Europe’s decarbonisation drive is increasing the commercial relevance of emissions from upstream steel inputs, including iron ore processing, direct reduced iron (DRI) and alloy production. For suppliers selling into the EU, product quality and benchmark prices remain central, while verified carbon intensity is becoming part of how industrial buyers assess feedstock costs.
The Carbon Border Adjustment Mechanism (CBAM) applies beyond finished steel products. It covers agglomerated iron ores and concentrates under CN 2601 12 00, including iron ore pellets, as well as pig iron, DRI and most of the iron and steel chain. This means carbon exposure can occur at the pellet-production stage rather than only when finished coils, beams or pipes enter the EU.
Upstream coverage becomes more significant as European steelmakers develop 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 approaches aim to cut emissions through different feedstocks, fuels and processing technologies. In that context, competition for suitable iron ore and lower-emission intermediate products is gaining weight.
Iron ore processing emissions tied to feedstock economics
Iron content, impurities and particle-size distribution remain key criteria in iron ore purchasing. Emissions linked to processing and downstream use can also affect the economics of a shipment. Lower-grade ore may require additional beneficiation or greater reductant consumption later in the production chain, potentially raising the overall carbon burden.
High-grade pellets produced with efficient equipment, lower-carbon electricity and lower-emission fuels may offer an advantage where 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, then 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 procurement under CBAM
DRI occupies a distinct role in the steel transition because it functions as an intermediate steelmaking material and an alternative to conventional blast-furnace iron. As Europe expands electric steelmaking capacity, domestic DRI output may be constrained by the availability and cost of natural gas and low-carbon hydrogen. That dynamic increases the relevance of imported DRI for European mills.
Imports of DRI and hot-briquetted iron (HBI) can therefore be part of a mill’s feedstock mix. Under CBAM, purchasing decisions need to 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 generally have a higher carbon burden than DRI production using low-carbon energy.
When embedded emissions and associated CBAM certificate requirements are reflected in comparisons, a lower headline price for pig iron may not correspond to a lower carbon-adjusted cost. As a result, production route details are increasingly important in commercial specifications for imported iron units.
Ferroalloy scope varies by product classification
CBAM treatment for ferroalloys is selective rather than uniform. Ferromanganese, ferrochrome and ferronickel are covered through the iron and steel chapter, exposing major third-country smelting operations to the mechanism. These alloys can require substantial electricity and reductants.
The emissions profile for covered ferroalloys 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 from 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.
Buyers comparing alloy benchmark prices and freight costs may also need installation-specific emissions information to evaluate total supply cost under CBAM. For ferronickel, customs classification and production stage determine exposure: ferronickel is covered while refined nickel classified under Chapter 75 is generally outside current CBAM scope.
This classification difference can lead to different border-carbon treatment for materials serving related stainless-steel and nickel value chains. Current exclusions include ferro-silicon, ferro-silico-manganese, ferro-silico-chromium, ferromolybdenum, ferro-tungsten, ferrovanadium, ferroniobium and several other ferroalloys not included in the current iron-and-steel list. The mechanism therefore does not apply a consistent carbon adjustment across all alloying materials.
Traceability requirements move into contracting
The selective coverage creates operational needs for trading companies handling both covered and uncovered alloys from the same supplier portfolio. Traders must establish 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.
For steelmakers, consequences extend beyond customs administration into procurement choices that affect final steel product emissions intensity. The selection of pellets, DRI and ferroalloys can also influence commercial cases for green-steel premiums and customers’ product-footprint requirements. Securing lower-emission inputs can strengthen a mill’s emissions 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 where producers develop lower-carbon pellet or DRI capacity. Such contracts can specify data sharing requirements, verification rights, emissions methodologies, changes in law considerations and allocation of CBAM-related costs.
Energy access shapes where capacity develops
The economics of pelletisation, DRI and ferroalloy production are linked to 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 better positioned to develop these activities. Potentially advantaged locations cited include parts of Scandinavia, the Middle East, North Africa and Canada.
The same energy-linked logic applies more broadly across 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. However, location attractiveness depends on more than carbon intensity.
Feedstock access, energy availability, production costs, logistics and the ability to deliver material meeting industrial specifications remain part of investment calculations alongside carbon-related factors.
Scrap availability links DRI demand to carbon-related costs
Europe’s scrap market contributes to changes in raw-material balance under decarbonisation pathways. Electric furnaces can use high proportions of recycled ferrous material, reducing reliance on primary iron units. Substitution remains limited by scrap quality constraints including residual elements as well as available volumes.
High-quality DRI and HBI can supplement scrap-based steelmaking as cleaner iron units that help manage feedstock quality. Their value links not only to iron ore and gas prices but also to scrap spreads and carbon-related costs under EU policy frameworks affecting supply economics.
For lenders financing pellet plants, DRI facilities or ferroalloy projects, scenario testing expands beyond commodity inputs. Financial models need variables such as electricity carbon intensity alongside EU ETS and CBAM exposure, default-value mark-ups under CBAM rules, verification expenses and logistics considerations tied to natural gas or hydrogen availability.
The role of carbon data extends across mines, concentrators, pellet plants, DRI modules and ferroalloy furnaces as well as blast furnaces and electric arc furnaces where steel is produced. Documenting upstream emissions is becoming a factor in how suppliers compete for European steelmaking demand under CBAM-linked procurement decisions.