ESG / CSR
Industries
MEASURE
ACT
COMFORM
FIFA World Cup 2026: What's the Real Carbon Footprint?
Level
By Kara Anderson, UK Copywriter, on 06/04/2026
Methodology disclaimer: The estimates in this report are based on publicly available data, recognised emissions factors, and transparent assumptions documented throughout. Where official figures are unavailable, the best available proxy data is used, with its basis and limitations clearly stated. All figures are
intended to provide context and order-of-magnitude insight rather than definitive measurements. Real-world emissions will vary.
The 2026 FIFA World Cup will be the biggest football tournament in history. For the first time, the competition expands to 48 teams and 104 matches - a 63% increase in games from Qatar 2022 - spread across 16 cities in the United States, Canada, and Mexico. More than five million tickets have already been sold, out of an anticipated total of around six million.
That scale raises a straightforward question: what is the actual climate cost of staging an event of this size?
Using publicly available data and established emissions methodologies, this report builds a bottom-up estimate of the 2026 World Cup’s total greenhouse gas footprint - covering team flights, spectator travel, stadium operations, renovations, accommodation, logistics, and waste.
👉 The headline figure: an estimated 7.8 million tonnes of CO₂e. That is approximately 2.1 times the official total reported for Qatar 2022.
But the more important story is in the structure of those emissions. Qatar built seven new stadiums from scratch, generating enormous upfront infrastructure emissions. The 2026 tournament uses existing NFL stadiums, so infrastructure accounts for just 3% of the total. Instead, spectator travel dominates at an estimated 87% of the overall footprint - because fans are travelling to a three-country tournament spread across a continent, and average journey distances are substantially longer than in Qatar.
👉 This report walks through every major emission source, explains how each figure was calculated, and places the results in context against Qatar 2022.
A Note on Methodology and Transparency
Calculating the carbon footprint of a major sporting event requires making choices about what to include, what to exclude, and how to estimate things that cannot be directly measured. Every one of those choices is made explicit in this report, with every data point sourced and linked.
Where a verified figure exists - a confirmed renovation cost, a published grid emission factor, an official attendance number - it is used directly. Where a specific figure cannot be found, the most defensible proxy available is used, with its basis and uncertainty clearly stated. Where data is genuinely unavailable, the category is either excluded or flagged as an indicative estimate.
A note on comparison with Qatar 2022: the two tournaments have different structures, different methodologies, and different reporting boundaries. Qatar’s official figure (3,631,034 tCO₂e) covers the full reporting period from 2011 to 2023, including over a decade of preparatory emissions. This report covers only the tournament phase and World Cup-attributable renovation costs. Comparisons throughout should be read as directional rather than exact.
The 2026 World Cup at a Glance
Before looking at emissions, it helps to understand what makes 2026 structurally different from Qatar.
| Parameter | Qatar 2022 | 2026 (USA / Canada / Mexico) |
|---|---|---|
| Teams | 32 | 48 |
| Matches | 64 | 104 |
| Host cities | 5 | 16 |
| Host countries | 1 | 3 |
| Total attendance (anticipated) | 3.4 million | ~6 million |
| Stadium construction | 7 new + 1 renovated | 0 new - renovations only |
| Tournament duration | 28 days | ~39 days |
The Results Up-front: Total Estimated Emissions for 2026
The estimated total for the 2026 FIFA World Cup is approximately 7.8 million tCO₂e - around 2.1 times the 3.63 million tCO₂e reported for Qatar 2022.
| Emissions category | 2026 estimate (tCO₂e) | Qatar 2022 (tCO₂e) | % of 2026 total |
|---|---|---|---|
| Team travel (flights) | 17,677 | ~17,000 |
0.2%
|
| Spectator travel | 6,817,762 | 1,878,106 |
87.8%
|
| Stadium operations | 63,126 | 52,404 |
0.8%
|
| Stadium renovations | 174,978 | 249,625 |
2.3%
|
| Merchandise and food | 80,670 | 45,770 |
1.0%
|
| Accommodation | 367,200 | 728,403 |
4.7%
|
| Intra-city transport | 161,604 | 91,690 |
2.1%
|
| Logistics and freight | 63,716 | 39,210 |
0.8%
|
| Waste management | 19,282 | 10,940 |
0.2%
|
| Media and broadcasting | 1,528 | 940 |
0.0%
|
| TOTAL | 7,767,543 | 3,631,034 | 100% |
Qatar 2022 figures from the FIFA GHG Accounting Report 2022 .
Team travel note: best case shown for 2026 (worst case: 18,764 tCO₂e - difference of ~1,100 tCO₂e, negligible at this scale). Qatar team travel is not separately disclosed in the official GHG report; the ~17,000 figure is derived.
Why does 2026 generate more emissions than Qatar?
The 2026 World Cup is simply a much bigger event. Attendance is anticipated to reach six million - up to 76% more than Qatar's 3.4 million cumulative attendances - and there are 63% more matches. More people travelling further, to more games, across three countries: that is the core driver of a higher total.
+76%
attendance
+63%
matches
Spectator travel distances compound this further. Fans from India face a return journey of nearly 28,000 km; from Saudi Arabia, 24,600 km; from the UK, nearly 15,000 km. Qatar sits at the geographic centre of the world’s major football-following regions - it is a relatively short flight from Europe, South Asia, and Africa simultaneously. North America is not.
The average international spectator travelling to 2026 faces a return journey of approximately 19,400 km, compared to an estimated 13,000 km average for Qatar. That distance gap, applied across 2.1 million international spectators, is the primary driver of the difference in spectator travel emissions.
But several structural factors push in the other direction, and they are significant. Qatar built seven new stadiums from scratch - its infrastructure emissions alone were 893,337 tCO₂e, nearly a quarter of its entire reported total. The 2026 tournament uses existing NFL stadiums, so that category falls to 238,105 tCO₂e, or just 3.1% of our total.
Qatar's hotels, running continuous industrial-scale air conditioning in desert heat, generated approximately 103 kg CO₂e per person-night; US hotels generate around 18 kg CO₂e per person-night (derived from the 36 kg CO₂e per room per night figure in DEFRA 2025 GHG Conversion Factors, which draws on Cornell Hotel Sustainability Benchmarking Index data for the USA, divided by standard occupancy of 2 persons per room) - around six times lower. And the 2026 host countries' electricity grids are approximately 25% less carbon-intensive than Qatar's, reducing stadium operations emissions despite 40 more matches being played.
What pushes emissions up
✈️
Average international spectator journey
19,400 km
compared with 13,000 km for Qatar 2022
🌍
International spectators
2.1 million
with the distance gap applied at scale
What pushes emissions down
🏟️
Stadium infrastructure
238,105 tCO₂e
compared with 893,337 tCO₂e for Qatar 2022
🏨
Hotel emissions per person-night
18 kg CO₂e
compared with 103 kg CO₂e for Qatar 2022
⚡
Grid carbon intensity
25% lower
than Qatar’s grid intensity
87.8%
The net result: spectator travel is dominant - at 87.8% of the total - that the structural advantages on infrastructure, accommodation, and grid intensity are not enough to offset it.
spectator travel
infrastructure
accommodation
grid intensity
Team Travel
How we calculated this
Distances are great-circle (airport-to-airport) using the Vincenty formula. Match 1 distances run from each nation’s principal airport to its match venue; Matches 2 and 3 use venue-to-venue distances; knockout rounds use each team’s previous match venue as the origin.
Emission factors are calculated bottom-up from aircraft fuel burn: kg fuel per hour ÷ cruise speed = kg fuel per km, then × 3.16 (IPCC jet fuel CO₂ factor) × 1.7 (radiative forcing multiplier, DEFRA/DESNZ guidance).
Haul bands: short ≤1,500 km at 15.99 kg CO₂e/km, medium 1,500–3,500 km at 19.59 kg CO₂e/km, and long >3,500 km at 37.01 kg CO₂e/km.
Team travel is the element of the World Cup’s carbon footprint most prominent in public discussion - but it’s actually one of the smallest in this estimate, at just 0.2% of the total. Forty-eight national teams flying to and around a three-country tournament generate approximately 17,677 tCO₂e in the best case. The Group Stage accounts for 91% of team travel emissions; knockout rounds contribute relatively little, as teams travel between US cities rather than crossing oceans. To put the total in context: the entire tournament’s team travel - 48 squads, 104 matches, flights across three continents - is equivalent to the annual carbon footprint of approximately 1,880 French people (based on the INSEE 2023 consumption-based figure of 9.4 tCO₂e per person per year).
Estimated team travel emissions range from
17,677 tCO₂e
to
18,764 tCO₂e,
a difference of just ~1,100 tCO₂e across the entire tournament.
| Round | Best case (tCO₂e) | Worst case (tCO₂e) | Notes |
|---|---|---|---|
| Group Stage | 16,152 | 16,152 | All venues fixed |
| Round of 32 | 650 | 1,737 | Qualifying team unknown |
| Round of 16 | 372 | 372 | Exact |
| Quarter Finals | 268 | 268 | Exact |
| Semi Finals | 121 | 121 | Exact |
| Bronze Final and Final | 114 | 114 | Exact |
| TOTAL | 17,677 | 18,764 | — |
Spectator Travel
How we calculated this
Total attendance of 6,000,000 (FIFA, April 2026)[1] is split 35% international (2.1 million) and 65% domestic (3.9 million), based on Qatar 2022 actuals[2]. International spectators fly from their home country’s largest city airport to a match venue and return. Nationality distribution follows Qatar 2022 top visiting nations[3], with USA, Canada, and Mexico reclassified as domestic. All international return journeys are long haul; the DEFRA 2025 economy class long-haul factor of 0.11704 kg CO₂e/pkm applies[4].
For domestic spectators (US, Canada, Mexico residents), we needed to estimate what proportion travel by air versus car. No published data exists for World Cup-specific domestic travel behaviour, so we used the Super Bowl as the closest available proxy. The LSU/EBPR 2025 Super Bowl Economic Impact Report found that 96% of game attendees came from outside Louisiana[5], and the Minnesota Super Bowl Host Committee's 2018 report found 95% of visitors came from outside Minnesota[6]. Both data points are consistent. We apply a more conservative 80% fly / 20% drive split, adjusted downward from the Super Bowl figures to reflect the multi-venue nature of the 2026 World Cup, where some fans will attend matches in their own city or state and drive rather than fly. This adjustment is our own judgement and is not drawn from a published source. The in-state/out-of-state distinction is used as a proxy for drive/fly, which is itself a simplification since state sizes vary enormously.
For the domestic flying distance, we needed a single representative figure for how far a fan who is flying to a World Cup match would travel. Rather than assuming a fixed origin city, we took the average distance between all 16 host cities: we calculated the straight-line flying distance between every possible pair of the 16 venues (120 pairs in total) and averaged them. This gives 2,367 km one-way (4,733 km return). The logic is that a fan flying domestically to a World Cup match is roughly as likely to be travelling between any two of the host cities, so the average inter-city distance is a reasonable proxy for the average domestic flight. This return distance is long haul (over 3,500 km), so the DEFRA 2025 long-haul economy class factor of 0.11704 kg CO₂e/pkm applies[4].
For the driving distance, we needed an average for fans travelling within their home state. Using US Census Bureau state land area data[7] (total US land area 9,158,022 km² ÷ 50 states = 183,160 km² average per state), and treating the average state as a circle, gives a radius of approximately 241 km. We use 200 km one-way (400 km return) as a round, conservative figure. This is a geometric approximation: state sizes vary enormously and venues are not always centrally located within states. Car factor: 0.113 kg CO₂e/pkm (EPA average passenger vehicle 0.170 kg CO₂/km ÷ 1.5 average vehicle occupancy)[8].
Limitations: the 35% international share is based on Qatar’s compact, single-country format[2]; 2026’s large domestic market may attract a higher proportion of local fans, reducing total emissions. Each spectator is modelled as attending one match only. Qatar data implies international visitors attended an average of ~2.9 matches, which, in Qatar's case, meant a short taxi ride between venues. For 2026, attending multiple matches means flying between cities - a fundamentally different emissions profile. We have not modelled this because no reliable data exists on how many matches 2026 international visitors will attend, and applying Qatar's figure directly would risk overstating a behaviour that was unique to a compact, single-city tournament. This is the most significant gap in our estimate. Additionally, as of early May 2026, some group stage matches still have available tickets, suggesting final attendance may be below 6 million. The drive/fly split uses state boundaries as a proxy, which is a simplification given the wide variation in state sizes.
A note on emission factors: DEFRA 2025 GHG Conversion Factors[4] are used for spectator flights, rather than the bottom-up aircraft fuel-burn methodology used for team travel. Team travel is modelled as charter-style arrangements. Spectators fly on scheduled commercial services of unknown aircraft type, where the DEFRA per-passenger methodology - based on real-world load factors and fleet mix - is the appropriate tool. Both approaches are standard in carbon accounting and use the same haul distance bands.
Sources
[1]
FIFA ticket sales announcement (April 2026)
[2] HVS – Qatar Beyond the World Cup
[3] The Peninsula Qatar – World Cup fans' top source countries
[4] UK Government Greenhouse Gas Reporting Conversion Factors 2025
[5] LSU / EBPR 2025 Super Bowl Economic Impact Report
[6] Minnesota Super Bowl visitor analysis
[7] US Census Bureau state land area data
[8] EPA greenhouse gas emissions from a typical passenger vehicle
87.8%
of total emissions
Spectator travel is, by a considerable margin, the largest emission source in this estimate - approximately 6.82 million tCO₂e, or 87.8% of the total. Qatar 2022 reported total travel emissions of 1.88 million tCO₂e for all spectators and teams combined. The spectator travel estimate for 2026 alone is nearly 3.6 times that figure.
✈️
6.82 million tCO₂e
estimated spectator travel emissions for 2026
📈
3.6×
Qatar 2022’s reported travel emissions
👥
725,000 people
approximately the annual carbon footprint of Marseille
Source for French per-person footprint:
INSEE 2023 consumption-based carbon footprint
.
International Spectators
How we calculated this
An estimated 2.1 million international spectators are modelled using Qatar 2022’s nationality distribution[1], adjusted to reclassify North American visitors as domestic.
The remaining 58% of international arrivals not individually identified in the Qatar data are assigned a distance of 9,710 km one-way - a weighted average derived from the top overseas inbound markets to the USA by visitor volume[2]. The weighting is based on reported visitor numbers from the United Kingdom (4.037 million), India (2.190 million), Germany (1.995 million), Brazil (1.910 million), and Japan (1.844 million).
All distances are calculated using the Vincenty formula from each nation’s principal international airport to the geographic centroid of the 16 World Cup venue cities.
| Origin | Share of intl visitors | Avg one-way distance (km) | Return (km) | Est. emissions per spectator (kg CO₂e) |
|---|---|---|---|---|
| Saudi Arabia | 11% | 12,300 | 24,600 | 2,879 |
| India | 9% | 13,895 | 27,790 | 3,253 |
| United Kingdom | 6% | 7,413 | 14,826 | 1,735 |
| Argentina | 4% | 8,681 | 17,362 | 2,032 |
| Egypt | 3% | 10,946 | 21,892 | 2,562 |
| Iran | 3% | 11,476 | 22,952 | 2,686 |
| Morocco | 3% | 7,866 | 15,732 | 1,841 |
| Sudan | 3% | 11,500 | 23,000 | 2,692 |
| Rest of world (58%) | 58% | 9,710 | 19,420 | 2,273 |
Nation shares from
The Peninsula Qatar (November 2022)
.
Rest-of-world distance weighted from
NTTO 2024 Survey of International Air Travelers (SIAT) inbound market data
.
All distances calculated via the Vincenty formula.
Emission factor:
DEFRA 2025 Greenhouse Gas Conversion Factors
,
long-haul economy class: 0.11704 kg CO₂e/pkm.
✈️
2,407 kg CO₂e
average emissions per international spectator
×
👥
2.1 million
international spectators
=
🌍
5.05 million tCO₂e
total international travel emissions
Weighted across all origin nations, the average international spectator generates approximately 2,407 kg CO₂e. Applied to 2.1 million international spectators, total international travel emissions are approximately 5.05 million tCO₂e.
Domestic Spectators
An estimated 3.9 million domestic spectators (US, Canada, Mexico residents) are split 80% fly / 20% drive. The Super Bowl 2025 economic impact report (LSU/EBPR) found 96% of game attendees came from outside Louisiana. The 80% figure is used as a conservative central estimate for a multi-venue tournament where some fans attend local matches.
| Segment | Spectators | Return distance (km) | EF (kg CO₂e/pkm) | Total emissions (tCO₂e) |
|---|---|---|---|---|
| Fly (80%) | 3,120,000 | 4,733 | 0.11704 | 1,728,690 |
| Drive (20%) | 780,000 | 400 | 0.113 | 35,256 |
| Total domestic | 3,900,000 | — | — | 1,763,946 |
Flight distance of 4,733 km return is the mean great-circle distance (Vincenty) across all 120 pairwise combinations of the 16 host cities.
Driving distance of 400 km return is derived from mean US state land area (183,000 km²,
US Census Bureau
),
converted to a circle radius of ~241 km.
Car factor:
EPA
0.170 kg CO₂/km ÷ 1.5 occupancy (
2022 NHTS, US DOE
) = 0.113 kg CO₂e/pkm.
Flight factor:
DEFRA 2025 long-haul economy
,
0.11704 kg CO₂e/pkm (domestic return of 4,733 km is long haul).
~4×
higher emissions per attendance than Qatar 2022
Qatar 2022
552 kg CO₂e
per attendance
2026 World Cup
2,003 kg CO₂e
per attendance
Average international spectator return journey
2026
19,400 km
Qatar
13,000 km
Qatar sits at the geographic centre of many of the world's major football-following regions, allowing relatively short journeys from Europe, South Asia, and Africa. North America does not. The longer average travel distance for international spectators is the primary driver of higher spectator travel emissions in the 2026 estimate.
Stadium Operations
How we calculated this
Qatar 2022 per-match and per-team figures from the FIFA GHG Accounting Report 2022[1] are used as the baseline and adjusted using the ratio of the 2026 weighted grid emission factor to Qatar’s.
Weighted 2026 grid factor: 0.344 kg CO₂e/kWh, based on US 0.367 kg CO₂/kWh[2], Canada 0.100 kg CO₂e/kWh[3], and Mexico 0.454 kg CO₂e/kWh[4], weighted 75/12.5/12.5% by match share.
Qatar: 0.460 kg CO₂e/kWh, from IEA data cited in the FIFA GHG Report[1].
Limitation: no cooling load adjustment is made - several 2026 venues face hot summer conditions, but the net energy difference vs Qatar cannot be reliably quantified without venue-level data.
Stadium operations are estimated at approximately 63,126 tCO₂e, or 0.8% of the total. The 2026 host countries generate electricity at a weighted carbon intensity of 0.344 kg CO₂e/kWh - around 25% lower than Qatar’s 0.460 kg CO₂e/kWh. Canada’s grid is particularly clean at 0.100 kg CO₂e/kWh, reflecting a predominantly hydro and nuclear mix.
Stadium Renovations
How we calculated this
Renovation costs in USD are converted to EUR at 0.92, then multiplied by the ADEME spend-based construction emission factor of 0.245 kg CO₂e/EUR[1] (ADEME Base Carbone, “Travaux de construction”, NACE sector F).
Only costs confirmed or reported after June 2022 - when FIFA announced host cities - are attributed to the World Cup.
For venues with no public cost figure, estimates are scaled from Seattle’s confirmed $19.4 million grass installation[2] as the anchor.
Limitation: the ADEME factor covers the French construction sector as a whole, not stadium-specific works; actual embodied carbon may be higher. Cost estimates for 8 of 16 venues are indicative only.
Stadium renovations are estimated at approximately 174,978 tCO₂e across all 16 venues - 2.3% of the total. All 2026 venues are pre-existing NFL stadiums. The $200 million Super Bowl renovations at SoFi Stadium and Levi’s Stadium are excluded, as those works are attributable to Super Bowl LX; World Cup-specific works at both venues are estimated at $12 million each (ENR, March 2026).
| Venue | WC renovation cost | Confidence | Source / basis | tCO₂e |
|---|---|---|---|---|
| Seattle (Lumen Field) | $19.4M | Confirmed | ENR, March 2026 | 4,375 |
| Toronto (BMO Field) | $114.4M (C$157.9M) | Confirmed | City of Toronto / CBC, March 2026 | 25,786 |
| New York (MetLife Stadium) | $25M | Reported | MetLife CEO statement, May 2026 | 5,635 |
| Mexico City (Azteca) | $80M | Reported | ENR, March 2026 | 18,032 |
| Vancouver (BC Place) | $128.5M (C$176M) | Reported | WorldCupWiki / CBC, 2026 | 28,964 |
| Boston (Gillette Stadium) | $250M | Reported - upper bound | ENR March 2026. Pre-2022 works may be included. | 56,350 |
| Kansas City (Arrowhead) | $50M | Reported | 22ZIN analysis, 2026 | 11,270 |
| Philadelphia (Lincoln Financial) | $25M | Estimated | Benchmarked vs MetLife (identical scope) | 5,635 |
| Los Angeles (SoFi Stadium) | $12M | Estimated | ~62% of Seattle benchmark; lighter scope | 2,705 |
| San Francisco (Levi’s Stadium) | $12M | Estimated | ~62% of Seattle benchmark; lighter scope | 2,705 |
| Atlanta (Mercedes-Benz) | $10M | Estimated | ~50% of Seattle; temporary works only | 2,254 |
| Dallas (AT&T Stadium) | $10M | Estimated | ~50% of Seattle; minor works | 2,254 |
| Houston (NRG Stadium) | $10M | Estimated | ~50% of Seattle; minor prep | 2,254 |
| Miami (Hard Rock Stadium) | $10M | Estimated | Major renovation was 2016; minimal WC prep only | 2,254 |
| Guadalajara (Estadio Akron) | $10M | Estimated | ENR: minor refreshing only | 2,254 |
| Monterrey (Estadio BBVA) | $10M | Estimated | ENR: minor refreshing only | 2,254 |
Renovation cost sources:
ENR Engineering News-Record
,
Outlook India (MetLife CEO statement)
,
CBC News Toronto
,
WorldCupWiki
,
22ZIN
.
Emission factor:
ADEME Base Empreinte®
,
0.245 kg CO₂e/EUR (Travaux de construction, NACE F).
Food, Drink, and Merchandise
How we calculated this
Qatar 2022 official per-spectator emission factors are derived from the FIFA GHG Accounting Report 2022[1].
Food and drink emissions are calculated as 26,560 tCO₂e ÷ 3,404,252 attendances = 7.80 kg CO₂e per spectator.
Merchandise emissions are calculated as 19,210 tCO₂e ÷ 3,404,252 attendances = 5.64 kg CO₂e per spectator.
Both factors are then scaled to the 2026 tournament’s anticipated attendance of 6 million spectators.
Food, drink, and merchandise are estimated at approximately 80,670 tCO₂e - 1.0% of the total. These are derived from Qatar’s official GHG report, which remains the only World Cup for which verified per-spectator factors exist. At maximum venue capacity (~7.24 million attendances), the estimate rises to approximately 97,355 tCO₂e.
| Category | Per-spectator EF (kg CO₂e) | 2026 central estimate (tCO₂e) | 2026 max capacity (tCO₂e) |
|---|---|---|---|
| Food and drink | 7.80 | 46,812 | 56,494 |
| Merchandise | 5.64 | 33,858 | 40,861 |
| Total | — | 80,670 | 97,355 |
Accommodation
How we calculated this
International spectators (2.1 million) are assigned a 6-night average stay, based on Qatar 2022 figures reported in Annex II of the FIFA Greenhouse Gas Accounting Report[1].
Domestic spectators (3.9 million) are assigned a 2-night stay. This is a central estimate with no direct published data source and is used as a plausible assumption for a short domestic sporting trip.
Hotel emissions are calculated using the DEFRA 2025 GHG Conversion Factors[2]: 36 kg CO₂e per room per night (USA, Cornell CHSB-based), divided by 2 persons per room under a standard occupancy assumption.
Limitation: accommodation emissions are sensitive to the assumed domestic stay length. At 1 night, domestic accommodation emissions fall by approximately 70,000 tCO₂e; at 3 nights they increase by approximately the same amount.
Accommodation is estimated at approximately 367,200 tCO₂e - 4.7% of the total. Despite nearly double the attendance, this is substantially below Qatar’s 728,403 tCO₂e. Qatar’s hotels required continuous industrial-scale air conditioning in extreme desert heat, resulting in approximately 103 kg CO₂e per person-night. US hotels at approximately 18 kg CO₂e per person-night (DEFRA 2025 / Cornell CHSB) are around six times less carbon-intensive.
| Segment | Spectators | Avg nights | EF (kg CO₂e/person/night) | Total (tCO₂e) |
|---|---|---|---|---|
| International | 2,100,000 | 6 | 18 | 226,800 |
| Domestic | 3,900,000 | 2 | 18 | 140,400 |
| Total | — | — | — | 367,200 |
Intra-City Transport, Logistics, Waste, and Media
How we calculated this
These categories use the Qatar 2022 FIFA Greenhouse Gas Accounting Report Scope 3 breakdown as the baseline[1].
Intra-city transport and waste use an attendance scalar: 6,000,000 ÷ 3,404,252 Qatar attendances = 1.763x. Logistics/freight and media/broadcasting use a match scalar: 104 ÷ 64 = 1.625x.
Limitation: Qatar was an unusually compact tournament[2]; intra-city transport in 2026 spans 16 cities across three countries and will be structurally different.
These four categories represent approximately 3.1% of the total.
| Category | Qatar 2022 (tCO₂e) | Scalar | 2026 estimate (tCO₂e) |
|---|---|---|---|
| Intra-city ground transport | 91,690 | Attendance 1.763× | 161,604 |
| Logistics and freight | 39,210 | Matches 1.625× | 63,716 |
| Waste management | 10,940 | Attendance 1.763× | 19,282 |
| Media and broadcasting | 940 | Matches 1.625× | 1,528 |
| Total | 142,780 | — | 246,130 |
Categories excluded
Training site construction is excluded: Qatar built dedicated facilities from scratch, whereas the 2026 tournament uses existing infrastructure.
Temporary stadium construction and seating - Qatar’s largest single infrastructure line at 640,058 tCO₂e, covering more than 170,000 temporary seats and the purpose-built Ras Abu Aboud stadium - does not apply to the 2026 tournament.
Temporary stadium construction and seating - Qatar’s largest single infrastructure line at 640,058 tCO₂e, covering more than 170,000 temporary seats and the purpose-built Ras Abu Aboud stadium - does not apply to the 2026 tournament.
Full Comparison with Qatar 2022
Qatar’s official total of 3.63 million tCO₂e covers the full reporting period from 2011 to 2023. This report covers only the tournament phase and World Cup-attributable renovation costs. The comparison is directional, and the structural drivers matter more than the ratio itself.
| Category | Qatar 2022 (tCO₂e) | 2026 estimate (tCO₂e) | Change | Driver |
|---|---|---|---|---|
| Travel (team + spectator) | 1,878,106 | 6,835,439 | +3.6× | More attendees + longer distances |
| Infrastructure | 893,337 | 238,105 | −71% | Existing venues vs new build |
| Accommodation | 728,403 | 367,200 | −50% | Lower hotel energy intensity |
| Food, merch, intra-city, logistics, waste, media | 131,188 | 326,800 | +1.7× | More attendance and matches |
| Total | 3,631,034 | 7,767,543 | +2.1× | — |
The most striking reversal is infrastructure. Qatar’s new-build stadiums and temporary seating accounted for 24.6% of its total. For 2026 that falls to 3.1%. This structural difference is what keeps the 2026 figure from being even higher, despite dramatically more matches and attendances.
24.6%
of Qatar 2022’s total came from new-build stadiums and temporary seating
3.1%
of the 2026 estimate comes from infrastructure
What This Estimate Does Not Include
The 7.8 million tCO₂e figure has a defined boundary. The following are not captured and are worth naming explicitly.
Multiple match attendance
A note on cumulative attendance: this estimate treats each of the 6 million attendances as a separate individual making a full return journey. In reality, some spectators - particularly international visitors - will attend multiple matches. Qatar data suggests international visitors attended an average of ~2.9 matches each. A fan attending three matches makes one return international flight plus shorter inter-city hops, not three separate return international flights. Our model, therefore, likely overstates spectator travel emissions for any fan attending more than one match. The direction and scale of this effect depend on how many 2026 spectators attend multiple matches, which is unknown in advance, but it is worth noting that our headline figure may overstate emissions in this respect.
Home viewing
Hundreds of millions of people watch the World Cup on television or streaming platforms. Around 5 billion people engaged with Qatar 2022 across all platforms (FIFA). Broadcast-related emissions are not included here.
Fan zones and public screenings
FIFA’s official fan festivals and unofficial public screenings generate additional travel, energy consumption, and waste not captured in this estimate.
Corporate and sponsor travel
Broadcasters, sponsors, corporate hospitality guests, and the wider commercial ecosystem surrounding the tournament generate emissions outside the scope of this estimate.
Pre-tournament operations
Qatar’s official figure covers activity from 2011. This report covers only the tournament phase; the comparison is therefore not fully like-for-like.
What the Numbers Mean
87.8%
of the total footprint comes from spectator travel
74%
of travel emissions come from international visitors
3.1%
comes from stadium operations and renovations
7.77M
tCO₂e total estimated footprint
This is a spectator travel problem, not a stadium problem
The most important finding is structural. The 2026 World Cup’s carbon footprint is dominated by spectator travel at 87.8% of the total - larger than every other category combined, several times over. Stadium operations and renovations together represent just 3.1%. The elements of the World Cup’s environmental story that receive the most attention - construction, operations, team logistics - are not where the problem sits.
Meaningful emissions reduction for 2026 and future tournaments will not come primarily from more energy-efficient stadiums or lower-emission team flights. It will come from decisions about where fans travel from, how they get there, and whether the tournament’s format encourages or discourages long-haul travel.
International travel is the dominant driver
Within spectator travel, international visitors account for approximately 74% of emissions despite representing only 35% of attendances. A single spectator flying from India generates approximately 3,253 kg CO₂e - based on the Vincenty-calculated distance of 13,895 km one-way from Mumbai to the average World Cup venue, at the DEFRA 2025 long-haul economy factor of 0.11704 kg CO₂e/pkm. At that scale, the nationality distribution of the audience is a more significant lever than almost any operational decision FIFA or the host countries can make.
If the international share is lower than the 35% assumption used here - plausible, given 2026’s large domestic market - total emissions would be meaningfully lower.
Qatar is not a useful baseline
Qatar's 3.63 million tCO₂e total reflects a tournament with a very different emissions profile from 2026. Qatar sits at the geographic centre of the world’s major football-following regions - a relatively short flight from Europe, South Asia, and Africa simultaneously. Its visitor mix included significant long-haul travellers from India, the UK, Argentina, and beyond, but its average journey distance was substantially shorter than 2026’s. It also generated enormous upfront infrastructure emissions from building seven new stadiums, which accounted for nearly a quarter of its total. Neither of those characteristics is typical. A compact Gulf tournament with largely new infrastructure is not a useful template for what future World Cups will look like - and the 2026 figures broadly reflect that.
Net zero claims need a clear boundary
Whether a sustainable World Cup is possible depends entirely on where the reporting boundary is drawn. If it covers only operational emissions - logistics, energy, official travel - meaningful progress is achievable. If it is expected to reflect the full climate impact of how millions of fans travel from around the world, the challenge is a different order of magnitude entirely.
It is worth being precise about what FIFA has and has not committed to. When the United States, Canada, and Mexico submitted their joint bid in 2018, sustainability consultants ARUP estimated the tournament’s total carbon footprint at 3.7 million tCO₂e. That figure - based on a tournament of 80 matches, not the 104 ultimately confirmed - remains the most widely cited official estimate for 2026. FIFA has since published a Sustainability and Human Rights Strategy for the tournament (inside.fifa.com/tournament-organisation/world-cup-2026-sustainability-strategy), built around four pillars including an environmental pillar covering energy efficiency, waste reduction, and transportation planning at host city level. The strategy does not, however, set a specific carbon budget or updated emissions estimate for the tournament, and contains no commitment on how the total footprint will be publicly reported. FIFA’s wider corporate commitments - a 50% emissions reduction by 2030 and net zero by 2040 - apply to FIFA as an organisation, not to this tournament specifically. They were announced at COP26 in 2021 as part of the UN Sports for Climate Action Framework.
The strategy does not address spectator travel, which this report identifies as 87.8% of the total estimated footprint. The gap between the official bid estimate and independent estimates is substantial: Greenly’s figure of 7.77 million tCO₂e is 2.1 times the ARUP estimate; Scientists for Global Responsibility, in partnership with the Environmental Defense Fund, put their independent estimate at 9 million tCO₂e (sgr.org.uk). FIFA’s claim of carbon neutrality for Qatar 2022 was ruled unsubstantiated by the Swiss advertising regulator in June 2023 (reported by The Guardian, June 2023) - the first formal regulatory finding against a governing body for greenwashing a major sporting event.
Spectator travel is not an externality. It is the reason the tournament exists.
The Final Score
The 2026 FIFA World Cup is estimated to generate approximately 7.8 million tCO₂e - around 2.1 times the official Qatar 2022 total of 3.63 million tCO₂e. The larger scale, multi-country format, and longer average travel distances all push emissions higher. But the tournament also requires no new stadiums, benefits from a cleaner electricity grid, and operates in markets with substantially less carbon-intensive hotel infrastructure.
The challenge is spectator travel. When millions of fans fly across the Atlantic, the Pacific, and the North American continent, the carbon arithmetic is straightforward and large. Stadium design and tournament operations - the things organisers control most directly - are not where the problem sits.
Share this article
Subscribe to the CSO Connect Newsletter
We care about your data in our privacy policy.
