Europe’s Carbon Border Adjustment Mechanism (CBAM) is introducing new competitive distinctions among metals suppliers, with product coverage, electricity sources, industrial emissions and verification capabilities shaping the position of exporters serving the European market.
China, Indonesia, South Africa, Kazakhstan, Turkey and the Western Balkans occupy different positions in European metals and raw-material trade. Their competitiveness under CBAM depends not only on production costs and industrial capacity, but also on which goods they export and whether they can substantiate the emissions associated with their production.
Product Coverage Determines Exposure to Carbon Border Costs
The scope of the EU mechanism creates an initial distinction between suppliers of covered and non-covered materials. Iron ore pellets, ferrochrome, ferronickel, steel and aluminium can fall within CBAM, whereas copper cathodes, lithium carbonate, cobalt, graphite and rare-earth oxides generally remain outside its current scope.
Consequently, exporters operating within the same country can face substantially different conditions in the European market, depending on their product portfolios and the customs classifications of individual goods.
The treatment of different nickel products illustrates this distinction. Ferronickel is covered by CBAM, while several other nickel products are not. Indonesian exporters may therefore encounter different European market economics depending on whether they ship ferronickel, matte, refined nickel or another intermediate product.
For investors and trading companies, the precise customs code and position of a product within the value chain are becoming important considerations when assessing exposure to the mechanism.
China’s Industrial Scale Meets Differences in Carbon Intensity
China combines large-scale processing capacity, integrated supply chains, established infrastructure and extensive industrial clusters. It is a major producer of steel and aluminium and a leading processing centre for numerous critical materials.
However, the emissions profile of Chinese production varies considerably between regions and individual facilities. Coal-intensive electricity can increase the carbon intensity of covered goods, while additional renewable capacity and more efficient installations can support lower emissions.
CBAM does not impose a uniform penalty on all production from a particular country. Its treatment of covered goods is linked to embedded emissions, the applicable calculation methodology and any carbon price paid that is recognised under the mechanism.
A Chinese manufacturer able to demonstrate low actual emissions may therefore be better positioned than a competitor in another country whose emissions are assessed using a higher default value.
Indonesia’s Nickel Processing Model Faces Product-Specific Exposure
Indonesia has used mineral policy and large-scale investment to develop domestic processing capacity rather than relying solely on nickel ore exports. Coal-based electricity has supported much of this industrial expansion.
The model has established a strong cost position in nickel units, although some production routes can carry a high carbon intensity. The commercial implications for European trade depend on the specific material being exported and whether it falls within CBAM’s existing product boundary.
This distinction is relevant to producers, traders and investors assessing the economics of Indonesian nickel processing. Different products from the same industrial base may receive different treatment under EU rules, making product classification central to evaluating potential carbon costs and market access.
Ferrochrome Producers Face Electricity and Emissions Pressures
South Africa occupies an important position in ferrochrome and other mined materials. Ferrochrome is used in European stainless steel production and is included within CBAM coverage.
South African smelters have faced persistent electricity-supply challenges, making the carbon intensity of their power supply an important commercial variable. Producers that secure renewable electricity or improve furnace efficiency may be able to demonstrate lower emissions for covered products and strengthen their position with European customers.
Kazakhstan also combines mining, ferroalloy production and access to comparatively low-cost energy. The country is a major producer of ferrochrome and other metals, with strategic geographic connections to Europe.
For Kazakh exporters, competitiveness in covered categories will depend partly on the emissions characteristics of the electricity system and the ability of individual facilities to supply reliable, verified emissions information. Energy costs alone will not determine the relative position of producers competing for European orders.
Turkey’s Supply-Chain Integration Increases the Importance of MRV
Turkey has close industrial links with Europe and serves as an important partner in steel and metal processing. Its integration into European supply chains gives exporters a commercial incentive to develop systems capable of meeting CBAM monitoring, reporting and verification requirements.
Geographic proximity to EU markets can reduce transport costs and delivery times. However, those advantages may be weakened where production depends on carbon-intensive electricity or where suppliers cannot provide sufficiently robust emissions evidence.
For Turkish manufacturers, establishing reliable emissions monitoring and documentation systems is therefore relevant to maintaining access to European industrial customers as carbon-related requirements become more prominent in procurement.
Western Balkan Suppliers Link Electricity Investment to Export Competitiveness
Serbia, Montenegro, Bosnia and Herzegovina, North Macedonia and Albania have differing combinations of steel, aluminium, ferroalloys, mining and electricity production.
Their proximity to the EU offers opportunities to supply European customers with shorter logistics chains. Their competitive positions nevertheless vary with their industrial structures and the carbon intensity of their electricity systems.
For producers in the region, renewable electricity can have direct commercial implications for covered exports. Power procurement arrangements, including renewable power purchase agreements (PPAs), can be connected to plant-level metering, industrial emissions monitoring and the documentation required to substantiate emissions claims.
Where these arrangements support lower verified emissions, they may strengthen relationships with European buyers and reduce the expected CBAM burden. The commercial value of electricity investment consequently depends not only on the power purchased, but also on the quality of the evidence linking that supply to industrial production.
Default Values and Verified Emissions Affect Buyer Costs From 2026
The verification of embedded emissions represents another dividing line between third-country suppliers. From 2026, EU importers can use European Commission default values or verified actual emissions under the applicable CBAM framework.
Default values for iron and steel and aluminium carry increasing mark-ups. Suppliers without robust monitoring and reporting systems may therefore expose their European customers to higher carbon costs than competing manufacturers able to provide verified, installation-level emissions data.
These differences can influence procurement decisions and negotiations between exporters, traders and importers. European buyers may increasingly incorporate emissions-data requirements into tenders, while trading companies may favour suppliers capable of delivering complete supporting documentation.
Financing arrangements can also be affected. Banks supporting export-oriented industrial projects may require investment in metering equipment, data-management systems and independent verification as part of a strategy to preserve access to European markets.
Proposed Downstream Extension Could Expand the Range of Affected Manufacturers
The proposed 2028 extension of CBAM to downstream goods is intended to reduce incentives to relocate fabrication outside Europe and subsequently import finished products containing substantial quantities of steel or aluminium.
The institutions have advanced different proposed coverage figures. The European Commission proposed 180 additional goods, the Council’s position covered approximately 200, and the European Parliament’s position included 457.
These figures represent differing institutional positions rather than a single agreed final list. If a broad extension is adopted, manufacturers in third countries producing machinery, electrical equipment, appliances and industrial components could become exposed to CBAM even where they do not currently export basic metals directly.
The potential change is relevant to global mining supply chains, where projects purchase substantial quantities of equipment from China, Turkey and other manufacturing centres. Manufacturers in those countries that use locally produced steel and aluminium could also face greater requirements to document metal inputs and associated emissions when supplying the European market.
The final scope will determine which additional products are covered and how far the mechanism extends into downstream industrial trade.
Procurement and Industrial Investment Shift Towards Verified Carbon Costs
The emerging competitive landscape places greater emphasis on the origin of electricity, production efficiency, product classification and the credibility of emissions data alongside conventional measures such as labour costs and electricity prices.
For European importers, sourcing strategies may increasingly involve supplier diversification, explicit contractual responsibilities for emissions documentation, audit rights and provisions governing the allocation of unexpected CBAM costs.
For third-country manufacturers, investment in decarbonisation and verification can strengthen their position in European trade. The ability to demonstrate actual emissions provides a potential advantage over competing suppliers whose carbon exposure is assessed using higher default values.
The resulting differences in market access will depend on individual installations, covered products and the emissions evidence available to European customers, rather than solely on the country of origin or nominal cost of production.
