The Official Information Portal on Anaerobic Digestion


The material that is used in anaerobic digestion is called feedstock. What goes into a digester determines what comes out, so careful choice of feedstocks is essential.  Securing a reliable feedstock supply is fundamental to profitable AD and if feedstocks are to be bought from a third party securing a long-term contract on acceptable terms is critical.

The feedstock doesn't have to be waste, any biodegradable non-woody plant or animal matter is a suitable feedstock for a digester. However, anaerobic micro-organisms cannot break down lignin, the complex polymer that gives plants their strength, which means that wood products, paper and straw will slow the digester.

The yield of biogas from a particular feedstock will vary according to the following criteria. Further detail on biogas yields and feedstock productivity is provided at the bottom of the page:

  • Dry matter content
  • The energy left in the feedstock, if it has undergone prolonged storage it may already have begun to break down
  • Length of time in the digester
  • The type of AD plant and the conditions in the digester
  • The purity of the feedstock

Common feedstock streams are described below and include:

Food and Drink Waste

Around 16 million tonnes (Mt) of post-farm gate food and drink waste arises annually in foodthe UK. Around half of this is waste is from households, the rest mostly comes from manufacture, retail, hospitality, other businesses and the public sector.

The most environmentally preferable treatment options for food waste are usually AD or composting. AD is generally preferable because it produces both renewable energy and a biofertiliser, which together do more to offset GHG emissions than producing compost. There are however some organic waste streams for which composting will remain the best option, such as co-collected food and garden waste, or woody garden waste that is collected on its own.

To be treated by ‘wet’ AD systems, food waste needs to be collected separately at source; to be treated by composting, or ‘dry’ AD systems, it can either be separately collected at source or mixed with green waste. The co-digestion of food waste in large sludge treatment plants has the potential to be an efficient way of producing energy from waste, particularly as many of the plants are conveniently located by urban centres.

There are several reports available on the treatment, use and availability of food waste;

  • Annual Organics Recycling Survey, providing information on the structure of the UK organics processing/recycling sector and the markets for its outputs.
  • Food Waste Collection Guidance, provides guidance for Local Authorities on the collection of food waste for recycling.
  • Annual Gate Fees report, presents a summary of gate fees charged for AD and alternative waste treatment, recovery and disposal options.
  • The Food Waste Resources Portal, a signposting tool which provides links to the most up to date and relevant sources of data on the different sources of food waste which could be used as feedstock for anaerobic digestion.
  • The Quality Protocol for anaerobic digestate which lists biodegradable wastes that can be used in AD can be found in Appendix B of the
Processing Residues

The key to a viable and sustainable AD project is a secure supply of quality feedstock. Processing residues such as bakery or brewery waste are good feedstocks for AD, as they offer consistency and a more stable supply. Interest from food and drink manufacturers is strong, developing on-site facilities to convert an otherwise costly waste-stream into a potentially valuable revenue stream.

Examples of such facilities are included on the Case Studies Page; particular examples are Nestle and BV Dairy.

Agricultural Residues

In the UK an estimated 90 million tonnes of manures and slurries are generated each year. These are generally used on the farms where they arise, recycling the nutrients that they contain. The Nitrate Vulnerable Zone (NVZ) Regulations mean that many organic manures cannot be spread in certain periods of the year and must be stored for an extended period before being landspread as fertilisers. There is potential for AD to be used in this situation to capture methane from stored slurries and manures, and also to stabilise and treat these materials.

The digestate produced has a lower biological oxygen demand and can be used as a more uniform, easily calibrated fertiliser than the original untreated manure. Methane emissions from manure management are reduced, and the fossil fuels used in the manufacture of artificial fertiliser are displaced, saving 5 tonnes of CO2 for every one tonne of nitrogen.

cowThe EA has issued guidance to confirm that manures and slurries used as feedstock for AD will also not be treated as ‘waste’ if used as fertiliser. This applies to both solid and liquid digestate. Other nutrient management regulations and the requirements of the Codes of Good Agricultural Practice for the protection of soil, water and air are still applicable.

Crop residues are also a suitable feedstock for AD. Crop residues are defined as ‘production residues’ produced as an integral part of the commercial production of agricultural crops; these may include damaged or misshapen fruit or vegetables, trimmings and other plant parts which are not the intended end product, such as straw, leaves or tops. These can be collected from the field or from a packing unit, prior to leaving the farm-gate.

The EA has published a briefing note about the Use of Crop Residues in AD which clarifies when they are deemed a by-product or a waste.


Crops can be grown specifically for anaerobic digestion, for stabilising or supplementing other feedstocks such as low yielding slurries or variable quality food waste. Such crops include maize, grass silage, energy beet and wholecrop cereals for example, all of which can be incorporated effectively into existing crop rotations or management regimes.

Encouragement of rotation can result in enhanced yields from subsequent crops by replenishing nutrients, conditioning the soil, reducing the occurrence of soil-borne diseases and improving soil and water quality. Likewise, land which is not suitable for the production of food crops may be suitable to supply biomass to AD plants. However, it is important to be mindful of potential unintended consequences should there be significant areas of crops grown for AD feedstock.

Any intensive production of a single crop could cause environmental concern, whether grown for food, as an AD-specific crop biomass or for transport biofuels; these concerns are generally managed by applying agricultural best practice. The AD industry has published ‘Voluntary Guidelines on Best Practice for Crop Feedstocks in Anaerobic Digestion’ which draws together other relevant best practice principles.

From October 2015, electricity and heat generated by any UK anaerobic digester above 1MWe capacity that uses crops as a feedstock, must achieve a minimum greenhouse gas (GHG) saving of 60 per cent relative to fossil fuel to receive Renewable Heat Incentive (RHI) payments. To support this requirement, NNFCC has launched a GHG reporting tool for use by generators.

Sewage Sludge

AD is one of the most important methods for treating sewage sludge and roughly two thirds of the country’s sludge is already treated in this way. The water industry has a well-established infrastructure of AD plants and extensive knowledge of the technology and its operation. Other organic waste can be ‘co-digested’ with sewage sludge, but different regulatory regimes apply.

Around 75% of the 1.1 Mt of sewage sludge produced in England and Wales is used on agricultural land. The use of sewage sludge on agricultural land is regulated through the European Commission’s (EC) Sewage Sludge Directive (86/278/EEC). This is transposed through the Sludge (Use in Agriculture) Regulations 1989 (amended 1990).

Biogas Yields and Feedstock Productivity

The table below shows data on the potential biogas yields of feedstocks commonly used in anaerobic digestion (numbers given in italics are taken from an AD calculator produced for NNFCC by The Andersons Centre, all other numbers are from Biogas from Energy Crop Digestion by the IEA). All figures are based on fresh weight unless stated.

Feedstock Biogas Yield (m3/t) Feedstock Biogas Yield (m3/t)
Cattle slurry 15-25 (10% DM) Potatoes 276-400
Pig slurry 15-25 (8% DM) Rye grain 283-492
Poultry 30-100 (20% DM) Clover grass 290-390
Grass silage 160-200 (28% DM) Sorghum 295-372
Whole wheat crop 185 (33% DM) Grass 298-467
Maize silage 200-220 (33% DM) Red clover 300-350
Maize grain 560 (80% DM) Jerusalem artichoke 300-370
Crude glycerine 580-1000 (80% DM) Turnip 314
Wheat grain 610 (85% DM) Rhubarb 320-490
Rape meal 620 (90% DM) Triticale 337-555
Fats up to 1200 Oilseed rape 340-340
Nettle 120-420 Canary grass 340-430
Sunflower 154-400 Alfalfa 340-500
Miscanthus 179-218 Clover 345-350
Flax 212 Barley 353-658
Sudan grass 213-303 Hemp 355-409
Sugar beet 236-381 Wheat grain 384-426
Kale 240-334 Peas 390
Straw 242-324 Ryegrass 390-410
Oats grain 250-295 Leaves 417-453
Chaff 270-316 Fodder beet 160-180


A comprehensive list of biogas yield data is available via the CROPGEN Database.  The full database contains data for 729 different feedstocks and is available to download in Access format from CROPGEN here (4th item on the table). Here you will also find a useful on-farm energy and emissions calculator which can be used for calculating the energy requirements and GHGs for crop production and potential energy generation using an on-farm AD plant.