The UK Emissions Trading Scheme (UK ETS) is the United Kingdom’s carbon pricing mechanism. It operates as a cap-and-trade system that places a cost on greenhouse gas emissions by requiring operators to surrender tradable emission allowances corresponding to their verified emissions.
| Element | UK Emissions Trading System |
|---|---|
| Mechanism | Cap-and-trade carbon market |
| Cost driver | Market price of UK ETS allowances (UKAs) |
| Ship threshold | Ships ≥ 5 000 GT |
| Geographic scope | UK domestic maritime + emissions in UK ports |
| Gases covered | CO₂, CH₄ and N₂O on a tank-to-wake (TTW) basis |
| Start date | Domestic maritime from July 2026; offshore vessels from January 2027 |
| Compliance party | Registered owner by default (may transfer responsibility to ISM company) |
From 1 July 2026, the scheme is set to expand to include domestic maritime transport. Shipping companies will therefore need to monitor emissions, report them to regulators, and surrender UK ETS allowances for emissions falling within the scheme.
For shipping, UK ETS represents a shift from pure emissions reporting toward direct financial exposure to carbon emissions, meaning emissions performance becomes a commercial factor in voyage planning, fleet operation, and fuel strategy.
Under UK ETS, operators must obtain and surrender UK ETS allowances equal to their verified greenhouse gas emissions. Each allowance represents one tonne of CO₂ equivalent emissions.
Allowances are traded on the UK carbon market and therefore have a market-based price, meaning the cost of compliance varies depending on market conditions.
The maritime extension of the scheme is designed to introduce a carbon cost into domestic shipping operations. The objective is to create incentives for operators to:
The UK government has stated that extending UK ETS to maritime transport is part of the wider strategy to decarbonise all sectors of the economy in support of the UK’s net-zero target by 2050.
Geographical coverage:
The maritime extension of UK ETS initially applies only to domestic maritime voyages within the United Kingdom.
A domestic voyage is defined as a voyage between two UK ports. This includes situations where:
Emissions generated during port operations, including manoeuvring, anchoring and shifting operations, are included.
Voyages between the UK and Crown Dependencies or Overseas Territories are not treated as domestic voyages.
International voyages
International voyages are not fully included in the scheme at the initial stage. However, emissions generated while vessels are in UK ports are included.
The UK ETS Authority is consulting on expanding the scheme from 2028 to include 50% of emissions from international voyages between a UK port and a foreign port, broadly similar to the structure used in the EU ETS.
Ship size threshold:
The scheme applies to ships of 5,000 gross tonnage (GT) and above.
Offshore vessels are excluded from the initial scope in July 2026 but are scheduled to enter the scheme from 1 January 2027.
Voyage Coverage:
UK ETS applies to the following emissions:
Greenhouse gases covered:
The maritime extension covers three greenhouse gases:
The scheme uses a tank-to-wake accounting approach, meaning emissions are calculated based on fuel combustion during ship operations.
Methane slips and nitrous oxide emissions are therefore included in the emissions calculation.
Exemptions:
Several categories of vessels and activities are excluded from the maritime scope.
Examples include:
Government Non-Commercial Maritime Activities (GNCMA) are exempt. These include vessels used for:
In addition, ferry services serving certain Scottish island and remote peninsula communities are exempt due to their essential role in providing transport links for remote populations.
The implementation schedule is:
The first compliance period for maritime runs from 1 July 2026 to 31 December 2026.
From 2027 onward, compliance periods follow the calendar year.
To facilitate the transition into the scheme, the UK ETS Authority has introduced a double-surrender arrangement for the first two maritime compliance years.
Under this system:
This provides operators additional time to integrate into the scheme.
Responsibility for compliance lies with the registered owner of the vessel by default.
However, responsibility may be transferred to the ISM company if a legally binding agreement assigns the monitoring and compliance obligations to that entity.
This structure is broadly similar to EU ETS rules, although the UK ETS framework places stronger emphasis on the registered owner as the default responsible entity.
Charterers are not responsible parties under UK ETS.
UK ETS introduces a carbon price exposure for shipping companies.
Each tonne of greenhouse gas emissions must be covered by surrendering one UK ETS allowance. The cost therefore depends on the market price of UK allowances (UKAs).
Because allowance prices fluctuate, the carbon cost per voyage can vary significantly over time.
This introduces a new economic factor into maritime operations, similar to fuel price volatility.
Operators therefore face increasing incentives to:

1. Monitoring, reporting and verification (MRV)
Operators must prepare an Emissions Monitoring Plan (EMP) outlining the methodology used to measure and calculate emissions from vessels covered by the scheme.
During each scheme year, operators must monitor emissions in accordance with the approved monitoring plan and submit a verified Annual Emissions Report (AER) to the regulator.
The monitoring plan is submitted to the regulator before reporting begins.
Verification must be performed by UKAS-accredited verifiers.
Monitoring and reporting are managed through the METS reporting system.
2. Allowance management
Operators must hold UK ETS allowances in the UK ETS Registry.
After emissions have been verified, companies must surrender a number of allowances equal to their verified emissions.
The introduction of UK ETS into maritime transport affects more than regulatory compliance. It also changes how shipowners, operators and charterers think about day-to-day commercial and operational decisions.
Carbon cost becomes part of voyage economics, not just a reporting outcome. That influences fuel strategy, as lower-carbon fuels can reduce allowance exposure. It also strengthens the business case for fleet efficiency improvements and may shape investment decisions around energy efficiency measures and alternative propulsion technologies. In parallel, UK ETS is likely to become a more visible issue in charter party negotiations, particularly where parties need to agree how carbon costs are allocated.
Carbon exposure therefore becomes an explicit line item in voyage profitability, rather than solely a sustainability metric.


Stavanger:
Smedvig building
Løkkeveien 107
4007 Stavanger, Norway
Oslo:
Rebel building
Universitetsgata 2
0164 Oslo