Cement is responsible for roughly 8% of global anthropogenic carbon dioxide emissions. That is roughly three times the contribution of the aviation industry and more than the entire emissions of India. The chemistry of cement production makes it uniquely difficult to decarbonize. About 60% of cement plant emissions come from the calcination of limestone itself, a chemical reaction inherent to clinker production. The remaining 40% comes from heating kilns to 1,450 degrees Celsius, almost always with fossil fuels. There is no way to electrify the reaction and no drop-in replacement for the material at anything approaching global scale.

Despite these structural challenges, 2026 marks a turning point. Three forces are converging: the EU Carbon Border Adjustment Mechanism entered its definitive phase on January 1, covering cement imports with real financial obligations; the U.S. federal government is operationalizing Buy Clean procurement across tens of billions of dollars in federally funded construction; and the cement industry itself, after years of pilot projects and corporate commitments, is bringing commercial low-carbon products to market. For chief procurement officers in construction, infrastructure, and real estate development, the regulatory push means new specification requirements, cost implications, and supply constraints that were not present even two years ago.

8%
Global CO2 emissions attributable to cement production
Source: IEA, GCCA, 2025

EU CBAM: Cement Is Front and Center

The EU Carbon Border Adjustment Mechanism entered its definitive phase on January 1, 2026. Unlike the transitional phase, which required only reporting, the definitive regime imposes real financial obligations. Importers of cement, clinker, and other CBAM-covered goods above 50 tonnes per year must hold authorized CBAM declarant status and purchase CBAM certificates. The certificates are priced in line with the EU Emissions Trading System, which means importers pay a carbon price equivalent to what EU producers already pay under the ETS. From 2027, importers must surrender certificates for the previous year's imports.

The 50-tonne threshold exempts smaller importers, but the European Commission estimates that roughly 90% of importers by count fall below that threshold. The remaining 10%, however, cover approximately 99% of embedded emissions. For construction procurement officers sourcing cement or ready-mix concrete in Europe, or for any infrastructure project with EU-linked funding, CBAM costs are now a line-item consideration.

The cost impact is material but manageable for low-carbon products. Cement production has an average CO2 intensity of approximately 0.58 tonnes per tonne of cement. At EU ETS prices that have ranged from EUR 65 to over EUR 100 per tonne of CO2 in recent years, the CBAM liability on a standard tonne of imported Portland cement can reach EUR 38 to EUR 58. That is a significant adder on a product that typically trades at EUR 80 to 120 per tonne. However, products with lower clinker factors, such as Portland limestone cement or blended cements, carry a proportionally lower liability. This creates a direct financial incentive for importers and buyers to shift toward lower-carbon specifications.

The Omnibus simplification package, enacted in October 2025, raised the previous EUR 150 per-shipment de minimis to a 50-tonne annual threshold and postponed certificate purchases to February 2027. Importers who have not yet applied for authorized declarant status must do so by March 31, 2026, or risk disruptions at the border. For procurement officers, the implication is clear: supplier CBAM compliance is now a procurement risk. Verifying that cement and concrete suppliers are registered and reporting is a prerequisite for any EU-market purchase.

U.S. Federal Buy Clean: IRA Dollars With Strings Attached

The Inflation Reduction Act allocated $3.375 billion to the U.S. General Services Administration for low-embodied-carbon construction materials, including $2.15 billion specifically for procurement of materials with substantially lower embodied carbon. The GSA has operationalized this through interim low-embodied-carbon material requirements covering concrete, cement, concrete masonry units, steel, asphalt, and flat glass. The thresholds are based on the EPA's December 2022 Interim Determination, which defines qualifying materials as those in the top 20% of lowest global warming potential based on product category rules and environmental product declarations.

In practice, the GSA pilot began with 11 projects in May 2023 and scaled to approximately 150 projects by November 2023, with an estimated $767 million allocated to low-embodied-carbon concrete. The requirements apply to assemblies such as reinforced concrete, where at least 80% of the total cost or weight must meet the per-PSI GWP limits. These requirements remain active through September 30, 2026. For contractors bidding on GSA projects, the requirement to source concrete that meets specific GWP thresholds, and to document that compliance with product-specific EPDs, is no longer optional.

The EPA is taking this further. Under Section 60116 of the IRA, the agency is developing a formal label program for low embodied carbon construction materials. The implementation approach was released in August 2024, and the EPA anticipates establishing thresholds for some concrete products by late 2025 or early 2026. The label program creates a standardized, federally recognized benchmark that state and local procurement programs can adopt. Several states, including California, Washington, Oregon, Minnesota, Colorado, and New York, have already enacted or proposed their own low-carbon concrete procurement preferences, often using more aggressive thresholds than the federal baseline.

$2.15B
IRA funds for GSA low-embodied-carbon material procurement
$767M
Est. allocated specifically for low-carbon concrete
150+
GSA projects using low-embodied-carbon concrete requirements

Portland Limestone Cement: The Low-Regret Default

Portland limestone cement, designated as Type IL under ASTM C595, is the fastest and most cost-effective decarbonization lever available to procurement teams today. PLC replaces a portion of clinker with interground limestone, typically achieving a 10% reduction in cement CO2 footprint with no meaningful change in performance. The material is approved by all 50 U.S. state departments of transportation, a milestone reached in 2024 when Connecticut gave its final sign-off. The U.S. Geological Survey reports that approximately 24.8 million tonnes of PLC were consumed in the United States in 2022, and that figure has grown rapidly since.

For procurement officers, the case for specifying PLC as the default is straightforward. It costs approximately the same as Type I/II Portland cement. It is widely available from all major producers. It meets standard performance specifications. And it delivers an immediate, verifiable emissions reduction. The Portland Cement Association has made PLC adoption a cornerstone of its Roadmap to Carbon Neutrality, and the material is now standard production at most U.S. cement plants. In Europe, equivalent blended cements under EN 197 are similarly widespread.

Despite this, many project specifications still default to Type I/II, either out of habit or due to prescriptive specifications that have not been updated. The single highest-impact action a construction procurement officer can take in 2026 is to review and update master specifications to permit, and eventually require, PLC or equivalent blended cements wherever codes allow.

50
U.S. state DOTs that have approved Portland limestone cement (Type IL)
Source: PCA, 2024

The Supply Landscape: Major Producers in Transition

Global cement production is concentrated among a small number of major players, and their decarbonization trajectories directly affect supply availability and pricing. The Global Cement and Concrete Association represents 40 of the world's leading producers, accounting for approximately 80% of global production outside China. The GCCA's 2050 Net Zero Roadmap, launched in 2021, was the first net-zero commitment from any heavy industry. Member companies committed to a 20% reduction in CO2 per tonne of cementitious materials and a 25% reduction in CO2 per cubic meter of concrete by 2030, against a 2020 baseline.

The 2025-2026 GCCA progress report shows a 25% reduction in CO2 per tonne of cementitious materials since 1990, with alternative fuel use increasing twelvefold over the same period. But the industry acknowledges that the pace must accelerate. The roadmap identifies four main decarbonization levers: clinker substitution (including PLC and blended cements), alternative fuels, material efficiency and design optimization, and carbon capture utilization and storage, which accounts for 36% of planned reductions.

Holcim has advanced its low-carbon brands ECOPact and ECOPlanet. ECOPact concrete offers at least 30% CO2 reductions versus standard CEM I concrete, with some mixes achieving up to 70% reductions through high SCM substitution. By 2025, ECOPact reached 31% of Holcim's ready-mix net sales and ECOPlanet reached 36% of cement net sales. CEMEX has set a target to reduce CO2 to below 475 kg per tonne of cement by 2030, approximately a 40% reduction, with SBTi validation of its full 2050 net-zero roadmap. CCUS projects in its portfolio have the potential to avoid more than 3 million tonnes of CO2 annually.

Heidelberg Materials has launched evoZero, the world's first carbon-captured net-zero cement, based on its Brevik CCS facility in Norway. The plant captures approximately 400,000 tonnes of CO2 per year, roughly 50% of the plant's emissions, with mechanical completion achieved in 2024 and first commercial deliveries beginning in 2025. The material is being supplied to flagship projects such as the new Nobel Center in Stockholm. However, IEA estimates place the production cost of near-zero cement with CCS at 75% to 150% higher than conventional production. In 2026, CCS-based cement remains a premium niche product suitable for high-profile, climate-committed projects rather than mainstream procurement.

"CCS-based near-zero cement at early commercial plants is estimated to have 75-150% higher production cost than conventional cement. Cost premiums may fall with SCMs and efficiency measures."

— IEA, Breakthrough Agenda Report 2025, Cement and Concrete

Alternative Binders: LC3 and the Future of Clinker Substitution

Limestone calcined clay cement, widely known as LC3, represents the next wave of clinker substitution. LC3 replaces up to 50% of clinker with a blend of calcined clay and limestone. When activated together, these materials form carboaluminate hydrates that fill pore spaces and contribute to strength development comparable to ordinary Portland cement. The CO2 reduction is approximately 40% versus OPC, with no requirement for carbon capture.

The technology was developed at the Swiss Federal Institute of Technology in Lausanne and has been made available in the public domain. Standardization is advancing rapidly: LC3 is now recognized under EN 197-5 in Europe and under IS 18831:2024 in India. The global market for low-carbon LC3 cement was valued at approximately $14.8 billion in 2025 and is projected to grow at 11.2% CAGR to $38.6 billion by 2034, according to market analysts. Asia-Pacific leads deployment, with India and China driving demand.

For procurement, LC3 is particularly relevant for projects in regions where traditional SCMs such as fly ash and slag are in short supply. Fly ash availability is declining as coal-fired power plants retire. Ground granulated blast furnace slag depends on blast furnace steelmaking, which is itself shrinking. Calcined clay is widely available and geographically distributed. Procurement specifications that reference EN 197-5 or equivalent standards enable suppliers to offer LC3 without requiring individual project-level approval.

Three Actions for Construction Procurement in 2026

  • Update master specifications to default to PLC/Type IL. The 10% CO2 reduction is cost-neutral, code-compliant, and universally available. OPC exceptions should require documented justification.
  • Require product-specific EPDs for all cement and concrete. The GSA, EPA Label Program, and state Buy Clean policies all use GWP thresholds tied to EPDs. Without an EPD, a supplier cannot demonstrate compliance.
  • Evaluate LC3 and high-SCM mixes for large pours and non-structural applications. These materials can deliver 30-50% CO2 reductions at modest cost premiums that are declining as capacity scales.

CarbonCure and CO2 Mineralization: The Operational Lever

CarbonCure's technology injects captured CO2 into fresh concrete, where it mineralizes into calcium carbonate and becomes permanently embedded. The process allows a reduction in cement content while maintaining or improving compressive strength. As of early 2025, CarbonCure had deployed over 800 systems across more than 35 countries, with over 8 million truckloads of concrete produced using the technology and more than 540,000 tonnes of CO2 permanently stored.

The CO2 savings from mineralization are additive to the savings from clinker substitution. A concrete mix that uses PLC as the binder plus CarbonCure mineralization can achieve total CO2 reductions of 15% to 25% versus a conventional OPC mix, often at neutral or marginally lower cost due to the cement reduction. For procurement teams, the technology is attractive because it integrates into existing batching systems and does not require changes to mix design or handling procedures. The Verra-certified methodology provides third-party assurance for carbon accounting.

However, availability is not uniform. CarbonCure's deployment is concentrated in North America, with growing presence in Europe, the Middle East, and Asia-Pacific. Regional readiness varies, and procurement teams should verify local availability early in the planning process rather than treating it as a specification assumption.

Cost Realities: The Decarbonization Premium Curve

The cost of decarbonizing cement and concrete is not linear. The first 30-40% of CO2 reduction is achievable at low or negative cost through clinker substitution, mix optimization, and material efficiency. These measures reduce the amount of clinker required per unit of concrete, which reduces both emissions and material cost. Specifying PLC, optimizing aggregate gradation, and reducing overdesign all fall into this category. For many projects, the net cost impact of the first 30% reduction is zero or slightly positive.

Beyond 40%, the curve steepens. High SCM substitution rates require careful quality control and may affect setting time or early strength. Advanced mix designs require more testing and validation. The 40% to 60% reduction range typically carries a cost premium of 5% to 15% depending on regional material availability, project scale, and specification flexibility.

Beyond 60%, carbon capture becomes necessary. At current technology costs, CCS-based cement carries a 75% to 150% production cost premium. The good news is that the volume of cement requiring CCS to meet global decarbonization targets remains small in the near term. The IEA's Net Zero Emissions scenario envisions CCS scaling significantly after 2030. For 2026 procurement, CCS-based products should be treated as a specialty material for specific applications, not a mainstream supply option.

A 2026 Stanford study modeling the EU cement sector found that with carbon prices around EUR 141 per tonne of CO2, approximately 96% emissions reductions are technically feasible at roughly a 12% increase in cement production cost. That is well below the cost-doubling figures often cited by industry incumbents. But it assumes rapid deployment of clinker substitution and CCS, both of which face regulatory, supply chain, and capital constraints that the modeling may understate.

Supply Constraints and Regional Variation

Cement markets are intensely regional. The economics of transport economics limit cement shipping to roughly 200 kilometers by truck. Low-carbon concrete introduces additional regional specificity because SCM availability, batching technology, and local code acceptance vary widely. The IEA estimates that only about 3% of global cement output qualified as low-carbon in 2023. That share is growing but from a small base.

SCM availability is an emerging bottleneck. Fly ash supply is declining in lockstep with coal plant retirements. Slag supply depends on blast furnace capacity, which is shrinking in Europe and North America. Alternative SCMs, including calcined clays, finely ground glass, and natural pozzolans, are entering the market but lack the established supply chains of traditional materials. Procurement teams should engage with suppliers 12 to 18 months before project start to understand local SCM availability and secure supply.

The NRMCA, supported by a $9.63 million EPA grant awarded in 2024, is expanding its EPD program from approximately 1,500 ready-mix plants to approximately 4,500. This expansion will dramatically improve the availability of plant-specific GWP data across the U.S. concrete supply chain. Combined with the Clean Concrete Pledge, which commits suppliers to clinker factors below 0.6 and demonstrations of 50% GWP reduction versus NRMCA benchmarks, the U.S. market is building the data infrastructure that makes low-carbon procurement feasible at scale.

FAQ

What is the EU CBAM and how does it affect cement procurement?

The EU Carbon Border Adjustment Mechanism entered its definitive phase on January 1, 2026. Importers of cement and clinker above 50 tonnes per year must hold authorized declarant status and purchase CBAM certificates priced to the EU ETS. This creates a financial penalty on high-carbon imported cement, effectively incentivizing lower-clinker blends and domestically produced low-carbon products.

What is Portland limestone cement (PLC) and why should I specify it?

PLC (Type IL under ASTM C595) replaces a portion of clinker with interground limestone, reducing CO2 emissions by approximately 10% compared to Type I/II Portland cement. It is approved by all 50 U.S. state DOTs, costs approximately the same as standard cement, and meets conventional performance requirements. It is the lowest-risk decarbonization option available to procurement teams.

How does the EPA Buy Clean program affect concrete specifications?

The EPA's Interim Determination defines low-embodied-carbon materials as those in the top 20% of lowest GWP based on EPD data. The GSA has operationalized this through concrete GWP limits tied to compressive strength. Projects using IRA funds must document that at least 80% of assembly cost or weight meets these thresholds. The EPA Label Program, under development, will extend this framework.

What is the cost premium for low-carbon concrete in 2026?

The cost premium depends on the level of CO2 reduction. The first 30-40% reduction via PLC, SCMs, and mix optimization is often cost-neutral or low-cost. Premiums of 5-15% apply for high SCM substitution and advanced mix designs. CCS-based net-zero cement carries a 75-150% production cost premium and should be treated as a specialty material.

What is LC3 and is it available for procurement?

Limestone calcined clay cement (LC3) replaces up to 50% of clinker with calcined clay and limestone, reducing CO2 by approximately 40%. It is standardized under EN 197-5 in Europe and IS 18831:2024 in India. The global market was valued at $14.8 billion in 2025. Availability is strongest in Asia-Pacific but expanding globally as more plants convert production lines.

How do I verify supplier low-carbon claims?

Require product-specific or plant-specific Environmental Product Declarations prepared in accordance with ISO 14025 or EN 15804. EPDs provide third-party verified GWP data. For CO2-mineralized concrete, look for Verra-certified methodologies. Cross-reference supplier claims against CDP disclosure scores and SBTi validation. The NRMCA EPD program is expanding to cover approximately 4,500 U.S. ready-mix plants.