Carbon capture technologies

Technical overview of the five main carbon capture methods (their integration constraints, industry fits, and commercial readiness) with a solution provider snapshot.

  1. Capture methods
    1. Post-combustion
    2. Pre-combustion
    3. Oxyfuel combustion
    4. Chemical looping combustion
    5. Direct air capture
  2. Post conditioning
  3. Technology selection
    1. Solution provider snapshot
  4. Footnotes
  5. Bibliography
  6. Backlinks

Deciding which carbon capture technology to use for an industrial facility is complicated. We have standardised technology readiness levels (TRL) 1 to help us evaluate the maturity and commercial viability of each technology (Kearns2025, pp.7), but plant managers also need to consider their own operational specifics (like excess heat output, power grid needs, and supply chain) to assess the feasibility and risks of a given solution as a whole. So, a general technical understanding of how these technologies work is also needed to get a performant capture facility up and running, while interfacing correctly with adjoining carbon transport and storage infrastructure.

Capture methods

Carbon capture technologies recover CO₂ from point sources or directly from the atmosphere turning it into a concentrated CO₂ stream which can be transported to permanent storage or processing facilities for utilisation in other industrial processes. Depending on perspective, there are five main carbon capture methods: post-combustion, pre-combustion, oxyfuel combustion, chemical looping combustion, and direct air capture, each with their own technological variations.

Post-combustion

With post-combustion carbon capture methods, you remove CO₂ from the flue gas 2 after the fuel has been combusted with air. Absorption 3 (solvent-based) is the most mature removal technology (Danish Energy Agency2024, pp.22), though adsorption (solid-based), membranes, and cryogenic separation are progressing with promising results. Overall these technologies are highly versatile because they can be retrofitted onto existing exhaust stacks in facilities like coal plants, cement kilns, waste-to-energy plants, and steel mills without major operational changes.

A flowchart showing the post-combustion carbon capture process. It starts with gas/solid fuels feeding into a power plant, which uses air and produces flue gases and power. The flue gases are then processed in a carbon capture unit that outputs CO₂ and receives a reactant.
Simplified post-combustion carbon capture process adapted from Danish Energy Agency2024.

Absorption technologies use amine solvents to scrub CO₂ from the flue gas, followed by thermal regeneration to produce a pure CO₂ stream. With the ability to capture >90% of CO₂, you can retrofit this technology onto nearly any point source with an exhaust gas. It has also been used for decades within the food and beverage industry for CO₂ recovery, and it can also be integrated with steam cycles or district heating to boost efficiency since it requires large amounts of heat. Efficiencies can also be gained from integrating excess heat from combined heat and power plants. Current research focuses on optimising energy use and developing alternative solvents like amino acid salts or ionic liquids.

Adsorption technologies, unlike absorption, use solids like carbon, zeolites, or metal-organic frameworks (MOFs) with amine functional groups to adsorb CO₂ at low temperatures, or calcium looping with lime-based sorbents at high temperatures (600-900°C). Low-temperature processes are often limited by low cyclic loading, rapid sorbent deactivation, and scaling difficulties, while high-temperature calcium looping requires heavy boiler integration, making it unsuitable for retrofits but viable for cement kilns where spent sorbent can be reused. Current research focuses on improving sorbent durability and process scalability, limiting their near-term applicability for retrofit projects.

Membrane technologies separate CO₂ from a flue gas like a sieve. Yet, flue gases are often at low pressure, so we need additional compression or vacuum systems to efficiently drive CO₂ through the membrane leading to increased electricity consumption. Membrane technologies are also sensitive to dust and other pollutants in the flue gas. The technology looks promising at pilot-scale, but with low TRL and limited scalability at this point, they are best suited for high-pressure applications than typical post-combustion scenarios, requiring further development to increase efficiency and robustness for broader industrial use.

Cryogenic separation technologies capture CO₂ by cooling flue gas to very low temperatures (below -100°C) to freeze out CO₂, often requiring compression to avoid extreme chilling. This energy-intensive process faces challenges with handling flue gas pollutants and the high cost of compression and refrigeration equipment. Currently at low TRL, with only small-scale pilot trials conducted, cryogenic separation shows potential but is not yet practical for widespread post-combustion applications. Its development lags behind other technologies, and significant advancements are needed to improve energy efficiency and economic feasibility for industrial deployment.

Potassium carbonate technologies mirror amine-based systems, using a caustic solvent circulated between absorber and desorber columns to capture CO₂ from flue gas. Widely used in chemical industries for gas sweetening, it absorbs CO₂ at higher pressures (1-15 bar) and releases it through pressure reduction and heating. Slower absorption rates require larger equipment, mitigated by flue gas compression or chemical/enzymatic promoters. Variants include fully electrified processes, steam-electrification hybrids, or enzymatically catalysed systems using hot water. Energy consumption is comparable to amine systems, but its flexibility with power or hot water inputs allows cost optimisation. Environmentally benign, PC avoids harmful emissions, but its TRL is lower, with pilot and demonstration projects ongoing.

Chilled ammonia is a proprietary technology using ammonium carbonate instead of amine solvents to capture CO₂, operating at low temperatures to minimise ammonia slip. It promises lower heat consumption and delivers CO₂ at higher pressures (5-25 bar) without amine-related emissions. However, slow absorption kinetics, complex process design, and issues with carbonate precipitation have increased heat demands beyond initial expectations. Demonstrated at a 100,000 tpa scale, it suits concentrated CO₂ sources but faces challenges in broader applications. Its complexity and operational drawbacks make it less competitive than amine systems, though it remains a viable alternative for specific industrial settings.

Pre-combustion

With pre-combustion carbon capture methods, you take a fuel like coal, natural gas, or biomass, break it down into syngas (a mixture of hydrogen and CO₂) using heat and steam or oxygen, then remove the CO₂ before burning or using the hydrogen (Danish Energy Agency2024, pp.26). The syngas stream is usually at high-pressure, so capturing CO₂ is easiest with pressure swing adsorption (PSA) 4 (using solid sorbents) or less reactive chemicals (like amine solvents). This technology is mainly used in the fertiliser industry producing ammonia from hydrogen, but it can also be used in the plastics industry or to produce hydrogen from natural gas to be used as a clean fuel. The name pre-combustion comes from its early use in power plants, but it can be misleading since the process doesn’t always involve combustion such as when producing hydrogen as an ammonia feedstock. Despite being an energy-intensive and complex system to setup, it can be built into new power plants designed around gasification.

A flowchart depicting the pre-combustion carbon capture process. It starts with gasification receiving solid fuels, connected to a shift reactor that produces CO₂ and H₂. The shift reactor feeds into a power plant (gas) that uses air and generates power.
Simplified pre-combustion carbon capture process adapted from Danish Energy Agency2024.

Oxyfuel combustion

With oxyfuel combustion carbon capture methods, you burn a fuel with concentrated oxygen instead of open air to produce a flue gas stripped of nitrogen, consisting mostly of CO₂ and water vapour making separation a lot easier (Danish Energy Agency2024, pp.25) with post-combustion methods. Oxygen separation units produce the pure oxygen, and to keep combustion temperatures manageable, 60-70% of the cooled flue gas is recirculated. After condensing out the water, you’re left with a high-concentration CO₂ stream (70-85% purity) that needs minimal purification and compression. Typical candidates for this capture method is power plants, modified cement kilns, or industrial furnaces, though most implementations require significant modifications to existing facilities. Despite removing nitrogen for a simplified capture process, producing pure oxygen is energy-intensive which can turn this method into a poor investment.

A flowchart showing the oxyfuel combustion carbon capture process. It begins with gas/solid fuels feeding into a power plant, which produces CO₂ and receives O₂ from an oxygen separation plant. The oxygen separation plant uses air and outputs H₂ + N₂, while the power plant also generates power.
Simplified oxyfuel combustion carbon capture process adapted from Danish Energy Agency2024.

Chemical looping combustion

With chemical looping combustion (a novel concept also known as solid-looping) carbon capture methods, a solid oxygen carrier (for instance a metal oxide) transports oxygen from an air reactor to a separate fuel reactor, where it reacts with the fuel to produce CO₂ and water (Danish Energy Agency2024, pp.25). The oxygen carrier is reduced through the reaction, so it must be regenerated in a dedicated oxidising reactor with air. Like the oxy-fuel combustion method, this gives us a clean combustion environment without nitrogen, simplifying the CO₂ separation process, while removing the need for a dedicated air separation unit. With seemingly high efficiencies and lower costs with a directly integrated capture process, this method looks mostly relevant for gasification-based power plants or hydrogen facilities. Yet, the technology has only reached pilot scale and can’t be retrofitted onto existing industrial point sources.

A flowchart illustrating the chemical looping combustion carbon capture process. It begins with an air reactor (oxidiser) receiving air and producing N₂, connected to a fuel reactor (reducer) that uses MeOₓ and Me₂O, producing CO₂ + H₂O. The fuel reactor receives fuel (gas) and the process ends with a condensation unit outputting CO₂.
Simplified chemical looping carbon capture process adapted from Danish Energy Agency2024.

Direct air capture

With direct air capture (DAC) methods, large fans pull ambient air through contactors where CO₂ can be absorbed by solvents or solid sorbents, then released as a concentrated stream through heating or other regeneration methods (Danish Energy Agency2024, pp.76). Given low atmospheric CO₂ concentrations (about 0.04%), this process is extremely energy-intensive because we need to move massive air volumes and the high temperature requirements for the reaction drive up costs. We’ve mostly seen smaller operational projects and demos, but there are some serious scaling and funding efforts going on. The biggest advantage is that you can place DAC plants anywhere, near renewable energy sources, carbon storage sites, or utilisation facilities where the facility can provide the CO₂ feedstock needed in e-fuel production, as well as carbon-negative outcomes when connected with permanent storage.

Flowchart illustrating the direct air capture process. It starts with an air reactor (oxidiser) receiving air and producing H₂O and N₂ + O₂. The air reactor is connected to a pellet reactor, which uses K₂CO₃ and produces CaCO₃. The pellet reactor is linked to a CO₂ separation unit, which outputs CO₂ and receives power and gas as well as H₂O. The process also involves a capture solution KOH.
Simplified direct air carbon capture process adapted from Danish Energy Agency2024.

Post conditioning

Regardless of technology, CO₂ must be conditioned after capture to achieve the appropriate purity and state where it can be transported and stored safely in accordance with the remaining value chain. Depending on the emissions point source and capture method, captured CO₂ contains different impurities like water, sulfur compounds, and particulates that can corrode pipelines, storage equipment or disrupt injection into geological formations. Conditioning happens through a combination of dehydration, compression, and sometimes additional purification processes.

A flowchart depicting the CO₂ conditioning process. It begins with a CO₂ processing unit receiving power and raw CO₂ from the carbon capture process. The unit outputs H₂O, O₂, N₂, and Ar, and produces pure CO₂ (with pressure and temperature specifications) using heat.
Simplified CO₂ conditioning process adapted from Danish Energy Agency2024.

Technology selection

The five capture methods vary widely in maturity, retrofit potential, and fit for specific industrial processes. Understanding where each sits on these dimensions is more useful than TRL scores alone (Kearns2025, pp.7).

Retrofit versus greenfield is the first constraint. Post-combustion is the only method that can be added onto an existing exhaust stack without redesigning the underlying process. Pre-combustion and chemical looping require integration at the fuel-conversion stage, making them greenfield or major-modification propositions. Oxyfuel combustion sits in between: technically feasible as a retrofit in some cement or power applications, but rarely economic without significant facility modifications.

CO₂ concentration in the source stream drives cost more than any other single factor. Pre-combustion syngas streams carry 15–35% CO₂, making separation relatively straightforward. Post-combustion flue gases typically run at 3–15%. Direct air capture contends with atmospheric concentrations of roughly 0.04%, which is why its energy and cost penalties are so much larger. It is not a failure of the technology, but just the physics of working with highly diluted streams.

Heat availability matters most for absorption-based post-combustion systems, which consume 3–4 GJ per tonne of CO₂ in solvent regeneration. Facilities with excess low-value heat (combined heat and power plants, waste-to-energy, some refineries) can integrate this step efficiently. Facilities without it face a harder economics case unless grid power is both cheap and clean.

Industry-specific fits follow from the above. Cement kilns, where fuel and process emissions are mixed and temperatures are high, suit calcium looping or oxyfuel combustion. Steel blast furnaces lean toward post-combustion or chemical looping once the latter reaches commercial scale. Hydrogen production via steam methane reforming is a natural home for pre-combustion separation, since the syngas already requires CO₂ removal as part of the process. Power plants have the widest menu of options depending on fuel type and whether the facility is new-build or existing.

For most operators today, post-combustion amine absorption is the default answer. They are commercially proven, retrofittable, and supported by supply chains. The other methods are worth tracking closely, particularly for new-build industrial assets where integration costs can be designed in from the start rather than bolted on later.

Solution provider snapshot

Kearns2025 provides and excellent catalogue of over 70 commercially available and emerging carbon capture solutions, covering performance data, cost ranges, and commercial readiness indicators for each. The table below is a partial excerpt from that report organised by capture method; refer to the full report for the complete inventory. The TRLs reflect those assessed at the time of publication, and the report seems to be updated annually.

SolutionProviderMethodTargetTRL
8RH₂8 RiversOxyfuel combustionHydrogen, ammonia/fertiliser, refining, transportation fuels, coal fuel switching, methanol, oxo-alcohols5
AFC-C & Biome8 RiversOxyfuel combustionPower generation6
Calcite8 RiversDirect air captureDirect air capture6
Flue gas aminesAir LiquidePost combustionSMR, boilers, fired heaters, waste incineration, refineries (FCC), BECCS, power plants, pulp and paper8-9
Syngas aminesAir LiquidePost combustionH₂ production (SMR, POX, ATR), syngas with 15-35% CO₂, oxo-syngas with 3-15% CO₂8-9
Cryocap H₂Air LiquidePost combustionH₂ production (SMR or ATR)7-8
Cryocap FGAir LiquidePost combustionFlue gases or off-gases with CO₂ content >= 15% (SMR, cement/lime, steel blast furnace, refineries (FCC), waste incineration/biomass power plant, pulp & paper)7-8
Cryocap OxyAir LiquidePost combustionCement/lime, power plant, any applications with CO₂ concentration >50%7-8
Cryocap SteelAir LiquidePost combustionIron and steel production7-8
Cryocap LQAir LiquideConditioningLiquefaction7
RectisolAir LiquidePre combustionNG-based low carbon H₂ or NH₃, biomass or MSW-based gasification for the production of SAFs, H₂, MeOH, NH₃, solid carbonaceous-based applications (IGCC, chemicals)9
RecticapAir LiquidePre combustionSyngas bulk CO₂ removal for production of decarbonised hydrogen, ammonia/urea9
DMXAxensPost combustionPower generation, steel mills, refineries, waste incinerators, and chemical, cement, lime, glass, paper, aluminium production8
Deoxygenation and dehydrationBASFConditioningTreatment downstream of CO₂ capture technology9
OASE WhiteBASFPost combustionRemoves CO₂ and sulfur from process gases, especially in syngas and NG applications, ammonia, hydrogen9
OASE BlueBASFPost combustionLarge-scale capture from flue gases, fossil power generation, waste incineration, cement9
Chilled ammonia processBaker HughesPost combustionFossil fuel-based power plants, waste to energy, biomass, cement, refineries, petrochemical complexes7
Compact carbon captureBaker HughesPost combustionFossil fuel-based power plants, waste to energy, biomass, cement, refineries, petrochemical complexes5
Mixed-salt processBaker HughesPost combustionWaste to energy, biomass, industrial (cement), oil and gas (SMR, boilers)5
CapsolEoPCapsol TechnologiesPost combustionFull scale capture, cement, biomass, waste to energy, lime, pulp and paper, power generation, process industries.7-8
CapsolGoCapsol TechnologiesPost combustionMobile demonstration unit for cement, biomass, waste to energy, lime7-8
CapsolGTCapsol TechnologiesPost combustionGas turbines, low-carbon power plants6
CycloneCCCarbon CleanPost combustionEnergy, industrial power, gas turbines, industrial emitters (cement, steel, waste to energy), maritime7-9
Amine capture plantChina EnergyPost combustionLarge scale capture, power generation7
CO₂ capture absorbentCNPCPost combustionPower generation, cement, steel, petrochemicals9
CO2SORBCO2CRCPost combustion,Pre combustionHigh pressure (50 bar) capture from oil and gas, hydrogen operations4-5
HyCapsCO2CRCPost combustionHybrid capture solution, power, industry, oil and gas, hard-to-abate sectors, small footprint operations (OCCS, remote/offshore platform)6-7

  1. Technology readiness levels (TRL); a method for consistently estimating the maturity of technologies during the acquisition phase of a project on scale of 1-9 (9 is the most mature). Levels are determined in a technology readiness assessment (TRA) examining technology concepts, requirements, and demonstrated capabilities. ↩︎

  2. Flue gas; a gas exiting to the atmosphere via a flue, a pipe/channel for conveying exhaust gases, as from a fireplace, oven, furnace, boiler or steam generator, often referring to the exhaust gas from a power plant. ↩︎

  3. Absorption; the process in which atoms, molecules, or ions enter the bulk phase of a material, such as a liquid or solid. This differs from adsorption, where particles adhere to the surface of a material. ↩︎

  4. Pressure swing adsorption (PSA); a method used to separate gases from a mixture based on their molecular characteristics and how strongly they adhere to an adsorbent material under pressure. This process operates at near-ambient temperatures and is commonly used to produce high-purity nitrogen or oxygen from air. ↩︎

Bibliography

  • Kearns2025 “State of the Art: CCS Technologies 2025”, Global CCS Insititute

    Global CCS Institute compendium documenting over 70 commercially available and emerging carbon capture technologies, including post-combustion amine scrubbing, oxyfuel combustion, chemical looping, pre-combustion separation, and direct air capture, with performance data, cost ranges, and commercial readiness indicators for each. The report provides the most comprehensive single-volume technology survey currently available, useful both for benchmarking capture options at specific industrial facilities and for understanding where the technology frontier is — and where the gap between claimed performance and commercial reality remains wide.

  • Danish Energy Agency2024 “Technology Data for Carbon Capture, Transport and Storage”, Danish Energy Agency & Energinet

    Technology catalogue published by the Danish Energy Agency and Energinet documenting commercially available and emerging solutions for carbon capture, CO₂ transport, and geological storage. The catalogue covers post-combustion capture, oxyfuel, pre-combustion, and direct air capture across thermal and industrial applications, alongside pipeline, ship, and rail transport options and a range of storage configurations. Its primary value is the cost and performance data it provides for benchmarking technology choices; the kind of reference that turns “we’ll figure out the details later” into a fundable project proposal.