Scale: The Size of the Solution Must Address the Problem
Why low emission cement or concrete solutions must scale under growth and time pressure as well as across diverse regional markets
The SPFC Framework
This is the second of four pillars that define how we evaluate cement decarbonization pathways:
Executive Summary
The cement industry produces over 4 billion tons per year โ enough concrete to build a Great Wall of China around the equator every single year.
A solution reaching 10 million tons per annum is a successful company; it is not a solution to a 4-billion-ton problem. We set the minimum viability threshold at ~100 million tons annually.
Feedstock availability is the binding constraint most scale analyses ignore โ traditional SCMs like fly ash and slag are declining or flat, forcing a reckoning with alternative supply chains.
Deployment speed matters as much as technology: retrofitting existing plants scales faster than greenfield, and different regions require different solutions.
The Picture of Scale
The world produces over 4 billion tons of cement every year. This makes it the most consumed manufactured material on Earth after water. To grasp the physical magnitude: the concrete poured globally each year would be sufficient to construct a replica of the Great Wall of China around the entire equator.
This is not a niche material. It is the substrate of civilization โ roads, bridges, hospitals, housing, ports, dams, data centers. Every continent, every climate, every income level. And demand is not declining. The Global South is building the infrastructure that developed nations built decades ago, and they are doing it with cement.
The question is not whether solutions exist.
The question is whether they can operate at the magnitude of the problem.
A company producing 10 million tons per year of low-carbon cement is a successful business. But it addresses less than 0.25% of the global market. That is a rounding error, not a solution.
To materially shift the emissions curve, we need pathways that can reach at least 100 million tons annually โ and ideally multiple such pathways operating simultaneously. Anything less is a demonstration. We invest in demonstrations only if the path from demonstration to system scale is credible.
The Magnitude Gap
From pilot to global production โ logarithmic scale reveals the true distance
We set the minimum viability threshold at approximately 100 million tons per annum. Below that, a technology may be commercially successful โ but it is not a cement decarbonization solution.
Feedstock Supply: The Constraint Most Models Ignore
Every cement decarbonization pathway depends on a physical input. The critical question is not "does this technology work?" but "does the feedstock exist at the volume required to matter?"
The Declining Legacy: Slag and Fly Ash
For decades, the cement industry relied on two industrial byproducts โ ground granulated blast furnace slag (GGBFS) from steelmaking and fly ash from coal power plants โ as supplementary cementitious materials. These are proven, effective, and widely used. But their supply ceilings are structurally constrained.
GGBFS is capped at ~430 Mt/yr โ the total output of blast furnace steelmaking globally โ and will shrink as the industry transitions to electric arc furnaces. Fly ash has a larger theoretical base (~800 Mt/yr including stockpiled material) but fresh supply is declining fast as coal plants close across the US and Europe. These are legacy feedstocks with contracting ceilings.
The Emerging Supply: Natural and Engineered Alternatives
This supply decline makes the search for alternative SCMs existentially important. Several promising categories are emerging:
- โข LC3 (Limestone Calcined Clay Cement): Kaolinitic clay exists on every continent in enormous quantities โ a theoretical supply ceiling of ~2,000 Mt/yr. Already commercial in Colombia, Ghana, India, and France. The most credible replacement at scale. [4]
- โข Natural Pozzolans: Billions of tons of volcanic ash, pumice, and tuff deposits exist globally โ a ceiling rivaling calcined clay. Unevenly distributed but abundant in Latin America, East Africa, Southeast Asia, and western North America. [5]
- โข Recycled Glass Pozzolan: If all global glass waste were collected and ground as pozzolan, theoretical supply reaches ~200 Mt/yr. Currently constrained by collection infrastructure, not by geology. [6]
- โข COโ Mineralization: If COโ injection technology (CarbonCure, Solidia) were deployed across global concrete production, theoretical capacity could reach ~50 Mt/yr. Currently sub-1 Mt. [10]
- โข Algae / Biocement: Theoretical ceiling of ~500 Mt/yr if bio-manufacturing were industrialized. Lab-stage only today โ zero commercial production โ but the biological supply chain is inherently renewable.
CCS and CCU: Super-Scalable if the Technology Works
Carbon capture technologies deserve special attention because their theoretical scale is enormous. CCS (Carbon Capture and Storage) could sequester over 5 Gt of COโ per year by 2050 according to IEA projections [7]. CCU (Carbon Capture and Utilization) โ where captured COโ is mineralized into concrete, converted to fuels, or used as chemical feedstock โ could utilize an additional 6.2 Gt COโ/yr globally [9]. At this scale, both pathways would dwarf every SCM category combined.
But each pathway faces a different binding constraint. CCS is limited by how much COโ we can actually store. The geological storage ceiling โ saline aquifers, depleted oil and gas reservoirs, deep coal seams โ is estimated at 1,460 Gt under prudent engineering assumptions [8]. That is large but not infinite, and it presupposes a global network of COโ transport pipelines that does not yet exist. As of 2025, operational CCS capacity across all industries is approximately 50 Mt/yr [7] โ less than 1% of what is needed.
CCU is limited by how much COโ we can capture and economically utilize. The current bottleneck is not the concrete industry's willingness to use COโ โ it is the cost and availability of captured COโ at sufficient purity and pressure. GCCA aims to have CCUS fully operational at just 10 cement plants globally by 2030. The Norcem Brevik plant in Norway โ the world's first full-scale cement CCS facility โ captures 400,000 tonnes of COโ per year, a landmark achievement that still represents 0.01% of the industry's annual emissions.
CCS and CCU are not feedstock-limited โ they are infrastructure-limited.
If capture costs fall below $40/ton and transport networks develop, these pathways become the most scalable decarbonization lever in the cement industry. We watch them closely as infrastructure plays, not chemistry experiments.
Theoretical Feedstock Supply Ceiling
Maximum annual volume if each feedstock were fully mobilized โ the green line marks the 100 Mt minimum viability threshold
The theoretical supply ceiling tells a different story than current production. Calcined clay, natural pozzolans, and recycled glass all have ceilings well above the 100 Mt viability threshold.
But ceiling is not the same as reality. The investable question is: which feedstocks have both the geological abundance AND the path to industrial mobilization? Calcined clay and natural pozzolans stand out โ they are earth-abundant, regionally distributed, and require no industrial byproduct dependency.
Building as a Scale Issue
Even if a technology is sound and its feedstock abundant, the speed of deployment determines whether it arrives in time to matter. Cement decarbonization is a race against cumulative emissions, and construction timelines are a binding constraint.
Retrofit vs. Greenfield
There are roughly 4,000 cement plants operating globally. Building new facilities is slow: permitting, environmental review, community engagement, financing, construction โ a 5โ8 year cycle for a single plant. Greenfield projects also carry enormous CAPEX risk.
By contrast, retrofitting existing plants โ adding SCM blending capability, modifying kilns for alternative fuels, bolting on carbon capture โ can happen in 1โ4 years. Solutions that leverage existing infrastructure scale faster, cost less, and face fewer political obstacles.
Deployment Speed by Approach
Years from decision to operational capacity โ retrofit wins on time-to-impact
We privilege solutions that can retrofit into the existing global fleet of ~4,000 cement plants. If a pathway requires building entirely new infrastructure, its scaling timeline may exceed the window in which it can make a climate difference.
Regional Deployment: No Single Solution Fits Everywhere
Cement is not traded globally. Concrete is rarely transported more than 100 miles. Markets are inherently regional ecosystems with different feedstock availability, regulatory regimes, energy costs, workforce capacity, and infrastructure maturity.
A solution that only works in Europe โ where carbon pricing, abundant gas infrastructure, and skilled workforces enable CCS โ does not solve cement in sub-Saharan Africa, where clay is abundant but capital is scarce. A pathway dependent on wealthy consumer demand is irrelevant to the Global South, where most new building will occur.
Therefore, global decarbonization requires a portfolio of regionally appropriate solutions. This table shows the structural fit between pathways and geographic contexts:
Regional Pathway Fit
Which solutions work where โ structural fit based on feedstock, infrastructure, and economics
| Pathway | Asia-Pacific | Europe | N. America | ME / Africa | Lat. America |
|---|---|---|---|---|---|
| SCMs (Slag/Fly Ash) | |||||
| LC3 / Calcined Clay | |||||
| Natural Pozzolans | |||||
| CCS (Storage) | |||||
| CCU (Utilization) | |||||
| COโ Mineralization | |||||
| Efficiency / Retrofit | |||||
| Alt Fuels |
The table makes a critical point visible: no single pathway is universally green. LC3 and efficiency retrofits come closest to universal deployment potential, which is why they receive structural priority in our framework. But CCS, alternative fuels, and mineralization each play essential roles in specific regional contexts.
Scale That Matters
The cement industry produces over 4 billion tons per year across every continent, every climate, every regulatory regime. Solutions that work under ideal conditions but collapse under growth pressure are not scalable โ they are demonstrations. We invest in pathways whose feedstocks exist at industrial volume, whose deployment can leverage the existing global fleet of plants, and whose regional adaptability makes them credible in Mumbai, Nairobi, and Sรฃo Paulo โ not just Munich and Montreal.
Sources & Citations (10)
- World Steel Association, "World Steel in Figures 2024." Global blast furnace iron production ~1.3 Bt/yr producing ~300 kg slag per ton of iron.
- ResearchGate (2023), "Global Fly Ash Production and Utilization." Estimated ~800 Mt/yr total fly ash generated from coal-fired power globally.
- GCCA Concrete Future 2050 Roadmap. Notes declining fly ash availability as coal power retires; recommends calcined clay alternatives.
- EPFL LC3 Project / Scrivener et al. (2018), "Calcined clay limestone cements (LC3)." Cement and Concrete Research, 114, 49-56.
- USGS Mineral Commodity Summaries (2024). Pumice and pumicite deposits; global volcanic ash resource estimates.
- Glass Packaging Institute (2023). Global glass container production ~50 Mt/yr; total glass waste stream ~130-200 Mt/yr incl. flat & specialty glass.
- IEA (2024), "CCUS Projects Database." Projects 5+ Gt/yr COโ storage need by 2050; current operational capacity ~50 Mt/yr.
- Kearns et al. (2017), "Constructing a Prudent Estimate of COโ Storage Capacity." Prudent global geological storage estimate ~1,460 Gt COโ.
- Hepburn et al. (2019), ACS Energy Letters. CCU in concrete, chemicals, and minerals could utilize ~6.2 Gt COโ/yr globally by 2050.
- CarbonCure Technologies (2024). Cumulative COโ mineralized ~540 kt across 700+ plants; Solidia Technologies ~4 kt.
Explore the next pillar โ Carbon โ to understand why not all COโ reductions are created equal and how measurement integrity determines investability.