Briefing

Floating hotels

Fanny Pointet, Leo Tricaud — July 3, 2026

How cruise ships are undertaxed despite their heavy environmental footprint and contribution to overtourism

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Cruising is booming. Over the past two decades, the cruise ship industry has expanded dramatically, with ships doubling both in size and in number, leading to a significant increase in their environmental footprint. In 2025, in the West European Mediterranean basin where most cruise ships sail, air pollution and greenhouse gas (GHG) emissions from cruise ships cost the community between €550 million and €930 million. When we include cruise operations along the Atlantic coastlines of these same countries, these external costs rise to between €790 million and €1.3 billion annually.

Regardless of their climate and environmental impact, cruises often remain largely outside the scope of standard regulatory and fiscal frameworks. They benefit from numerous exemptions or preferential regimes in areas such as Value Added Tax (VAT), energy taxation on fossil fuels, tourism levies, and tonnage taxes, resulting in a comparatively low tax contribution to national budgets.

Cruises are often seen as a symbol of mass and unsustainable tourism. They are perceived as contributing disproportionately to pollution while failing to pay their fair share of taxes. To put this into perspective, a night on board a cruise is taxed on average 40% less than a night in a hotel. This constitutes a major distortion of competition, given that cruise activity is much closer to tourist accommodation than to a mode of transport.

This has fuelled growing public opposition in many destinations. In response, an increasing number of port cities, regions, and national governments are considering or implementing measures to restrict cruise ship access or to introduce passenger-based levies, in line with the polluter pays principle.

External costs of cruise ships

The unpaid environmental bill of the cruise ship industry

Cruise ships have become one of the most visible symbols of mass tourism in European port cities, imposing a staggering cost on the environment and on local communities. The cruise industry is responsible for the resulting public health and environmental impacts of their economic activity. Today, these costs—which reached a total of €790 million to €1.3 billion in France, Spain, and Italy combined in 2025—far exceed existing environmental tax revenues, particularly in areas of the Mediterranean basin.

The environmental impact of the cruise sector is significant

Cruises are sold as leisure tourism, but a significant part of their real cost is not paid through the ticket price (see details in Annex). Their greenhouse gas emissions (GHG) and air pollution impose costs on the climate, public health systems, coastal ecosystems and port communities. As cruise demand continues to boom, the industry's impacts are steadily rising alongside it. The Mediterranean is Europe’s top cruise destination, capturing a major share of itineraries aimed at exploring the cultural and heritage wonders of Spain, Italy, and France. In 2025, 65% of cruise passengers in Europe sailed in the Mediterranean.

In this particular area, the level of impact can be perceived as overcoming the benefits of this economical activity. By way of an example, in the Balearic Islands, the accumulation of passengers in a short time can overload local transport, infrastructure, and public space.The phenomena of mass tourism has often led to local protests against cruise ships. Places such as Venice, Barcelona, Marseille, Dubrovnik and Santorini have become focal-points of the anti-cruising movement, where citizens and activists organized numerous demonstrations against large cruise ships.

Among the environmental damages, the easiest to quantify are greenhouse gases (GHGs), including carbon dioxide [CO₂], methane [CH₄], and nitrous oxide [N₂O], as well as air pollutants such as nitrogen oxides [NOₓ], sulfur oxides [SOₓ], and particulate matter [PM]. The Mediterranean regions are particularly exposed, together France, Spain and Italy’s cruise ships emitted 2.7 Mt CO₂e, 40.5 kt of NOₓ, 5.5 kt of SOₓ, 2.3 kt of PM2.5 and 2.5 kt of PM10 in 2025.

These pollutants have different impacts but all impose costs on society. GHGs contribute to climate change, while air pollutants contribute to respiratory and cardiovascular harm. The European Environment Agency identifies air pollution as the largest environmental health risk in Europe, with long-term exposure to fine particulate matter and nitrogen dioxide linked to major health impacts.

When the existing policies are not sufficient to tackle the environmental footprint of an economic activity, these costs are called negative externalities or external costs.

In the west Mediterranean basin alone - including France, Spain and Italy, the external costs of cruise ships (GHG and air pollutants) reached between €557 million and €930 million in 2025. When we include cruise operations along the Atlantic coastlines of these same countries, these external costs rise to between €792 million and €1.3 billion annually.

Italy and Spain carry the largest absolute external costs in the assessment, reflecting their high cruise activity in the Mediterranean and, for Spain, the additional West Atlantic region. France’s costs are lower in absolute terms but still significant, with impacts spread across the Mediterranean, Atlantic and North Sea/Channel areas. As cruise activity in Europe continues to grow, these externalities are expected to increase further.

The distribution of costs also shows why cruise pollution is not only a climate problem.

Depending on the climate valuation, air pollutants represent between 25 and 40% of the costs from cruise ship emissions, with the remainder costs coming from GHG emissions. This matters for policy design, even a strong carbon price would not address the full unpaid bill unless it is accompanied by measures targeting NOₓ, SOₓ and PM.

Existing policies are insufficient to cover the negative externalities of the cruise ship sector

Current green shipping regulations fail to adequately address the cruise industry's true footprint.

Key legislative measures, such as the EU’s mandate to use onshore power supply (OPS) at berth from 2030 under the AFIR regulation, the integration of shipping into the EU Emissions Trading System (ETS), the gradual fuel transition under FuelEU Maritime, and the newly established Mediterranean Sulphur Emission Control Area (SECA), are step-by-step advancements towards full decarbonization by 2050.

However, as of today, climate and clean air regulation remain profoundly insufficient to fully internalise and cover the heavy negative externalities generated by the cruise sector.

The revenues generated by the EU ETS applied to cruise ships leave a significant gap in covering externalities. On average, the climate-related external costs of this sector exceed ETS revenues by a factor of two to three depending on the cost of carbon. For costs related to air pollution, there is no such tax existing at the EU level. The environmental and public health impacts of these giant floating resorts remain largely unmitigated due to their size. Additionally, their enormous power requirements - directly driven by their size - puts a substantial pressure on local electricity grids, leading to heavy infrastructure investments.

In absolute terms, cruise ships represent a minor fraction of global maritime traffic, accounting for just 1% of the world’s fleet and less than 2% of EU shipping CO₂ emissions in 2024. Yet, on an individual basis, they are the single most carbon-intensive category of vessels afloat. One single cruise ship emits, on average, as much GHG in one year as 19,000 cars according to our calculations.

This massive footprint is driven by their scale and nature: these vessels are among the largest ships ever built, carrying thousands of passengers and requiring immense amounts of energy not just for propulsion, but to power energy-intensive amenities, hospitality services, and onboard entertainment.

The deployment of alternative-fuel engines in the cruise sector is a recent phenomenon. Among available options, only synthetic e-fuels offer genuine potential regarding deep emission reductions, sustainability, and scalability. Despite tightening EU decarbonisation targets, the industry remains heavily reliant on fossil fuels: out of the ten highest-emitting ships in the EU in 2024, four were cruise ships.

Currently, the global cruise fleet’s transition away from fossil fuels is moving very slowly:

  • 6% run on Liquefied Natural Gas (LNG)

  • 0.3% on methanol

  • 1% on hydrogen

  • 3% on plug-in hybrid power

Consequently, roughly 90% of the cruise ship fleet still relies entirely on conventional, highly polluting marine fuels. This heavy lock-in to fossil fuels is structurally reinforced by the long operational lifespan of these vessels, which typically remain in service for several decades.

This makes cruises an exceptionally high-impact form of tourism, far exceeding the footprint of alternative holiday options. To better contextualise this impact, it is useful to compare cruise tourism with functionally similar sectors, in particular land-based accommodation such as hotels and resorts, rather than transport modes alone. To put this footprint into perspective, independent analysis by the International Council on Clean Transportation (ICCT) exposes the true scale of the industry’s climate impact:

  • A cruise passenger emits twice as much CO₂ as a tourist who flies to their destination and stays in a high-end hotel.

  • A cruise passenger generates two to four times more CO₂ than holidaymakers taking a traditional road trip and staying in a hotel.

Taxation of cruise ships

End the cruise ship tax gap



Driven by global competition, the shipping industry has always enjoyed favourable tax treatment. However, cruise ships represent a completely different reality: they are primarily tourism and leisure destinations rather than transport services. A more appropriate benchmark is the land-based hospitality sector, with which cruise ships directly compete for tourists and holiday spending.

A serious tax gap between cruise ships and land-based resorts

To establish a fair baseline, cruise ships must be compared with land-based resorts rather than commercial vessels.

Legally classified as passenger ships, cruise ships fall under regulations designed for maritime transport. Consequently, they benefit from the tax exemptions granted to commercial cargo fleets, including exemptions on corporate income tax, Value Added Tax (VAT) and marine fuel taxes. Historically, these preferential regimes have been justified by geopolitical constraints and intense international competition between shipowners, and the ability of shipowners to relocate vessels between jurisdictions through reflagging or calling at low-tax ports.

In reality, however, cruises represent a leisure activity that is entirely decoupled from global trade and free from the structural constraints of freight transport. Cruises are not merely a mode of transportation to a destination but the destination itself. Cruise passengers select their trips based on the destinations offered but also on onboard amenities such as swimming pools, dining options or entertainment.

A comparison analysis performed by T&E reveals a profound disparity between the taxation levels of cruise ships and land-based hotels. The data demonstrates that due to the structurally distinct tax regimes applied to maritime traffic versus onshore real estate, cruises face a significantly lower tax burden than traditional hotels.

When considering high-end cruises, the difference is even starker: cruises pay seven times less tax than hotels. In a high-end hotel, taxes account for 20% of the total overnight price. By contrast, taxes represent less than 3% of the ticket price for a night onboard a high-end cruise ship. This figure demonstrates that the wealthiest tourists, who can afford luxury vacations at sea, contribute a disproportionately low amount to public finances.

This regression occurs because the levies applied to international cruises are predominantly flat. Because these charges do not scale with the price of the ticket and therefore revenues, they represent a negligible fraction of the total revenue generated by premium and luxury cruise lines.

The high level of environmental and public health impacts of the cruise sector have sparked widespread community protests globally, particularly across Mediterranean port cities.

In response, several governments have introduced dedicated cruise ticket levies to address this fiscal loophole, while others have enacted stricter operational limits, including total bans or capacity caps in historic city centres.

Proposal for a national cruise ship passenger levy

As demonstrated in Section 1, existing market-based policies fail to cover the heavy external costs of cruise tourism, notably its GHG emissions and localized air pollution.

To rectify this market failure, targeted fiscal instruments must be introduced. Implementing a dedicated levy on cruise tickets would internalize the sector's negative externalities and ensure a robust application of the "polluter pays" principle.

Such a mechanism would generate hundreds of millions of euros in recurring public revenues, which could be used by general national budgets or directly earmarked to accelerate the maritime energy transition or protect vulnerable coastal ecosystems and biodiversity.

Designing an effective national cruise levy

Local and national governments worldwide are increasingly adopting cruise ship levies. These pioneering jurisdictions generally fall into two categories:

  • Highly frequented markets in the Mediterranean and the Caribbean (e.g., Spain, Greece, Mexico, Croatia, and The Bahamas) reacting to intense local backlash against overtourism.

  • Nature-based markets: Vulnerable or remote regions whose reception infrastructure cannot sustainably absorb mega-cruise ships (e.g., Iceland, Norway, Scotland).

A flat-rate passenger tax represents the most transparent and straightforward mechanism for a cruise levy.

In most jurisdictions, this takes the form of a "day-tripper tax" assessed at the port of call, calculated dynamically based on the exact number of passengers onboard or disembarking. Alternatively, the levy can be structured using different ranges based on the vessel's total passenger capacity. Furthermore, several countries apply the tax across all operational phases, no matter whether the vessel is at berth, anchored offshore, or transiting through territorial waters.

A phased implementation timeline or a time-limited transitional framework could also be deployed. For instance, Mexico adopted a multi-year scale that applies a flat €4.5 tax per night per passenger starting August 1st, 2025, rising incrementally to €18.5 as of August 1st, 2028.

In the EU, a national levy could function as a temporary measure until the broader EU legislative framework becomes sufficiently stringent and effective. This levy would bridge the gap until EU ETS carbon prices fully internalize the cost of CO₂ emissions, onshore power supply (OPS) becomes legally mandatory for all port calls, and FuelEU GHG reduction targets require switching to green fuels. Beyond the EU framework, the International Maritime Organization (IMO) could expand Emission Control Areas (ECAs) to comprehensively regulate not only SOₓ emissions, but also NOₓ and particulate matter. The use of exhaust gas cleaning systems (i.e. scrubbers), as an option to comply with air quality standards should also be banned under international, regional, or national frameworks.

Existing global cruise taxes typically range from a few euros to over €20 per passenger. Notable examples include:

  • State/national level: Mexico (rising from €4.5 today to €18.5 by 2028); Greece (€5–€20 during peak summer months, with discounted rates off-season), Iceland (€2-€11/day); Norway (€9 starting in 2027) and the Caribbean (ranging from a low €1.3 in the Dominican Republic to a much higher fee of €20-€26 in The Bahamas).

  • Regional or local level: Catalonia (€4–€6, supplemented by a €5 city surcharge in Barcelona, which currently discusses a possible increase of the tax to €24 for cruise ships staying at berth for less than 12 hours); Lisbon (€2); Amsterdam (€15); the Balearic Islands (€2); Alaska (€30.5); Genoa (€3); Civitavecchia and Scotland (under discussion).

T&E has modelled the impact of a standard €15 levy per disembarking passenger across France, Italy, and Spain. This figure sits within the mid-to-high range of current European benchmarks.

In terms of passenger optics, a €15 charge is virtually negligible compared to standard onboard upsells, such as premium Wi-Fi packages, averaging around €20 per day.

Such a measure could raise hundreds of millions of euros in yearly revenues - €145m in Italy, €134m in Spain and €55m in France.

In order to ensure a fair and effective tax model, the design of the levy could incorporate targeted exemption regimes and explicitly earmark revenues toward environmental mitigation.

A cruise passenger levy will not detrimentally affect local tourism

Because many modern cruise levies have been adopted recently, long-term empirical data on passenger elasticity remains limited. However, historical performance suggests that existing global levies have had zero negative impact on overall passenger volumes.

In the case of Barcelona, the city quadrupled its local cruise tax over a ten-year period, yet experienced a 30% increase in cruise tourist arrivals during that exact timeframe. Similarly, Greece recorded an 11% surge in total visitor numbers within a single year, even with its nationwide cruise levies fully active. In the Caribbean, the market leaders in cruise volumes—Mexico and the Bahamas—are the nations that impose the highest baseline cruise fees.

A formal impact assessment by the Scottish Government corroborates this resilience, noting the following trends:

  • Short-notice implementation: When taxes were introduced at short notice (e.g. announced and implemented within two months, as in Amsterdam), their introduction caused only a temporary reduction in the number of cruise ship calls.

  • Long-term recovery: Once the tax had been in force for some time, the number of port calls returned to its previous levels and, in some cases, continued to rise.

  • Advanced notification: Where taxes were introduced well in advance (e.g. a two-year advance notice in Dubrovnik), the impact on the number of cruise ship port calls was marginal.

Ultimately, a cruise passenger tax is an essential economic tool designed to internalise the hidden costs of the sector into the ticket price. However, price signals alone cannot solve the physical challenges of overtourism as the cruise ship industry continues to grow.

A tax alone fails at bridging the gap of the external costs of cruise ship

While a €15 passenger levy generates vital revenue, it remains insufficient on its own to offset the total environmental costs of the cruise sector. Indeed, the revenues of a cruise ship levy combined with the revenues generated by the ETS mechanism would still be insufficient to cover the negative externalities caused by the cruise ship sector.

Thus, a cruise ship levy must be viewed as part of a broader regulatory mix.

To fully mitigate the sector's environmental footprint, parallel supply-side policies are necessary, including strengthening EU regulations on sustainable marine fuels (FuelEU Maritime) and tightening energy efficiency benchmarks (slow steaming, wind propulsion, electrification and onboard efficiency technologies). To drive industry leadership, cruise ships should face more stringent environmental performance standards than standard commercial cargo vessels.

If the primary objective of local and national policymakers is to systematically reduce localized environmental degradation and crowding, economic instruments must be coupled with strict operational caps.

Several pioneering European destinations have already deployed successful non-fiscal caps to stabilize visitor flows:

  • Daily and annual passenger caps: Dubrovnik (Croatia) and the Alpes-Maritimes region (France) enforced hard ceilings on the total number of cruise passengers permitted to disembark per day or per calendar year.

  • Vessel slot constraints: Ports like La Rochelle (France) and Barcelona (Spain) have established strict caps on the absolute number of cruise ship port calls per year or cruise terminals in the city.

  • Zoning and terminal relocation: Cities including Barcelona (Spain), Bordeaux (France), Venice (Italy), and Amsterdam (The Netherlands) have decided to restrict or ban mega-cruise vessels from entering their historic city centers, relocating terminals to peripheral industrial zones.

  • Mandatory minimum berthing times: To eliminate rapid, high-turnover day-trips and lower peak passenger spikes, jurisdictions have mandated extended stays. In Dubrovnik (Croatia), vessels must remain docked for a minimum of eight hours, extending to twelve hours for mega-ships carrying more than 4,000 passengers.

Recommendations at EU level

  • 1

    Reform the EU VAT Directive to specifically eliminate VAT exemptions for “international cruise voyages” and align cruise ship VAT with land-based tourism

  • 2

    In the revision of the Energy Taxation Directive, exclude cruise vessels operating in EU waters from full marine fuel tax exemptions

  • 3

    Adopt an EU obligation establishing minimum environmental levies on cruise operators to reflect the external costs of cruise tourism

  • 4

    Tighten decarbonisation rules for cruise ships, including stronger FuelEU Maritime GHG targets and extending AFIR so cruise ships must use shore power or zero-emission alternatives at berth to avoid overloading electricity grids.

  • 5

    Mandate speed reduction for cruise ships in EU waters

  • 6

    Ban the use of scrubbers in all European waters

Recommendations at national level

  • 1

    Establish a national levy aimed at internalizing the environmental externalities associated with cruise operations (more or less €15 per passenger / port call)

  • 2

    Earmark all tax revenues to accelerate the rollout of port OPS infrastructure and to support the conservation and restoration of marine and coastal ecosystems

  • 3

    Restrict cruise traffic in overtourism hotspots through daily passenger caps, vessel berth limitations, and bans from historic city centers or sensitive marine areas

  • 4

    Encourage voluntary, sector-led initiatives to improve environmental performance (e.g. Mediterranean sustainable cruise ship charter)