Carbon capture and storage (CCS) involves capturing CO2 from large point sources (e.g., combined heat and power plants or cement making); transporting it; and then permanently storing it underground in geological formations or through mineralisation.
Nordic leadership in carbon capture and storage innovation
The Nordic region has taken a global lead in developing CCS. In 2019, the Helsinki Declaration on Nordic Carbon Neutrality was adopted, and the Nordic countries jointly acknowledged the important role of CCS and the significance of collaboration towards its development. All Nordic countries are investing in research, development, and piloting of CCS technology. Norway has been an early mover in using carbon pricing and regulatory instruments to deploy CCS. Today, over 25 years of experience of CCS has been accumulated, including geological storage of CO2 under the seabed outside the coast of Norway. Denmark, Sweden and Norway are currently developing some of the world’s first support systems to incentivise Bioenergy with CCS (BECCS) and Direct Air CCS (DACCS). With the Longship and Northern Lights projects, Norway is taking steps to develop geological CO2 storage as a service (Möllersten, Marklew, & Ahonen, 2023). In 2021, Denmark adopted a roadmap for CCS, which includes several initiatives. Overall goals include building an entire CCS value chain and that Denmark should become a European hub for CO2 storage.
In Iceland, a unique technology, the ‘Carbfix method’, is deployed building on dissolving carbon dioxide in water and the subsequent injection into basaltic layers, where it solidifies through mineralisation in less than two years. A storage hub for carbon dioxide is planned, with a terminal that would enable the import of CO2 to Iceland via ships, e.g., from European industry.
Advancing carbon capture technologies
Applying CCS to fossil CO2 sources can reduce emissions by up to 90 per cent. Carbon removal (also known as “negative emissions”) can be achieved through various so-called Carbon Dioxide Removal (CDR) methods that remove CO2 are already present in the atmosphere on a net basis (IPCC, 2022). For BECCS, CO2 is first removed from the atmosphere through photosynthesis before the CO2 is captured and permanently stored. DACCS separates CO2 directly from ambient air and then stores it. Significant demonstration will be required before the entire CCS value chain reaches commercial maturity (IEA, 2020). The cost of CCS is high and can vary significantly depending on the specific case. The IPCC indicates a cost of abatement above 100 EUR per tonne CO2 when the technology reaches maturity (IPCC, 2022). Current costs are in many cases significantly higher. The current cost of DACCS, 500 to over 1,000 EUR per tonne CO2 (Bednar, Höglund, Möllersten, Obersteiner, & Tamme, 2023), will require significant cuts before the technology can give meaningful contributions to mitigation efforts.
Policy frameworks driving CCS investments
Sufficient financial incentives must be in place for investments in CCS to happen. This responsibility primarily falls on regulators (Honegger, 2023). The current design of the EU ETS includes CCS for CO2 emissions from fossil fuels and industrial processes among the rewarded technologies. However, EU-ETS price levels have so far not been sufficient to incentivise CCS. Moreover, the EU has not yet introduced policy instruments to drive investments in carbon removals through BECCS or DACCS (Fridahl, et al., 2023). National initiatives in Norway, Denmark and Sweden have been implemented, or are being prepared, to enable investments in CCS, BECCS and DACCS (Möllersten, Tynkkynen, and Zetterberg, 2023). Furthermore, the emerging carbon markets can catalyse early financing of BECCS and DACCS (Honegger, 2023; Hickey, Fankhauser, Smith, and Allen, 2023). All Nordic countries have transposed the EU CCS Directive into their national legislation. The Nordic countries have been proactive in developing a more permissive national and international regulatory environment for CCS and continue working actively to eliminate remaining regulatory gaps and lower barriers to facilitate the deployment of CCS technologies (Möllersten, Marklew, and Ahonen, 2023).
Engaging stakeholders for effective implementation
Local resistance to establishing onshore CO2 storage sites can delay implementation. Therefore, it is crucial to engage stakeholders in an inclusive process, provide transparent and objective information and ensure that the local community shares some of the benefits derived from CO2 storage.
Impact on climate change mitigation
CCS applied to CO2 emissions from fossil sources allows for significant emission reductions where alternative mitigation solutions are not technically or economically feasible. However, even when CCS is applied there will be remaining emissions since a 100 per cent capture rate is infeasible. BECCS and DACCS as well as other CDR methods will be required to counterbalance ‘residual emissions’ that are extremely challenging to fully mitigate, such as those from aviation, shipping, agriculture, and fossil-based processes equipped with CCS. Secondly, later in this century, CDR can be used to reduce carbon dioxide-induced warming from an 'overshoot' level, down to the Paris Agreement target level.
Scalability
CCS is being developed at numerous sites globally. Whilst transitioning away from fossil fuels, the application of CCS as well as BECCS and DACCS can be adapted to meet the decarbonization needs of power, heat, industrial processes, and transportation fuels, making it highly scalable. The global technical geological CO2 storage capacity is estimated to be on the order of 1,000 billion tonnes CO2, which is more than the CO2 storage requirements through 2100 in pathways that limit global warming to 1.5 °C (IPCC, 2023). This estimate excludes the potential for the Carbfix method, which could potentially increase the outcome by several thousand billion tonnes CO2 (Carbfix, 2024).
Potential for global replication and transferability
Implementation of CCS currently faces technological, economic, institutional, ecological-environmental and socio-cultural barriers. Currently, the availability of the technology and technological readiness are major roadblocks. The regional availability and readiness of geological storage is also a limiting factor. Enabling conditions such as policy instruments, economic incentives, global carbon management, greater public support and technological innovation could reduce these barriers. Similarly, the business case for BECCS and DACCS requires payments for CO2 removal (Bednar et al., 2023). The transferability of these technologies to other regions is primarily determined by national and regional policies.