Use Methane Removal
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.
Improving district heating for industry involves using low-carbon alternatives, such as electric boilers, heat pumps, and waste heat from other industries, to provide heat to industries for their operations. Currently, most district heating for industry relies heavily on fossil fuels to generate heat. Low-carbon alternatives have the potential to make a significant dent in the global emissions from industry, but such projects are also challenging to implement due to their scale and complexity, and there is currently a lack of publicly available data that would allow for a deeper analysis. Based on our assessment, we will “Keep Watching” this potential solution.
Based on our analysis, improving district heating for industry by integrating low-carbon heat sources has the potential to significantly reduce the use of fossil fuels and the emissions they generate. However, the lack of data, combined with the complexity of such projects and the growing interest in alternative decarbonization pathways, makes this a potential solution to “Keep Watching.”
| 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? | No |
District heating systems consist of a network of underground pipes that distribute heat to a large number of buildings, including industrial buildings. In the industrial sector, district heating is used by light industries and for processes such as drying, paper making, food processing, as well as space heating and even heat-driven chillers for refrigeration. Industry is well-suited to district heating because it typically has steady and predictable heat demand throughout the year. Current district heating systems rely heavily on coal and natural gas for heat generation, often as part of combined heat and power generation. Low-carbon alternatives for district heating can include electric heat pumps, solar thermal, deep geothermal, and even waste heat from other industries.
Shifting district heating for industry from conventional heat sources to low-carbon heat sources will significantly reduce emissions. Our analysis for district heating use by commercial and residential buildings shows that significant emissions can be avoided by shifting to electric boilers, heat pumps, and the use of waste heat (see Improve District Heating: Buildings). Similar outcomes are likely possible for industrial district heating use, and emissions reductions will increase as more renewables are integrated into the electricity systems used to power electric boilers and heat pumps.
District heating for industry currently produces significant emissions. According to the International Energy Agency (IEA), district heating for all applications accounted for 4% of global emissions in 2022, and roughly 40% of the heat energy from district heating was delivered to industry. China is a major adopter of district heating for industries, with the combustion of coal supplying much of that heat. The shift to renewable heat sources is likely to increase because both China and the EU have policies targeting the adoption of renewables in district heating. Because district heating systems serve multiple buildings, a single project to replace fossil fuels with renewables can have a large impact. Such projects also have the benefit of reducing local air pollution.
Although simple on paper, replacing fossil fuel systems with lower-carbon alternatives in district heating systems can be an extended undertaking involving many stakeholders and years of planning. Some low-carbon options may not be suitable for industrial processes that require higher temperatures than those needed for space heating. There is also a significant lack of publicly available data about how industry currently uses district heating and the opportunities and challenges involved in shifting to renewables. In the meantime, industrial heat pumps with higher temperature outputs (100–200°C) are increasingly available and could become a low-carbon competitor to the use of a conventional district heating system.
Bellevrat, E., & West, K. (2018). Clean and efficient heat for industry. IEA. Link to source: https://www.iea.org/commentaries/clean-and-efficient-heat-for-industry
Difs, K., Danestig, M., & Trygg, L. (2009). Increased use of district heating in industrial processes – Impacts on heat load duration. Applied Energy, 86(11), 2327–2334. Link to source: https://doi.org/10.1016/j.apenergy.2009.03.011
European Commission. (2022). Implementing the repower EU action plan: Investment needs, hydrogen accelerator and achieving the bio-methane targets. Link to source: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:52022SC0230
Gouy, A., Mooney, E., & Voswinkel, F. (2023). Light Industry. IEA. Link to source: https://www.iea.org/energy-system/industry/light-industry
IEA. (2025). District heating. Link to source: https://www.iea.org/energy-system/buildings/district-heating#programmes
IRENA, IEA, & REN21. (2020). Renewable energy policies in a time of transition: Heating and cooling. Link to source: https://www.irena.org/-/media/Files/IRENA/Agency/Publication/2020/Nov/IRENA_IEA_REN21_Policies_Heating_Cooling_2020.pdf
Lake, A., Rezaie, B., & Beyerlein, S. (2017). Review of district heating and cooling systems for a sustainable future. Renewable and Sustainable Energy Reviews, 67, 417–425. Link to source: https://doi.org/10.1016/j.rser.2016.09.061
Werner, S. (2017). International review of district heating and cooling. Energy, 137, 617–631. Link to source: https://doi.org/10.1016/j.energy.2017.04.045
Seaweed (also called macroalgae) ecosystem restoration involves the reestablishment of wild red, brown, and green seaweed through interventions that recover degraded, damaged, or destroyed seaweed ecosystems. Healthy seaweed ecosystems remove CO₂ from the water column and convert it into biomass through photosynthesis, allowing additional CO₂ to be taken up in the ocean from the atmosphere. Some of this biomass carbon ends up sequestered, either on-site in sediment or off-site in the deep sea or at the seafloor. Advantages include the widespread human and environmental benefits associated with restored, healthy seaweed ecosystems. Disadvantages include its unclear effectiveness and climate impact, as well as its potentially high costs and difficulty of adoption at scale. Currently, we conclude that we should “Keep Watching” this solution.
Based on our analysis, the climate impact of restoring seaweed ecosystems is unclear but likely to be low. While restoration offers important ecological benefits, its effectiveness in removing carbon is understudied, and the implementation costs may be prohibitively high, but require further research. Therefore, we conclude that Restore Seaweed Ecosystems is a solution to “Keep Watching.”
| Plausible | Could it work? | Yes |
|---|---|---|
| Ready | Is it ready? | Yes |
| Evidence | Are there data to evaluate it? | No |
| Effective | Does it consistently work? | ? |
| Impact | Is it big enough to matter? | ? |
| Risk | Is it risky or harmful? | No |
| Cost | Is it cheap? | No |
Seaweed ecosystem restoration is the deliberate action of reestablishing seaweed in degraded, damaged, or destroyed ecosystems. Seaweed removes CO₂ from seawater through photosynthesis, which allows the ocean to absorb additional CO₂ from the atmosphere. Some of the fixed carbon can be sequestered through export to the deep sea or burial at the seafloor, while a portion may also persist as carbon forms that resist degradation even in the surface ocean. Restoration of seaweed ecosystems helps restore biomass and therefore the productivity of these ecosystems, which can enhance their sequestration capacity. Restoration can occur in a number of ways, but commonly includes transplanting adults, controlling grazers, building artificial reefs, seeding with propagules or spores, remediating pollution, removing competitive species, and culturing. Most restoration efforts have focused on canopy-forming species, such as giant kelp (Macrocystis pyrifera).
Seaweed ecosystem restoration can be somewhat effective, with nearly 60% of restoration efforts achieving survival rates of over 50%. The first large-scale restoration is thought to have occurred in Japan in the late 1800s. Still, few projects have been implemented at scale, with most restoration efforts below 0.1 ha in size. Moreover, little data exist to evaluate the effectiveness of restored seaweed ecosystems at removing carbon. While theoretically, they should regain functional equivalence to intact systems, this requires further research. The extent of lost and degraded seaweed ecosystems is also poorly understood, making it unclear how restoration efforts might be scaled globally. Additionally, the air-to-sea transfer of CO₂ to replace the CO₂ taken up by photosynthesis in the ocean is not always efficient, meaning removal in the water column may not always translate to equivalent atmospheric CO₂ removal. However, this aspect of effectiveness also remains understudied. Consequently, the climate impact of restoration is uncertain.
Healthy seaweed ecosystems provide a range of ecological benefits. Seaweed can help buffer against ocean acidification in some places as functional systems better regulate pH. These systems also provide complex habitats that support a wide range of marine life, such as fish and invertebrates, so restoring seaweed ecosystems can help recover biodiversity. Seaweed ecosystem restoration can also improve nutrient cycling and overall ecosystem resilience to climate stressors.
Restoration of seaweed ecosystems is currently expensive, with costs varying widely depending on the method used. In kelp forests, chemical or manual urchin removal, which reduces grazing pressure, may cost between US$1,700/ha and US$76,000/ha in 2023 dollars, while most other approaches exceed US$590,000/ha.
It’s also unclear whether seaweed restoration efforts could scale enough to have a globally meaningful impact on GHG emissions. Using estimates from intact subtidal brown seaweed ecosystems, which are among the most productive and represent a likely upper limit on the effectiveness of seaweed restoration as a whole, restoration might remove 2.3 tCO₂‑eq
/ha/yr. At this rate, over 40 Mha would need to be restored to exceed 0.1 GtCO₂‑eq/yr.
However, most restoration projects are under 0.1 ha in size. For kelp forests, only roughly 2% (19,000 ha) have been restored out of the Kelp Forest Challenge’s target of 1,000,000 ha by 2040, suggesting that this practice may not be scalable currently.
The effectiveness of restoration can also be offset by the lifecycle emissions of products required to re-establish some seaweed ecosystems. For example, emissions from the production of cement blocks needed to afforest some seaweed habitats have been estimated to potentially delay carbon removal benefits for 5–13 years in some systems.
Bayraktarov, E., Saunders, M. I., Abdullah, S., Mills, M., Beher, J., Possingham, H. P., Mumby, P. J. & Lovelock, C. E. (2015). The cost and feasibility of marine coastal restoration. Ecological Applications 26, 1055–1074. Link to source: https://doi.org/10.1890/15-1077
Carlot, J. (2025). Restoring coastal resilience: The role of macroalgal forests in oxygen production and pH regulation. Journal of Phycology, 61(2), 255-257. Link to source: https://doi.org/10.1111/jpy.70019
Danovaro, R., Aronson, J., Bianchelli, S., Boström, C., Chen, W., Cimino, R., Corinaldesi, C., Cortina-Segarra, J., D’Ambrosio, P., Gambi, C., Garrabou, J., Giorgetti, A., Grehan, A., Hannachi, A., Mangialajo, L., Morato, T., Orfanidis, S., Papadopoulou, N., Ramirez-Llodra, E., Smith, C. J., Snelgrove, P., van de Koppel, J., van Tatenhove, J., & Fraschetti, S. (2025). Assessing the success of marine ecosystem restoration using meta-analysis. Nature Communications, 16(1), Article 3062. Link to source: https://doi.org/10.1038/s41467-025-57254-2
Eger, A. M., Vergés, A., Choi, C. G., Christie, H., Coleman, M. A., Fagerli, C. W., Fujita, D., Hasegawa, M., Kim, J. H., Mayer-Pinto, M., Reed, D. C., Steinberg, P. D., & Marzinelli, E. M.(2020). Financial and institutional support are important for large-scale kelp forest restoration. Frontiers in Marine Science, 7, 535277. Link to source: https://doi.org/10.3389/fmars.2020.535277
Eger, A. M., Marzinelli, E. M., Christie, H., Fagerli, C. W., Fujita, D., Gonzalez, A. P., Johnson, C., Ling, S. D., Mayer-Pinto, M., Norderhaug, K. M., Pérez-Matus, A., Reed, D. C., Sala, E., Steinberg, P. D., Wernberg, T., Wilson, S., & Vergés, A. (2022). Global kelp forest restoration: past lessons, present status, and future directions. Biological Reviews, 97(4), 1449-1475. Link to source: https://doi.org/10.1111/brv.12850
Eger, A. M., Baum, J. K., Campbell, T., Cevallos Gil, B., Earp, H. S., Falace, A., Freiwald, J., Hamilton, S., Lonhart, S. I., Rootsaert, K., Rush, M. Å., Schuster, J., Timmer, B., & Vergés, A. (2026). Creating a Global Kelp Forest Conservation Fundraising Target: A 14-Billion-Dollar Investment to Help the Kelp. Biological Conservation, 313. Link to source: https://doi.org/10.1016/j.biocon.2025.111573
Filbee-Dexter, K., Wernberg, T., Barreiro, R., Coleman, M. A., de Bettignies, T., Feehan, C. J., Franco, J. N., Hasler, B., Louro, I., Norderhaug, K. M., Staehr, P. A. U., Tuya, F. & Verbeek, J. (2022). Leveraging the blue economy to transform marine forest restoration. Journal of Phycology, 58(2), 198–207. Link to source: https://doi.org/10.1111/jpy.13239
Gibbons, E. G., & Quijon, P. A. (2023). Macroalgal features and their influence on associated biodiversity: implications for conservation and restoration. Frontiers in Marine Science, 10, 1304000. Link to source: https://doi.org/10.3389/fmars.2023.1304000
Kelp Forest Alliance. (2024). State of the world’s kelp report. Kelp Forest Alliance. Link to source: https://kelpforestalliance.com/state-of-the-worlds-kelp-report/
Martin, D. M. (2017). Ecological restoration should be redefined for the twenty‐first century. Restoration Ecology, 25(5), 668-673. Link to source: https://doi.org/10.1111/rec.12554
Pessarrodona, A., Franco‐Santos, R. M., Wright, L. S., Vanderklift, M. A., Howard, J., Pidgeon, E., ... & Filbee‐Dexter, K. (2023). Carbon sequestration and climate change mitigation using macroalgae: a state of knowledge review. Biological Reviews, 98(6), 1945-1971. Link to source: https://doi.org/10.1111/brv.12990
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