At a glance
- Anaerobic digestion breaks down organic material without oxygen to produce renewable gas and a nutrient-rich fertiliser.
- The biomethane it produces goes straight into the existing gas grid in place of fossil natural gas.
- It runs on farm residues, slurry, grass silage and food waste, turning low-value material into energy.
- Ireland targets up to 5.7 TWh of biomethane by 2030, which needs an estimated 140 to 200 new AD plants.
- The EU targets 35 billion cubic metres of biomethane by 2030, most of it from anaerobic digestion.
What it is
Anaerobic digestion breaks down organic material through micro-organisms that work without oxygen. It happens inside a sealed tank called a digester, where the same biology that breaks down matter in a marsh or a cow's stomach is captured and put to work. The process yields two useful things: biogas, a renewable energy carrier, and digestate, a nutrient-rich material that returns to the land.
Anaerobic digestion is one of the oldest energy processes known, used in some form for thousands of years1. Its value today rests as much on independence as on emissions. A plant built on local waste produces local energy, which loosens dependence on imported fossil fuel and builds resilience into the farms and communities that host it.
Anaerobic digestion turns material that would otherwise sit as waste or low-value residue into energy and fertiliser, which places it at the heart of a circular bioeconomy.
How it works
Organic material enters a warm, sealed digester and stays for several weeks while communities of micro-organisms break it down in four biological stages2,6. A steady temperature and gentle stirring keep the biology working evenly. Two streams come out: biogas rises off the top, and digestate is drawn from the bottom.
The raw biogas is a little over half methane, with most of the balance carbon dioxide3. Upgrading removes the carbon dioxide and trace gases, leaving biomethane that is chemically almost identical to fossil natural gas. Because it is so similar, biomethane injects straight into the existing gas grid and serves heat, industry or transport with no change to the appliances that burn it.
Biogas and biomethane, the difference
Biogas and biomethane are two stages of the same output, and the difference between them is purity. Biogas is the raw gas that leaves the digester. Biomethane is the upgraded gas that remains once the carbon dioxide and trace gases are removed.
Biogas is a mixture. It is a little over half methane, with most of the balance carbon dioxide, alongside small amounts of water vapour, hydrogen sulphide and other trace gases3. In that raw form it burns well on site for heat and electricity, which suits a plant that uses its energy where it stands.
Biomethane is almost pure methane. Upgrading strips out the carbon dioxide and trace gases until the gas reaches around 98 per cent methane, chemically almost identical to fossil natural gas. That purity lets biomethane inject straight into the existing grid and serve heat, industry and transport, with no change to the appliances that burn it. The carbon dioxide removed during upgrading is biogenic, so a plant can capture it for horticulture, food or industry rather than release it.
| Feature | Biogas | Biomethane |
|---|---|---|
| What it is | Raw gas straight from the digester | Upgraded, purified gas |
| Methane content | A little over 50 per cent | Around 98 per cent |
| Main use | Heat and electricity on site | Grid injection, industry, transport |
| Grid ready | Not without upgrading | Yes, interchangeable with natural gas |
| Carbon dioxide | Stays within the gas | Captured separately as biogenic CO2 |
Reputed to date back to the ancient world, anaerobic digestion is among the oldest processes now being repurposed for modern energy.
How anaerobic digestion evolved
Anaerobic digestion is an old technology, not a new one. People often place its origins in the 1970s energy crisis, yet the process reaches back thousands of years1.
The Sumerians recognised fermentation around 4000 BC, and anecdotal accounts have the Assyrians using biogas to heat bath water as early as the 10th century BC1. Scientific understanding arrived much later. In the 17th century Jan Baptista van Helmont recorded combustible gas rising from decomposing matter, and in 1776 Alessandro Volta put marsh gas on a scientific footing. In 1808 Sir Humphry Davy confirmed that methane forms during the anaerobic digestion of manure. Builders raised the first purpose-built digester at a colony in Bombay in 1859, and by 1895 biogas recovered from a sewage works lit the streets of Exeter. The 1930s marked the turning point, when advances in microbiology identified the anaerobic bacteria and the conditions that promote methane, work that still underpins how the four stages of digestion are understood today6. Across the twentieth century the technology moved from waste treatment towards energy recovery, and today it stands as a mature route to renewable gas, integrated into combined heat and power and into the biomethane systems on which policy now depends4.
| Date | Milestone |
|---|---|
| 4000 BC | Sumerians identify the fermentation process. |
| 10th century BC | Assyrians reportedly use biogas to heat water. |
| 17th century | Van Helmont observes combustible gas from decomposing biomass. |
| 1776 | Volta places marsh gas on a scientific footing. |
| 1808 | Davy confirms methane from the digestion of manure. |
| 1859 | First purpose-built digester, Bombay. |
| 1895 | Sewage biogas lights the streets of Exeter. |
| 1907 | Imhoff tank patented in Germany. |
| 1930s | Microbiology identifies the anaerobic bacteria and the conditions for methane. |
| 1970s | Energy crisis drives funding and the plug-flow manure digester. |
| 2000 to date | Biogas fuels combined heat and power and tri-generation systems. |
Milestones after Rufai (2010).
The crop that feeds the digester
Multi-species swards give the digester a better feedstock and the land a lighter footprint. These leys combine grasses, clovers and deep-rooting forbs such as plantain and chicory, an approach with deep roots of its own in the Clifton Park system of deep-rooting leys that till, manure and clean the land20.
Figures below run in kilograms of dry matter per hectare, the standard unit across the EU, with the acre equivalent in brackets for Irish and UK readers.
Diverse swards produce more herbage on less nitrogen. A multi-species sward of ryegrass, timothy, red clover, plantain and chicory yielded 11,679 kg of dry matter per hectare (4,730 kg per acre) with no fertiliser nitrogen, against 5,885 kg per hectare (2,380 kg per acre) for perennial ryegrass grown the same way7. The same mixtures matched at 120 kg of nitrogen per hectare (49 kg per acre) the yield that ryegrass reached only at 360 kg per hectare (146 kg per acre)7. Red clover carries its own weight: across six years it averaged 14,906 kg of dry matter per hectare (6,030 kg per acre) each year, level with perennial ryegrass fed 600 kg of nitrogen per hectare (243 kg per acre)8.
More methane from a mixed feedstock
Grass and forbs digested together yield more methane than either yields alone. The mixture balances the carbon-to-nitrogen ratio that the micro-organisms need.
Co-digesting grass and forbs raised methane yield by 31 litres per kilogram of volatile solids, an 11 per cent gain, and shortened the start-up lag by 0.8 of a day10. Plantain drove the most consistent gain. In field trials, unfertilised grass-clover-forb mixtures met the European target of a 60 per cent cut in greenhouse gas emissions against fossil fuel, and plantain mixtures produced the highest methane energy output9.
The feedstock
Anaerobic digestion runs on organic feedstocks, and a well-designed plant draws on several at once:
- Farm residues and animal slurry, which would otherwise release methane as they break down in the open.
- Grass silage and crop residues grown or gathered for the purpose.
- Food waste and by-products from processing, such as brewers' grain.
Because it uses residues and wastes, anaerobic digestion produces energy alongside food production rather than in place of it, provided the feedstock system is designed with that in mind. Organic and food waste, which makes up a large share of municipal waste, is a particularly well-studied feedstock for biogas5.
The outputs
Anaerobic digestion earns its value across the whole of its output, not the gas alone:
- Biomethane. Renewable gas for the grid, industry and transport, displacing fossil natural gas.
- Digestate. A nutrient-rich material returned to the land as fertiliser, keeping nitrogen and phosphorus in the soil cycle and reducing the need for manufactured fertiliser.
- Biogenic carbon dioxide. The carbon dioxide separated during upgrading is biogenic, so it can be captured and used or stored rather than released.
Where a plant adds pyrolysis, digestate converts into biochar, a stable form of carbon that locks carbon into the soil for the long term.
The environmental case
Anaerobic digestion captures methane that would otherwise reach the air. The waste and agriculture sectors produce around 60 per cent of human-caused methane emissions, and digestion turns that methane into fuel16.
Diverse swards cut emissions in the field as well as in the tank. A six-species mixture lowered nitrous-oxide emissions per unit of nitrogen yield by 41 per cent against a ryegrass monoculture at the same fertiliser rate, and by 24 per cent per unit of dry-matter yield11. Digesting cattle manure cut storage emissions by a median of 43 per cent12. Processing the digested manure adds a further cut: high-efficiency solid-liquid separation lowers greenhouse gas emissions from manure by up to 60 per cent13. At global scale, biomethane could avoid up to 1,000 million tonnes of greenhouse gas emissions a year by 204016.
Decoupling from fossil fuel
Home-grown biomethane replaces imported fossil gas unit for unit. Ireland imports most of its energy, which leaves prices and supply exposed to events beyond national control.
Biomethane closes part of that gap. Ireland's National Biomethane Strategy targets 5.7 TWh of domestic biomethane a year by 2030, enough for around 10 per cent of national gas demand, built across 140 to 200 new plants17. Meeting that target would save cumulative emissions of more than 2.1 million tonnes of carbon dioxide equivalent17. Every unit of home-grown renewable gas that flows through the grid displaces a unit of imported fossil gas.
What resilience means for a renewable energy project
Resilience describes how well an energy system holds up when something goes wrong. The IEA defines it as the capacity of the system to cope with a hazardous event, keep its essential functions, and recover afterwards15.
Four properties carry that capacity. Robustness lets the system absorb stress and keep working. Redundancy supplies backup routes so one failure stays contained. Flexibility lets the system adjust as conditions shift. Recovery restores full service after an outage15.
Biomethane strengthens each property. The plants run continuously and store gas for dispatch on demand, which adds robustness when wind and solar drop. Local feedstock and distributed plants add redundancy and reduce dependence on imports. The gas moves through infrastructure that already exists, which speeds recovery. Diverse crops give diverse feedstock, and a diverse supply resists shocks.
One system, four benefits
Anaerobic digestion earns its place for several reasons at once. It displaces fossil gas with a renewable alternative that uses infrastructure already in the ground. It captures methane from slurry and waste before that methane reaches the atmosphere, where it warms far more strongly than carbon dioxide. It returns nutrients to the soil and keeps organic material in productive use. It supports rural economies, giving farmers a market for residues and a stake in the energy transition happening on their own land.
Those benefits together make anaerobic digestion one of the few technologies that serve energy, agriculture, waste and rural livelihoods in a single system.
Living alongside a digester
Modern anaerobic digestion plants run sealed and monitored, which keeps them safe to operate and manageable for the community around them. A well-run plant contains its process from the moment feedstock arrives to the point gas leaves for the grid. Climaticus plants run on agricultural waste, and the slurry is dewatered in preparation before it enters the digester, which concentrates the feedstock and cuts the volume handled on site.
Odour stays contained because the process is enclosed. Slurry and farm residues sit within covered tanks and sealed handling rather than open stores, so the smells usually linked to them stay inside the system. Plants use covered reception areas and biofilters to manage air quality, which is why a well-sited digester works as a good neighbour. Digestate adds a further gain, because it is more stable and lower in odour than raw slurry, so spreading seasons stay quieter14.
Safety rests on containment and monitoring. Operators run the digester as a sealed vessel, track gas composition and pressure continuously, and follow established procedures for handling biogas. Traffic and siting are planned in advance, with feedstock logistics designed to hold steady across the seasons and to route sensibly around the local area.
The community's role
Anaerobic digestion runs on material that comes from the land around it, which gives the local community a real place in a project rather than a view of it from the fence. That place takes several forms, and Climaticus structures each one to be genuine.
As feedstock suppliers. Farmers and landowners provide the slurry, residues and grass that feed the digester, and a fair return on that supply is the first way value flows back into the local economy. Climaticus organises this supply through cooperative hubs, which aggregate feedstock across neighbouring farms and keep the value in the local area. A well-run hub pays farmers properly and holds steady across the seasons.
As hosts. The community around a plant lives with its siting, its traffic and its daily operation, so it holds a legitimate voice in how the project is planned. Engagement that begins before decisions are fixed, and that answers the questions people actually hold, turns a host community from a bystander into a participant.
As owners and investors. Communities can hold a stake in the infrastructure itself, through cooperative structures, community shares, green bonds or revenue-sharing arrangements, so that financial return reaches beyond developer level. Green bonds raise finance specifically for environmental projects, and anaerobic digestion qualifies under the recognised use-of-proceeds categories of renewable energy, sustainable waste management and the circular economy19. Where these mechanisms suit a project, they attach real money to local participation.
As beneficiaries. Digestate returns nutrients to local soil, community benefit funds direct revenue to local priorities, and locally produced gas serves local energy needs. The benefit lands where the material and the goodwill come from.
As monitors. A community that sees a plant's real performance data, in plain language and without having to ask, holds the project to its commitments. Open access to operating information keeps trust once a plant is running.
The sector already supports work at scale. Biogas and biomethane support more than 210,000 jobs across the European Union, projected to reach around 420,000 by 203018. Taken together, these roles make the community a genuine partner in the project. That is the standard Climaticus applies through Civitas by Climaticus and its shared-value commitments.
Recognised in policy
Governments now treat anaerobic digestion as core infrastructure for decarbonising gas. Ireland's National Biomethane Strategy commits to up to 5.7 TWh of indigenous biomethane by 2030, which would meet around a tenth of national gas demand, requires an estimated 140 to 200 new AD facilities, and saves cumulative emissions of more than 2.1 million tonnes of carbon dioxide equivalent17.
Across the European Union, the REPowerEU plan targets 35 billion cubic metres of biomethane by 2030, most of it produced through anaerobic digestion, backed by a dedicated Biomethane Action Plan.
The scale of that ambition is large and the timetable is short, which is why building the industry well matters as much as building it quickly.
The full Irish, EU and UK regulatory landscape, including RED III, the Nitrates Directive, RENURE, the Carbon Removal Certification Framework and the UK Green Gas Support Scheme, sits on The Biomethane Market page.
How Climaticus works with anaerobic digestion
Climaticus works across the whole chain that an AD project depends on: feedstock origination, project development, community engagement, verification and market connection. Our aim is anaerobic digestion done in a way that stands up technically, earns genuine consent locally, and delivers real benefit to the farmers and communities whose land and material make it possible.
To see how we ground that work in evidence, read about our research. To understand how we build community consent, read about Civitas.
Frequently asked questions
For the Irish market and stakeholder pathways, see Anaerobic Digestion in Ireland. For demand-side and reporting regulation, see The Biomethane Market.
Notes and references
- 1. Rufai, I.A. (2010). A Review of the Evolution and Development of Anaerobic Digestion Technology. Journal of Engineering and Technology, 5(1). https://www.researchgate.net/publication/335992164
- 2. Appels, L., Baeyens, J., Degrève, J., Dewil, R. (2008). Principles and potential of the anaerobic digestion of waste-activated sludge. Progress in Energy and Combustion Science, 34(6), 755–781. https://www.sciencedirect.com/science/article/abs/pii/S0360128508000312
- 3. Weiland, P. (2010). Biogas production: current state and perspectives. Applied Microbiology and Biotechnology, 85(4), 849–860. https://doi.org/10.1007/s00253-009-2246-7
- 4. Uddin, M.M., Mba Wright, M. (2021). Anaerobic digestion fundamentals, challenges, and technological advances. Physical Sciences Reviews. https://doi.org/10.1515/psr-2021-0068
- 5. Triviño-Pineda, J.S. et al. (2024). Biogas production from organic solid waste through anaerobic digestion: A meta-analysis. Case Studies in Chemical and Environmental Engineering, 9, 100618. https://www.sciencedirect.com/science/article/pii/S2666016424000124
- 6. Harirchi, S. et al. (2022). Microbiological insights into anaerobic digestion for biogas, hydrogen or volatile fatty acids: a review. Bioengineered, 13(3), 6521–6557. https://doi.org/10.1080/21655979.2022.2035986
- 7. Moloney, T. et al. (2020). Yield of binary- and multi-species swards relative to single-species swards in intensive silage systems. Irish Journal of Agricultural and Food Research, 59, 12–26. https://sciendo.com/article/10.2478/ijafr-2020-0002
- 8. Clavin, D. et al. (2016). Red clover for silage: management impacts on herbage yield, nutritive value, ensilability and persistence. Grass and Forage Science, 72, 414–431. https://doi.org/10.1111/gfs.12249
- 9. Cong, W.-F. et al. (2017). Forbs enhance productivity of unfertilised grass-clover leys and support low-carbon bioenergy. Scientific Reports, 7, 1422. https://doi.org/10.1038/s41598-017-01632-4
- 10. Cong, W.-F. et al. (2018). Anaerobic co-digestion of grass and forbs. Biomass and Bioenergy, 119, 90–96. https://doi.org/10.1016/j.biombioe.2018.09.009
- 11. Cummins, S. et al. (2021). Beneficial effects of multi-species mixtures on N2O emissions from intensively managed grassland swards. Science of the Total Environment, 792, 148163. https://doi.org/10.1016/j.scitotenv.2021.148163
- 12. Miranda, N.D., Tuomisto, H.L., McCulloch, M.D. (2015). Meta-Analysis of Greenhouse Gas Emissions from Anaerobic Digestion Processes in Dairy Farms. Environmental Science and Technology, 49(8), 5211–5219. https://doi.org/10.1021/acs.est.5b00018
- 13. Aguirre-Villegas, H.A., Larson, R.A., Sharara, M.A. (2019). Anaerobic digestion, solid-liquid separation, and drying of dairy manure. Science of the Total Environment, 696, 134059. https://doi.org/10.1016/j.scitotenv.2019.134059
- 14. Martín-Sanz-Garrido, C. et al. (2025). A Review on Anaerobic Digestate as a Biofertilizer. Applied Sciences, 15, 8635. https://doi.org/10.3390/app15158635
- 15. Jasiunas, J. et al. (2021). Energy system resilience: a review. Renewable and Sustainable Energy Reviews, 150, 111476. https://doi.org/10.1016/j.rser.2021.111476
- 16. International Energy Agency (2020). Outlook for Biogas and Biomethane: Prospects for Organic Growth. https://www.iea.org/reports/outlook-for-biogas-and-biomethane-prospects-for-organic-growth
- 17. Gas Networks Ireland (2024). National Biomethane Strategy and biomethane network pages. https://www.gasnetworks.ie/network/biomethane
- 18. European Biogas Association (2023). Statistical Report. https://www.europeanbiogas.eu
- 19. ICMA (2021). Green Bond Principles. https://www.icmagroup.org
- 20. Elliot, R.H. (1943). The Clifton Park System of Farming.
