Blue Carbon Explained: The Ocean’s Role in Climate Change Mitigation

 


In the era of accelerating climate change, the search for effective and sustainable carbon sequestration strategies has become a global priority. Among emerging solutions, blue carbon has increasingly garnered scientific and political attention for its capacity to capture and store atmospheric carbon dioxide in coastal ecosystems (Feng et al., 2023; Pang et al., 2024). These ecosystems, mangroves, seagrass meadows, and salt marshes, act as powerful carbon sinks while also providing ecological and socioeconomic benefits (Duarte et al., 2013). Recent research further confirms their critical role as nature based solutions for climate change mitigation and adaptation (Mondal et al., 2026).


             Blue Carbon Explained: The Ocean’s Role in Climate Change Mitigation

Introduction

Climate change continues to intensify due to increased greenhouse gas emissions, particularly CO₂ (IPCC, 2019). While terrestrial ecosystems have traditionally dominated discussions on carbon mitigation, coastal ecosystems are now recognized as highly efficient carbon sinks (Feng et al., 2023). The concept of blue carbon refers to the carbon captured and stored in marine and coastal ecosystems, such as mangroves, seagrass meadows, and salt marshes (McLeod et al., 2011). Recent global assessments indicate that blue carbon ecosystems provide disproportionately high carbon storage relative to their area, making them critical for achieving climate goals (Pang et al., 2024). Furthermore, recent studies highlight their role as scalable, nature-based climate solutions (Pessarrodona et al., 2024).

Understanding Blue Carbon Ecosystems

Blue carbon ecosystems refer to coastal and marine habitats that possess the remarkable capacity to capture, store, and sequester atmospheric carbon dioxide (CO₂) over long periods. These ecosystems, primarily mangroves, seagrass meadows, and salt marshes, play a disproportionately important role in the global carbon cycle, despite occupying a relatively small fraction of the Earth's land surface (McLeod et al., 2011; Duarte et al., 2013). In recent years, the concept of blue carbon has evolved from a minority scientific idea to a fundamental pillar in climate change mitigation strategies, especially within the framework of nature-based solutions (Feng et al., 2023; Pang et al., 2024).

Essentially, blue carbon ecosystems function through a combination of high biological productivity and efficient carbon sequestration mechanisms. Unlike many terrestrial ecosystems, where carbon is stored primarily in aboveground biomass, blue carbon systems store a significant portion of carbon in underground sediments, where it can remain trapped for centuries or even millennia (Alongi, 2014; Pendleton et al., 2012). This long-term storage capacity makes them highly effective at reducing atmospheric CO₂ concentrations. Understanding blue carbon ecosystems is fundamental to developing sustainable climate solutions. Their unique ability to efficiently store carbon, along with their ecological and socioeconomic benefits, makes them crucial assets in the fight against climate change (Feng et al., 2023; Pang et al., 2024). The main types of blue carbon ecosystems are described below:

Mangrove forests: Mangroves are salt-tolerant woody plants that thrive in the intertidal zones of tropical and subtropical coasts. They are widely recognized as one of the most carbon-dense ecosystems on the planet (Alongi, 2014). Their complex root systems not only stabilize coastlines but also retain organic matter and sediments, thus promoting carbon sequestration (Choudhary et al., 2024). Recent studies highlight that mangrove sediments can store carbon at depths of up to several meters, significantly increasing their long-term sequestration potential (Feng et al., 2023). Furthermore, mangroves act as barriers against extreme weather events, thereby linking climate change mitigation with the benefits of adaptation.

Seagrass meadows: Seagrass meadows are submerged flowering plants found in shallow coastal waters of tropical and temperate regions. They form extensive underwater meadows that support marine biodiversity and contribute to carbon storage (Duarte et al., 2013). A distinctive feature of seagrass ecosystems is their ability to trap and stabilize sediments, preventing the resuspension of stored carbon (Macreadie et al., 2024). Their root and rhizome systems facilitate the accumulation of organic carbon in sediments, making them highly efficient long-term carbon sinks. Recent research also indicates that seagrass ecosystems can adapt to changing environmental conditions, which could increase their carbon sequestration capacity in certain scenarios (Pessarrodona et al., 2024).

Salt marshes: Salt marshes are coastal wetlands dominated by salt-tolerant grasses, herbs, and shrubs. These ecosystems are typically found in temperate regions and are characterized by high rates of primary productivity (McLeod et al., 2011). Salt marshes accumulate organic matter through plant growth and sedimentation, leading to the formation of carbon-rich soils (Pendleton et al., 2012). Waterlogged, low-oxygen conditions slow decomposition, allowing carbon to be stored for long periods (Alongi, 2014). Recent studies highlight that salt marshes are particularly resilient to environmental changes, making them important components of climate adaptation strategies (Friess et al., 2024).

Characteristics of Blue Carbon Ecosystems

Blue carbon ecosystems possess several distinctive characteristics that differentiate them from terrestrial carbon sinks:

High carbon sequestration rates: They can sequester carbon up to 5–10 times faster per unit area than terrestrial forests (Duarte et al., 2013; Feng et al., 2023).

Long-term storage: Carbon is stored in anaerobic sediments, which reduces decomposition rates and ensures long-term sequestration (Alongi, 2014).

Carbon reserves in sediments: A large proportion of the carbon is stored underground, making these ecosystems less vulnerable to immediate disturbances compared to aboveground biomass (Pendleton et al., 2012).

Multifunctional ecosystem services: In addition to carbon storage, they provide coastal protection, biodiversity support, and livelihood opportunities (IPCC, 2019).

Mechanisms of Carbon Sequestration in Blue Carbon Ecosystems

Blue carbon ecosystems, such as mangroves, seagrass meadows, and salt marshes, are highly efficient at capturing and storing atmospheric carbon dioxide (CO₂). Their sequestration mechanisms involve a combination of biological production, sedimentary processes, and long-term storage, making them more effective than many terrestrial systems (Duarte et al., 2013; McLeod et al., 2011).

The process begins with photosynthesis, where plants absorb CO₂ from the atmosphere or seawater and convert it into organic matter (Duarte et al., 2013). Mangroves primarily absorb atmospheric CO₂, while seagrass meadows utilize carbon dissolved in the water (Macreadie et al., 2024). Due to favorable coastal conditions, these ecosystems typically exhibit high rates of productivity and carbon sequestration (Feng et al., 2023).

Once fixed, carbon is stored in plant biomass, including leaves, stems, and roots. A distinctive feature of blue carbon ecosystems is the large proportion of subterranean biomass, especially in roots and rhizomes (Alongi, 2014). This subterranean storage enhances carbon stability and reduces the risk of rapid release into the atmosphere (Pendleton et al., 2012).

Another important mechanism is the continuous production of organic matter through litter, such as fallen leaves and dead roots. This material accumulates in the soil or seabed and contributes to carbon sequestration (McLeod et al., 2011). In mangroves and seagrass meadows, tides and ocean currents help transport and deposit this organic matter in the sediments, further increasing carbon storage (Choudhary et al., 2024).

A key feature of these ecosystems is their ability to trap and stabilize sediments. Mangrove roots, seagrass leaves, and marsh vegetation slow water flow, allowing suspended particles to settle (Alongi, 2014). Over time, this leads to the formation of carbon-rich sediment layers. These sediments can store carbon for long periods, often to depths of several meters (Pendleton et al., 2012).

The most important mechanism is the burial of organic carbon under anoxic (low oxygen) conditions. In these environments, decomposition slows significantly, preventing the release of carbon into the atmosphere (Alongi, 2014). This allows carbon to remain stored for centuries or even millennia, making blue carbon ecosystems long-term carbon sinks.

Furthermore, continuous sedimentation leads to the accumulation of sediments, with new layers overlying older ones (Duarte et al., 2013). This not only enhances carbon storage but also helps ecosystems adapt to sea-level rise (IPCC, 2019).

Some carbon is also exported to adjacent marine systems, where it can eventually become buried in deep-sea sediments (McLeod et al., 2011). Recent studies highlight the importance of this connectivity for expanding the overall potential for carbon sequestration (Pessarrodona et al., 2024).

Conclusion

Blue carbon ecosystems represent a powerful natural solution to climate change. Their capacity to sequester large amounts of carbon, along with their ecological and socioeconomic benefits, makes them indispensable in the global fight against climate change. However, their continued degradation poses a serious threat to both environmental sustainability and human well-being.

For countries like India, investing in the conservation and restoration of coastal ecosystems can generate significant climate, economic, and social benefits. A coordinated approach that includes political support, scientific research, and community engagement is essential to harnessing the full potential of blue carbon.

References

Alongi, D. M. (2014). Carbon sequestration in mangrove forests. Carbon Management, 5(1), 1–3.

Choudhary, B. (2024). Blue carbon and the role of mangroves in climate mitigation. Environmental Science and Policy. Advance online publication.

Duarte, C. M., Losada, I. J., Hendriks, I. E., Mazarrasa, I., and Marbà, N. (2013). The role of coastal plant communities for climate change mitigation and adaptation. Nature Climate Change, 3(11), 961–968.

Feng, C., Ye, G., Zeng, J. et al.  (2023). Sustainable development and blue carbon: Global perspectives. Nature Communications, 14, Article number:6144. https://doi.org/10.1038/s41467-023-41870-x

Friess, D. A. (2024). Restoring blue carbon ecosystems. Cambridge Prisms: Coastal Futures, 2, e7. https://doi.org/10.1017/cft.2024.7

Intergovernmental Panel on Climate Change (IPCC). (2019). Special report on the ocean and cryosphere in a changing climate. Cambridge University Press. https://doi.org/10.1017/9781009157964

Macreadie, P.I., Wartman, M., Roe, P., Hodge, J.M., Helber, S.B., Waryszak, P. and Raoult, V. (2024) Seagrasses produce most of the soil blue carbon in three Maldivian islands. Front. Mar. Sci. 11:1359779. doi: 10.3389/fmars.2024.1359779

Mcleod, E., Chmura, G. L., Bouillon, S., Salm, R., Björk, M., Duarte, C. M., Lovelock, C. E., Schlesinger, W. H., and Silliman, B. R. (2011). A blueprint for blue carbon: Toward an improved understanding of the role of vegetated coastal habitats in sequestering CO₂. Frontiers in Ecology and the Environment, 9(10), 552–560.

Mondal, I., et al. (2026). Blue carbon sequestration in Sundarbans. Journal of Marine Systems. Advance online publication.

Pang, S., Majid, M. A., Perera, H. A. C. C., Sarkar, M. S. I., Ning, J., Zhai, W. (2024). A systematic review and global trends on blue carbon and sustainable development. Sustainability, 16(6), 2473.

Pendleton, L., Donato, D. C., Murray, B. C., Crooks, S., Jenkins, W. A., Sifleet, S., Craft, C., Fourqurean, J. W., Kauffman, J. B., Marbà, N., Megonigal, P., Pidgeon, E., Herr, D., Gordon, D., and Baldera, A. (2012). Estimating global “blue carbon” emissions from conversion and degradation of vegetated coastal ecosystems. PLoS ONE, 7(9), e43542.

Pessarrodona, A., Moore, P. J., Sayer, M. D. J., Smale, D. A., and Burrows, M. T. (2024). Carbon sequestration potential of marine ecosystems. Science of the Total Environment, 912, 170123. https://doi.org/10.1016/j.scitotenv.2024.170123

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