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EU Aluminium Import Needs
A data-driven eBriefing on the European Union's aluminium import needs and external supply, analysing major supplier countries, import prices, sourcing competitiveness and the growing impact of CBAM on access to the EU market.
eBriefing DaaS · 12-month cloud-based access · Updated during the subscription period
Executive Summary
Aluminium is a strategically important input for European industry, including automotive manufacturing, aerospace, construction, electrical equipment, renewable energy technologies, packaging and defence-related supply chains.
The European Union remains strongly dependent on external aluminium supplies. In 2024, the EU imported approximately €29.5 billion of aluminium and related articles under HS Chapter 76. Norway was the largest external supplier in value terms, followed by China, Türkiye, Iceland and Switzerland.
From 1 January 2026, the definitive phase of the Carbon Border Adjustment Mechanism (CBAM) introduced an additional carbon-related dimension into aluminium sourcing decisions.
Import competitiveness therefore increasingly depends not only on the commercial price of aluminium, but also on the origin of the product, the production route, verified embedded emissions, applicable default values, the EU ETS-linked CBAM certificate price, and any eligible carbon price already effectively paid in the country of production.
What EUALU measures
EUALU separates three different concepts that should not be confused:
1. Customs import unit value — the statistical value of imports divided by imported net mass.
2. Carbon-value reference — the monetary value obtained by multiplying embedded emissions by the applicable CBAM certificate price.
3. Actual CBAM liability — the number of CBAM certificates ultimately required after the applicable regulatory adjustments, including the free-allocation adjustment and eligible deductions for carbon prices effectively paid in the country of production.
1. EU Aluminium Demand and Import Dependence
Eurostat reported that EU imports of aluminium and related articles reached €29.5 billion in 2024, compared with €18.4 billion of exports, producing an EU trade deficit of approximately €11.1 billion.
Leading EU aluminium suppliers by import value — 2024
| Supplier | EU import value | Share |
|---|---|---|
| Norway | €4.4 bn | 15.0% |
| China | €3.9 bn | 13.1% |
| Türkiye | €2.8 bn | 9.4% |
| Iceland | €2.1 bn | 7.3% |
| Switzerland | €1.7 bn | 5.8% |
Source: Eurostat. These figures cover HS Chapter 76 — aluminium and articles thereof — and must not be interpreted as CN 7601 prices or volumes.
2. Unwrought Aluminium (CN 7601): The Core Import Benchmark
EUALU uses CN 7601 — unwrought aluminium as its principal benchmark product because it provides a much more meaningful basis for comparing major primary and secondary aluminium suppliers than the entire HS Chapter 76.
Finished and semi-finished products such as plates, sheets, foil, profiles and tubes should be analysed separately because their customs values and CBAM default values differ materially.
3. Comparing EU Aluminium Import Prices
The resulting figure is expressed in €/tonne. It is an average customs unit value, not an LME quotation and not necessarily the contractual price paid by an individual buyer.
Eurostat international trade statistics report imports on a CIF basis — cost, insurance and freight to the EU border.
4. How CBAM Changes EU Aluminium Sourcing
The definitive CBAM regime has applied since 1 January 2026. EU importers covered by the mechanism must declare embedded emissions associated with CBAM goods and surrender the corresponding number of CBAM certificates in accordance with the applicable rules.
The price of CBAM certificates is linked to the EU ETS allowance price. For 2026, the European Commission publishes one price for each calendar quarter.
5. The Carbon Price Component: 2026 CBAM Certificate Prices
| Quarter | CBAM certificate price | Publication |
|---|---|---|
| Q1 2026 | €75.36/tCO₂e | 7 April 2026 |
| Q2 2026 | €75.28/tCO₂e | 6 July 2026 |
| Q3 2026 | Pending | 5 October 2026 |
| Q4 2026 | Pending | 4 January 2027 |
One CBAM certificate corresponds to one tonne of CO₂ equivalent for the purposes of the mechanism. From 2027, the Commission will calculate and publish CBAM certificate prices weekly.
6. Carbon Intensity of External Suppliers
Where the applicable CBAM rules require the use of default values, Commission Implementing Regulation (EU) 2025/2621, as corrected by Implementing Regulation (EU) 2026/1740, establishes country- and product-specific values.
For aluminium, the regulatory default value receives a 10% mark-up in 2026, 20% in 2027 and 30% from 2028 under the rules currently applicable.
7. Comparing the Carbon Exposure of EU Suppliers
The following table compares selected major or strategically relevant suppliers of unwrought aluminium. The figures are based on the official 2026 CBAM default values for CN 7601 where applicable.
| Origin | Base default tCO₂e/t |
2026 default incl. 10% mark-up |
Carbon-value reference at €75.28 |
CBAM position |
|---|---|---|---|---|
| Norway | -- | -- | €0 | Outside CBAM scope |
| Iceland | -- | -- | €0 | Outside CBAM scope |
| India | 1.870 | 2.057 | €154.87/t | CBAM applies |
| United Arab Emirates | 1.870 | 2.057 | €154.87/t | CBAM applies |
| Bahrain | 1.870 | 2.057 | €154.87/t | CBAM applies |
| Canada | 1.960 | 2.156 | €162.30/t | CBAM applies |
| South Africa | 2.358 | 2.594 | €195.27/t | CBAM applies |
| Mozambique | 3.198 | 3.518 | €264.84/t | CBAM applies |
Carbon-value reference = 2026 CBAM default value including the applicable 10% mark-up × Q2 2026 CBAM certificate price of €75.28/tCO₂e. This is a comparative analytical indicator and must not be interpreted as the final CBAM amount payable. The actual number of certificates to be surrendered is subject to the CBAM free-allocation adjustment and other applicable rules.
8. From Import Price to Carbon-Adjusted Competitiveness
The comparison immediately shows that the carbon component can alter the relative attractiveness of suppliers even before the final CBAM liability is calculated.
Under the 2026 default-value methodology, one tonne of CN 7601 from India, the UAE or Bahrain carries a carbon-value reference of about €155/t, while the corresponding reference for Mozambique is approximately €265/t.
The difference is approximately €110 per tonne of aluminium.
9. Verified Emissions and Supplier Competitiveness
Country default values are not a substitute for verified installation data.
Two aluminium producers located in the same country may use different electricity sources, smelting technologies, anode processes and precursor inputs. Their actual embedded emissions can therefore differ significantly.
This creates an increasingly important commercial incentive for low-emission producers to provide reliable, verifiable emissions data to their EU customers.
10. The Effective Cost of Imported Aluminium
EUALU therefore analyses supplier competitiveness through several layers rather than through the customs import price alone.
Where relevant, the analysis should also take into account transport, financing, insurance, logistics and other identifiable border-related costs.
11. Carbon Pricing in Supplier Countries
CBAM rules allow an importer to claim a reduction where it can demonstrate that a carbon price has already been effectively paid in the country of origin for the emissions embedded in the imported goods, subject to the applicable legal and evidentiary conditions.
Consequently, the relevant comparison is not simply between countries with and without a carbon-pricing system. What matters is the carbon price effectively attributable to the imported goods and recognised under the CBAM rules.
12. India as an Emerging EU Aluminium Supplier
India is particularly relevant for EUALU because its aluminium industry combines significant production capacity with growing trade ambitions in the European market.
For CN 7601, the official CBAM default value used in this comparison is 1.870 tCO₂e/t, rising to 2.057 tCO₂e/t in 2026 after the applicable 10% default-value mark-up.
At the Q2 2026 CBAM certificate price of €75.28/tCO₂e, this produces a gross carbon-value reference of approximately €154.87 per tonne of unwrought aluminium.
For Indian producers, the strategic issue is therefore not only tariff access to the EU. The ability to document verified installation-specific emissions and demonstrate lower carbon intensity may become a direct competitive advantage.
13. India: Trade Opportunities and CBAM Constraints
Preferential customs treatment and CBAM are separate regulatory mechanisms.
A future preferential tariff under the EU–India Free Trade Agreement would therefore not, by itself, eliminate CBAM obligations for Indian aluminium covered by the mechanism.
14. Norway and Iceland: The CBAM-Free Supply Advantage
Norway and Iceland occupy a special position in the EU aluminium supply chain.
Under Annex III of Regulation (EU) 2023/956, goods originating in Norway and Iceland are outside the territorial scope of CBAM.
Their competitive position should therefore not be compared with CBAM-covered suppliers by assigning them an artificial emissions cost. For the purposes of EUALU's CBAM comparison, their CBAM exposure is shown as €0.
15. Comparing EU Aluminium Supply Sources
A useful sourcing comparison requires more than one indicator. EUALU therefore separates trade, carbon and regulatory variables.
16. EU Supplier Competitiveness Matrix — CN 7601
| Supplier | CBAM status | 2026 default tCO₂e/t |
Carbon-value reference €/t |
Carbon-price deduction | Verified-data opportunity | Strategic reading |
|---|---|---|---|---|---|---|
| Norway | Outside scope | -- | €0 | Not applicable | Not required for CBAM | Structural CBAM advantage |
| Iceland | Outside scope | -- | €0 | Not applicable | Not required for CBAM | Structural CBAM advantage |
| India | CBAM | 2.057 | €154.87 | Possible if eligible and proven | High relevance | Competitive position can improve with verified low-emission production |
| UAE | CBAM | 2.057 | €154.87 | Possible if eligible and proven | High relevance | Same CN 7601 default reference as India |
| Bahrain | CBAM | 2.057 | €154.87 | Possible if eligible and proven | High relevance | Same CN 7601 default reference as India and UAE |
| Canada | CBAM | 2.156 | €162.30 | Possible if eligible and proven | High relevance | Slightly higher default carbon reference |
| South Africa | CBAM | 2.594 | €195.27 | Possible if eligible and proven | Very high relevance | Verified data may materially affect competitiveness |
| Mozambique | CBAM | 3.518 | €264.84 | Possible if eligible and proven | Very high relevance | Highest default carbon reference in this comparison |
The matrix is a sourcing-intelligence tool, not a customs or CBAM assessment for an individual shipment. “Carbon-value reference” uses the Q2 2026 CBAM certificate price of €75.28/tCO₂e and the applicable 2026 default value including the 10% mark-up. It is not the final CBAM liability.
17. Why Verified Emissions Data Affect Market Access
CBAM creates a direct connection between environmental data quality and market competitiveness.
A producer whose verified actual emissions are lower than the applicable default value can potentially offer its EU customers a more attractive carbon profile.
Consequently, emissions monitoring, verification and data exchange are becoming part of the commercial relationship between aluminium producers and European buyers.
18. EU Import Needs Beyond Unwrought Aluminium
EUALU monitors other aluminium products separately, including:
CN 7603 — aluminium powders and flakes
CN 7604 — aluminium bars, rods and profiles
CN 7605 — aluminium wire
CN 7606 — aluminium plates, sheets and strip
CN 7607 — aluminium foil
CN 7608 — aluminium tubes and pipes
and other aluminium products falling within the CBAM scope.
These products should not be mixed with CN 7601 when calculating import unit values or supplier competitiveness because processing stages and embedded-emissions values differ.
19. Aluminium Scrap, Recycling and Circular Supply
Chapter updated: 30 September 2026 · Trade baseline: 2023–2024, as verified for this edition.
Aluminium scrap is a commercially valuable feedstock for secondary production. Its availability connects collection and sorting, recycling investment, industrial demand and international trade. EUALU therefore analyses CN 7602 — aluminium waste and scrap separately from unwrought aluminium and finished products.
Recycling can reduce reliance on primary production, but tonnes of collected scrap are not equivalent to tonnes of usable secondary metal. Alloy composition, contamination, sorting losses and melting yield determine which products can be made and at what cost. A growing scrap supply can coexist with shortages of particular grades.
19.1. Classification: Customs Code, Waste Status and Quality
Three separate checks are required: the customs code, the waste classification and whether the material has legally ceased to be waste. Metallic, non-dispersible aluminium scrap may fall under Basel entry B1010. Contamination or other characteristics can change the applicable shipment controls. CN 7602 alone does not establish eligibility for a simplified waste-shipment procedure.
Commercial specifications should distinguish clean production scrap from post-consumer material, mixed alloys, turnings and other grades. Residues such as dross and hazardous material must not automatically be treated as clean aluminium scrap.
19.2. Waste Shipments: Operational Rules
Regulation (EU) 2024/1157 governs waste shipments. The applicable procedure depends on classification, origin, destination and recovery or disposal operation.
| Route / material | Practical requirement |
|---|---|
| Eligible green-listed waste for recovery within the EU | General information requirements under Article 18, normally including Annex VII information and a contract; the threshold is shipments exceeding 20 kg. |
| Hazardous, unlisted or otherwise controlled waste | Prior written notification and consent where required; do not dispatch on the basis of a customs declaration alone. |
| Imports into the EU for recovery | Check the permitted origin-country framework, including OECD or Basel Convention status, applicable agreements and the shipment procedure. |
| Exports for recovery to OECD destinations | Destination and classification controls remain applicable; OECD membership does not remove environmental compliance obligations. |
| Green-listed exports to non-OECD destinations from 21 May 2027 | Check the final EU authorisation list for both the destination and the waste stream, plus destination-country requirements. |
For exports, the new facility-audit provisions require advance verification of environmentally sound management, subject to the Regulation’s applicable exceptions. Article 46 specifies an audit carried out no more than two years before export. Check the operative text and transitional provisions for each shipment.
19.3. Key Dates and Current Regulatory Status
- 20 May 2024: the new Waste Shipment Regulation entered into force.
- 21 May 2026: most provisions became applicable; DIWASS, the digital waste-shipment system, went live.
- 18 September 2026: the Commission published a draft list of non-OECD destinations for specified non-hazardous waste. Consultation remains open until 16 October 2026; the Commission expects the first final list by the end of 2026.
- 21 May 2027: most new export provisions apply. Green-listed waste exports to non-OECD countries will generally be prohibited unless the destination and relevant waste stream are authorised.
The Commission also introduced customs surveillance of aluminium and other metal scrap imports and exports on 23 July 2025. Separately, it consulted on a targeted trade instrument to retain more aluminium scrap in Europe. Surveillance, preparatory consultations and legally applicable export measures are different instruments: an announced policy objective does not establish a payable export duty.
19.4. End-of-Waste: When Scrap Becomes a Secondary Raw Material
Regulation (EU) No 333/2011 establishes EU end-of-waste criteria for aluminium scrap. These address input material, treatment, output quality, a verified quality-management system and a statement of conformity. Among the output criteria, foreign materials must be no more than 5% by weight, or metal yield must be at least 90%. Meeting this threshold alone does not satisfy all requirements.
A commercial description such as “recycled raw material” is insufficient to establish end-of-waste status. Where compliant material has ceased to be waste, the waste-shipment regime no longer applies on that basis; customs classification, product requirements and the treatment of its status in the destination jurisdiction still need checking.
19.5. EU External Trade: Quantity, Value and Unit Value
The following matched annual series uses the European Union aggregate reported in WITS / UN Comtrade, HS 760200. It measures external trade rather than adding Member States’ trade with each other. Quantities are converted from kilograms to tonnes; values are shown in USD million.
| Flow | Year | Quantity (t) | Value (USD million) | Unit value (USD/t) |
|---|---|---|---|---|
| EU exports | 2023 | 1,161,780 | 2,053.78 | 1,768 |
| EU exports | 2024 | 1,257,620 | 2,341.92 | 1,862 |
| EU imports | 2023 | 606,600 | 1,101.51 | 1,816 |
| EU imports | 2024 | 656,430 | 1,278.27 | 1,947 |
Exports: between 2023 and 2024, volume increased by 8.3%, value by 14.0% and average unit value by 5.3%. Imports: volume increased by 8.2%, value by 16.0% and average unit value by 7.2%. Both greater quantities and higher average values contributed to the increase in trade value.
Net exports rose from 555,180 tonnes to 601,190 tonnes. This establishes the EU’s net-export position in this dataset, but does not quantify a domestic scrap shortage. Such an assessment also requires collection, consumption, inventories, recycling capacity and grade-specific demand.
Method: unit value = reported trade value ÷ reported quantity in tonnes, calculated before rounding. These are customs-derived averages, not spot quotations. The series is a historical baseline; no unverified 2025 annual or 2026 year-to-date estimates are included.
19.6. Trading Partners and Exposure to Destination Rules
Selected 2024 partners illustrate the scale of individual trade routes. The selection is not a complete ranking.
| Flow / partner | Quantity (t) | Value (USD million) | Unit value (USD/t) |
|---|---|---|---|
| Export to India | 345,424 | 632.49 | 1,831 |
| Export to Thailand | 157,135 | 303.36 | 1,931 |
| Export to Malaysia | 117,087 | 200.65 | 1,714 |
| Export to Türkiye | 91,281.5 | 161.40 | 1,768 |
| Import from Switzerland | 164,245 | 268.21 | 1,633 |
| Import from the United Kingdom | 127,949 | 225.97 | 1,766 |
| Import from the United States | 43,703.5 | 110.68 | 2,533 |
India accounted for approximately 27.5% of EU scrap export tonnage in 2024. Together, India, Thailand and Malaysia represented approximately 49.7%. These flows make non-OECD authorisation commercially significant. Historical trade volumes do not establish permission to ship after May 2027.
The United States’ higher average import unit value does not, by itself, establish a premium for equivalent material. Grade composition, processing, transport and valuation conventions can explain differences between partners.
19.7. How to Interpret Market Changes
A rise in unit value may reflect stronger metal prices, tighter availability, improved quality or a different mix of traded grades. Conversely, a fall can reflect lower benchmark prices or a greater share of low-yield material. Import values generally include freight and insurance to the importing border, while export values generally use an FOB-type basis; the gap between aggregate import and export unit values is not a trading margin.
Commercial implications — analytical assessment: stricter export conditions could redirect some material towards EU recyclers, supporting local feedstock availability. They could also reduce outlets and returns for collectors, increase compliance costs, or create stock accumulation where domestic processing cannot absorb the available grades. These are conditional effects, not measured forecasts.
Secondary-metal economics should therefore be assessed per tonne of usable output: purchase cost adjusted for metal yield, plus sorting, energy, alloy correction, transport, treatment of residues and compliance costs. A cheaper tonne of scrap may produce a more expensive tonne of usable metal.
19.8. Monitoring Priorities for EUALU
- Trade: track extra-EU imports and exports separately, by partner and consistent CN subheading, with tonnes, total EUR value and EUR/t from Eurostat Comext or the Commission’s surveillance series.
- Comparability: compare identical year-to-date periods and rolling twelve-month totals. Record revisions, missing quantities and changes in country or product coverage.
- Quality: distinguish production scrap, post-consumer scrap and other grades where the source permits; do not infer grade-specific prices from HS 760200 averages.
- Regulation: check the final destination list, authorised waste streams, facility requirements, destination-country restrictions and any separately adopted trade measure.
- Industrial conditions: monitor collection, sorting and recycling capacity, energy costs, inventories and demand for particular secondary alloys.
Before contracting a shipment: confirm customs and waste codes, waste or end-of-waste status, composition and yield, permitted destination, receiving-facility credentials, required documentation and responsibility for rejected or illegal shipments. Contracts should specify quality tolerances, valuation and adjustment mechanisms, and the allocation of regulatory-change risks.
19.9. Sources and Data Notes
- Regulation (EU) 2024/1157 — waste shipments and Commission implementation information; EUR-Lex summary of shipment procedures.
- Application and DIWASS launch, 21 May 2026.
- Draft non-OECD list: Commission announcement, 18 September 2026.
- Regulation (EU) No 333/2011 — end-of-waste criteria.
- Commission customs surveillance and targeted trade-measure consultation.
- WITS / UN Comtrade, EU aggregate, HS 760200: 2023 exports; 2023 imports; 2024 exports; 2024 imports. Calculations by eEuropa; quantities and values retain the source’s reporting precision. USD series must not be labelled as EUR.
© 2026 eEuropa. All rights reserved.
20. Implications for EU Aluminium Buyers
EU aluminium importers should increasingly request clear information on the installation producing the goods, production route, embedded direct emissions, relevant precursor emissions, verification status, applicable CN code and any carbon price effectively paid in the country of production.
Procurement decisions based only on the quoted price per tonne risk overlooking a growing component of the effective EU sourcing cost.
21. Requirements for Non-EU Suppliers
Chapter updated: 2 October 2026. This is a screening matrix by product family and intended use, not an exhaustive shipment-specific legal assessment.
21.1. CBAM verification and practical contacts
Meeting CBAM obligations does not authorise a product to be sold in the EU. Customs, chemical, product-safety and sector-specific requirements must be assessed separately.
For actual embedded emissions, independent verification by a verifier accredited for CBAM by an EU national accreditation body is required. A producer's self-declaration or a general ISO greenhouse-gas certificate does not replace this verification. Official default values are an alternative under the applicable rules; they are not self-certified actual emissions. Verification concerns the production installation and relevant emissions data, rather than a general certificate approving every product made by a company.
Indian verification companies can apply to EU accreditation bodies accepting third-country applicants. Before commissioning work, ask for the CBAM accreditation certificate, its validity and scope covering aluminium, and CBAM Registry registration. The Commission's page currently announces that the verifier list will be published; this edition does not identify an Indian organisation as already CBAM-accredited without documentary confirmation.
- Commission: verification rules, accreditation status and forthcoming verifier directory .
- NABCB, Quality Council of India: [email protected]; +91-11-26186680. NABCB provides national accreditation and information on Indian verification bodies. NABCB accreditation alone must not be represented as EU CBAM accreditation.
- CBAM Registry and third-country installation portal : installation data exchange with authorised importers and accredited verifiers. Registry registration is not itself accreditation or product approval.
21.2. Market-access screening by product and intended use
Start with the exact CN/TARIC code, composition, manufacturing stage, origin, destination Member State and intended use. Check the current rules at the date of import and placing on the market. CE marking applies only where the relevant EU legislation requires it; aluminium content alone does not create a CE-marking obligation.
| Product family / use | Checks before supplying the EU |
|---|---|
| Unwrought aluminium, CN 7601 | Customs classification, origin, duties and trade measures; CBAM scope and importer threshold; installation emissions; REACH/CLP obligations according to whether supplied as a substance, mixture or article and applicable exemptions. |
| Powders, CN 7603; wire and semi-finished metal, CN 7604–7608 | Exact subheading and CBAM coverage; composition and chemical restrictions; safety data/classification where applicable; intended use and customer technical specifications. Do not assume all semi-finished products require CE marking. |
| Profiles or fabricated components intended for construction | Applicable construction-product rules and transitional provisions; relevant harmonised technical specification or assessment route; performance documentation and CE marking where required. A generic profile is not automatically a structural construction product. |
| Foil, containers or other articles intended for food contact | Regulation (EC) No 1935/2004 and GMP Regulation (EC) No 2023/2006; traceability, labelling and evidence of safe use; applicable national metal rules and specific rules for coatings or plastic layers. Check conformity-declaration requirements for the relevant material and destination. |
| Aluminium packaging | Applicable packaging rules, substance limits, recyclability, labelling and producer-responsibility obligations, with their respective application dates; food-contact rules additionally apply where relevant. |
| Automotive, electrical or machinery components | Requirements of the final product and the component's legal status; applicable type-approval or conformity rules, substance restrictions and documentation; distinguish legal requirements from buyer qualification and contractual specifications. |
| Scrap, CN 7602, and secondary feedstock | Waste versus end-of-waste status, shipment procedure, composition and receiving-facility conditions: see Chapter 19. Customs classification alone does not determine waste-shipment permission or end-of-waste status. |
21.3. A readiness dataset for exporters
AL Circle and industry organisations could invite companies to provide a voluntary, confidential survey covering installations, products/CN codes, EU export volumes, monitoring systems, use of actual or default values, verifier accreditation and scope, verification stage, missing product documentation and planned corrective actions. Publish aggregated results with sample size, coverage and reporting period, distinguishing company-reported information from independently verified evidence. A directory of verifiers cannot establish what proportion of producers is ready, and company counts alone do not measure the share of export volume covered.
21.4. Official sources for product-specific checks
- Commission Access2Markets: product requirements and its My Trade Assistant for exact product/origin/destination searches.
- Your Europe: when CE marking is required .
- ECHA: REACH restrictions .
- Commission: food-contact legislation .
22. Opportunities for Indian Aluminium Producers
For Indian aluminium producers, EU market access will increasingly depend on the interaction of trade policy, industrial competitiveness and carbon regulation.
The EU–India trade relationship may improve tariff conditions, but CBAM creates a separate competitive variable. Indian producers able to document efficient, lower-emission production may therefore be better positioned than suppliers relying on regulatory default values.
23. EUALU Supply Monitoring
During the subscription period, EUALU will monitor:
• EU import values and quantities for key aluminium CN codes;
• supplier-level average customs unit values;
• changes in major countries of origin;
• quarterly and weekly CBAM certificate prices;
• changes to CBAM default values and benchmarks;
• verified-emissions methodology and guidance;
• carbon-price deduction rules;
• EU trade measures affecting aluminium;
• EU–India trade developments relevant to aluminium;
• changes in the competitive position of major suppliers.
24. Key EU Aluminium Supply Indicators
| Indicator | Why it matters |
|---|---|
| CN 7601 import unit value | Measures average customs value per tonne by supplier |
| CBAM certificate price | Changes the monetary value of embedded emissions |
| Country default value | Can materially affect exposure where actual verified data are not used |
| Verified installation emissions | Can change the supplier's carbon competitiveness |
| Carbon price paid abroad | May reduce CBAM liability where legally eligible and demonstrated |
| Trade preference / customs duty | Affects landed cost independently of CBAM |
| Production route | Relevant to emissions and CBAM benchmark treatment |
25. Outlook for EU Aluminium Supply
Aluminium sourcing in Europe can no longer be analysed solely through commodity prices and customs tariffs.
The definitive CBAM regime introduces a new measurable variable: the carbon characteristics of imported aluminium.
The 2026 default-value comparison already illustrates significant differences between supplier origins. For CN 7601, the carbon-value reference calculated at the Q2 2026 certificate price ranges from approximately €155/t for India, UAE and Bahrain to approximately €265/t for Mozambique, while Norway and Iceland remain outside CBAM scope.
However, country defaults do not determine the competitiveness of every individual producer. Verified installation-level emissions can substantially change the picture.
The central objective of EUALU is therefore to combine trade price, supplier origin, carbon exposure and regulatory treatment into a single sourcing-intelligence framework.
EUALU Update Framework
This eBriefing is designed as a living Data-as-a-Service product. During the subscription period, eEuropa may update trade data, supplier comparisons, CBAM certificate prices, default emissions values, legal references and market-access information as new official information becomes available.
Main Official Sources
Eurostat — International trade in goods
European Commission — Carbon Border Adjustment Mechanism
European Commission — Price of CBAM certificates
European Commission — CBAM legislation and guidance
EUR-Lex — Regulation (EU) 2023/956 establishing CBAM
EUR-Lex — Commission Implementing Regulation (EU) 2026/1740
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Acronyms and Abbreviations
The following acronyms and abbreviations are used throughout this eBriefing.
| Acronym / Abbreviation | Meaning |
|---|---|
| CBAM | Carbon Border Adjustment Mechanism |
| CCTS | Carbon Credit Trading Scheme (India) |
| CN | Combined Nomenclature |
| CO₂ | Carbon dioxide |
| DaaS | Data as a Service |
| EEA | European Economic Area |
| ETS | Emissions Trading System |
| EU | European Union |
| EU ETS | European Union Emissions Trading System |
| EUALU | eEuropa eBriefing on Aluminium Imports into the European Union |
| FTA | Free Trade Agreement |
| LME | London Metal Exchange |
| MFN | Most-Favoured-Nation |
| MRV | Monitoring, Reporting and Verification |
| PFCs | Perfluorocarbons |
| t | Tonne (metric tonne) |
| tCO₂ | Tonne of carbon dioxide |
| €/t | Euro per tonne |
| €/tCO₂ | Euro per tonne of carbon dioxide |