EU selects 46 raw-material projects as refining costs threaten 2030 capacity goals

The European Commission selected 46 additional strategic projects in 16 EU member states on 9 October 2026, expanding an earlier project pipeline as Europe seeks to build domestic raw-material processing capacity. High energy costs, environmental safeguards and the commercial economics of refining could complicate efforts to meet the bloc’s 2030 targets while maintaining a strong carbon-price signal for energy-intensive industry.

Targets do not ensure commercial output

The Critical Raw Materials Act sets benchmarks for the EU to extract at least 10% of its annual needs domestically, process 40% and recycle 25% by 2030. It also sets a diversification goal of limiting reliance on any one third country at a given processing stage.

Those figures are strategic capacity objectives, not guarantees that proposed plants will operate commercially or that their materials will be available at globally competitive prices. New mining and refining capacity could diversify supply and replace higher-emissions imports, but high energy costs and environmental safeguards can make projects uneconomic.

Turning mineral concentrate into a usable chemical or metal is often the most difficult supply-chain stage. Copper ore production does not by itself provide the cathodes needed by cable makers, spodumene output is not battery-grade lithium hydroxide, and mixed rare-earth concentrates cannot be used directly in electric motors.

Conversion requires energy, reagents, skilled staff, environmental controls, continuous process optimisation and reliable waste management. A refinery can therefore have greater capital costs and a more complex commercial challenge than the mineral-resource narrative suggests.

The International Energy Agency’s 2026 critical-minerals assessment says global processing concentration remains high and announced upstream mining expansions are not matched by sufficient refining and downstream manufacturing capacity. The agency warns that refining projects outside dominant supplier countries can face substantially higher capital and operating costs.

Energy, inputs and carbon costs

A processing plant’s unit cost depends on electricity intensity, fuel mix, reagent consumption, recovery rate, availability, water requirements, by-product credits and effluent treatment. An expensive electricity supply contract can erase the cost advantage of a favourable ore price.

Securing a mineral deposit and receiving strategic designation do not ensure a plant can operate. A project may still lack a power connection, reagent supply or waste-treatment capacity; some facilities depend on acid, oxygen or caustic soda supplied through separate markets.

Feasibility studies should account for supplier failures and utility curtailments, because nameplate operating-cost estimates can be unrealistic when ramp-up and unplanned downtime are included. Specialised processing-equipment suppliers may control software and maintenance parts for years, making technology licensing, guarantees and commissioning performance important alongside advertised tonnage.

European projects can face costs under the EU Emissions Trading System (EU ETS) when operations fall within its installation and activity scope. The direct perimeter of the Carbon Border Adjustment Mechanism (CBAM) does not cover every critical mineral or refined input.

A CBAM charge should not be assumed to apply to all concentrates simply because a downstream metal belongs to a covered sector. The relevant customs code and emissions method matter at each border crossing; transport costs, rules of origin, free-trade arrangements and the actual product scope also need separate assessment.

A concentrator in the Western Balkans could supply an EU refinery, while a Turkish metallurgical plant could provide finished alloys to EU customers. The location of processing and how products enter the EU depend on transport costs, rules of origin, free-trade arrangements and the product’s actual scope.

More targeted policy support could include shared testing laboratories, skilled-workforce programmes, long-term electricity contracts and recycling collection systems to reduce costs across multiple plants. Governments should assess whether projects build reusable industrial capability or depend on incentives for a single site without developing a wider ecosystem.

For EU customers, qualified annual output of a specified material is a more useful indicator than the combined theoretical capacity announced across projects. A strong European raw-material strategy would connect offtake, power procurement, capital finance and technology transfer with project permits.

Without coordination between permits, offtake, power, finance and technology, strategic designations could produce project announcements while manufacturers continue buying the same refined inputs from abroad. Carbon pricing will reward lower emissions only when an industrial chain exists to deliver the materials.

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