The EU’s Carbon Border Adjustment Mechanism (CBAM) is creating new competitive distinctions for metals exporters serving the European market. Differences in product coverage, electricity sourcing, industrial emissions and verification capacity are shaping how suppliers are positioned. The mechanism also affects how exporters can substantiate emissions linked to their production.
China, Indonesia, South Africa, Kazakhstan, Turkey and the Western Balkans each hold different roles in European metals and raw-material trade. Under CBAM, competitiveness depends not only on industrial scale and production costs, but also on which goods are exported and whether emissions can be supported with evidence. This means exporters from the same country can face different outcomes based on product portfolios and customs classifications.
Covered versus non-covered materials determine CBAM exposure
CBAM’s scope establishes an initial split between suppliers of materials that fall within the mechanism and those that do not. Iron ore pellets, ferrochrome, ferronickel, steel and aluminium can be covered. Copper cathodes, lithium carbonate, cobalt, graphite and rare-earth oxides generally remain outside the current scope.
As a result, exporters operating in the same country may encounter substantially different conditions in Europe depending on the specific products they ship. Customs classification of individual goods becomes a key factor for determining whether CBAM applies. For investors and trading companies, the customs code and a product’s position within the value chain are increasingly relevant when assessing exposure.
The nickel product mix illustrates how product-level coverage can diverge. Ferronickel is included in CBAM coverage, while several other nickel products are not. Indonesian exporters may therefore experience different European market economics depending on whether they export ferronickel, matte, refined nickel or other intermediate materials.
China’s processing scale varies by facility emissions profile
China combines large-scale processing capacity with integrated supply chains, established infrastructure and extensive industrial clusters. It is a major producer of steel and aluminium and a leading processing centre for multiple critical materials. Within this scale, the emissions profile of production differs across regions and individual facilities.
Coal-intensive electricity can raise the carbon intensity of covered goods produced in China. Additional renewable capacity and more efficient installations can support lower emissions in other locations. CBAM’s treatment of covered goods is linked to embedded emissions and the applicable calculation methodology.
The mechanism also considers whether any carbon price paid is recognised under CBAM. It does not apply a uniform penalty across all production from a given country. A Chinese manufacturer demonstrating low actual emissions may be better positioned than a competitor whose emissions are assessed using higher default values.
Indonesia’s nickel processing faces product-specific CBAM treatment
Indonesia has developed domestic processing capacity through mineral policy and large-scale investment rather than relying only on nickel ore exports. Coal-based electricity has supported much of this industrial expansion. The approach has created a strong cost position in nickel units while some production routes can carry high carbon intensity.
Commercial implications for European trade depend on which material is exported and whether it falls within CBAM’s existing product boundary. The same industrial base can produce outputs that receive different treatment under EU rules. Product classification therefore becomes central to evaluating potential carbon costs and market access for European buyers.
Ferrochrome supply depends on power carbon intensity and verified data
South Africa holds an important position in ferrochrome and other mined materials used in European industry. Ferrochrome is used in European stainless steel production and is included within CBAM coverage. South African smelters have faced persistent electricity-supply challenges that make power carbon intensity a commercial variable.
Producers that secure renewable electricity or improve furnace efficiency may be able to demonstrate lower emissions for covered products. That capability can strengthen their position with European customers seeking covered inputs under CBAM rules. Kazakhstan also combines mining with ferroalloy production and access to comparatively low-cost energy.
Kazakhstan is a major producer of ferrochrome and other metals with strategic geographic connections to Europe. For Kazakh exporters competing for covered categories, competitiveness depends partly on the emissions characteristics of the electricity system. It also depends on whether individual facilities can provide reliable verified emissions information rather than energy costs alone.
Turkey’s MRV needs align with European supply-chain integration
Turkey has close industrial links with Europe and serves as an important partner in steel and metal processing. Its integration into European supply chains creates incentives for exporters to develop systems aligned with monitoring, reporting and verification (MRV) requirements under CBAM. Geographic proximity to EU markets can reduce transport costs and delivery times.
Those logistics advantages may be reduced where production relies on carbon-intensive electricity or where suppliers cannot provide sufficiently robust emissions evidence. For Turkish manufacturers, establishing reliable emissions monitoring and documentation systems is relevant for maintaining access to European industrial customers as carbon-related requirements become more prominent in procurement.
Western Balkans suppliers connect renewable power procurement to export competitiveness
Serbia, Montenegro, Bosnia and Herzegovina, North Macedonia and Albania combine different mixes of steel, aluminium, ferroalloys, mining activities and electricity production. Their proximity to the EU offers opportunities to supply European customers with shorter logistics chains. Competitive positions vary according to industrial structures and the carbon intensity of local electricity systems.
For producers in the region, renewable electricity procurement can have direct implications for covered exports under CBAM. Power procurement arrangements, including renewable power purchase agreements (PPAs), can be linked to plant-level metering, industrial emissions monitoring and documentation needed to substantiate emissions claims.
Where such arrangements support lower verified emissions, they may strengthen relationships with European buyers while reducing expected CBAM burden. The commercial value of electricity investment depends not only on purchased power but also on evidence quality connecting that supply to industrial production.
From 2026, default values versus verified emissions affect importer costs
The verification of embedded emissions is another dividing line between third-country suppliers under CBAM. Starting in 2026, EU importers can use European Commission default values or verified actual emissions under the applicable framework. Default values for iron and steel and aluminium involve increasing mark-ups.
Suppliers without robust monitoring and reporting systems may expose European customers to higher carbon costs than competitors able to provide verified installation-level emissions data. These differences can affect procurement decisions among exporters, traders and importers participating in tenders or contract negotiations.
Banks supporting export-oriented industrial projects may also require investment in metering equipment, data-management systems and independent verification as part of efforts to preserve access to European markets. This financing impact reflects how verification readiness can influence compliance-related requirements for future trade flows.
A proposed downstream extension could broaden coverage beyond basic metals
A proposed extension of CBAM to downstream goods is set out for 2028 with the aim of reducing incentives to relocate fabrication outside Europe followed by imports of finished products containing substantial quantities of steel or aluminium. Coverage figures advanced by institutions differ: the European Commission proposed 180 additional goods, while the Council’s position covered about 200 goods.
The European Parliament’s position included 457 additional goods within its proposal set. These figures reflect institutional positions rather than one agreed final list at this stage. If a broad extension is adopted, manufacturers producing machinery, electrical equipment, appliances and industrial components could become exposed even if they do not currently export basic metals directly.
The potential change could affect global mining supply chains where projects purchase substantial quantities of equipment from China, Turkey and other manufacturing centres. Manufacturers using locally produced steel and aluminium could face greater requirements to document metal inputs and associated emissions when supplying the European market under an expanded scope.
Procurement shifts toward contractual responsibility for verified carbon costs
The competitive landscape increasingly emphasizes electricity origin, production efficiency, product classification and credibility of emissions data alongside conventional factors such as labour costs and electricity prices. For EU importers, sourcing strategies may involve supplier diversification alongside explicit contractual responsibilities for emissions documentation.
Such arrangements may include audit rights as well as provisions governing allocation of unexpected CBAM costs between parties involved in trade flows into Europe. For third-country manufacturers, investment in decarbonisation measures paired with verification capability can strengthen their position when competing for orders subject to CBAM requirements.
The ability to demonstrate actual emissions provides an advantage over suppliers whose carbon exposure is assessed using higher default values under CBAM rules. Market access differences depend on individual installations producing covered goods or inputs within scope categories as well as the availability of emissions evidence provided to European customers rather than solely country-level cost profiles.