For Low-Carbon Fuels, Sustainability Is the Product—and Quality Is the Value

Key Takeaways

• CORSIA, the program intended to address international aviation emissions, is currently the world’s largest international compliance carbon market, with approximately 200 million tonnes of eligible emissions units (EEUs) expected to be retired for Phase 1 (2024-2026) compliance. 
• Airlines have already begun retiring significant volumes of credits (clean cookstoves and jurisdictional REDD+) toward their Phase 1 obligations ahead of the January 2028 compliance deadline, signaling that the industry is treating CORSIA as a binding policy mandate.
• In addition to the four already approved, a record 25 carbon standards have applied for eligibility to supply credits under Phase 2 (2027–2035), pointing to a diversifying pipeline of credits.
• Legal enforcement of CORSIA at the national level remains uneven. A handful of jurisdictions, including the EU, Japan, Brazil, New Zealand, and Canada, have established compliance regimes, but it is unclear whether other major aviation markets will implement domestic enforcement requirements by 2027.
• As CORSIA matures alongside other compliance and voluntary frameworks, strategic engagement increasingly depends on understanding where eligibility overlaps and where the most value can be found.

Introduction to CORSIA 

The Carbon Offsetting and Reduction Scheme for International Aviation (CORSIA) was established and is managed by the International Civil Aviation Organization (ICAO)—a specialized agency of the UN—and provides a compliance mechanism to reduce emissions from international aviation that do not fall within a single country’s contributions to the Paris Agreement. For years, CORSIA generated more commentary than activity—airlines weren’t required to offset a single tonne of CO₂ emissions (tCO₂) during the pilot phase (2021–2023). That is changing; in early 2026, Singapore Airlines and Japan Airlines retired significant volumes of carbon credits against their Phase 1 (2024–2026) obligations. Increasing authorization announcements showcase the eligible supply steadily entering the market, and 25 carbon standards have applied for Phase 2 (2027–2035) eligibility. As CORSIA becomes an active compliance market, this article explains how the program works, what is driving the current trends, and what to watch as Phase 1 draws to a close.

Who is Covered by CORSIA Phase 1 and Phase 2?

Because emissions from international aviation are not tied to any individual nation, the International Civil Aviation Organization (ICAO) adopted CORSIA in 2016 to complement the Paris Agreement framework and address these emissions. CORSIA applies to international airlines operating flights registered between participating countries. 

• During Phase 1, offsetting obligations apply only to routes between the 130 countries that have voluntarily opted in. 
• From Phase 2, participation becomes mandatory for all 193 ICAO member states, except for those below the aviation activity threshold or classified as Least Developed Countries, Small Island Developing States,  or Landlocked Developing Countries—although they can voluntarily participate. 

Several major aviation markets, including China, that are not participating in Phase 1 will be required to do so from 2027. 

Offsetting Obligations

Airlines are required to offset the portion of their emissions that exceeds the program’s baseline on routes subject to offsetting. The key input is the annual Sectoral Growth Factor (SGF), which reflects how much annual emissions on covered routes have grown above the baseline (set at 85% of 2019 emissions). In simple terms, each airline's offsetting obligation is calculated by multiplying its CORSIA-regulated emissions by the SGF.

For example, an airline that emits 1 million tCO₂ on covered routes in a year when the SGF is 10%, would have an offsetting obligation of 100,000 tCO₂. An airline that emits 500,000 tCO₂ in the same year would have an obligation of 50,000 tCO₂. The actual 2024 SGF was 15.4%, exceeding the baseline and triggering offsetting obligations for the first time since the COVID-induced reduction in international aviation activity. 

Beginning in 2033, CORSIA’s offsetting formula combined the SGF with an individual component that accounts for each airline's own emissions growth. The individual weighting starts at 15% in 2033 (with an SGF weighting of 85%) and rises to 45% by 2035 (SGF 55%). This progressively ties each airline’s obligations to its own emissions trajectory rather than sector-wide trends alone.

Airlines can also reduce their obligations by reporting the use of CORSIA Eligible Fuel (CEF). In order to qualify as CEF, Sustainable Aviation Fuel (SAF) must meet ICAO’s certification criteria. Offsetting remains a lower-cost option than sustainable fuel procurement, and CORSIA obligations are currently not influential drivers of CEF/SAF uptake compared to supply mandates, such as ReFuelEU Aviation. However, these dynamics will evolve as CORSIA matures and SAF prices continue to fall. 

CORSIA Eligible Carbon Credits: Phase 1 and Phase 2 

To determine the eligibility of carbon crediting standards and credits issued under those standards, ICAO's Technical Advisory Body (TAB) reviews applications and recommends approval to the ICAO Council, subject to restrictions on methodologies, vintages, and more granular project elements. Currently, no standard is approved without exclusions. Credits eligible for use under CORSIA are known as Eligible Emissions Units (EEUs).

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TAB broadly excludes some project types across standards, including large-scale grid-connected renewable energy projects and most project-level REDD+ activities. The exclusions reflect TAB's assessments of baselines, safeguards, and quantification gaps. However, these assessments are not static; ICAO updates its determinations as the evidence base improves. For example, in 2025, TAB approved certain direct air capture (DAC) and biochar pathways for the first time.

A record 25 carbon standards—certifying projects from emissions avoidance to engineered carbon dioxide removal (CDR)—have applied for Phase 2 eligibility in the 2026 assessment cycle, reflecting the scale of the opportunity. The International Air Transportation Association (IATA) projected a demand of 170–236 million EEUs for Phase 1 alone; developers are eager to serve this growing market. Assessment results are expected in October 2026.

Article 6 and Corresponding Adjustments

The biggest bottleneck for eligible supply has been requirements relating to Article 6.2 of the Paris Agreement. CORSIA requires that EEUs carry a host country Letter of Authorization (LoA) confirming that the host country will not count the underlying mitigation toward its Nationally Determined Contribution (NDC). This prevents double counting between CORSIA and national emission inventories, but it also means eligible supply depends on host country authorization, not just meeting methodological requirements. Authorized credits are called Internationally Transferred Mitigation Outcomes (ITMOs). 

To manage the risk that a host country fails to apply the promised corresponding adjustment, projects must secure legally enforceable insurance policies that either provide replacement EEUs or funds to secure them. Several providers have been approved to insure EEUs registered by Gold Standard and Verra. 

Insurance requirements do not apply when the host country has already confirmed the corresponding adjustments in its mandatory Paris Agreement reporting. For example, in March 2026, Madagascar submitted a Biennial Transparency Report (BTR) and annual information report that reflect the application of corresponding adjustments to CORSIA-eligible clean cookstoves credits listed on the Verra registry. According to Verra, BTR accounting is the “highest level of assurance” that ITMOs will not be double counted. 

The Enforcement Challenge

With the authorization bottleneck loosening, market attention is turning to demand. Critically, ICAO has no direct enforcement power; for CORSIA to work, participating countries must pass laws requiring airlines to comply with its requirements. Under CORSIA rules, airlines must retire their Phase 1 EEUs by January 2028, but most are not yet subject to legal sanctions for failing to comply. Where regulations do exist, it remains unclear whether penalties will be stringent enough to matter, or whether they will be enforced at all.

Where legal enforcement of offsetting requirements does exist, it varies by design. For example, in Brazil, failure to comply attracts a penalty of BRL 50/tCO₂ (US$10/tCO₂) and an administrative fine. Meanwhile, the Canadian Aviation Regulations impose administrative fines capped at CAD 25,000 (US$18,000) per infraction, but there is no specific fine for each tCO₂ not offset. However, the absence of a statutory penalty framework does not necessarily mean compliance will not be enforced. For example, New Zealand manages CORSIA participation through an administrative Memorandum of Understanding with Air New Zealand, rather than a dedicated legal regime (though this will change from 2027). Similar informal arrangements may be more common than the legislative record suggests.

According to 2024 data, US-based airlines account for around 15% of CORSIA-covered emissions. However, there is no indication that the federal government will implement CORSIA penalties under the current administration. It is unclear how non-compliance by a major economy will impact market confidence or enforcement by other governments, but uncertainty about US participation in multilateral climate programs is not new. 

What to Watch

• Global enforcement: As Phase 2 approaches, the prospects for CORSIA enforcement in key aviation markets will become clearer. China, which has not participated in the voluntary phase and has raised objections to CORSIA’s design on grounds of fairness, presents an uncertain picture for domestic transposition. The UK government has consulted on a draft legal amendment that would penalise non-compliance for UK airlines at £100/tCO₂ (US$130/tCO₂), but has not published updates since February 2025. 

• EU Emissions Trading Scheme (ETS) update: In July 2026, the European Commission proposed to expand the ETS to address emissions from flights departing the European Economic Area (EEA) to destinations within 5,000 km. To avoid double charging emissions also regulated under CORSIA, the Commission proposed to deduct CORSIA costs from airlines’ ETS obligations. While the Commission flagged concern about the stringency of CORSIA eligibility criteria, the proposed rules would not impact demand for Phase 1 EEUs. Still, it is worth watching for future restrictions on which credits EU airlines can use for CORSIA, whether in Phase 1 or 2. 

• Supply financing vehicles: The LEAF Coalition—which purchases credits verified under the CORSIA-eligible ART TREES standard—has signed over US$1.5 billion worth of purchase agreements with host countries. The Forest Carbon Partnership Facility (FCPF) and BioCarbon Fund Initiative for Sustainable Forest Landscapes (ISFL), both CORSIA-approved for Phase 1 in early 2026, have built jurisdictional REDD+ pipelines across dozens of countries. As projects mature, it will be worth watching how issued credits are marketed across compliance and voluntary channels.

Strategic Considerations

Avoided emissions credits dominate early CORSIA supply—and consequently demand—principally from avoided deforestation and clean cooking projects. As there is no regulatory premium for higher-cost CDR, this is not surprising. But as the market matures and supply diversifies, airlines are likely to begin differentiating on geography, co-benefits, and environmental performance. Corporate interest is growing in projects that abate non-CO₂ superpollutants, due to their outsized near-term climate impact. As many of these projects are based in countries actively issuing LoAs, this may soon translate into a supply of superpollutant EEUs. Some airlines are reluctant to procure aggressively now, anticipating the upcoming availability of higher-quality credits.

Credits that hold value across multiple frameworks could carry a strategic premium. A credit also eligible for Singapore's carbon tax, Switzerland's CO₂ Act, or SBTi claims may offer more durable demand than one tied to a single use case. While specific requirements vary significantly, we are beginning to see convergence around broad principles, such as the need for Article 6 authorization for credits used in compliance markets tied to NDCs. Procurement and project development strategies could begin to favour credits that confer wider market optionality. 

The precondition for all of this is policy stability. Longer-term offtake agreements, portfolio strategies, and meaningful investment in project development depend on confidence that CORSIA rules will hold. Efforts to soften emissions regulations in response to energy price shocks are now testing this confidence, from proposed changes to soften the EU ETS to Singapore's deferral of its SAF levy. Tracking price signals, enforcement developments, and authorization trends will be essential for identifying firm demand and where the opportunities lie.

Conclusion

Effective engagement with CORSIA requires more than developing quality projects. It means understanding methodological eligibility requirements, navigating Article 6.2 authorization processes, tracking a network of overlapping national regulations, and staying ahead of a rapidly evolving market landscape. Relae (formerly Carbon Direct) brings together policy, market, and scientific expertise to help clients on all of these fronts.

Frequently Asked Questions

Which carbon credits can airlines use for CORSIA compliance?

CORSIA Eligible Emissions Units (EEUs) must be issued by crediting standards approved by ICAO's Technical Advisory Body. Every approved standard currently has exclusions on certain methodologies and project types, so eligibility is granular rather than blanket. EEUs must also have a host country Letter of Authorization confirming a corresponding adjustment under Article 6.2 of the Paris Agreement.

Is CORSIA actually enforceable?

In all phases, CORSIA obligations are legally binding when a country writes them into domestic law. Countries participating in Phase 1 are expected to do this, but not all have, and enforcement remains uncertain in several key aviation markets (e.g., the United States). Even where enforcement exists, penalty regimes vary significantly in stringency and design. 

How does the July 2026 EU ETS proposal affect CORSIA?

The European Commission's proposal to expand ETS coverage to more flights does not reduce demand for CORSIA credits. While it would lead to overlap between flights covered under CORSIA and the ETS, as proposed, airlines could have CORSIA costs effectively deducted from their ETS allowance obligations. However, the Commission has signalled continued scrutiny of CORSIA's effectiveness, which could shape future limits on the credits EU airlines are allowed to use.

Key Takeaways

• Cement is the key ingredient in concrete and is responsible for more than 80% of concrete’s emissions. Cement’s GHG emissions are the primary technical challenge in decarbonizing an industry that accounts for over 8% of annual global greenhouse gas emissions. 
• The global market for low-carbon concrete is constrained by the slow deployment of breakthrough technologies, yet demand from major buyers such as hyperscalers, developers, and infrastructure investors is accelerating. This mismatch between demand and supply is creating a new market mechanism: environmental attribute certificates (EACs) for building materials. 
• EACs represent the climate benefits of low-carbon materials and can be traded separately from the physical product. These certificates, when backed by robust technical diligence, offer a near-term funding mechanism to accelerate decarbonization across the cement and concrete supply chain.

The AI Boom Meets an Industrial Reality

As the market for AI infrastructure expands, data center construction is accelerating—and with it, demand for concrete, one of the most carbon-intensive materials in the built environment. For both builders and material suppliers, the embodied carbon of cement and concrete is under a microscope due to its significant climate impact. Hyperscalers, like Microsoft and Meta, have 2030 targets that far outpace the concrete industry’s readiness to provide near-term low-emissions materials. 

This piece explores why cement and concrete decarbonization is so challenging and how credible, high-quality EACs can help bridge the ambition gap. 

Cement and Concrete: An Important Distinction 

These two terms are often used interchangeably, but they are not the same—and the distinction matters for decarbonization strategy. Cement is the reactive ingredient in concrete, acting like an egg in a cake batter. Concrete itself is a blend of cement, aggregates (like sand and gravel), and water (the batter overall). While concrete is widely used and often seen as the emissions culprit, it is actually cement—just 15% of the mix by volume—that is responsible for more than 80% of concrete’s lifecycle carbon emissions. 

Why Is Concrete so Hard to Decarbonize?

Concrete is the second most-used material on Earth after water. Despite emitting only ~0.13 kg of CO₂ per kilogram, its sheer scale gives it an outsized climate impact—contributing around 8% of global CO₂ emissions. Yet decarbonization has been slow, held back by technical, structural, and accounting challenges across a complex supply chain. 

The Supply Chain Behind Concrete’s Carbon Footprint

To understand why decarbonizing concrete is so difficult, it’s essential to understand how it’s made and what drives its emissions. Three factors explain much of the difficulty: 

• Cement is made in an emissions-intensive process. Cement is produced by heating limestone to extreme temperatures (~1450 °C) to create clinker, a reactive material that binds sand and aggregates into concrete. This energy and carbon-intensive process is where the majority of the emissions occur. 
• Concrete is made to order. Concrete is a blend of cement, aggregate, and water. It is made to order at local batch plants and poured on-site or used in precast molds, with mix designs tailored to specific compressive strength and durability requirements. 
• The supply chain is decentralized and performance-driven. Because concrete mixtures must meet application-specific performance requirements, low-carbon innovations are limited to those that do not decrease product quality and performance at any point in the value chain. 

This layered supply chain, from kiln to batch plant to job site, means decarbonization strategies must be compatible with local infrastructure, material availability, and performance needs. There is no single lever to pull. 

Clinker Is the Main Emissions Driver

Clinker production alone accounts for the majority of cement’s emissions, due to the chemical process (calcination) that converts limestone into lime and releases CO₂. Not only does calcination directly produce CO₂, but the combustion of fossil fuels used to heat the kiln adds to the emissions of the overall process. 

Low-Carbon Concrete Technology: Invented, Not Yet Deployed

Six promising technologies are in development to address cement and concrete emissions, including: 

1. Carbon Capture and Storage (CCS): CCS can be retrofitted to capture the fuel and process emissions from clinker production, delivering nearly complete decarbonization of the cement manufacturing process. CCS can be combined with electrification or fuel switching to deliver deeper decarbonization
2. Supplementary cementitous materials (SCMs): SCMs offer two key benefits: they can partially replace conventional cement in concrete mixtures, and certain SCMs react with CO₂ from industrial or atmospheric sources to enable durable carbon storage.
3. Electrification: Electrifying kiln heating systems can reduce emissions from fossil fuel combustion during clinker production. When powered by low-carbon electricity, this approach lowers the carbon intensity of cement manufacturing while maintaining the high temperatures required for clinker formation.
4. Fuel Switching: Natural gas, biomass, and renewable natural gas are low carbon-intensity fuels that can replace the higher-emitting coal and refuse derived fuel that usually drive the clinker production process. Unlike electrification, some alternative fuels can be used as 'drop-in' replacements in existing equipment. 
5. Synthetic and recycled aggregates: Alternatives to traditional gravel and crushed stone, made from waste materials or industrial byproducts, which can lower emissions and reduce resource extraction.
6. CO₂ curing: A process where concrete is cured with captured CO₂ instead of air, helping lock carbon into the material and partially offsetting upstream process emissions.

Each solution faces deployment challenges, from raw material availability and geographic constraints to cost, performance certification, and integration with legacy infrastructure. 

Few decarbonization strategies have reached industrial scale today, but these strategies are being piloted and demonstrated, and given targeted support, some have the potential to significantly decarbonize the future of the industry. 

The Gap Between Targets and Real Market Capacity

Hyperscalers, utilities, real estate developers, and other large organizations with ambitious scope 3 targets are looking to significantly reduce the embodied carbon throughout their supply chain. However, the current supply of deeply decarbonized cement and concrete is insufficient to support these targets through direct procurement alone; the low-carbon material simply does not exist at the required volume or in the right geographies. In some cases, pilot plants produce too little material to meet large-scale demand, while projects capable of larger volumes may not yet be located in regions where interested buyers are concentrated.

In this context, EACs offer a flexible mechanism to fund innovation and bridge the gap. By unbundling climate attributes from physical materials, near-term obstacles, such as geographic availability, can be overcome while channeling capital toward scalable and catalytic solutions. 

When backed by rigorous life cycle assessments and high-quality, transparent traceability standards, EACs can provide the financial bridge for truly innovative suppliers to invest in the capital solutions required to decarbonize cement and concrete. EACs can serve a catalytic role to support scalable strategies and help ensure that first-of-a-kind facilities are built, and direct procurement of low-carbon concrete is increasingly feasible in the years to come.

How Environmental Attribute Certificates Work in Cement and Concrete Markets

EACs translate emissions reductions from low-carbon cement and concrete production into climate attributes that can be purchased separately from the physical material. Instead of requiring buyers to procure low-carbon concrete directly from a specific supplier site, EACs allow the climate benefit associated with that production to be transacted independently through a book and claim model.

In practice, a producer implements a verified emissions reduction intervention, such as reducing clinker content through supplementary cementitious materials, installing carbon capture at a kiln, or deploying alternative cement chemistries. The resulting emissions reductions are quantified through life cycle assessment and product-level disclosures such as Environmental Product Declarations. Verified reductions can then be converted into certificates representing the climate benefit of that lower-emissions production.

Buyers can purchase these certificates to support the deployment of low-carbon cement and concrete technologies while making progress toward embodied carbon reduction targets. In this way, EACs provide an early demand signal and a revenue stream that can help producers finance capital-intensive decarbonization investments across the cement and concrete supply chain.

What This Means for Suppliers and Buyers

Whether you are procuring concrete or producing it, EACs are only one part of a broader decarbonization strategy. Navigating this space requires decisions at the intersection of technical feasibility, GHG accounting, and capital strategy. Key considerations include: 

• GHG accounting and reportability: Life cycle assessments, Environmental Product Declarations, and other product-level attributes must be tracked and transacted with high integrity. Buyers should report their EAC activities responsibly, especially in the current absence of formal standards and guidance.
• Procurement alignment: EAC buyers must ensure purchased certificates reflect equivalent performance grade materials to what was directly procured for structural applications.
• Monetization pathways: Book-and-claim EAC models offer producers a way to fund capital-intensive decarbonization upgrades while giving buyers a credible way to meet interim scope 3 goals. EAC transactions can take many forms and should be designed thoughtfully to minimize risks such as double counting.

Frequently Asked Questions

What is low-carbon cement, and how does it work?‍

Low-carbon cement reduces emissions by replacing traditional clinker with supplementary cementitious materials (SCMs), switching to cleaner fuels, electrifying kilns, or capturing CO₂ at the point of production. Because cement is responsible for more than 80% of concrete's lifecycle emissions, interventions targeting clinker production deliver the greatest climate impact. Most approaches are technically proven at smaller scales but have not yet reached the industrial volumes needed to meet mainstream demand.

How do EACs for cement and concrete compare to direct procurement of low-carbon materials?‍

Direct procurement means physically buying low-carbon concrete from a supplier, which requires that product to exist at conditions that often can not be met today. EACs decouple the climate benefit from the physical material, allowing buyers to fund verified emissions reductions across the supply chain even when direct sourcing isn't feasible. Both approaches can count toward scope 3 targets, but EACs offer more flexibility in the near term while the low-carbon materials market matures.‍

Is low-carbon concrete proven and available at scale today?‍

The core technologies for decarbonizing cement and concrete are technically demonstrated, but most have not reached commercial scale. Supply is geographically concentrated and insufficient to meet the volume demands of large buyers like hyperscalers, utilities, and real estate developers. This gap between technical readiness and market availability is precisely what makes EACs a valuable bridging mechanism right now.

What should a company look for when evaluating EACs for cement and concrete?‍

‍High-quality EACs should be backed by rigorous life cycle assessments and transparent traceability standards that tie the certificate to a specific, verifiable emissions reduction intervention. Buyers should also confirm that the certificates represent materials with equivalent performance grades to what they are directly procuring for structural applications, and that accounting practices minimize risks like double counting. Working with a technically credible advisor to evaluate EAC quality is essential, since the market currently lacks formal standards and guidance.

How Relae Can Help Decarbonize Cement and Concrete 

Decarbonizing cement and concrete is both a technical and a strategic challenge. Relae brings integrated expertise across geochemistry, life cycle assessment, carbon accounting, and industrial decarbonization strategy to help buyers and producers navigate the complex path to decarbonization. Relae works directly with producers developing low-carbon cement and concrete technologies and with global buyers seeking credible pathways to address embodied emissions in construction. Our team combines industrial decarbonization engineering, geochemical expertise, and carbon accounting to evaluate emerging EAC frameworks and ensure they deliver real climate impact.

• EAC advisory for buyers: Relae helps buyers procure high-quality EACs through criteria development and in-depth technical diligence of EAC offerings across a range of low-carbon commodities, supporting purchased certificates that reflect genuine, verifiable climate impact. 
• EAC advisory for suppliers: Relae helps producers design high-quality EAC interventions and assess potential EAC claims throughout the supply chain, informed by technical assessment, book-and-claim systems, and market landscaping.
• For both: Relae’s levelized cost of carbon abatement tooling provides custom modeling to assess trade-offs across cement and concrete decarbonization pathways, helping ensure that every dollar of climate spend goes further.

Key Takeaways

1. The decision to fund a project is determined by a holistic review of project development maturity. This applies across capital-intensive projects, including low-carbon power generation, carbon capture and storage (CCS) solutions, sustainable aviation fuel (SAF), and broader transition infrastructure build-out. Both technical and commercial workstreams must be developed in parallel to avoid project failure. 
2. Early scope decisions, such as site selection, core technology selection, and nameplate capacity, are cheap to make but become exponentially disruptive and costly to reverse. 
3. Independent challenge and verification is tangible evidence of a disciplined, well-managed capital development process. 

Bridging the Gap from Announcement to Delivery

Among project developers, a perception often persists: seeking external review signals a project in distress. In capital budgeting discussions, subjecting engineering scope and commercial assumptions to third-party interrogation can be misconstrued as a vote of no confidence in the primary delivery team.

In reality, the reverse is true. Across complex infrastructure, independent challenge is the disciplined stage-gate practice that protects capital by reconciling technical reality with commercial terms before designs are locked.

Independent Challenge Is a Sign of Strength, Not Doubt 

Across capital projects, and in particular within emerging low-carbon industrial infrastructure, the gap between announced projects and delivered assets remains stark. Data from the Mission Possible Partnership’s Global Project Tracker reveals that fewer than 17% of announced commercial-scale clean industrial facilities worldwide have reached Final Investment Decision (FID) or commercial operations, leaving more than 800 major decarbonization projects stalled in front-end development.

The causes of developmental paralysis are multifaceted. While macroeconomic interest rate shifts and global supply chain disruptions sit largely outside a developer's control, project definition and developmental discipline remain entirely manageable. Even amid external volatility, a project designed with resilience will have a far greater likelihood of success.

Independent review and assurance directly strengthen a project’s chance of success and overall value. Large global project delivery organizations have applied this discipline for decades by deploying independent teams to evaluate project readiness at every stage gate. For teams lacking a dedicated internal oversight organization, or those deploying first-of-a-kind facilities, third-party independent review provides the necessary rigor to facilitate project success.

Relae’s (formerly Carbon Direct) work with Stockholm Exergi is a clear example: independent assurance helped build funder and regulator confidence in a first-of-a-kind carbon removal facility with no direct precedent to benchmark against.

Why Projects Stall Between Announcement and FID 

Low-carbon infrastructure and net-zero industrial projects carry unique risks compared to the repeat delivery of established designs. Exciting new developments run a higher risk of falling victim to optimism bias or compressing development timelines to meet public announcement milestones.

It is a natural human tendency for project champions to focus on the upside during early development. However, early momentum must be balanced with processes that reintroduce industrial lessons, supply-chain realities, and operational resilience.

Front-End Loading (FEL) is a well-evidenced approach for improving capital project outcomes. Decades of benchmarking by Independent Project Analysis (IPA) show that approximately two-thirds of industrial megaprojects suffer capital cost overruns or schedule slippage of 25% or more, or encounter severe operational problems lasting more than two years post-startup. This pattern is repeating in low-carbon infrastructure: IPA’s analysis of 12 completed low-carbon projects found average cost escalation of 31% and schedule slip of almost 50%. Rigorous front-end definition remains the single strongest predictor of whether a project will achieve its cost and schedule targets. 

As highlighted in the CDR 2.0: Five Pillars of Successful Project Deployment and Delivery report published by Relae, projects falter when developers push ahead without stress-testing the full delivery framework. Stage gate reviews are the mechanisms that evaluate the total project concept and underlying business case. They are most effective when executed as independent cold-eye evaluations prior to each funding gate, identifying and mitigating vulnerabilities long before final investment decisions are reached. 

What Funders Need to See at Each Gate 

Different stages of project development rely on distinct capital sources, each requiring specific proof points before deploying funds.

Before FEED Funding: Justifying the Engineering Spend

Front-End Engineering Design (FEED) is a major financial commitment, typically costing between 2% and 4% of total project capital cost. The funders backing this stage are usually the developer’s own balance sheet equity, strategic partners, or public grant programs. Before allocating millions of dollars to detailed engineering, these funders need confidence on the fundamentals:

• A technically sound process concept, confirmed utility balances, and an energy integration scheme that fits the site.
• Secured site control, clear zoning pathways, and no environmental fatal flaws that could derail permitting.
• Documented availability of required feedstocks, water and power, paired with demonstrable interest from target off-takers.

Before FID: Proving Bankability and Commercial Closure

As a project approaches FID, the funding audience shifts to conservative commercial lenders, infrastructure funds, and binding offtake counterparties. These capital providers are not underwriting strategic vision; they are underwriting long-term operational cash flows and debt service. Depending on the project and financing structure, capital providers may require:

• A high-confidence capital cost estimate (AACE Class 2 or Class 3) backed by frozen Piping and Instrumentation Diagrams (P&IDs), firm equipment quotes, and a realistic execution schedule with clear critical paths.
• Bankable engineering, procurement, and construction (EPC) structures that clearly allocate risk, include performance guarantees and enforceable liquidated damages.
• Fully executed, binding offtake and feedstock agreements, along with non-appealable permits and completed utility interconnection agreements, with remaining conditions clearly understood.
• An objective, third-party challenge review that assesses operational viability and distinguishes an executable engineering plan from an aspirational concept.

Commercial and Technical Co-Development: The Stage-Gate Method in Practice

A project rarely fails because of an isolated mechanical issue or a purely commercial misstep; failure happens when technical decisions and commercial terms are negotiated in silos and decisions are made without understanding of the wider implications. 

We see this disconnect play out in several ways, including: 

• Sizing capacity before testing market demand: An engineering team may size a facility to maximize thermodynamic efficiency and economies of scale, only for the commercial team to discover buyers will only commit to half that volume. The developer is left with an oversized, unbankable design requiring fundamental rework. 
• Setting product specifications before negotiating offtake: Process engineers frequently design systems around standard vendor packages. However, when downstream transport, processing, or storage networks enforce strict purity standards, the facility faces costly equipment redesigns. This issue has materialized directly within European CCS networks. Open-access offshore storage operators, such as Norway's Northern Lights project, established strict cross-border CO₂ specifications requiring tighter moisture and impurity thresholds than originally designed for. 
• Locking Electrical Loads Prior to Interconnection Verification: As detailed in Relae’s analysis of physical infrastructure bottlenecks, scale is rarely constrained by capital availability; it is dictated by electrical transmission queues, substation headroom, and 24/7 firm power availability. Freezing electrical demand before verifying utility interconnection timelines risks stranding engineering work on an asset that cannot connect to the grid. 

How Relae Stress Tests Projects at Each Gate 

Independent reviews at each stage-gate improve success rates by stress-testing assumptions before presenting to lenders, infrastructure investors, or corporate buyers. Relae reviews projects across five categories using the TECOP framework:

• Technical: Verifying technology readiness levels (TRL), mass and energy balances, plot plan constructability, and operational availability under real-world conditions.
• Economic: Capex benchmarking, operating contingency adequacy, utility tariff sensitivities, and financial model cash-flow resilience.
• Commercial: Offtake agreement structures, feedstock contracts, contracting boundaries, EPC contract structures, and counterparty creditworthiness.
• Organizational: Owner's team capabilities, internal stage-gate governance, contractor oversight mechanisms, and execution capabilities. 
• Political: Statutory permitting status, regulatory durability, carbon market policy exposure, and local community social license.

The TECOP framework is relevant for evaluating delivery risk across all project types, see more in Relae’s Criteria for High-Quality Carbon Dioxide Removal, Delivery Risk Appendix.

What makes this approach effective is sitting on both sides of the table. Having completed over 250 deep-dive technology reviews, 900+ project evaluations, and advised on more than $6 billion in industrial project finance, Relae has extensive experience evaluating the considerations important to institutional funders and buyers.

The Value of Early Independent Project AssuranceIncorporating independent review should be standard practice for modern infrastructure delivery. Because funders will perform their own rigorous diligence regardless, conducting an independent evaluation early enables developers to address vulnerabilities proactively and present a more resilient business case.

Commissioning an independent team for a cold-eye review during early project formation can be a  cost-effective way to identify potential risks before they become expensive to address. Catching an unworkable process assumption, an oversized capacity plan, or a misaligned commercial interface during pre-FEED costs a tiny fraction of what it takes to fix those issues during construction

Ultimately, independent challenge is not an admission of doubt, but the disciplined stage-gate practice that protects capital by reconciling technical reality with commercial terms before designs are locked, signaling to partners, and your future funders that your project is built to deliver. 

To dive deeper into the frameworks that support successful projects, read Relae's white paper: CDR 2.0: Five Pillars of Successful Project Deployment and Delivery and take a look at project assurance in action through our Stockholm Exergi Case Study.

Frequently Asked Questions

What is independent project assurance?

Independent project assurance is a structured review of a capital project by a team that sits outside the project’s delivery organization. Reviewers test the engineering scope, cost estimate, schedule, commercial agreements and permitting position against what funders will require at the next stage gate. The developer receives a clear list of gaps, risks and proposed mitigations prior to presenting the project to lenders, investors or buyers.

When should a developer commission an independent project review?

Periodically throughout the project development process - at a minimum before each major funding gate, but smaller reviews are also beneficial at earlier stages when key concept and technology decisions are being made. A review before Front-End Engineering Design (FEED) tests whether the process concept, site and supply of feedstock, water and power justify the engineering spend. A review before Final Investment Decision (FID) tests whether the cost estimate, EPC structure and binding agreements will satisfy lenders. Site, technology and capacity decisions are cheap to change in pre-FEED and expensive to reverse once detailed engineering starts.

What does an independent project review assess?

Relae structures its reviews around the TECOP framework, which covers five risk areas: technical (technology readiness, mass and energy balances, constructability), economic (capex benchmarking, contingency, financial model resilience), commercial (offtake, feedstock and EPC contracts), organizational (owner’s team capability and stage-gate governance) and political (permitting, regulatory durability and social license). Reviewers also check that technical and commercial decisions are aligned, because projects often fail where the two are developed in silos.

How does an independent project review differ from lender due diligence?

An independent project review applies a holistic approach identifying not only gaps, but also opportunities to add value and strengthen the business case. Lender and investor due diligence is often purely looking at risks and gaps, prior to committing capital. Lender diligence protects the funder and reports its findings at a point when changes are costly and can delay financial close. A developer-commissioned review takes place earlier, so the project team can fix weaknesses in scope, cost or contracts before funders see them.

Key Takeaways

• High-quality carbon dioxide removal (CDR) projects require robust project management and oversight to deliver credits on time and at the promised volume; delivery risk is a distinct concern that quality standards alone don't catch.
• The sixth edition of the Criteria for High-Quality Carbon Dioxide Removal is the first to provide an approach to evaluating both credit quality and delivery risk, adding a new delivery risk appendix built around the TECOP framework: technical, economic, commercial, organizational, and political risk.
• The 2026 Criteria provides a framework for developers, investors, and buyers to evaluate both project quality and delivery risk.
• This year's update draws on 170 new diligence reports from 2025 and the input of more than 60 subject matter experts, building on a foundation of six years of lessons from professional diligence across hundreds of real-world CDR projects.

The Criteria Create a Shared Standard for Credit Quality

Relae (formerly Carbon Direct) first launched the Criteria for High-Quality Carbon Dioxide Removal (the Criteria) in collaboration with Microsoft in 2021 to help rapidly and justly scale the development of high-quality carbon dioxide removal (CDR) credits. The market didn't yet have a shared definition of what "high-quality" meant, so we laid out transparent, science-based benchmarks that gave developers, investors, and buyers a common foundation to work from. Every year since, we have gone back and sharpened those benchmarks so that they keep pace with the quickly evolving industry.

But a shared definition of quality doesn't guarantee the delivery of credits as planned. The 2026 edition is the first to tackle that gap directly, pairing the Criteria's quality benchmarks with a new framework for evaluating delivery risk.

The Six Principles of High-Quality Carbon Removal

The Criteria defines six science-based principles that apply across engineered, hybrid, and nature-based CDR approaches:

• Social harms, benefits, and environmental justice: The extent to which the project prevents new social harms to people and communities, reduces existing harms, and provides meaningful benefits distribution.
• Environmental harms and benefits: The extent to which the project minimizes and mitigates environmental harms, as well as provides environmental benefits.
• Additionality and baselines: The evidence that the project’s carbon removal would not have occurred without carbon finance.
• Measurement, monitoring, reporting, and verification (MMRV): The ability to accurately quantify carbon removal in a repeatable and verifiable way, and to develop a plan for long-term monitoring of the project.
• Durability: The likelihood that removed carbon remains stored over time, with mechanisms in place to mitigate reversal risk.
• Leakage: The extent to which project activities cause increased emissions elsewhere.

These principles provide a consistent foundation for carbon removal procurement, evaluation, and project benchmarking.

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Supporting the Delivery of High-Quality CDR Credits

"Projects must work better operationally and be more commercial. Quality and delivery risk shape a project's risk profile at every point in its life, and this edition of the Criteria is the first to give buyers a way to judge both at once." Dr. Julio Friedmann, Chief Scientist, Relae

Designing projects to meet high-quality CDR criteria is only part of the challenge. Effective project planning, management, and execution are also essential to ensure that high-quality CDR tonnes successfully reach the market as planned. As discussed in CDR 2.0: Five Pillars of Successful Project Deployment and Delivery, managing delivery risk requires developers, investors, and buyers to understand the risks that can affect project success and align on how these risks are assessed and mitigated.

To support this alignment, the 2026 Criteria introduced a new Delivery Risk Appendix, which establishes a common framework and language for identifying and evaluating key delivery risks for the first time. Drawing on our broader observations of the carbon removal market and established approaches to project risk management, the appendix highlights common delivery risks across two broad CDR project types: open systems and closed systems. It organizes these risks into five categories: technical, economic, commercial, organizational, and political factors, also known as the TECOP framework. 

The TECOP Framework for CDR Delivery Risk

• Technical delivery risks are associated with the technical feasibility of the project design, implementation, and long-term operation of the project
• Economic delivery risks are associated with the project’s financing structure, financial modeling assumptions, and expenditure profile
• Commercial delivery risk reflects the extent to which a project's purchase agreements, supply arrangements, and key contractual relationships are secured or well-advanced. 
• Organizational delivery risks center on the project developer's capacity and capability to successfully plan, execute, and manage a project of the appropriate size and complexity.  
• Political delivery risks are associated with governance, policies, and potential changes in regulatory environments, as well as the local communities’ perception of and willingness to participate in projects.

New Additions to the 2026 Criteria

Since publishing the 2025 Criteria, Relae has conducted an additional 170 diligence reports across established and emerging CDR pathways, ranging from reforestation and enhanced rock weathering (ERW) to direct air capture (DAC). To date, less than 10% of all 900+ projects the team has reviewed have met the bar for high-quality. These diligence efforts, together with insights from market analysis and ongoing synthesis of the latest scientific and technical literature, have deepened our understanding of how CDR project quality has evolved over the past year. 

The 2026 Criteria leverage these insights and the expertise of more than 60 subject matter experts to reflect advances across the CDR industry and address key weaknesses that remain in the market across all pathways. 

A few of the most significant updates to the Criteria include:

Addition of Direct Counterparty Considerations: Direct counterparties are the organizations that developers partner with, and are structurally dependent on, to generate credits. This can include: 

• Primary feedstock providers (e.g., mines, biomass providers, tree nurseries)
• Major implementing partners (e.g., local implementation partners, base facilities, transportation and storage providers, major product offtakers)
• Land owners that make up a significant proportion of project land 

To reflect the key role that direct counterparties play in high-quality credit generation, developers must conduct diligence and disclose on their direct counterparties to demonstrate that they are not causing social or environmental harm.

Increased Rigor for Enhanced Rock Weathering Projects: Over the past year, ERW’s presence in the CDR market has grown substantially, and so too has the market’s understanding of the corresponding scientific and technical rigor required to deliver high-quality tonnes. The 2026 Criteria raised the bar for how ERW projects:

• Measure and prove their carbon removal claims
• Mitigate risks related to potentially toxic elements (PTEs)
• Incorporate more sophisticated farmer protections and benefits 

Projects now have to back up their numbers with multiple physical field measurements, not just computer models; and they must now track and account for every significant loss pathway, from plants taking up minerals to carbon escaping from rivers and oceans.

Use of Dynamic Baselines for ARR Projects: ARR projects are increasingly using dynamic baselines to provide a more accurate reflection of the counterfactual scenario (e.g., what would have happened in the absence of the project). This is reflected in the 2026 Criteria with a requirement that ARR projects, with the exception of agroforestry projects, use dynamic baselines with statistically matched controls.

What’s Next?

The 2026 Criteria create a clear, science-driven framework for both designing and delivering measurable, just, and durable carbon removal. However, the Criteria cannot ensure high-quality tonnes reach the market on its own; good criteria do not replace robust diligence. To put these criteria into practice, we encourage developers, standard-setting bodies, buyers, investors, and policymakers to consider how the Criteria can be used to inform their role in enabling the carbon market to deliver high-quality tonnes and to engage in deep diligence and ongoing monitoring over the life of a project.

This edition of the Criteria reflects what we have learned over the past year, but our work is not done. We will continue to update it so that it remains a living document that evolves with the science and the market. To do so effectively, it must be a collaborative effort; we welcome input from carbon market actors, academia, and communities.

Frequently Asked Questions

Who publishes the Criteria for High-Quality Carbon Dioxide Removal, and how often is it updated?

Relae (formerly Carbon Direct) first published the Criteria for High-Quality Carbon Dioxide Removal with Microsoft in 2021 and have updated it every year since. The 2026 edition reflects six years of lessons from real-world project diligence and advances in climate science.

What are the six principles of the Criteria for High-Quality Carbon Dioxide Removal?

The Criteria define six science-based principles that apply across all CDR pathways: social harms, benefits, and environmental justice; environmental harms and benefits; additionality and baselines; measurement, monitoring, reporting, and verification (MMRV); durability; and leakage.

What CDR pathways does the Criteria cover?

The Criteria include pathway-specific criteria across nine CDR pathways: afforestation, reforestation, and revegetation (ARR); mangrove forestation; improved forest management (IFM); soil carbon; enhanced rock weathering (ERW) in croplands; biomass carbon removal and storage (BiCRS); abiotic marine CDR; carbon mineralization; and direct air capture (DAC).

What is delivery risk in carbon removal?

Delivery risk is the likelihood that a project generates credits on the timeline and at the quantity committed to buyers. It's a distinct concern from credit quality: even a high-quality project can fail to deliver as planned because of technical, economic, commercial, organizational, or political risk, the five categories the Criteria's TECOP framework evaluates. The 2026 Criteria's new Delivery Risk Appendix gives developers, investors, and buyers a shared benchmark for identifying and managing these risks before they derail a project.

What's the relationship between carbon removal credit quality and delivery risk?

Credit quality and delivery risk are distinct but interrelated. A project that fails to deliver credits as planned reduces the availability of high-quality CDR tonnes in the market, and weaknesses in credit quality can themselves increase delivery risk by creating buyer uncertainty or limiting access to project financing. The 2026 Criteria provides a framework for evaluating both quality and delivery risk.

Key Takeaways

• Decarbonizing steel is key to meeting ambitious climate targets in the face of rapidly expanding AI infrastructure as well as broader infrastructure growth.
• The gap between corporate climate ambitions and near-term commercial reality is widening. Despite strong demand signals from hyperscalers and other major buyers, leading producers have recently canceled or delayed flagship green steel projects, citing high energy costs, slow hydrogen market development, and unfavorable policy environments. 
• Bridging this gap requires significant capital investment and supporting mechanisms to scale low-carbon technologies. Environmental attribute certificates offer an effective mechanism to channel capital toward transformative, low-carbon steel projects, supporting technology scale-up, as well as providing a way for buyers to meet their emissions reduction targets.  
• To protect the credibility of environmental attribute certificates as a market mechanism for decarbonization, projects should seek to meet rigorous quality criteria such as additionality, verifiability, and catalytic impact.

Forging New Climate Ambitions for Steel Production

Decarbonizing steel production is essential to meet global climate targets. Steel production accounts for approximately 7–9% of global CO₂ emissions. This is driven chiefly by coal-based primary steelmaking, which still accounts for the majority of global production. Globally, at least 1.8 billion tonnes of crude steel were produced in 2025 to serve a broad array of industries including real estate, infrastructure, automotive, and data center construction. 

As hyperscalers race to build the infrastructure underpinning the AI revolution, steel demand for data center construction, and associated energy infrastructure, is increasing. While the relative share of data center demand for steel versus global steel demand is small, the need for approximately 20,000 tonnes of steel per data center has a material impact on hyperscaler’s public climate commitments. Microsoft, Meta, and other large technology companies have set ambitious 2030 climate targets that include their scope 3 emissions. The embodied carbon of the steel used to build their data centers sits squarely in scope 3.

Hyperscaler’s climate commitments have generated sector-specific demand for decarbonized steel, presenting an opportunity to affect steel decarbonization more broadly. Despite this demand, the supply of low-carbon steel remains limited. The industry faces significant scale-up challenges due to the diffuse nature of demand and the nascent market. Catalyzing growth in decarbonized steel production will require market innovations and new production pathways designed to overcome these challenges. Credible environmental attribute certificates can help bridge the gap between today’s market and tomorrow’s low-carbon steel sector.

What is an Environmental Attribute Certificate?

An environmental attribute certificate (EAC) represents the environmental attributes of a product that can be unbundled and transacted separately from the underlying physical commodity. The most widely used EACs today are renewable energy certificates (RECs), which track the environmental attributes of renewable electricity. The same concept can also be applied to steel and iron, as well as to materials such as cement and concrete.

In a book and claim model, a steel producer can implement a verified emissions reduction intervention, quantify the resulting lowered carbon intensity per tonne of steel produced, and convert that into tradeable certificates. Buyers can then purchase those certificates to support the deployment of low-carbon steelmaking capacity in cases where direct procurement of low-carbon steel is currently impractical due to geographic, contracting, or scheduling incompatibilities.

EACs are distinct from carbon credits. They do not represent emissions reduced or avoided relative to a counterfactual; they represent the intrinsic carbon intensity of the material produced, measured through a life cycle assessment. 

Decarbonizing Steel Requires Significant Capital and Infrastructure Deployment

Steel Production Today

Steel is currently made via three main production routes. About 71% of the world’s steel is produced through the blast furnace–basic oxygen furnace (BF-BOF) route, which emits an average of 2.33 tonnes of carbon dioxide (tCO₂) per tonne of crude steel. A further 24% is produced using scrap-based electric arc furnaces (EAFs), which emit 0.68 tCO₂ per tonne on average—far lower, but still dependent on the carbon intensity of grid electricity. The remaining roughly 5% uses direct reduced iron combined with an EAF (DRI-EAF), typically using natural gas, emitting 1.37 tCO₂ per tonne on average.

While increasing scrap-based production is a critical decarbonization lever, scrap availability is limited. Primary steel production, which uses iron ore as the main feedstock rather than recycled scrap, will remain necessary at large volumes through 2050. This makes it essential to decarbonize ore-based pathways, especially ironmaking: the step where iron ore is reduced to iron and where most emissions occur.

Decarbonizing ore-based steel production requires one of three fundamental interventions: (1) replacing coal and natural gas with low-carbon fuels such as hydrogen or bio-coke, (2) electrifying ironmaking directly, or (3) capturing and storing the CO₂ generated from fossil-fuel-based processes. All three involve significant capital expenditure and dependencies on infrastructure that is not yet in place at the necessary scale. As a result, the energy and cost challenge is substantial.

Low-Carbon Steel: Emerging Pathways

A range of transformative technological pathways are currently in development to overcome these barriers, offering the potential to deliver deep decarbonization to the steel industry exceeding 90% by 2050: 

• Hydrogen-based DRI-EAF: Using green hydrogen instead of natural gas within the DRI process provides a pathway to significantly lower the carbon intensity of ironmaking. Producers such as Stegra are deploying commercial-scale facilities designed to utilize 100% green hydrogen to reduce iron ore.
• Electrifying ironmaking: 
  
  • Molten oxide electrolysis: Boston Metal is commercializing a process that uses electricity to directly convert iron ore to molten metal through electrolysis at high temperature, eliminating the need for hydrogen or carbon reductants entirely.
  • Low-temperature electrowinning: Colorado-based startup Electra uses renewable electricity to extract iron from ore via an aqueous electrochemical process that operates at near-ambient temperature. 
• Carbon capture and storage (CCS): For blast furnaces and DRI plants with long remaining lifetimes, retrofitting with CCS technology can significantly reduce emissions. With new high-emitting capacity still being built, and assets expected to operate for decades, integrating CCS will be essential to avoid long-term carbon lock-in and to decarbonize these facilities over time. To date, commercial-scale deployment remains limited. The Al Reyadah facility at Emirates Steel is the only project currently capturing CO₂ from a DRI process at scale, though a handful of other large-scale projects have entered the development pipeline.

Progress and Setbacks: A Mixed Picture

The past year sent contradictory signals about the pace of steel decarbonization. On the demand side, technology companies with ambitious climate targets are actively signaling their intent to procure near-zero steel and support its development.

In September 2025, Microsoft and Stegra announced a landmark agreement that combines a physical supply deal for low-carbon steel with a separate EAC purchase agreement. Around the same time, Meta announced an agreement with Electra to purchase EACs tied to the startup’s clean iron production, becoming one of the first buyers to use the EAC model for an entirely novel, pre-commercial ironmaking technology. Nucor, the largest US steelmaker, also entered into a physical iron purchase agreement with Electra.

Despite these demand signals, the industry has experienced significant setbacks. A series of low-carbon steel project cancellations and delays has raised questions about the pace and viability of the steel transition, especially due to the high costs associated with green hydrogen production.

At present, the green premium for most low-carbon steel remains too high for buyers. A combination of sustained policy support, long-term demand signals from buyers willing to pay more, and scaling of supporting industries, such as green hydrogen production, is necessary for the low-carbon steel industry to be successful in the long run.

How EACs Can Bridge the Funding Gap in Steel

EACs unbundle low-carbon steel attributes from the physical material, reducing the friction between buyers who are willing to pay a green premium and geographic or logistical constraints that may inhibit physical offtake. Buyers, such as hyperscalers procuring conventional steel for data center construction in locations where low-carbon steel is not yet available, can purchase these certificates to support the development of low-carbon capacity, attribute lower-carbon production to their steel use via a market-based mechanism, and advance toward their scope 3 targets.

A primary objective of the Criteria for High-Quality Environmental Attribute Certificates in the Concrete and Steel Sectors, jointly developed by Relae (formerly Carbon Direct) and Microsoft, is to establish high-integrity standards for the EAC market in these sectors. For steel EACs, that means demonstrating significant emissions reduction performance by reaching at least Progress Level 2 in the ResponsibleSteel Decarbonization Progress Levels framework, and aiming to achieve Progress Level 3 by 2030. ResponsibleSteel’s scrap-variable benchmark provides a technology-neutral mechanism to evaluate emissions reduction performance by accounting for the specific proportion of scrap used.

EACs for steel are designed to be catalytic. Rather than supporting incremental improvements that are already becoming cost-competitive, they should target transformative capital changes, such as replacing BF-BOF routes with DRI-EAF, adopting low-carbon hydrogen in DRI processes, or deploying novel ironmaking technologies. Multi-year purchase agreements are particularly powerful because they provide the investment certainty that first-of-a-kind projects need to access capital at a lower cost.

What this Means for Buyers and Suppliers of Low-Carbon Steel 

Whether you are producing or procuring steel, EACs are only one part of a broader decarbonization strategy. For buyers with significant emissions from steel, and other building materials such as cement and concrete, EACs can be a powerful tool to help advance scope 3 reduction goals where supply for physical low-carbon materials is limited. Suppliers can complement commercialization strategies for low-carbon materials by using EACs to monetize emissions reductions, generate additional revenue to support decarbonization investments, and help scale markets for low-carbon materials. Navigating the steel market requires decisions at the intersection of technical feasibility, greenhouse gas accounting, and capital strategy. Key considerations include:

• Greenhouse gas accounting and reportability: Cradle-to-gate emissions for steel production must be tracked using life cycle assessments and should strive for interoperability with environmental product declarations (EPDs). EAC transactions must be reported transparently, especially given the absence of formal market standards at this stage.
• Additionality and catalytic impact: EAC purchases must demonstrably support projects that would not proceed without financial support from the EAC market mechanism, and projects should have a credible pathway toward the near-zero (Progress Level 4) threshold on the ResponsibleSteel framework.
• Avoiding double counting: EAC buyers must verify that the environmental attributes they purchase are not also being claimed by the physical product buyer via an EPD.

FAQs

What is an environmental attribute certificate (EAC) for steel?
An EAC represents the environmental attributes of low-carbon steel, unbundled from the physical material itself, so a producer can quantify a verified reduction in carbon intensity per tonne and sell that value as a separate, tradeable certificate. Buyers can purchase EACs to support low-carbon steel production while still working toward their own emissions targets.

How is an EAC different from a carbon credit?
An EAC reflects the intrinsic carbon intensity of the material itself, measured through a life cycle assessment. That's different from a carbon credit, which represents carbon dioxide actively avoided, reduced or removed from the atmosphere relative to a baseline.

How are AI data centers impacting the demand for low-carbon steel?

Data centers use roughly 20,000 tonnes of steel each, and as hyperscalers build out AI infrastructure, that steel use counts toward their scope 3 emissions and public climate targets. That's turned data center construction into a meaningful driver of demand for low-carbon steel, even though supply remains limited.

What makes an EAC credible enough to count toward a company's emissions goals?
A credible steel EAC needs to meet criteria like additionality (the project wouldn't happen without the EAC revenue), verifiability through life cycle assessment, and catalytic impact toward transformative technology rather than incremental gains. Relae (formerly Carbon Direct) and Microsoft jointly developed criteria for high-quality EACs in the steel and concrete sectors, which set a threshold of at least Progress Level 2 on the ResponsibleSteel Decarbonization framework today, rising to Progress Level 3 by 2030.

Can a producer sell an EAC and also get credit for the physical steel elsewhere?
No. EAC producers need to confirm the environmental attributes they're selling aren't also being claimed by whoever buys the physical steel through an environmental product declaration; otherwise the same emissions reduction gets counted twice.

Key Takeaways

• Buyers have been navigating the low-carbon fuels (LCF) market without a map.  The LCF market is expanding rapidly, but standards, definitions, and quality claims vary widely across regions, certification schemes, and regulatory systems, leaving voluntary buyers without a holistic framework for evaluating what they procure.
• Certifications cover some of the picture, not all of it. Existing certification schemes provide valuable assurance but vary in scope and rigor, and few, if any, were designed specifically with voluntary market buyers in mind. 
• The 2026 criteria give buyers a legible quality framework. The 2026 Criteria for High-Quality Low Carbon Fuels bring together key sustainability considerations across six principles, including social and environmental integrity, carbon accounting, additionality, feedstock sourcing, and leakage, giving buyers and producers a legible, living framework to navigate procurement decisions with confidence.

Verifying Quality Is Challenging in the Current Low-Carbon Fuels Market

For airlines, logistics companies, and large corporations with hard-to-abate transportation emissions, low-carbon fuels (LCFs) have become an important part of the decarbonization toolkit. Yet it remains difficult for procurement teams to answer a fundamental question: what does high-quality procurement actually look like? 

Standards, definitions, and sustainability claims vary widely across regions, certification bodies, and regulatory programs. The result is a market where quality is difficult to verify, certifications are difficult to compare, and the gap between a fuel's claims and its actual sustainability profile can be hard to close. Sustainable production will be especially critical as the market scales, because low-carbon fuel systems are deeply embedded in land, agriculture, forestry, and communities. 

The 2026 Criteria for High-Quality Low Carbon Fuels are designed to close this gap, giving voluntary buyers a consistent framework to evaluate the quality of what they procure and identify where additional diligence is still needed.

What Is a Low-Carbon Fuel?

For the purposes of the criteria, a low-carbon fuel, or LCF, is defined as a fuel or energy source whose lifecycle greenhouse gas (GHG) emissions are lower than those of a relevant, use-case-specific fossil fuel alternative. In this case, we are referring to the physical biofuel and its associated environmental attributes. 

While LCFs may be produced through biological, synthetic, or other non-fossil pathways, the 2026 edition focuses on biofuels for transportation, which currently represent the majority of LCF production and use. 

Understanding the Complex LCF Regulatory and Certification Landscape

The LCF market sits at the intersection of multiple regulatory and voluntary markets. In the US, this includes compliance programs such as the Renewable Fuel Standard (RFS) and state-level Low Carbon Fuel Standards (LCFS). Europe, the United Kingdom, Canada, and many other nations host comparable programs, often with specialized regulatory regimes for various transport sectors, e.g., aviation or maritime. 

These regulatory markets coincide with and often intersect voluntary markets, which contain a multitude of standards and certifications. For producers, this creates a complex landscape of market options. For buyers, it creates a signal problem: a fuel may carry one or more certifications, comply with one or more regulatory programs, and still leave meaningful sustainability questions unaddressed.

Several organizations, including the Roundtable on Sustainable Biomaterials (RSB) and the International Sustainability and Carbon Certification (ISCC), have developed widely used standards for LCFs. These certifications assess supply chains from feedstock to end use and provide important baseline assurance. 

However, they were developed with different primary audiences in mind and can vary in scope and rigor. Few existing schemes were designed to serve as a comprehensive sustainability reference for voluntary market buyers evaluating what a given fuel's certification covers and where gaps may still exist.

Simplifying High-Quality Procurement for Voluntary Buyers 

The 2026 Criteria for High-Quality Low Carbon Fuels are not designed to replace or compete with existing certification schemes. Rather, they consolidate key sustainability considerations from across the landscape of existing frameworks into a single, legible reference built specifically for voluntary market decision-makers.

The criteria apply across the full LCF supply chain, covering not only fuel producers but also fuel blenders, aggregators, and certificate traders. This LCF systems view encompasses the full set of production, certification, and procurement arrangements through which LCFs are generated and claimed. This reflects the reality that sustainability outcomes in this market are shaped by many actors, not just at the point of production.

The criteria distinguish between requirements that must be met (minimum thresholds for quality and integrity) and considerations that should be addressed, reflecting best practices and aspirational standards. This distinction is intentional: the criteria set a floor while leaving room for market participants to demonstrate quality in ways appropriate to their specific context. 

The criteria are organized around six core principles that together define what high-quality LCF production and procurement looks like. 

Six Principles for Procuring High-Quality Low-Carbon Fuels

1. Social harms, benefits, and environmental justice: preventing new harms to communities, reducing existing ones, and ensuring equitable distribution of benefits
2. Environmental harms and benefits: minimizing impacts on air, soil, water, and biodiversity
3. Carbon accounting: accurately quantifying lifecycle GHG emissions using credible methodologies and tracking environmental attributes to prevent double-counting
4. Additionality: demonstrating that voluntary market support enables outcomes that would not otherwise occur
5. Feedstock sourcing: ensuring responsible and equitable sourcing practices and requiring end-to-end chain-of-custody documentation traceable to the point of generation
6. Leakage: assessing and mitigating activity-shifting and market leakage associated with the LCF system

Where a fuel's existing certification or regulatory program adherence already addresses one or more of these core principles, that coverage should be disclosed to the buyer by the producer. Buyers can then use the criteria to identify where certification coverage aligns with quality expectations, and where supplemental diligence is needed.

A Living Framework for a Market in Motion  

The LCF market will continue to evolve as policy frameworks are shifting, certification systems are maturing, and new production pathways are emerging. The 2026 edition reflects the current state of the LCF market and is intended as a living resource, with future updates possible as the market develops and new science emerges. Future editions may expand to cover synthetic LCF pathways, renewable natural gas, and sector-specific considerations such as maritime fuels.

For buyers navigating voluntary LCF procurement, the criteria offer a practical starting point: a framework to evaluate what existing certifications cover, identify where additional diligence is needed, and build procurement decisions on a consistent quality foundation. For producers, they provide clear guidance on what a sustainability demonstration looks like for voluntary market buyers.

Read the 2026 Criteria for High-Quality Low Carbon Fuels to learn more about how the criteria apply to your procurement strategy or production system.

Frequently Asked Questions

What is a low-carbon fuel?
A low-carbon fuel is a fuel whose lifecycle greenhouse gas emissions are lower than a comparable fossil fuel alternative for the same use case. The 2026 LCF Criteria focus specifically on biofuels for transportation, which currently make up most LCF production and use.

What do the 2026 Criteria for High-Quality Low Carbon Fuels cover?
The criteria are organized around six principles: social harms, benefits, and environmental justice; environmental harms and benefits; carbon accounting; additionality; feedstock sourcing; and leakage. Together they give buyers and producers a consistent way to evaluate what high-quality LCF production and procurement looks like.

Do the LCF criteria replace existing certifications like RSB or ISCC?
No. The criteria aren't designed to replace or compete with existing certification schemes such as the Roundtable on Sustainable Biomaterials (RSB) or the International Sustainability and Carbon Certification (ISCC). Instead, they consolidate key sustainability considerations from across those frameworks into a single reference so buyers can see what their certification already covers and where supplemental diligence may be needed.

Who do the LCF criteria apply to across the supply chain?
The criteria apply across the full LCF supply chain, not just producers, but also feedstock suppliers, fuel blenders, aggregators, and certificate traders, reflecting that sustainability outcomes are shaped by many actors, not only the producer.

What's the difference between the "must" and "should" requirements in the LCF criteria?
"Must" requirements set minimum thresholds for quality and integrity that need to be met, while "should" considerations reflect best practices and aspirational standards market participants can work toward. This sets a floor while leaving room for participants to demonstrate quality in ways suited to their specific context.