Europe’s decarbonisation push is increasing the commercial relevance of emissions from iron ore processing, direct reduced iron (DRI) and alloy production as carbon accounting moves further into the steel supply chain. For suppliers selling into the EU, product quality and benchmark prices remain central, while verified carbon intensity is increasingly used to assess feedstock costs.
The Carbon Border Adjustment Mechanism (CBAM) also applies upstream of finished steel. Agglomerated iron ores and concentrates under CN 2601 12 00, including iron ore pellets, are covered, alongside pig iron, DRI and most of the iron and steel chain. This means carbon exposure can arise at the pellet-production stage rather than only when finished coils, beams or pipes enter the EU.
Iron ore processing emissions enter procurement comparisons
European steelmakers are developing production routes that combine higher-grade iron ore with natural-gas- or hydrogen-based DRI and electric furnaces. Traditional blast-furnace production relies heavily on coke and coal, while newer routes aim to reduce emissions through different feedstocks, fuels and processing technologies. As a result, competition for suitable iron ore and lower-emission intermediate products is becoming more significant.
Iron content, impurities and particle-size distribution continue to drive iron ore purchasing decisions. However, emissions linked to processing and downstream use can also affect the economics of a shipment. Lower-grade ore may require additional beneficiation or higher reductant consumption later in the chain, potentially raising the overall carbon burden.
High-grade pellets produced with efficient equipment and lower-carbon electricity and fuels may offer an advantage when emissions influence import costs. The commercial distinction increasingly depends on both physical feedstock properties and the ability to substantiate its production footprint. For pellet producers outside the EU, this creates a choice between using applicable CBAM default values or building monitoring, reporting and verification systems for actual emissions data.
Under the definitive CBAM rules for iron and steel, default values face mark-ups that rise from 10% in 2026 to 20% in 2027 and 30% from 2028 onward. Where verified actual emissions are materially below the applicable default, reliable documentation can improve a product’s carbon-cost position.
DRI imports and pig iron route differences
DRI has a distinct role in the steel transition because it is both an intermediate steelmaking material and an alternative to conventional blast-furnace iron. As Europe expands electric steelmaking capacity, domestic DRI output may be limited by natural gas availability and cost as well as low-carbon hydrogen supply. These constraints increase the relevance of cross-border supply for European mills.
Imports of DRI and hot-briquetted iron (HBI) can therefore be part of European mills’ feedstock mix. Under CBAM, buyers must consider not only price and metallisation but also emissions at the producing installation and the energy system supplying it. Pig iron faces a related procurement challenge because conventional blast-furnace routes typically have a higher carbon burden than DRI production using low-carbon energy.
When embedded emissions and associated CBAM certificate requirements are incorporated into comparisons, a lower headline price for pig iron may not result in a lower carbon-adjusted cost. Differences in production routes are thus becoming more important within commercial specifications for imported iron units.
Ferroalloys: selective coverage affects carbon-adjusted costs
CBAM treatment for ferroalloys is selective rather than uniform. Ferromanganese, ferrochrome and ferronickel fall under the iron and steel chapter, bringing major third-country smelting operations within scope. These alloys can require substantial electricity and reductants.
The emissions profile for each alloy depends on factors including electricity source, furnace efficiency, ore grade, reductant consumption and process design. Producers using lower-carbon electricity may therefore have a different carbon-adjusted position than competitors relying on more emissions-intensive power. Ferrochrome is particularly relevant to stainless-steel production because Europe relies heavily on imported chromium units and external ferrochrome production.
Procurement teams may need installation-specific emissions information in addition to benchmark alloy prices and freight costs to evaluate total supply cost under CBAM. This requirement links alloy sourcing decisions more directly to documented upstream emissions performance.
Ferronickel versus refined nickel classification outcomes
Customs classification and production stage can determine CBAM exposure for nickel-related materials. Ferronickel is covered under CBAM, while refined nickel classified under Chapter 75 is generally outside current CBAM scope. This can lead to different border-carbon treatment for materials serving related stainless-steel and nickel value chains depending on classification.
The current exclusions extend beyond nickel-related categories to include ferro-silicon, ferro-silico-manganese, ferro-silico-chromium, ferromolybdenum, ferro-tungsten, ferrovanadium and ferroniobium, along with several other ferroalloys not included in the current iron-and-steel list. As a result, CBAM does not apply a consistent carbon adjustment across all alloying materials.
For trading companies handling covered and uncovered alloys from the same supplier portfolio, precise classification becomes necessary alongside shipment-level documentation. Traders need to identify which installation produced each consignment, whether its emissions have been verified, whether a carbon price has already been paid in the country of origin, and how evidence reaches the EU importer.
Contracting shifts toward traceable upstream emissions data
The implications extend beyond customs administration for steelmakers purchasing pellets, DRI and ferroalloys. These inputs can affect final steel product emissions intensity as well as how buyers support green-steel premiums tied to product-footprint requirements. Securing lower-emission inputs can strengthen a mill’s position before material reaches melting stages.
This increases the value of supply arrangements combining reliable volumes with documented emissions performance. Multi-year offtake agreements may become more relevant than anonymous spot-market purchases for some materials. Producers developing lower-carbon pellet or DRI capacity may seek long-term contracts with European mills that value both supply security and traceable emissions data.
Contracts can set requirements for data sharing, verification rights, emissions methodologies, changes in law and allocation of CBAM-related costs. Such provisions define how carbon information and financial exposure move through the supply chain.
Energy availability shapes where pelletisation, DRI and alloys develop
The economics of pelletisation, DRI production and ferroalloy manufacturing also depend on where suitable resources and energy supplies are available. Regions with abundant renewable electricity, access to natural gas, low-carbon hydrogen potential or high-grade ore may be positioned to develop these activities.
Potentially advantaged locations mentioned include parts of Scandinavia, the Middle East, North Africa and Canada alongside other markets with low-carbon power. Conversely, coal-intensive production hubs may face greater pressure as emissions become more relevant to supplying European customers under CBAM-linked cost comparisons.
The attractiveness of these locations depends on more than carbon intensity alone. Feedstock access, energy availability, production costs, logistics and the ability to deliver material meeting industrial specifications remain part of investment calculations.
Scrap availability links DRI demand with carbon-related costs
Europe’s scrap market forms another element of changing raw-material balances for steelmaking inputs. Electric furnaces can use high proportions of recycled ferrous material but substitution depends on scrap quality, residual elements and available volumes. High-quality DRI and HBI can supplement scrap-based steelmaking as cleaner iron units that help manage feedstock quality.
The value of these inputs is linked not only to iron ore and gas prices but also to scrap spreads and carbon-related costs. For lenders financing pellet plants, DRI facilities or ferroalloy projects, scenarios need to account for electricity carbon intensity alongside EU ETS and CBAM exposure, default-value mark-ups and verification expenses.
Lenders’ assessments also consider logistics plus natural gas or hydrogen availability as well as premiums available for lower-emission feedstock. Carbon data’s commercial role extends across mines, concentrators, pellet plants, DRI modules and ferroalloy furnaces as well as blast furnaces and electric arc furnaces where steel is produced.
The ability to document upstream emissions increasingly influences how suppliers compete for European steelmaking demand under CBAM coverage that reaches beyond finished products into earlier stages such as pellets, DRI intermediates and covered alloys.