Carbon footprint of coffee
How much greenhouse gas a coffee causes from farm to cup, how life-cycle studies measure it, where the main emissions arise and why published results differ so widely.
Across the chain: Sustainability
Contents
In brief
- A carbon footprint is a life-cycle assessment limited to climate change; ISO 14067 sets its requirements, consistent with ISO 14040 and ISO 14044.1,2,3
- A review of 34 studies found 0.15–14.5 kg CO₂e (carbon dioxide equivalent) per kg green coffee, median 3.6.7
- On the farm, land-use change, fertilisers and washed processing (“wet processing” in the review) contributed most; over the whole chain, green coffee production contributed most.7
- Shipping by sea added a few percent; where air freight was assumed, transport could make up more than 73% of the footprint.7,8
- In two studies, drinks with milk had a clearly higher footprint per serving than espresso.8,11
What a carbon footprint measures#
A carbon footprint adds up the greenhouse gases released over the life of a product. ISO 14067 sets out how to quantify and report it, consistently with the life-cycle assessment standards ISO 14040 and ISO 14044.1 It covers one impact category only: climate change.1 Water, biodiversity, and social or economic effects are outside its scope.1
Results are given in kilograms of carbon dioxide equivalent (kg CO₂e). This unit expresses any greenhouse gas as the amount of carbon dioxide with the same effect on climate over a set time.4 In coffee studies, global warming potential (GWP) is the impact category most often reported.7
A footprint is always a footprint of something. It can be a hectare, 1 kg of green or ground coffee, or a volume of drink.7 It also depends on where the study starts and stops. The same coffee can therefore appear with very different published numbers.7
How a life-cycle assessment is built#
A life-cycle assessment (LCA) follows the steps that ISO 14040 and ISO 14044 describe. These are goal and scope, inventory analysis, impact assessment, and interpretation.2,3 Three choices in the first step matter most when coffee studies are compared.7
- Functional unit. It is the “quantified performance of a product system for use as a reference unit”, in the European Commission’s glossary based on ISO 14040.5 Coffee studies have used hectares, kilograms of cherry, parchment, green or ground coffee, and volumes of drink.7
- System boundary. This sets which stages are counted. Some coffee studies stop at the farm gate; others run from cradle to grave, that is, to the cup and the waste.7 The farm stage was not always fully included; in one study, energy accounting started with cherry processing.7
- Allocation. A process that yields more than one product shares its emissions between them; this sharing is called allocation.6 In a 2024 review of coffee LCAs, most studies did not consider or mention any co-product allocation.7
ISO 14040 describes the framework; it does not prescribe the methods for each phase.2 Two studies that both follow it can therefore still differ.2,7
Where the emissions arise#
A 2024 systematic review gathered 34 coffee LCAs covering 234 coffee systems.7 It describes where, along the chain, the emissions arise.7
- On the farm. Land-use change, fertilisers and washed processing (“wet processing” in the review) were the main contributors to the footprint of green coffee.7 Land-use change here means clearing land to establish the plantations.7 Leaving it aside, synthetic fertilisers contributed a median 66%, counting both their manufacture and their emissions in the field.7 Field trials and farm surveys point the same way (see Deep dive).12,13
- At the mill. The review names washed processing (“wet processing” in its words) among the main contributors.7 It found it modelled inconsistently across studies.7
- In transport. Where coffee was shipped by sea, transport added a few percent (median ≈3%, up to 12%).7 Where air freight was assumed, transport could make up more than 73% of the footprint.7
- At the roastery. Roasting and grinding together contributed a median 8% in cradle-to-grave studies.7
- Packaging. Packaging contributed a median 9–18%; the higher figure applied to single-serve pods and capsules.7
- In the cup. Brewing, cup washing and waste management each contributed about 18% (median).7 Heating water was the first or second contributor to energy use, depending on the drink and on whether a machine or a kettle was used.7
Taken over the whole chain, green coffee production was the largest contributor, with a median share of 63%.7 Drinks with milk were outside that review. Two studies that included milk found that it raised the footprint of a drink well above that of an espresso.8,11
Data table
| kg CO₂e per kg green coffee | Source | |
|---|---|---|
| Conventional · growing | 1.01 | 8 |
| Conventional · milling | 0.10 | 8 |
| Conventional · export by air | 10.44 | 8 |
| Conventional · roasting to cup | 3.05 | 8 |
| Conventional · total | 14.61 | 8 |
| Sustainable · growing | 0.05 | 8 |
| Sustainable · milling | 0.08 | 8 |
| Sustainable · export by sea | 0.19 | 8 |
| Sustainable · roasting to cup | 3.05 | 8 |
| Sustainable · total | 3.37 | 8 |
The figure shows one study’s result stage by stage. In that study, flying the coffee to the UK made up most of the conventional footprint.8 The authors chose air freight because, in their words, “retailers are increasingly transporting coffee beans via freight flight to get fresher coffee”.8 The review cited above excluded this study from its averages (see Contested).7
Why studies disagree#
The review found that GWP “varied greatly at both the farm and drink levels”.7 For green coffee it ranged from 0.15 to 14.5 kg CO₂e per kg (median 3.6).7 For drinks, it ranged from 2 to 23 kg CO₂e per kg of coffee consumed (median 8.8).7 It names several reasons.
- Land-use change. Counting it raised results up to four-fold; it made up 1–75% of the footprint of green coffee.7
- Field emissions. Most studies did not say whether indirect nitrous oxide, or carbon dioxide from urea and liming, was counted.7
- Washed processing. Fermentation and wastewater emissions were not modelled consistently, and some studies left them out.7
- Functional unit and dose. No study defined its functional unit by moisture or by sensory quality.7 How much coffee goes into a cup, and how much it is diluted, changed results but was mostly not built into the functional unit.7
- Transport mode. Ship transport was negligible to a few percent; air freight could exceed 73%.7 One study assumed that freight flights emit about 100 times more CO₂e per km than cargo ships.8
- Background assumptions. Energy results depended on the electricity mix assumed.7
Data table
| kg CO₂e per kg green coffee | Source | |
|---|---|---|
| Green coffee, across studies (review, 2024) | 0.15–14.5, median 3.6 | 7 |
| Green coffee, with land-use change (review, 2024) | 1.63–10.52 | 7 |
| Brazil, conventional, to farm gate (2024) | ≈1.4 | 13 |
| Brazil, organic, to farm gate (2024) | ≈0.3 | 13 |
| Brazil and Vietnam to UK cup, air freight (2020) | 14.61–16.04 | 8 |
| Brazil and Vietnam to UK cup, sea freight (2020) | 3.37–3.64 | 8 |
Stages a roaster or café controls#
The studies attribute shares of the footprint to stages; they do not rank businesses. Read that way, the stages a roastery or café runs itself carried smaller shares than the farm.7 Roasting and grinding contributed a median 8%, against 63% for green coffee production.7
- Which coffee, from where. Green coffee production carried the largest share.7 According to the research programme behind a 2014 farm study, commercial polycultures are among the most promising ways to grow coffee with a low footprint.14
- How it travels. Shipping by sea added a few percent; air freight could dominate.7,8
- Packaging. Single-serve pods and capsules carried the largest packaging share.7,10
- How it is brewed. Heating water and machine energy were a major part of the use phase.7,8 One 2009 study named the amount of extra water boiled as a key parameter.9
- Milk. In two studies, drinks with milk had a clearly higher footprint than espresso.8,11 One named cow’s milk among the raw materials with the highest emissions.11
The authors of the 2020 study list ways to lower its footprint: optimal use of agrochemicals, less packaging, more efficient water heating, renewable energy, roasting before export and carbon offsetting.8 These are the authors’ suggestions from one modelled supply chain. Claims about offsetting are covered in the planned entry on sustainability claims.
The method in detail#
ISO 14044 specifies the requirements for an LCA, including critical review and the limitations of the method.3 ISO 14067 applies these rules to climate change alone. It also specifies requirements for a partial carbon footprint, covering part of the life cycle.1 Carbon offsetting and the communication of footprint results are outside its scope.1 As of October 2026, ISO 14040 and ISO 14044 were confirmed in 2022, ISO 14067:2018 was confirmed in 2024, and a revision of ISO 14067 was under development.1,2,3
The 2020 UK study followed a different specification, PAS 2050:2011, which allows emissions to be excluded as long as at least 95% are assessed.8 It assumed the farms had grown coffee for at least 20 years, so land-use change was excluded.8 Its roasting-to-cup stage was not modelled anew: the values were “taken from a previous coffee LCA carried out by PCF Pilotprojekt Deutschland (2008)”, a German product-footprint pilot.8
The review recommends that coffee LCAs standardise the functional unit, including the moisture of green coffee and the sensory quality of drinks.7 It also asks for mass balances when biomass flows, land-use change, co-products and residues are assessed, and for more primary data on wet and semi-wet processing (the review’s terms).7
Farm-stage emissions#
Nitrogen. In two long-term agroforestry trials in Costa Rica and Nicaragua, the main contributor for all management systems was the input of organic and inorganic nitrogen.12 Conventional plots emitted 0.26–0.67 kg CO₂e per kg of fresh cherry, organic plots 0.12–0.52.12 In a 2024 study of farms in Minas Gerais and São Paulo, Brazil, about 70% of the carbon dioxide emissions came from field emissions of urea and limestone.13
Organic and conventional. In that Brazilian study, conventional coffee came to about 1.4 kg CO₂e per kg green coffee and organic coffee to about 0.3, cradle to farm gate.13 In the Central American trials, the conventional and organic ranges per kg of cherry overlapped.12 The two studies use different functional units and cannot be compared directly.12,13
Trees and carbon stocks. A 2014 study compared four main types of coffee production system.14 According to the research programme that ran it, polycultures, where coffee grows together with other trees, store substantial amounts of carbon compared with shaded and unshaded monocultures and use relatively moderate amounts of fertiliser.14 The strategies it lists are introducing trees in plantations, optimising fertiliser production and use, and reducing emissions from fermentation and wastewater.14 The study’s own footprint values could not be checked for this entry, because the paper is not openly available, so they are not given here.
Land-use change. Studies that counted land-use change, using the Intergovernmental Panel on Climate Change (IPCC) Tier 1 method, found 1.63–10.52 kg CO₂e per kg green coffee.7 The review describes at least 20 years as the consensual time frame for these carbon estimates.7
From roastery to cup#
In the 2020 UK study, the roasting-to-cup stage came to 3.05 kg CO₂e per kg green coffee; 70% of it was attributed to consumption.8 In the earlier German study it drew on, roasting made up 6% of that stage and packaging 4%.8 For one cup, that earlier study estimated 60.27 g CO₂e for an automatic machine, against 10.04 g for filter drip or French press.8
A 2021 study compared three ways of making a 40 mL cup without milk or sugar.10 It left out the coffee itself: cultivation, green coffee transport, roasting and grinding were assumed equal for all three.10 What remains is transport, packaging, electricity and waste.10 The values below are from the paper’s Table 5; some percentage shares in its text do not match that table.10
| 40 mL cup, g CO₂e | Transport | Packaging | Electricity | End of life | Total |
|---|---|---|---|---|---|
| Moka pot (induction hob) | 0.9 | 0.9 | 2.9 | 3.4 | 8.110 |
| Capsule machine | 1.4 | 5.5 | 2.8 | 0.3 | 10.010 |
| Pod machine | 2.4 | 9.5 | 5.3 | 1.3 | 18.510 |
A 2009 study, covering the full life cycle, compared a 1 dl (100 mL) cup made from spray-dried soluble coffee, capsule espresso and drip filter coffee.9 Soluble coffee came to 0.07 kg CO₂e per cup, and drip filter coffee had the highest environmental impacts per cup.9 The study assumed 13.5 g of ground coffee per filter cup, including 33% losses, 6.5 g per capsule and 2 g of soluble coffee.9 For soluble coffee, more than half of the impacts arose in the use phase.9 The 2024 review found that press-based and instant drinks tended to have lower impacts than pod coffee.7
Milk drinks#
Two studies give footprints per drink. They differ in boundary and in the coffee they assume, so the values are shown side by side, not combined.
Data table
| g CO₂e per serving | Source | |
|---|---|---|
| Espresso · UK, air freight | 280 | 8 |
| Espresso · UK, sea freight | 60 | 8 |
| Espresso · Thailand | 160 | 11 |
| Flat white · UK, air freight | 340 | 8 |
| Flat white · UK, sea freight | 130 | 8 |
| Cappuccino · UK, air freight | 410 | 8 |
| Cappuccino · UK, sea freight | 200 | 8 |
| Cappuccino · Thailand | 506 | 11 |
| Latte · UK, air freight | 550 | 8 |
| Latte · UK, sea freight | 330 | 8 |
| Latte · Thailand | 541 | 11 |
| Mocha · Thailand | 625 | 11 |
| 40 mL cup, coffee left out · moka pot | 8.1 | 10 |
| 40 mL cup, coffee left out · capsule | 10 | 10 |
| 40 mL cup, coffee left out · pod | 18.5 | 10 |
| Drink | 2020 UK study, conventional | 2020 UK study, sustainable | 2023 Thai study |
|---|---|---|---|
| Espresso | 2808 | 608 | 16011 |
| Flat white | 3408 | 1308 | – |
| Cappuccino | 4108 | 2008 | 50611 |
| Latte | 5508 | 3308 | 54111 |
| Mocha | – | – | 62511 |
Values in g CO₂e per serving; the 2020 study reports kg (0.28 kg = 280 g).8 In the 2020 study, “the larger proportion of milk than coffee used in these beverages resulted in a significant increase in carbon footprint”.8 In the Thai study, cow’s milk and chocolate were the raw materials with the highest emissions.11 No study opened for this entry compared plant-based drinks in coffee.
Reference values#
| Parameter | Value | Functional unit and boundary | Source |
|---|---|---|---|
| Range across studies | 0.15–14.5 (median 3.6) kg CO₂e | Per kg green coffee, up to green coffee production; review of 34 studies | Chéron-Bessou et al.7 |
| With land-use change | 1.63–10.52 kg CO₂e | Per kg green coffee; systems that included land-use change, IPCC Tier 1 | Chéron-Bessou et al.7 |
| Drinks | 2–23 (median 8.8) kg CO₂e | Per kg coffee consumed in drinks | Chéron-Bessou et al.7 |
| Share of green coffee production | Median 63% | Cradle to grave | Chéron-Bessou et al.7 |
| Share of synthetic fertilisers | Median 66% | Green coffee, land-use change apart | Chéron-Bessou et al.7 |
| Share of transport | Median ≈3%, up to 12% (sea); up to >73% (air) | Cradle to grave | Chéron-Bessou et al.7 |
| Share of roasting and grinding | Median 8% | Cradle to grave | Chéron-Bessou et al.7 |
| Brazil to UK, conventional | 1.01 growing; 0.10 milling; 10.44 export (air); 3.05 roasting to cup; total 14.61 kg CO₂e | Per kg green arabica; land-use change excluded | Nab & Maslin8 |
| Brazil to UK, sustainable | 0.05 growing; 0.08 milling; 0.19 export (sea); 3.05 roasting to cup; total 3.37 kg CO₂e | Same | Nab & Maslin8 |
| Vietnam to UK | 16.04 (conventional); 3.64 (sustainable) kg CO₂e | Same | Nab & Maslin8 |
| Average of both origins | 15.33 ± 0.72 (conventional); 3.51 ± 0.13 (sustainable) kg CO₂e | Same | Nab & Maslin8 |
| Brazil, farm gate | ≈1.4 (conventional); ≈0.3 (organic) kg CO₂e | Per kg green coffee, cradle to farm gate | Coltro et al.13 |
| Costa Rica and Nicaragua trials | 0.26–0.67 (conventional); 0.12–0.52 (organic) kg CO₂e | Per kg fresh cherry | Noponen et al.12 |
| Soluble coffee | 0.07 kg CO₂e | 1 dl cup, cradle to grave | Humbert et al.9 |
| Brewing per cup | 60.27 g (automatic machine); 10.04 g (filter or French press) CO₂e | Per cup, use phase (from the 2008 German pilot study) | Nab & Maslin8 |
Open questions#
- How to account for land-use change and carbon stored in shade trees in a way that all studies share is not settled; the review names at least 20 years as the consensual time frame and asks for a mass balance.7
- Emissions from fermentation and wastewater in wet and semi-washed processing are poorly measured; the review calls for more primary data.7
- No common functional unit exists that includes green coffee moisture or the sensory quality of the drink.7
- The 2024 review left drinks with milk or sugar out, so its ranges for drinks do not cover milk drinks.7
Key studies#
Chéron-Bessou et al., 2024 – Why coffee LCA results differ. A systematic review of 34 life-cycle studies covering 234 coffee systems. Footprints ranged from 0.15 to 14.5 kg CO₂e per kg green coffee; land-use change, fertilisers and washed (“wet”) processing drove the farm stage, and green coffee production the drink. The authors name inconsistent accounting choices among the sources of the spread and call for a standard functional unit.
Nab & Maslin, 2020 – Brazil and Vietnam to the UK. A synthesis LCA of arabica coffee, comparing a conventional chain (air freight, synthetic inputs) with a “sustainable” one (sea freight, organic inputs). The “sustainable” chain came out 77% lower, which the authors attribute to sea instead of air freight and fewer agrochemicals. Its roasting-to-cup data came from an earlier German pilot study, and a later review excluded it from its averages.
Humbert et al., 2009 – Soluble, capsule and filter coffee. A full life-cycle LCA of a 1 dl cup made three ways, with primary data from a coffee producer; it was not critically reviewed by an external panel. Soluble coffee had the lowest footprint and drip filter coffee the highest environmental impacts per cup. The amount of extra water boiled and the efficiency of cup cleaning were key parameters.
Cibelli et al., 2021 – Moka, capsule and pod. Compared the footprint of a 40 mL cup made with an induction moka pot, a capsule machine and a pod machine, leaving out the coffee itself. The moka pot came out lowest, at about 8 g CO₂e; packaging production was the largest part of the capsule and pod footprints.
- Size of the footprint per kg of green coffee: a 2024 systematic review of 34 studies found 0.15–14.5 kg CO₂e per kg (median 3.6). It names land-use change accounting, field emissions and wet-process modelling as sources of inconsistency, but could not separate how much of the spread is methodological.7 One Brazilian farm-gate study found about 1.4 (conventional) and 0.3 (organic).13
- Air freight in the 2020 UK comparison: the authors attribute the 77% lower footprint of their “sustainable” chain to sea instead of air freight and fewer agrochemicals.8 The 2024 review excluded the study from its averages because of “a possible flaw in the theoretical modelling of supply chains”, and found sea transport to add a median of about 3%.7
- Filter, capsule and instant per cup: a 2009 LCA found drip filter coffee to have the highest environmental impacts per cup, assuming 13.5 g of coffee including losses.9 The 2024 review found press-based and instant drinks lower than pod coffee.7 A 2021 study found an induction moka pot lower than capsule and pod machines, but left out the coffee itself.10 Dose and boundary differ between them.
- Shade and footprint: according to the research programme behind a 2014 study of four coffee production systems, commercial polycultures “are among the most promising ways of producing coffee with a low carbon footprint”.14 The 2024 review, across its studies, found “no clear difference in the GWP between different cropping system type, with large variabilities within each type”.7
- Organic versus conventional per kg: in a Brazilian cradle-to-farm-gate study, organic coffee came to about 0.3 kg CO₂e per kg green coffee against 1.4 for conventional.13 In Central American trials, the conventional (0.26–0.67) and organic (0.12–0.52) ranges per kg of cherry overlapped.12
Coffearium (2026). Carbon footprint of coffee. Coffearium – The open coffee compendium. Retrieved 22 October 2026, from https://coffearium.org/entries/carbon-footprint-of-coffee/
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title = {{Carbon footprint of coffee}},
year = {2026},
howpublished = {Coffearium -- The open coffee compendium},
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}Entries are updated when the evidence changes; the retrieval date tells your readers which version you used.
Sources
- AInternational Organization for Standardization (ISO) (2018). ISO 14067:2018 – Greenhouse gases – Carbon footprint of products – Requirements and guidelines for quantification. ISO, Geneva.
- AInternational Organization for Standardization (ISO) (2006). ISO 14040:2006 – Environmental management – Life cycle assessment – Principles and framework. ISO, Geneva.
- AInternational Organization for Standardization (ISO) (2006). ISO 14044:2006 – Environmental management – Life cycle assessment – Requirements and guidelines. ISO, Geneva.
- AEuropean Commission, Knowledge for Policy Carbon dioxide equivalent (glossary entry, after IPCC AR6 WGIII 2022). European Commission.
- AEuropean Commission, Knowledge for Policy Functional unit (glossary entry, after EN ISO 14040:2006). European Commission.
- AEuropean Commission, Knowledge for Policy Allocation (glossary entry, after Commission Recommendation 2013/179/EU and EN ISO 14040:2006). European Commission.
- AChéron-Bessou, C.; Acosta-Alba, I.; Boissy, J.; Payen, S.; Rigal, C.; Setiawan, A. A. R.; Sevenster, M.; Tran, T.; Azapagic, A. (2024). Unravelling life cycle impacts of coffee: Why do results differ so much among studies?. Sustainable Production and Consumption 47, 251–266. doi:10.1016/j.spc.2024.04.005 · other copies
- ANab, C.; Maslin, M. (2020). Life cycle assessment synthesis of the carbon footprint of Arabica coffee: Case study of Brazil and Vietnam conventional and sustainable coffee production and export to the United Kingdom. Geo: Geography and Environment 7(2), e00096. doi:10.1002/geo2.96 · other copies
- AHumbert, S.; Loerincik, Y.; Rossi, V.; Margni, M.; Jolliet, O. (2009). Life cycle assessment of spray dried soluble coffee and comparison with alternatives (drip filter and capsule espresso). Journal of Cleaner Production 17(15), 1351–1358. doi:10.1016/j.jclepro.2009.04.011 · other copies
- ACibelli, M.; Cimini, A.; Moresi, M. (2021). Carbon footprint of different coffee brewing methods. Chemical Engineering Transactions 87, 373–378. doi:10.3303/CET2187063 · other copies
- APhunphiphat, R.; Haputta, P. (2023). Carbon footprint of coffee drinks. Journal of Applied Science and Emerging Technology 22(1), e249700 (King Mongkut’s University of Technology North Bangkok).
- ANoponen, M. R. A.; Edwards-Jones, G.; Haggar, J. P.; Soto, G.; Attarzadeh, N.; Healey, J. R. (2012). Greenhouse gas emissions in coffee grown with differing input levels under conventional and organic management. Agriculture, Ecosystems & Environment 151, 6–15. doi:10.1016/j.agee.2012.01.019 · other copies
- AColtro, L.; Tavares, M. P.; Sturaro, K. B. F. S. (2024). Life cycle assessment of conventional and organic Arabica coffees: from farm to pack. The International Journal of Life Cycle Assessment 29(9), 1672–1687. doi:10.1007/s11367-024-02317-7 · other copies
- BNeno, S. (2014). Keys to climate-friendly coffee production. CGIAR Research Program on Climate Change, Agriculture and Food Security (CCAFS), news, 12 May 2014 – reports van Rikxoort et al. (2014), Agronomy for Sustainable Development 34(4), 887–897.
Tier A · authoritative · B · trade and expert · C · general. Supporting quotes for every source are in the data version of this entry. If a publisher’s site refuses access, try the doi link or “other copies”.
Discussion
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