4208-baa5-6c648d10cacc
Net Zero Industry. (n.d.). Net zero steel pathways. Net Zero Industry. Link to source: https://netzeroindustry.org/net-zero-parhways /
Russell, C. (2025, May 29). Green steel is distant and expensive, but teal steel is coming. Reuters. Link to source: https://www.reuters.com/markets/commodities/green-steel-is-distant-expensive-teal-steel-is-coming-russell-2025-05-29/
Ryan, N. A., Miller, S. A., Skerlos, S. J., & Cooper, D. R. (2020). Reducing CO2 emissions from U.S. steel consumption by 70% by 2050. Environmental Science & Technology, 54(22). Link to source: https://doi.org/10.1021/acs.est.0c04321
Wrede, I. (2025, July 19). ArcelorMittal’s pullout plunges German green steel in doubt. DW. Link to source: https://www.dw.com/en/arcelormittals-pullout-plunges-german-green-steel-in-doubt/a-73303680
Zhang, J., Shen, H., Chen, Y., Meng, J., Li, J., He, J., Guo, P., Dai, R., Zhang, Y., Xu, R., Wang, J., Zheng, S., Lei, T., Shen, G., Wang, C., Ye, J., Zhu, L., Sun, H. Z., Fu, T.-M., … Tao, S. (2023). Iron and Steel Industry Emissions: A Global Analysis of Trends and Drivers. Environmental Science & Technology, 57(43), 16477–16488. Link to source: https://doi.org/10.1021/acs.est.3c05474
Nitrous oxide removal involves treating agricultural fields with photocatalytic chemicals that convert nitrous oxide into oxygen and nitrogen. Nitrous oxide is a GHG that persists in the atmosphere for more than 100 years and is ~270 times stronger than CO₂ at trapping heat, so removing it from the atmosphere has large climate benefits.
Nitrous oxide removal is still in the early phases of research, most of the limited data are from laboratory studies, and the effectiveness and feasibility of this climate solution is unknown. Research on one of the most studied nitrous oxide photocatalysts, titanium dioxide, has indicated benefits for crop yields and resilience at low application rates but some risk of adverse effects at high application rates. There are also concerns about health, food safety, and environmental impacts. Tools and GHG accounting methods and standards for measuring and reporting nitrous oxide removal need to be further developed. In addition, other ways to reduce nitrous oxide emissions from agriculture and industry are more practical, cost-effective and readily used. Despite these limitations, because this solution addresses such a potent GHG, we will “Keep Watching” it.
Nitrous oxide removal technology is at a very early stage of development. Other available technologies and practices can effectively reduce nitrous oxide emissions. However, because this solution aims to remove such a potent GHG from the atmosphere, we will “Keep Watching” it.
| Plausible | Could it work? | Yes |
|---|---|---|
| Ready | Is it ready? | No |
| Evidence | Are there data to evaluate it? | Limited |
| Effective | Does it consistently work? | ? |
| Impact | Is it big enough to matter? | ? |
| Risk | Is it risky or harmful? | ? |
| Cost | Is it cheap? | ? |
Nitrous oxide removal is a technology that uses photocatalytic chemicals to convert nitrous oxide, a GHG that has 270 times more warming potential than CO₂ and persists in the atmosphere for more than 100 years, into gaseous nitrogen and oxygen.
Nitrous oxide is found naturally in the atmosphere, but 40% of emissions come from human activities, and human-caused emissions have increased more than 30% during the past four decades. Most anthropogenic contributions are from fertilizers applied to croplands and other farming activities, while the rest are from fossil fuel use, industrial activities, and waste and wastewater.
This solution involves spraying a chemical photocatalyst onto agricultural fields. When the photocatalyst is exposed to sunlight and nitrous oxide, it drives a chemical reaction that decomposes nitrous oxide into gaseous nitrogen and oxygen.
Research into atmospheric nitrous oxide removal is still in its early stages. The concentration of nitrous oxide in the atmosphere is very low, so nitrous oxide removal would likely be implemented in agricultural areas where fertilizer use locally elevates atmospheric concentrations. Laboratory testing has shown that nitrous oxide can be converted into nitrogen and oxygen using light energy and photocatalysts. However, the effectiveness of the solution in practice is uncertain because few experiments have been conducted in real-world settings. The single field study that applied titanium dioxide to a field crop did report a measurable reduction in nitrous oxide emissions. However, there is no evidence that this technology can remove atmospheric nitrous oxide at a meaningful scale.
Because nitrous oxide is such a potent GHG, reducing its concentration in the atmosphere could have a disproportionately beneficial climate impact. In addition, unlike direct air capture or carbon capture and storage, there is no need to capture or store any gases because the nitrous oxide breaks down into gases that have no climate impact. Also, titanium dioxide application to crops is being researched as a method for improving crop resilience.
Serious concerns include technical feasibility, environmental risk (including environmental and food safety), scalability, cost, and monitoring, reporting, and verification. While there is currently very little research on the real-world use of photocatalysts to destroy atmospheric nitrous oxide, ongoing research on the application of nanoparticles of titanium dioxide to crops to enhance productivity and resilience to stress suggests that high concentrations of titanium dioxide can have adverse effects. Furthermore, these nanoparticles are not approved for direct food consumption, and their fate and environmental impacts are poorly understood.
Tools, methods, and standards need to be developed to quantify nitrous oxide removal for accurate accounting and verification. Costs are unknown. Finally, numerous other approaches for reducing human-caused nitrous oxide emissions exist, including improving nutrient management, rice production, manure management, and industrial processes, as well as reducing fossil-fuel use for power generation and transportation and increasing use of centralized composting.
Bueno-Alejo, C. J., Khambhati, Y. K., & Papadopoulos, A. (2025). Photocatalytic removal of N2O in cropped fields using R-Leaf. Applied Catalysis O: Open, 201, Article 207032. Link to source: https://doi.org/10.1016/j.apcato.2025.207032
Carbon Registry. (n.d.). Atmospheric nitrous oxide (N2O) destruction using photocatalysts. International Carbon Registry. Retrieved May 7, 2026, from https://www.carbonregistry.com/methodologies/m-icr-011
Ma, H., Li, Y., Wang, C., Li, Y., & Zhang, X. (2025). TiO2-based photocatalysts for removal of low-concentration NOx contamination. Catalysts, 15(2), Article 103. Link to source: https://doi.org/10.3390/catal15020103
Olaifa, O., Alimard, P., Itskou, I., Eisner, F., Petit, C., Díez-González, S., & Kafizas, A. (2025). Purifying the air with photocatalysis: Developing bismuth oxybromide/ copper phthalocyanine composite photocatalyst filters with enhanced activity for NOx removal. ChemPhotoChem, 9(6), Article e202400346. Link to source: https://doi.org/10.1002/cptc.202400346
Rehman, M., Salam, A., Ulhassan, Z., Ali, B., Haider, Z., Ahmad, I., Yasin, M. U., Javaid, M. H., Yang, C., Fayyaz, M., & Gan, Y. (2025). Titanium dioxide nanoparticles TiO2 NPs in crop stress management: Mechanisms, applications, and abiotic stress mitigation. Plant Nano Biology, 14, Article 100207. Link to source: https://doi.org/10.1016/j.plana.2025.100207
Schödel, S. (2024). Nitrous oxide—The underestimated greenhouse gas [Fact sheet]. German Environment Agency. Link to source: https://www.umweltbundesamt.de/en/publikationen/nitrous-oxide-the-underestimated-greenhouse-gas
Thiagarajan, V., & Ramasubbu, S. (2021). Fate and behaviour of TiO2 nanoparticles in the soil: Their impact on staple food crops. Water, Air, & Soil Pollution, 232(7), Article 274. Link to source: https://doi.org/10.1007/s11270-021-05219-8
Tian, H., Xu, R., Canadell, J. G., Thompson, R. L., Winiwarter, W., Suntharalingam, P., Davidson, E. A., Ciais, P., Jackson, R. B., Janssens-Maenhout, G., Prather, M. J., Regnier, P., Pan, N., Pan, S., Peters, G. P., Shi, H., Tubiello, F. N., Zaehle, S., Zhou, F., … Yao, Y. (2020). A comprehensive quantification of global nitrous oxide sources and sinks. Nature, 586(7828), 248–256. Link to source: https://doi.org/10.1038/s41586-020-2780-0
United Nations Environment Programme, & Food and Agriculture Organization of the United Nations. (2024). Global nitrous oxide assessment [Report]. Link to source: https://doi.org/10.59117/20.500.11822/46562
U.S. Environmental Protection Agency. (2026). Nitrous oxide emissions. Link to source: https://www.epa.gov/ghgemissions/nitrous-oxide-emissions
Verra. (n.d.). Methodology for using photocatalysts to remove atmospheric nitrous oxide. Retrieved April 28, 2026, from Link to source: https://verra.org/methodologies/methodology-for-using-photocatalysts-to-remove-atmospheric-nitrous-oxide/
Xue, T., Li, J., Chen, L., Li, K., Hua, Y., Yang, Y., & Dong, F. (2024). Photocatalytic NOx removal and recovery: Progress, challenges and future perspectives. Chemical Science, 15(24), 9026–9046. Link to source: https://doi.org/10.1039/D4SC01891E
Lead Fellow:
Internal Reviewers:
Reducing grazing intensity involves lowering ruminant livestock stocking rates or grazing pressure. This removes carbon from the atmosphere by reducing land damage and increasing soil organic carbon (SOC). While this approach can quickly be adopted and reduce soil degradation, SOC outcomes are highly variable and driven as much, or more, by climate, grass types, soil properties, and prior land use as by grazing intensity itself. In many cases, lowering grazing pressure does not consistently or reliably lead to additional carbon storage; where it does, this predominantly requires reduced herd sizes that are likely to be offset elsewhere in the beef production system under rising global demand. We will Keep Watching this potential solution.
Reduced grazing intensity can temporarily reduce soil degradation and erosion. However, SOC outcomes depend on a number of factors, such as climate zone, land use history, soil properties, and grass type. Therefore, until stronger, long-term evidence is available to guide more effective implementation, we will Keep Watching this solution.
| Plausible | Could it work? | Yes |
|---|---|---|
| Ready | Is it ready? | Yes |
| Evidence | Are there data to evaluate it? | Limited |
| Effective | Does it consistently work? | No |
| Impact | Is it big enough to matter? | ? |
| Risk | Is it risky or harmful? | No |
| Cost | Is it cheap? | ? |
Reducing grazing intensity refers to lowering ruminant livestock stocking rates or shortening grazing duration to reduce pressure on grazing lands. As a climate solution, it is intended to remove carbon from the atmosphere by increasing SOC through enhanced plant productivity, root inputs, and soil stability. Grazing intensity is typically classified as heavy, moderate, or light, based on the proportion of forage removed per unit time.
In general, while heavy grazing reduces SOC, the effects of grazing intensity on SOC recovery varies with climate zones, grass types, soil properties, and prior land use. Increases in SOC under reduced grazing intensity are largely limited to wetter regions, often with high annual rainfall. In arid and semi-arid regions, which represent a major share of global grazing land, reduced grazing intensity often results in neutral or negative SOC responses. A global review and meta-analysis that normalized SOC to 30 cm depth found that even grazing below carrying capacity was associated with an overall decline in SOC, with gains limited to lower-intensity grazing conditions in specific climate zones.
Reducing grazing intensity provides ecological benefits. This usually involves reducing the number of ruminant livestock on a farm, which in turn reduces the farm’s methane emissions, land-use pressure, and threats to biodiversity–at least in isolation. It can reduce soil degradation, erosion, and vegetation loss. It is already practiced in many contexts and requires no new technology or infrastructure, making it easy and relatively low cost as a climate intervention, though not necessarily cost-neutral for ruminant livestock producers.
Several limitations, risks, and trade-offs are associated with reducing grazing intensity as a carbon removal strategy.
First, even low-intensity grazing can prevent ecosystem recovery when pastures are seeded with, or invaded by, aggressive grasses that suppress native plants, prevent tree regrowth where ecologically appropriate, and lock landscapes into lower-biodiversity, grass-dominated states.
Second, SOC gains are limited, slow, and reversible. Soil organic carbon is a finite sink that approaches saturation within decades and can be lost through drought, warming, fire, or management changes. SOC accumulation through reduced grazing intensity has been shown to be a temporary and fragile form of carbon storage.
Third, SOC gains are difficult to measure and verify. Many studies lack baseline SOC measurements, adequate controls, sufficient duration, and/or adequate soil-depth sampling, making it difficult to attribute carbon gains to grazing intensity. To show an increase in SOC from reduced grazing intensity, an ideal experiment would adopt a before-and-after control intervention at a commercial scale and follow SOC changes for 5–10 years.
Fourth, while reducing grazing intensity compares favorably with alternative grazing when it reduces total stocking numbers, it is still less durable and certain as a carbon removal strategy than protecting intact ecosystems, restoring degraded grasslands, or restoring forests where ecologically appropriate.
Fifth, reducing grazing intensity often lowers herd sizes, but under rising global beef demand this can simply shift production elsewhere. This underscores the value of improving diets and shifting food system infrastructure away from ruminant consumption rather than simply altering ruminant production practices.
Overall, reducing grazing intensity can reduce some local damage from heavier grazing, but in climate-favorable regions especially, the stronger opportunity is often restoring ecosystems or producing higher-yielding plant-based foods.
Abdalla, M., Hastings, A., Chadwick, D. R., Jones, D. L., Evans, C. D., Jones, M. B., ... & Smith, P. E. T. E. (2018). Critical review of the impacts of grazing intensity on soil organic carbon storage and other soil quality indicators in extensively managed grasslands. Agriculture, Ecosystems & Environment, 253, 62-81. Link to source: https://doi.org/10.1016/j.agee.2017.10.023
Bai, Y., & Cotrufo, M. F. (2022). Grassland soil carbon sequestration: Current understanding, challenges, and solutions. Science, 377(6606), 603-608. Link to source: https://doi.org/10.1126/science.abo2380
Dhakal, S., Minx, J. C., Toth, F. L., Abdel-Aziz, A., Figueroa Meza, M. J., Hubacek, K., Jonckheere, I. G. C., Kim, Y.-G., Nemet, G. F., Pachauri, S., Tan, X. C., & Wiedmann, T. (2022). Emissions trends and drivers. 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. 215–294). Cambridge University Press. Link to source: https://doi.org/10.1017/9781009157926.004
Eze, S., Palmer, S. M., & Chapman, P. J. (2018). Soil organic carbon stock in grasslands: Effects of inorganic fertilizers, liming and grazing in different climate settings. Journal of environmental management, 223, 74-84. Link to source: https://doi.org/10.1016/j.jenvman.2018.06.013
Fournier Gabela, J. G., Spiegel, A., Stepanyan, D., Freund, F., Banse, M., Gocht, A., Söder, M., Heidecke, C., Osterburg, B., & Matthews, A. (2024). Carbon leakage in agriculture: When can a carbon border adjustment mechanism help? Climate Policy, 24(10), 1410–1425. Link to source: https://doi.org/10.1080/14693062.2024.2387237
Garnett, T., Godde, C., Muller, A., Röös, E., Smith, P., de Boer, I. J. M., van Zanten, H., Herrero, M., Schader, C., van Middelaar, C., & Thornton, P. (2017). Grazed and confused? Ruminating on cattle, grazing systems, methane, nitrous oxide, the soil carbon sequestration question. Food Climate Research Network, University of Oxford. Link to source: https://www.tabledebates.org/sites/default/files/2022-04/fcrn_gnc_report.pdf
Godde, C. M., Boone, R. B., Ash, A. J., Waha, K., Sloat, L. L., Thornton, P. K., & Herrero, M. (2020). Global rangeland production systems and livelihoods at threat under climate change and variability. Environmental Research Letters, 15(4), 044021. Link to source: https://doi.org/10.1088/1748-9326/ab7395
Maestre, F. T., Le Bagousse-Pinguet, Y., Delgado-Baquerizo, M., Eldridge, D. J., Saiz, H., Berdugo, M., Gozalo, B., Ochoa, V., Guirado, E., García-Gómez, M., Valencia, E., Gaitán, J. J., Asensio, S., Mendoza, B. J., Plaza, C., Díaz-Martínez, P., Rey, A., Hu, H.-W., He, J.-Z., … Gross, N. (2022). Grazing and ecosystem service delivery in global drylands. Science, 378(6622), 915–920. Link to source: https://doi.org/10.1126/science.abq4062
Metz, T., Farwig, N., Dormann, C. F., Schaefer, H. M., Guevara-Andino, J. E., Brehm, G., Burneo, S., Chao, A., Chazdon, R. L., Colwell, R. K., Diniz, U. M., Donoso, D. A., Endara, M.-J., Erazo, S., Escobar, S., Falconí-López, A., Feldhaar, H., Garcia Villamarin, M., Grella, N., . . . Blüthgen, N. (2026). Biodiversity resilience in a tropical rainforest. Nature, 652, 1232–1239. Link to source: https://doi.org/10.1038/s41586-026-10365-2
Niu, W., Ding, J., Fu, B., Zhao, W., & Eldridge, D. (2025). Global effects of livestock grazing on ecosystem functions vary with grazing management and environment. Agriculture, Ecosystems & Environment, 378, 109296. Link to source: https://doi.org/10.1016/j.agee.2024.109296
Sanderman, J., Partida, C., Xia, Y., Lavallee, J. M., & Bradford, M. A. (2025). Low quality evidence dominates discussion of carbon benefits of alternative grazing strategies. bioRxiv, 2025-12. Link to source: https://doi.org/10.64898/2025.12.09.693242
Smith, P. (2014). Do grasslands act as a perpetual sink for carbon?. Global change biology, 20(9), 2708-2711. Link to source: https://doi.org/10.1111/gcb.12561
Tang, S., Wang, K., Xiang, Y., Tian, D., Wang, J., Liu, Y., ... & Niu, S. (2019). Heavy grazing reduces grassland soil greenhouse gas fluxes: A global meta-analysis. Science of the Total Environment, 654, 1218-1224. Link to source: https://doi.org/10.1016/j.scitotenv.2018.11.082
Contrails, the long, thin clouds that form behind airplanes, trap heat radiating from the Earth, creating a strong but short-lived warming effect similar to that of greenhouse gases in the atmosphere. Rerouting airplanes to avoid areas where warming contrails can form reduces the warming impact of these human-made clouds. Rerouting aircraft to avoid turbulence is already an industry practice, and modeling studies plus industry trials have demonstrated that strategically rerouting a small fraction of flights can reduce contrail-induced warming at very low cost. However, adoption will require new regulations and policies, and the effect may be limited by uncertainties in the models used to predict both where warming contrails will form and their climate impacts, as well as by safety concerns in congested airspaces. The immediate and direct decrease in warming by reducing contrails makes this a high-priority “emergency brake” climate solution. However, because the industry is not ready to adopt the solution at scale today and because there are major gaps in the data on its potential effectiveness, we will “Keep Watching” this solution.
Based on our assessment, Reduce Airplane Contrails has the potential to rapidly reduce the direct climate warming impact of the aviation industry. However, because the solution is not already being adopted at scale and there is a lack of data on its effectiveness, we will “Keep Watching” this solution.
| 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? | Yes |
This solution reduces the warming impact of contrails by rerouting airplanes to avoid areas where contrails are likely to form. Contrails (also known as condensation trails) are long, thin clouds that form behind aircraft when the exhaust combines with cold, humid air to produce ice crystals at high altitudes. Contrails can trap heat radiating from the Earth, producing a strong but short-lived warming effect similar to that of greenhouse gases in the atmosphere. Most contrails dissipate quickly (<10 minutes), but under some meteorological conditions, they can persist for many hours. In regions with high air traffic density, contrails can cover a large fraction of the sky area, and even though they may last for only hours, the heat trapped in the atmosphere and oceans by contrails is multiplied by the tens of millions of flights per year. It’s important to note that not all contrails have a warming impact. The degree to which contrails warm or cool the atmosphere varies with time of day, season, atmospheric conditions at cruising altitudes, and whether the clouds form over land or ocean. Contrails that form during the day can have a net cooling effect by reflecting solar radiation back into space. However, the scientific consensus is that contrails overall have a net warming effect.
Modeling studies and field testing suggest that strategically rerouting flights to avoid areas where warming contrails are likely to form can substantially reduce contrail formation and their warming impacts. It is estimated that less than 20% of flights produce persistent contrails with a net warming effect, and rerouting the most impactful of these flights could reduce contrail-induced warming by as much as 80%, providing an immediate climate benefit. Rerouting aircraft to avoid turbulence is already a standard industry practice. These same protocols could be used for contrail avoidance with the addition of model forecasts for contrail formation into pre-flight planning and in-flight sensors and satellite measurements for in-flight responses.
Research suggests that the warming impact of contrails is roughly comparable to and additional to the warming from the direct GHG emissions from the aviation industry’s use of fossil fuels. Strategically rerouting air traffic to reduce the formation of warming contrails could have an immediate and globally meaningful climate impact, making this an “emergency brake” solution with the potential to deliver a beneficial impact more rapidly than many other climate solutions. In addition, this solution could be implemented at scale relatively quickly, even as supportive predictive models, meteorological monitoring, and instrument integration technologies improve. Progress is already being made. Industry trials are already underway, and on-board humidity sensors that can identify when an airplane is moving through a contrail-forming region are being developed. The European Union now requires major aircraft operators to report modeled data on their contrail formation as part of their emissions reporting. This sets the stage for policies that require warming contrail avoidance. Finally, this high-impact climate solution is relatively low-cost. The costs for additional sensors and fuel are estimated to be US$10–15 per flight, or the equivalent of US$1–6/t CO₂‑eq avoided.
Policy and regulatory changes will be needed to support the adoption of rerouting protocols to avoid warming contrails, and implementation could be restricted by uncertainties in the models and by safety concerns. Multilateral industry and government cooperation will be necessary to draft new regulations to support rerouting to avoid warming contrails, and timelines must be established for mandatory implementation. While models that forecast where warming contrails are likely to form exist, they are limited by a lack of data on humidity levels at cruising altitudes and require more validation to assess how accurately they project contrail formation. In addition, better tools to monitor and model the effectiveness of rerouting in preventing the formation of warming contrails are needed, especially when the added emissions from fuel use could exceed the climate benefits of the contrails avoided. Rerouting opportunities may also be limited by safety concerns in congested airspaces.
Cathcart, J., Andrews, S., Chen, A., Cornec, H., Kumar, S., Majholm, J., Meijers, M., Meijers, N., Miller, R., Mukhopadhaya, J., Sachdeva, N., Shapiro, M., Stern, C., & Wendling, Z. (2024). Understanding contrail management: Opportunities, challenges and insights. Rocky Mountain Institute. Link to source: https://rmi.org/wp-content/uploads/dlm_uploads/2024/07/understanding_contrail_management_report.pdf
Hodgson, R. (2024, September 2). Airlines must monitor vapour trails under new EU climate rules. Euro News. Link to source: https://www.euronews.com/green/2024/09/02/airlines-must-monitor-vapour-trails-under-new-eu-climate-rules
International Air Transport Association. (2024). Aviation contrails and their climate effects. Link to source: https://www.iata.org/contentassets/726b8a2559ad48fe9decb6f2534549a6/aviation-contrails-climate-impact-report.pdf
International Air Transport Association. (2025). Industry statistics. Link to source: https://www.iata.org/en/iata-repository/pressroom/fact-sheets/industry-statistics/
Kärcher, B. (2018). Formation and radiative forcing of contrail cirrus. Nature Communications, 9(1), 1824. Link to source: https://doi.org/10.1038/s41467-018-04068-0
Lee, D. S., Fahey, D. W., Skowron, A., Allen, M. R., Burkhardt, U., Chen, Q., Doherty, S. J., Freeman, S., Forster, P. M., Fuglestvedt, J., Gettelman, A., De León, R. R., Lim, L. L., Lund, M. T., Millar, R. J., Owen, B., Penner, J. E., Pitari, G., Prather, M. J., … Wilcox, L. J. (2021). The contribution of global aviation to anthropogenic climate forcing for 2000 to 2018. Atmospheric Environment, 244, 117834. Link to source: https://doi.org/10.1016/j.atmosenv.2020.117834
Lombardo, T. (2025, January 16). Aviation. International Energy Agency (IEA). Link to source: https://www.iea.org/energy-system/transport/aviation
Martin Frias, A., Shapiro, M. L., Engberg, Z., Zopp, R., Soler, M., & Stettler, M. E. J. (2024). Feasibility of contrail avoidance in a commercial flight planning system: An operational analysis. Environmental Research: Infrastructure and Sustainability, 4(1), 015013. Link to source: https://doi.org/10.1088/2634-4505/ad310c
Ritchie, H. (2025). Eliminating contrails from flying could be incredibly cheap. Sustainability by numbers. Link to source: https://www.sustainabilitybynumbers.com/p/eliminating-contrails
Teoh, R., Schumann, U., & Stettler, M. E. J. (2020). Beyond Contrail Avoidance: Efficacy of Flight Altitude Changes to Minimise Contrail Climate Forcing. Aerospace, 7(9), 121. Link to source: https://doi.org/10.3390/aerospace7090121
Thomas, T. M., Duan, L., Bala, G., & Caldeira, K. (2025). A Stylized Study of the Climate Response to Longwave and Shortwave Forcing at the Altitude of Aviation‐Induced Cirrus. Earth’s Future, 13(10), e2025EF006201. Link to source: https://doi.org/10.1029/2025EF006201
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.