Co-disposal of food waste and sewage sludge is a sustainable waste management strategy primarily implemented through anaerobic co-digestion (AcoD) at wastewater treatment plants (WWTPs). This process offers significant environmental and economic benefits, including enhanced renewable energy generation, waste reduction, and nutrient recovery.
Key Points
- Co-disposal of food waste and sewage sludge can increase biogas production by up to 7 times, providing renewable energy that covers up to 100% of a sewage treatment plant's electricity needs.
- The integrated approach creates a triple win of economic, environmental, and social benefits through resource recovery and waste reduction.
- Anaerobic co-digestion optimizes organic loading rates and system stability while reducing greenhouse gas emissions substantially compared to traditional separate treatment methods.
- Pre-treatment of food waste is essential before mixing with secondary sludge to ensure optimal digestion performance.
- Modern wastewater treatment facilities can transform from energy consumers into energy producers through strategic implementation of co-disposal systems.
Food waste and sewage sludge co-disposal represents one of the most promising advancements in sustainable waste management today. Rather than treating these waste streams separately, integrated systems leverage the complementary properties of both materials to maximize resource recovery and energy generation.

Integrating Food Waste and Sewage: A Potent Solution for Resource Recovery
Combining food waste with sewage sludge can create a symbiotic effect that tackles many waste management problems at once. When done right, co-disposal systems can turn conventional wastewater treatment plants from energy users into energy creators. This change in perspective provides a circular economy solution that recovers resources from materials that were once seen as nuisances to be disposed of at a high cost.
Present Waste Management Issues
Conventional waste management methods treat food waste and sewage as individual streams, overlooking important recovery possibilities. Food waste often ends up in landfills, where it produces methane—a powerful greenhouse gas—and takes up valuable landfill space.
On the other hand, traditional sewage treatment uses a lot of energy and produces surplus sludge that must be disposed of. The separated approach results in inefficiencies, increased operational expenses, and unnecessary environmental damage.
There are many challenges associated with the logistics of food waste collection. Many municipalities have a hard time implementing effective systems for separating and transporting waste.
These challenges have resulted in low capture rates and contaminated waste streams, which limit the options for recovery. The economic burden of managing these separate systems falls on local governments and, ultimately, taxpayers. To address these issues, some municipalities are exploring best practices for recycling organic waste to improve efficiency and reduce costs.
Advantages of Merging These Two Waste Products
Co-disposal turns these problems into possibilities. Studies have shown that combining food waste with sewage sludge can multiply biogas production by up to seven times compared to processing sewage sludge by itself.
This increased energy recovery generates a useful source of renewable energy while decreasing waste amounts and the costs associated with disposal. For more information on how innovative technologies are reducing landfill dependence, check out this resource.
This combined method also enhances the carbon-to-nitrogen ratio of the feedstock, creating more ideal conditions for microbial activity during anaerobic digestion.
This balanced nutrient profile boosts process stability and efficiency, making treatment plants more resistant to changes in waste composition and flow.
The environmental advantages are also substantial. Research indicates that combined approaches can enhance energy balance by 83-126% and lower net greenhouse gas emissions by around 90% in comparison to individual treatment techniques.
These advancements demonstrate significant strides towards achieving carbon neutrality in waste management operations.
Effective Approaches in Practice
A number of wastewater treatment facilities have proven the success of co-disposal methods.
In one such success story, a sewage treatment plant that implemented co-digestion was able to handle around 197 tons of food waste every day, and in doing so, generated 11,280 kW of electricity daily. This production of renewable energy covered 31.8% of the plant's total electricity requirements, resulting in substantial savings in operational costs.
Research from Hong Kong has shown that co-disposal scenarios can significantly improve both economic and environmental outcomes.
The research found that integrated treatment greatly improved the energy balance, reduced the amount of greenhouse gas emissions, and improved the economic viability of operations compared to existing separate treatment methods.

Understanding Co-disposal: The Mechanics of the Operation
Basics of Anaerobic Digestion
Co-disposal systems are primarily powered by anaerobic digestion (AD), a biological procedure where microbes decompose organic materials without the presence of oxygen.
This is a natural process that takes place in four key steps: hydrolysis, acidogenesis, acetogenesis, and methanogenesis.
Each step involves a variety of microbial communities that work in a specific order to transform complex organic compounds into biogas (mainly methane and carbon dioxide) and digestate (a byproduct rich in nutrients).
How Food Waste and Sewage Work Together
When food waste and sewage sludge are mixed together, they create the perfect environment for microbial activity. Food waste usually has a high carbon content and energy potential, but it can be hard to digest on its own because it acidifies quickly.
Sewage sludge provides the capacity to buffer and a variety of microbial communities that stabilize the digestion process. This mutually beneficial relationship allows for higher organic loading rates and a more stable system than systems that digest a single substrate.
While the perfect blend depends on the nature of the waste, studies have shown that including food waste in the mix at 20-50% of the total volume of feedstock often yields the best results. This ratio balances the production of biogas with the stability of the process.
Pre-treating food waste, which historically has involved grinding, screening, but nowadays due to concerns about creating microplastic and nanoplastic is best done using Depackaging and Separation machines like the Drycake Twister. These produce a clean pulp, and guarantee that the particle size is appropriate and that any contaminants are removed before the waste is mixed with the secondary sludge from the wastewater treatment process.
Creating Biogas and Recovering Energy
Co-disposal produces biogas that is about 60-70% methane, which is an outstanding source of renewable fuel. Contemporary facilities collect this biogas and use it in combined heat and power (CHP) units to generate electricity and thermal energy.
The electricity can be used to power the operations of the plant, while the thermal energy is used to heat the digesters to the optimal temperatures (usually 35-38°C for mesophilic digestion or 50-57°C for thermophilic processes) and to provide heat for the buildings of the facility.
Modern facilities have the ability to enhance biogas to biomethane by eliminating carbon dioxide and other pollutants, resulting in a renewable natural gas that adheres to pipeline quality requirements.
This biomethane can be injected into natural gas systems or used as fuel for vehicles, increasing the potential income streams and environmental advantages of the combined disposal method.
Opportunities for Nutrient Retrieval
Co-disposal systems offer more than just energy production, they also have a high potential for nutrient recovery. The digestate that is left over after anaerobic digestion is rich in valuable nutrients like nitrogen, phosphorus, and potassium that can be reused as agricultural fertilizers.
More advanced technologies such as struvite precipitation can be used to recover phosphorus in a crystalline form that can be used as a slow-release fertilizer. Nitrogen can be recovered through ammonia stripping processes or it can be preserved in the liquid part of the digestate for use in agriculture.
Not only does this nutrient recovery process create additional value streams, but it also reduces the environmental impacts associated with synthetic fertilizer production.
It closes nutrient cycles by returning food-derived nutrients to agricultural systems and reducing the risk of waterbody eutrophication from excess nutrient discharge, as discussed in this related study.
Why Co-disposal Systems Are Better for the Environment
Compared to traditional waste management methods, co-disposal systems offer significant environmental benefits. These systems capture methane that would otherwise be released into the atmosphere, directly reducing greenhouse gas emissions.
In addition, the renewable energy produced by these systems displaces the consumption of fossil fuels, providing even more benefits for the climate. Moreover, by reducing the need for separate waste collection, these systems also reduce vehicle emissions and traffic congestion in cities.
Life cycle assessments have consistently shown that integrated treatment methods are superior to managing food waste and sewage sludge separately across a variety of environmental impact categories.
The circular economy approach maximizes the value of resources while reducing the need for new materials and energy sources.
Lowering Carbon Emissions (by as much as 47%)
Research shows that co-disposal systems can lower carbon emissions by as much as 47% compared to traditional waste management methods. The reduction is the result of three main factors: reduced methane emissions from landfills, less reliance on fossil fuels, and lower transportation needs.
Methane's effect on the climate is especially significant, as it has about 28 times the global warming potential of carbon dioxide over a 100-year period. By capturing this powerful greenhouse gas and converting it into energy, co-disposal systems offer immediate climate benefits and produce renewable energy that further reduces emissions from traditional power generation.
Less Landfill Space Needed
In developed countries, food waste usually makes up 20-30% of the municipal solid waste that ends up in landfills.
If this waste is instead diverted to co-disposal systems, cities can greatly increase the lifespan of their landfills and cut down on the need for new ones. This also gets rid of the problems of leachate, bad smells, and pests that come with putting food waste in landfills.
Using anaerobic digestion to reduce volume also cuts down on the need for solid waste management, as this process breaks down around 50-70% of the volatile solids in the feedstock. This leaves a much smaller volume to be processed or reused.
Water Saving Effects
There are also water-saving benefits to combined treatment methods, as they optimise water use across waste streams. The water content of food waste is typically 70-90%, which adds valuable moisture to the digestion process without the need for additional freshwater inputs.
The liquid fraction that is separated from the digestate can be recirculated within the treatment system or used for irrigation after the quality has been checked, which further reduces the demand for freshwater.
These water-saving benefits are becoming more and more important as climate change and population growth increase the pressure on water resources in many parts of the world.
Financial Benefits of Combined Disposal Systems
The financial advantages of co-disposing food waste and sewage make a strong argument for wastewater treatment plants. What was once considered a cost to operations can become a source of income through the strategic use of co-digestion systems.
The many financial benefits go beyond just reducing costs to also creating new sources of income and strengthening the infrastructure for the long term.
Energy Independence in Treatment Plants
Wastewater treatment is a significant expense for utilities, typically consuming 1-3% of a nation's total electricity. However, co-disposal systems can dramatically reduce this dependency. Documented examples have shown that up to 31.8% of a treatment plant's electricity needs can be met through on-site biogas generation.
Some advanced facilities have even achieved complete energy self-sufficiency or have become net energy exporters. This turns a major cost centre into a revenue opportunity. Additionally, this energy independence provides resilience against electricity price volatility and supply disruptions, enhancing operational security.
Saving Money on Operations
Co-disposal systems do more than just save energy, they also cut down on a number of other operating costs. When food waste and sewage sludge are turned into resources instead of waste, the fees for transporting and disposing of them drop dramatically.
The cost of chemicals often goes down too, because the combined feedstock has a balanced nutrient profile that reduces the need for additional chemicals during digestion.
The maintenance needs of digesters are usually about the same as they are for sludge-only operations, but the pre-treatment systems for food waste do need to be factored into the overall operating plan because they require additional maintenance.
Profit from Biogas and Byproducts
Biogas produced by co-digestion offers several ways to make money. You can generate electricity directly and use it to lower your utility costs. If you produce more than you need, you can sell it to the power grid. If your area has feed-in tariffs or renewable energy credits, you can earn even more.
You can also upgrade biogas to biomethane and sell it for use in natural gas grids or as vehicle fuel. The byproduct of the digestion process, digestate, can be sold as a soil amendment for agriculture or for the nutrients it contains, like struvite (magnesium ammonium phosphate). Struvite is a high-quality, slow-release fertiliser.
By producing several things you can sell, you can make your operation more financially stable. You won't have to rely on just one market.
Timeline for Recouping Investments
Financial evaluations suggest that co-disposal systems generally reach payback periods of 3-7 years, depending on local energy costs, tipping fees, and existing incentives. Initial capital costs include pre-treatment equipment for food waste, possible digester expansion, and biogas use infrastructure.
Although these investments are substantial, the operational savings and new income sources provide appealing returns compared to traditional infrastructure investments. Many facilities adopt phased strategies, starting with modest co-digestion rates and growing as operational experience and financial returns prove successful.
Solving the Problems of Implementation
Getting the Ratio of Food to Sewage Right
Getting the right balance of food waste and sewage sludge is a big challenge in operations. If there is too much food waste, the system can be overwhelmed by acidification that happens too quickly. If there is not enough, the potential for biogas is not reached. Most operations that are successful keep the addition of food waste at 20-50% of the total volume of digester feed.
This is adjusted based on the continuous monitoring of key parameters like biogas production, alkalinity, and volatile fatty acids. Facilities that are advanced have feeding systems that are automated. These adjust the ratios of input based on the analysis of digestate in real time. This ensures the best performance even if the composition of the waste changes. For more on sustainable waste management, explore organic waste recycling best practices.
Handling Varying Waste Amounts
The production of food waste follows expected seasonal and weekly trends that seldom match the variations in sewage flow.
Retail and restaurant waste usually reaches its peak on weekends, while food processing waste may follow seasonal harvest calendars. Efficient co-disposal systems include enough storage capacity to buffer these fluctuations, enabling constant digester feeding despite irregular collection times.
Many facilities use scalable methods that can handle increasing volumes of food waste as collection programs grow. This adaptability allows for testing and optimisation on a smaller scale before full implementation, reducing the operational risks during the transition period.
Regulatory Compliance Requirements in the US, Europe and the UK
Regulations for co-disposal vary significantly by region, creating compliance challenges for implementation. In the European Union, the Waste Framework Directive and Renewable Energy
Directive provide supportive frameworks for food waste diversion and biogas utilisation, though specific requirements vary by member state. The UK's Anaerobic Digestion Strategy and Action Plan specifically encourages co-disposal approaches while setting strict requirements for digestate quality when used in agriculture.
Across the United States, there are a variety of regulations at the federal, state, and local levels. The EPA's biosolids regulations (40 CFR Part 503) oversee the management of digestate, while the acceptance of food waste is typically regulated by state-level solid waste permits.
Facilities looking to co-dispose must start navigating this complex regulatory landscape early in the planning process, proactively engaging with regulators to address potential compliance challenges before making significant investments. For more insights, check out this guide on recycling organic waste.
How Can This Work In Your Town?
Successful co-disposal systems are not a one-size-fits-all solution. They require the collaboration of many different municipal departments. For example, water/wastewater utilities need to work closely with solid waste divisions, transportation departments, and environmental agencies to develop a comprehensive approach.
The first step is a feasibility assessment that takes into account the existing infrastructure, the amount of food waste available, the current disposal costs, and potential revenue opportunities. It's important to get stakeholders involved early in the process.
This includes local food businesses, waste haulers, and community representatives. This will help to build support and identify any potential issues. It may be a good idea to start with a pilot-scale operation. This could use food waste from controlled sources like food processors or institutional kitchens.
Once this is successful, it could then be expanded to include residential collection programs. EnviroSolutions offers a comprehensive consultation service.
This guides communities through each phase of implementation, from the initial assessment to full-scale operation. This ensures optimized performance and maximum environmental benefits.

Common Queries
There are often many queries from communities considering co-disposal systems, regarding how to implement them, what impacts they may have, and what benefits they offer.
The following responses are based on established research and operational experience from existing facilities around the world, and aim to address these concerns.
Is it safe to mix food waste and sewage together?
Yes, it is safe. When done correctly, co-disposal systems offer the same public health protections as traditional wastewater treatment, but with additional safeguards. The anaerobic digestion process usually works at higher temperatures (35-38°C for mesophilic or 50-57°C for thermophilic systems), which lowers pathogen levels.
Many systems include pasteurization steps that heat the material to 70°C for at least an hour, effectively eliminating any pathogens that may be present.
Modern digestion systems are closed off, which helps to prevent any potential health risks that could occur if there was exposure. All emissions, such as biogas and process air, are treated before they are released.
Additionally, digestate is managed appropriately based on what it will be used for. These multiple layers of protection help to prevent any potential health risks that could be associated with either waste stream.
How much food waste can be added to current sewage sludge digester systems?
Most wastewater treatment facilities can include food waste at 20-30% of the total digester feed volume without significant changes to the existing infrastructure. This addition usually boosts biogas production by 40-70% compared to sewage sludge alone.
Facilities looking for higher food waste ratios (up to 50%) usually need extra mixing capacity, improved biogas handling systems, and possibly increased digester volume.
Several factors determine the specific capacity, such as current digester loading rates, available hydraulic retention time, and existing biogas utilization infrastructure.
Facilities that have excess digester capacity due to being initially designed too large or changes in the service area often handle higher volumes of food waste without physically expanding.
Usually, the process begins with the addition of a small amount of food waste (5-10% by volume) and gradually increases while keeping an eye on key performance indicators.
This cautious approach allows operators to spot and deal with potential problems before they can affect the performance of the entire system.
Prior to embarking on any co-disposal project, it's crucial to carry out an in-depth capacity evaluation.
This should include a review of existing organic loading rates, hydraulic retention times, biogas handling capacity, and digestate management systems. This will help you understand the specific potential of your facility.
- Typical loading range: 0.5-2 kg volatile solids per cubic meter of digester volume per day
- Minimum recommended hydraulic retention time: 15-20 days
- Optimal pH range for stable digestion: 6.8-7.2
- Key monitoring parameters: volatile fatty acids, alkalinity ratio, biogas composition, volatile solids reduction
- Common pre-treatment requirements: grinding to <12mm, removal of contaminants, screening, optional pulping
What size of sewage treatment plant benefits most from co-disposal implementation?
Medium to large treatment plants serving populations of 50,000+ typically realize the greatest economic benefits from co-disposal due to economies of scale in equipment, operations, and biogas utilisation. However, smaller facilities can also implement successful systems, particularly when serving areas with concentrated food waste sources like food processing facilities or university campuses.
The critical factors are less about absolute size and more about the relationship between available digester capacity, local food waste volumes, and existing biogas utilization infrastructure.
Even small plants can achieve significant benefits when these factors align favourably, particularly in communities with high disposal costs for food waste or strong incentives for renewable energy production.
Will co-disposal cause a bad smell in my community?
Modern co-disposal systems use comprehensive smell control measures that effectively stop nuisance conditions. Food waste receiving areas usually have enclosed designs with negative air pressure systems that capture and treat potential smells through biofilters or chemical scrubbers.
The digestion process itself happens in completely sealed vessels, eliminating the potential for fugitive emissions during treatment.
Operational facilities have shown that systems that are properly designed produce fewer odour complaints than traditional waste management methods.
The quick integration of food waste into the anaerobic environment actually stops the decomposition processes that cause nuisance odours in landfills or composting operations.
For odour management to be effective, it requires a well-thought-out facility design, appropriate maintenance procedures, and plans for unexpected situations.
These considerations should be a part of the early planning stages and should also include input from the community to address particular local concerns and conditions.
How soon can you expect to see an increase in energy production after starting the process?
After adding food waste to the system, you should see an increase in biogas production in about 2-4 weeks. After operating for 2-3 months, the system should reach a stable level of enhanced production.
This slow transition gives the microbial communities time to adapt to the new feedstock characteristics while keeping the digestion processes stable.
The time it takes to see financial benefits will vary depending on the specific energy utilisation infrastructure. Facilities that already have combined heat and power systems will see immediate benefits through increased electricity production and reduced utility purchases.
Projects that require new biogas utilisation equipment will usually see a 3-6 month period between stable biogas production and energy system commissioning.
Many facilities use a step-by-step approach that allows for the gradual optimisation of the system.
This careful implementation reduces operational disruptions and provides opportunities to adjust procedures based on real performance data rather than theoretical projections. For more insights, explore how innovative technologies are reducing landfill dependence.
For communities that are looking to get the most out of their waste while also creating renewable energy, the combined disposal of food waste and sewage is one of the most promising integrated solutions available today.
Food waste management is a critical issue facing urban areas today. Many cities are exploring innovative solutions to reduce landfill dependence and promote sustainability. One such approach is the co-disposal of food waste with sewage, which can enhance the efficiency of waste treatment processes.
This method not only reduces the volume of waste sent to landfills but also generates renewable energy through biogas production. By adopting these strategies, municipalities can take significant steps towards achieving a zero-waste future.
For more information on similar innovative technologies, you can read about technologies reducing landfill dependence.
[Article first published on 21 June 2018. Rewritten December 2025.]





Hi there. Where can I get the sewage sludge?
Debate? What is there not to like about Co-disposal of Food Waste and Sewage Sludge?
In Malaysia my country, the characteristics of sewage sludge in Malaysia are considered to be a factor regarding feasibility. There is a concern that such a process is not technically or profitably feasible.