Non-EU exporters have 5 CBAM strategy options: provide verified actual emissions data, accept default values, decarbonize operations, redirect exports away from the EU, or pursue Article 9 recognition through a national carbon pricing scheme.
Non-EU exporters face 5 distinct CBAM strategy options, with the right choice depending on embedded emissions intensity, EU market dependence, and the timeline of cost escalation through 2034. The financial pressure is modest in 2026 (the CBAM factor is only 2.5%, meaning a BF-BOF steel producer pays approximately €3.50 per tonne net), but it reaches €72.75 per tonne for the same producer by 2030 as free allocation phases out. Choosing the wrong CBAM strategy now creates a structural competitive disadvantage that compounds year over year.
The EU carbon border adjustment mechanism applies to six sectors: iron and steel, cement, aluminium, fertilizers, electricity, and hydrogen. For producers in any of these sectors exporting to EU buyers, the commercial mechanics are immediate. EU importers must surrender certificates priced at the EU ETS rate (approximately €70 per tonne CO₂e as of late March 2026), and they need verified embedded emissions data from the production installation to calculate that liability accurately. This article evaluates all 5 strategic options available to CBAM for non-EU exporters and defines the decision criteria for each.
Caption: The 5 CBAM strategy options for non-EU exporters range from immediate data provision to long-term decarbonization, with cost and feasibility differing significantly across sectors.
The 5 CBAM Strategy Options for Non-EU Exporters at a Glance
The 5 strategic responses available to non-EU exporters under Regulation (EU) 2023/956 differ in upfront cost, time horizon, financial outcome, and dependency on third parties. The table below compares all 5 options across the dimensions that matter most for planning:
| Option | Upfront Cost | Time to Implement | Best For | 2030 Cost Impact |
|---|---|---|---|---|
| 1. Provide actual emissions data | €5,000–€50,000 (verifier fee) | 6–18 months | Producers with actual emissions below default | Avoids default mark-up (saves €24–83/t in cement, steel, aluminium) |
| 2. Accept default values | Near-zero | Immediate | Low-EU-exposure producers in 2026 only | Default mark-up rises to +30% from 2028; growing cost pass-back |
| 3. Decarbonize operations | High (technology-dependent) | 3–10 years | High-volume EU exporters; sectors with clean alternatives | Reduces embedded emissions; lowers certificate liability permanently |
| 4. Redirect exports away from EU | Variable (market development cost) | 1–3 years | Producers with fungible product and alternative market access | Removes EU CBAM exposure entirely; window narrowing (UK CBAM starts January 2027) |
| 5. Pursue Article 9 recognition | Political and government-led | 2–5 years | Countries with operational carbon pricing (South Korea, South Africa) | Deducts carbon price paid from CBAM certificate obligation |
The 5 options are not mutually exclusive. Producers in high-carbon sectors with significant EU exposure typically combine Option 1 (immediate data provision) with Option 3 (medium-term decarbonization) as a two-phase response.
Option 1: Provide Actual Emissions Data via the CBAM Operators Portal
Providing verified actual emissions data is the highest-leverage short-term CBAM strategy for most non-EU exporters whose actual production emissions fall below the CBAM default values. The CBAM default values are set conservatively high: the default for Chinese steel slab is 3.167 tCO₂e per tonne, while typical actual emissions from a modern BF-BOF mill run 1.8–2.1 tCO₂e per tonne. At €70 per tonne and a 48.5% CBAM factor in 2030, that gap of roughly 1.0–1.4 tCO₂e per tonne translates to €34–48 per tonne of avoided cost for the EU importer, which the importer passes back to the exporter as a price premium or retained contract.
The mechanism for data sharing is the CBAM Operators Portal, operated by the European Commission under DG TAXUD. Operators register on the portal, upload installation-level production data and specific embedded emissions calculations, and grant access to the EU-authorized CBAM declarants (importers) they supply. One upload serves all EU buyer relationships simultaneously.
The data required covers 4 categories: installation identification (UN/LOCODE, geographic coordinates, production route), production data (activity data per process step, total volume), specific direct embedded emissions calculated under IR 2025/2547, and, where applicable, the carbon price paid for Article 9 deduction. From 2026 onward, only the full EU calculation methodology is accepted. "Alternative methods" based on third-country standards that were permitted during the 2023–2025 transitional period are no longer valid.
Verification is mandatory. An accredited verifier (accredited under EN ISO/IEC 14065 by an EA-recognized National Accreditation Body) must physically visit the production installation for the first verification period. Verifier fees range from €5,000 to €50,000 per installation per reporting period, depending on complexity and geography. For CBAM data requirements for exporters, including the full specification of what each data field requires, producers should review the Communication Template published by the Commission.
The default value mark-up structure penalizes non-reporting increasingly over time: +10% above the calculated default in 2026, +20% in 2027, and +30% from 2028 onward. For steel, cement, and aluminium producers with actual emissions meaningfully below the default, the data provision investment repays within a single export season.
Option 2: Accept Default Values (and Understand the Cost Premium)
Accepting default values is a viable CBAM strategy only in a narrow window and for a specific type of exporter. The financial penalty for using defaults is modest in 2026 because the CBAM factor is just 2.5% of the gross certificate obligation. For Portland cement at €70 per tonne CO₂e with a default of 1.584 tCO₂e per tonne and an actual emission rate of 0.88 tCO₂e per tonne, the 2026 net cost difference between defaults and actual data is approximately €1.19 per tonne. Exporters with modest EU volumes (under 500 tonnes per year) will often accept this cost rather than invest in verification in year one.
The problem is that this calculus reverses sharply. By 2030, with the CBAM factor at 48.5%, the same Turkish cement producer using defaults pays approximately €27 per tonne more than a competitor who submits actual data. On a product with an FOB price of €60–80 per tonne, this is commercially unsustainable. EU buyers faced with two otherwise equivalent cement suppliers will consistently prefer the one whose actual data produces a lower certificate obligation.
The CBAM default values are published by the Commission under Implementing Regulation (EU) 2025/2621. Producers should check their sector-specific default before deciding to rely on it. For sectors or production routes where actual emissions are close to or above the default (less common but possible for older or coal-heavy production facilities), defaults may actually be lower than verified actuals in 2026 due to a transitional paradox in how defaults interact with free allocation. This paradox reverses from 2027.
Exporters who choose to accept defaults in 2026 as a deliberate deferral strategy face 3 risks: growing cost pass-back from EU importers, loss of EU market share to lower-carbon competitors, and a harder verification task in 2027–2028 when they eventually must submit data with 2 years of back-records. Starting the monitoring process in 2026, even before formal verification, reduces that future burden.
Option 3: Decarbonize Operations to Reduce Embedded Emissions
Decarbonizing production is the only CBAM strategy that permanently reduces the embedded emissions liability rather than managing how it is reported or who bears it. Decarbonization is a long-horizon CBAM strategy, typically requiring 3–10 years to implement at scale, but the compounding financial incentive is significant: every tonne of CO₂e removed from the production process reduces CBAM certificate obligations proportionally for the life of the mechanism.
The decarbonization pathways vary by sector. Steel producers face the clearest choice: transitioning from blast furnace (BF-BOF) production at approximately 2.0 tCO₂ per tonne to electric arc furnace (EAF) scrap-based production at approximately 0.5 tCO₂ per tonne, or direct reduced iron (DRI-EAF) routes at 0.9–1.4 tCO₂ per tonne using natural gas or green hydrogen. Turkish steel producers, who supply approximately 6 million tonnes per year to EU buyers, face a total CBAM exposure that makes this transition commercially rational despite the capital cost.
Cement producers face a harder decarbonization path. Approximately 60% of Portland cement's 0.83 tCO₂/t emission factor comes from the chemical decomposition of limestone (calcination), which is unavoidable in conventional clinker production. The viable paths are clinker substitution using blast furnace slag, fly ash, or calcined clay, and carbon capture and storage (CCS) at the kiln. Neither is fast or cheap, but the financial arithmetic at 2030 and 2034 makes both worth modeling.
Fertilizer and hydrogen producers have a more immediate decarbonization option: switching feedstock from natural gas (grey hydrogen production at 9–12 tCO₂ per tonne H₂) to electrolysis using renewable electricity (green hydrogen at approximately 0–0.3 tCO₂ per tonne H₂). This eliminates CBAM liability entirely for the hydrogen and derived fertilizer production, and positions the exporter to capture EU premium pricing for green molecules.
Decarbonization investment decisions should be modeled against the full 2026–2034 CBAM cost trajectory, not against 2026 prices alone. The effective surcharge for BF-BOF steel at €75 ETS reference price rises from €3.75 per tonne in 2026 to €150 per tonne in 2034.
Caption: The CBAM cost trajectory for non-EU exporters compounds sharply from 2028 as EU free allocation phases out, making early decarbonization investment financially rational for high-volume producers.
Option 4: Redirect Exports Away from EU Markets
Redirecting exports away from EU markets eliminates CBAM exposure entirely and represents a viable CBAM strategy for producers whose products have fungible demand in non-CBAM markets. The strategic logic is straightforward: if the EU market imposes a growing carbon price burden that competitors in non-EU markets do not face, redirecting volume preserves margin. The window for this strategy is narrowing.
The United Kingdom launched its own CBAM on January 1, 2027 (tax-based, covering the same 6 sectors). Canada is developing a carbon border adjustment. The US Congress has introduced the Foreign Pollution Fee Act (FPFA) as a potential equivalent. The set of major economies without any carbon border mechanism is contracting, and producers who divert away from the EU may find their alternative markets imposing equivalent costs within 3–5 years.
Market redirection is most viable for 3 types of exporters: producers in developing economies whose domestic markets are growing rapidly (for example, Indian steel producers redirecting toward Southeast Asian infrastructure demand), producers with genuinely high carbon intensity who cannot make the economics of data provision or decarbonization work, and smaller-volume producers for whom the EU represented a small share of total exports and transition costs outweigh the retained margin.
Market redirection carries its own costs: new market development, logistics reconfiguration, potentially lower margin in alternative markets, and the risk of anti-circumvention provisions if the goods are subsequently processed and re-exported to the EU. Regulation (EU) 2023/956 includes anti-circumvention provisions specifically targeting processing in third countries to avoid CBAM registration.
Option 5: Pursue Article 9 Recognition Through National Carbon Pricing
Article 9 of Regulation (EU) 2023/956 allows EU importers to deduct the carbon price effectively paid in the country of production from the CBAM certificate obligation. Pursuing Article 9 recognition is a government-led CBAM strategy that requires the exporter's home country to establish a qualifying carbon pricing scheme and seek Commission recognition. Exporters cannot claim Article 9 individually; the deduction flows through the EU importer once the Commission formally recognizes the third-country carbon price.
The qualifying criteria for an Article 9 carbon price are demanding: the scheme must be legally binding, effectively enforced, apply an absolute cap on emissions (not just an intensity target), and not provide such extensive free allocation that the effective price paid approaches zero. Voluntary carbon offsets, internal corporate carbon prices, and government subsidies that reduce energy costs indirectly are explicitly excluded.
As of April 2026, no third-country carbon pricing scheme has been formally recognized by the Commission for Article 9 purposes. South Korea's K-ETS (operating since 2015, covering approximately 70% of national emissions at $6–7 per tonne CO₂e) is the closest to recognition. South Africa's Carbon Tax (approximately R159 per tonne, or $9/tCO₂) is also under assessment. China's expanded ETS (covering steel, cement, and aluminium from March 2025 at approximately $11 per tonne) faces uncertainty because it is intensity-based rather than absolute-cap-based; absolute cap transition is planned post-2027.
Even where Article 9 deduction is recognized, the financial offset is partial. At South Korea's K-ETS price of $6–7 per tonne versus the EU ETS reference of €70 per tonne, the deduction covers approximately 9% of CBAM liability. The strategy reduces costs but does not eliminate them. Exporters in countries with low or zero carbon prices derive no benefit from Article 9 and should focus their CBAM strategy on Options 1–4 instead.
How to Choose the Right CBAM Strategy: Decision Framework
Non-EU exporters should evaluate CBAM strategy options across 4 decision dimensions: EU market dependency, emissions intensity relative to defaults, access to decarbonization capital, and the timeline of CBAM cost escalation in their sector.
The decision framework below maps these dimensions to the most appropriate primary strategy:
| Decision Dimension | High | Low |
|---|---|---|
| EU share of total exports | Options 1, 3 most important | Option 4 viable |
| Actual emissions vs. default | Option 1 saves the most | Option 2 acceptable short-term |
| Carbon-intensive sector (steel BF-BOF, grey hydrogen) | Option 3 critical by 2030 | Option 2 transitionally acceptable |
| Home country has qualifying carbon scheme | Option 5 applicable | Options 1–4 only |
| Large production installation (high data collection ROI) | Option 1 repays quickly | Option 2 until data system is built |
The 2026 filing calendar matters for planning. Verifier registration opens September 1, 2026. The first CBAM declaration covering calendar year 2026 is due September 30, 2027. Certificate purchases begin February 1, 2027. Exporters who begin building emissions monitoring systems and verifier relationships in 2026 are better positioned for the first full compliance cycle. Those who wait until 2027 face both a compressed verification timeline and a growing default mark-up.
The most common strategic error for non-EU exporters is treating 2026 as a low-stakes year. The CBAM cost is minimal in 2026, but the monitoring data collected in 2026 becomes the basis for the first verified declaration. Producers who do not monitor in 2026 cannot retroactively reconstruct the data that verifiers need for the September 2027 cycle.
Contextual Border: How CBAM Strategy Connects to the Broader Export Compliance Picture
Choosing a CBAM strategy does not exist in isolation from the broader compliance obligations of EU-bound exports. The CBAM Operators Portal is the technical infrastructure through which exporters interact with the EU system. Registering on the portal, uploading installation data, and granting importer access are operational steps that underpin Options 1 and 5. Without portal registration, even a producer with excellent actual data cannot transmit it to EU buyers in a format the authorized CBAM declarant can use for their declaration.
Does CBAM Strategy Differ by Sector?
CBAM strategy varies significantly by sector because embedded emissions intensity, default value penalties, and decarbonization pathways differ across the 6 covered sectors. The sector-specific CBAM default values determine how large the financial gap is between reporting actual data and accepting the published benchmark. The 3 key sector patterns are listed below.
Steel and aluminium producers face the highest gross embedded emissions but also the widest gap between defaults and best-in-class actual emissions. The incentive to submit actual data is strongest in these sectors.
Cement producers face an unusual constraint: calcination chemistry makes deep decarbonization structurally harder than in steel. Options 1 and 3 (data provision plus long-run CCS investment) are the dominant strategic combination.
Fertilizer and hydrogen producers have the most dramatic decarbonization option available: green hydrogen production eliminates CBAM liability entirely at the product level. The capital cost is high, but the EU premium for green ammonia and green urea creates a revenue-side offset that no other sector has.
Is CBAM Strategy Different for Small Exporters?
Small exporters whose EU buyers fall below the 50-tonne annual mass de minimis threshold face no direct CBAM exposure from those buyers. The de minimis threshold exempts approximately 90% of EU importing companies by count, though these exempted buyers represent only approximately 1% of total CBAM-affected import volume. If your EU buyers are large industrial importers purchasing hundreds or thousands of tonnes per year, they are above the threshold and the CBAM obligation is active regardless of the volume from any single exporter.
Can Exporters Avoid CBAM by Changing CN Codes?
Changing tariff classification to avoid CBAM coverage is considered circumvention under Regulation (EU) 2023/956. The anti-circumvention provisions in Article 27 cover artificial alteration of goods or processing in third countries with the primary intent of avoiding CBAM registration. EU customs authorities and the Commission have enforcement powers to reclassify goods and apply CBAM obligations retrospectively. This is not a viable CBAM strategy. Exporters whose home country operates a qualifying carbon pricing scheme can pursue a cost reduction through CBAM Article 9, which is the only legitimate route to reducing the certificate obligation without changing what is produced or how.
Will More Products Be Covered by CBAM in Future?
The Commission proposed expanding CBAM downstream to approximately 180 additional products under COM(2025)989, with a target implementation date of January 1, 2028, pending Council and Parliament approval. This expansion would include downstream steel products such as pipes, profiles, and structural components that are currently outside Annex I. Producers of these products should monitor the expansion process and begin preparing data infrastructure now rather than waiting for formal adoption.
Frequently Asked Questions
What is the best CBAM strategy for a non-EU exporter?
The best CBAM strategy for non-EU exporters whose actual emissions fall below the CBAM default values is to provide verified actual emissions data through the CBAM Operators Portal. This avoids the default mark-up (which rises to +30% from 2028) and protects EU market share as cost pass-back from importers increases through 2034.
Do non-EU exporters have any direct legal obligation under CBAM?
Non-EU exporters have no direct legal obligation under Regulation (EU) 2023/956. The legal and financial obligation falls entirely on the EU-authorized CBAM declarant (the importer). The commercial obligation exists because EU importers require verified embedded emissions data from exporters to calculate their certificate liability accurately.
Can exporters claim Article 9 carbon price deductions directly?
Exporters cannot claim Article 9 deductions directly. The deduction is claimed by the EU importer based on the carbon price effectively paid by the production installation in the country of origin. The home country's carbon pricing scheme must be formally recognized by the European Commission before any deduction is available, and no third-country scheme has been recognized as of April 2026.
What happens if an exporter provides no emissions data?
If an exporter provides no emissions data, the EU importer applies the CBAM default values published under Implementing Regulation (EU) 2025/2621. These defaults carry a mark-up of +10% above the calculated sector default in 2026, rising to +30% from 2028 onward. The importer typically passes this extra cost back to the exporter as a lower purchase price or switches to a supplier who can provide data.
Is redirecting exports away from the EU a viable long-term CBAM strategy?
Redirecting exports away from the EU is viable only in a narrowing window. The UK launched its CBAM on January 1, 2027. Canada is developing a carbon border adjustment. The US Congress has introduced equivalent legislation. Producers who rely on export redirection as their primary CBAM strategy face the risk of encountering equivalent mechanisms in alternative markets within 3–5 years.