Mesophilic anaerobic digestion is one of the most widely used methods of treating sewage sludge and biodegradable organic waste. Operating at moderate temperatures, it offers a reliable way to stabilise organic material, reduce waste quantities, and recover renewable energy in the form of biogas. This article explains the process, its typical operating conditions, advantages and limitations, and how technologies such as thermal hydrolysis can improve its performance.
Mesophilic anaerobic digestion (MAD) is a biological process in which microorganisms break down organic matter in the absence of oxygen. The process operates at moderate temperatures, typically between 30°C and 40°C, with most systems operating between 35 and 39°C.
The process takes place in enclosed tanks called anaerobic digesters, where microorganisms convert biodegradable organic matter into two main products:
Mesophilic anaerobic digestion is used to treat sewage sludge from wastewater treatment plants, as well as food waste, manure, agricultural residues, and other biodegradable organic materials.
In municipal wastewater treatment, it plays an important role in stabilising sludge, reducing its biodegradable organic content, and recovering energy that would otherwise remain unused.
Like all anaerobic digestion processes, MAD involves four interconnected biological stages. The main difference is that microorganisms operate within the mesophilic temperature range.
These stages occur simultaneously within a conventional mesophilic digester, with different microbial communities working together to break down organic matter progressively:
For a more detailed explanation of the biological stages and how they interact, read our guide to anaerobic digestion.
Mesophilic anaerobic digestion is widely used in wastewater and organic waste treatment because it offers a favourable balance of process stability, energy efficiency and reliable biogas production. Much of this advantage comes from its moderate operating temperature.
Temperature is one of the main ways anaerobic digestion systems are classified. The two most common approaches are mesophilic digestion (30–40°C) and thermophilic digestion (50–60°C). Both rely on microorganisms to break down organic matter and produce biogas, but their different operating temperatures influence treatment speed, energy requirements and process stability.
MAD's established performance, relatively stable operation, and moderate heating requirements have made it a widely adopted approach for municipal wastewater and organic waste treatment.
The success of mesophilic anaerobic digestion depends on maintaining conditions that support mesophilic microorganisms. Several operating parameters influence how efficiently and reliably the process performs.
|
Parameter |
Typical Conditions and Importance |
|
Temperature |
Usually 30–40°C in conventional digesters. Maintaining a stable temperature is important, as sudden changes can disrupt microbial activity and reduce biogas production. |
|
Acidity/Alkalinity (pH) |
Generally maintained near neutral, around a pH of 6.8–7.5. Methane-producing microorganisms are particularly sensitive to acidic conditions, which can inhibit biogas production. |
|
Retention time (HRT and SRT) |
Conventional mesophilic sewage sludge digesters typically operate at retention times of 15–30 days, depending on the feedstock and system design. Hydraulic retention time (HRT) describes how long liquid remains in the digester, while sludge retention time (SRT) describes how long solids remain in the digester. |
|
Organic loading rate (OLR) |
The amount of organic material fed into the digester relative to its volume over time. Adding too much material too quickly can overwhelm microorganisms, causing acid accumulation and process instability. |
|
Mixing |
Mixing helps distribute microorganisms, organic material, and heat evenly throughout the digester. This prevents material from accumulating in certain areas and helps maintain consistent conditions |
Did You Know?
Longer retention times generally allow microorganisms more time to degrade organic matter and produce biogas but also require greater digester capacity for the same daily feed volume.
For example, a conventional mesophilic sewage sludge digester with a hydraulic retention time of 20 days would receive approximately one-twentieth of its working volume in fresh sludge each day, with an equivalent volume leaving the system every day.
In this type of continuously mixed digester, HRT and SRT are approximately equal, meaning both the liquid and the solids remain in the system for an average of 20 days. However, some digester designs retain or recycle solids separately, allowing microorganisms and other solids to remain in the digester longer than the liquid.
Together, these operating conditions help maintain a balanced microbial environment, enabling organic matter to be progressively converted into biogas while producing stabilised digestate.
Mesophilic anaerobic digestion is used across wastewater treatment, organic waste management, and agricultural biogas production. Although the underlying biological process remains the same, feedstock characteristics influence digester design, operating conditions, and treatment performance.
Municipal wastewater treatment is one of the most established applications for [AS4] mesophilic anaerobic digestion.
Wastewater treatment generates sewage sludge containing organic material removed during primary settling and biological treatment. Rather than treating this material solely as waste, wastewater utilities can use anaerobic digestion to reduce its biodegradable organic content and recover energy in the form of biogas.
Two main types of sewage sludge are commonly treated:
Many wastewater treatment plants digest a mixture of primary sludge and WAS, although the proportions depend on the plant's wastewater treatment configuration.
Following digestion, the remaining sludge is typically dewatered to reduce the amount of material that requires transport, further processing, or disposal. Depending on the treatment achieved and applicable regulations, the resulting biosolids may be suitable for agricultural use or other beneficial applications.
Beyond sewage sludge, mesophilic anaerobic digestion is widely applied to biodegradable organic waste, including food waste, agricultural residues and animal manure.
Food waste is an attractive feedstock because of its high content of biodegradable organic matter and its potential for biogas production. However, its composition can vary considerably, requiring careful management of organic loading, nutrients and process stability.
Mesophilic digestion is also commonly used in codigestion, where two or more organic feedstocks are processed together.
For example, wastewater treatment plants may introduce food waste or other suitable organic materials into existing sludge digesters to increase biogas production and make better use of available digestion capacity.
Codigestion can improve overall resource recovery, although additional feedstocks must be assessed for their compatibility with the existing process, including potential impacts on loading rates, nutrient balance, and digester stability.
Mesophilic anaerobic digestion offers several operational and environmental advantages, which have contributed to its widespread adoption.
Did You Know?
Conventional mesophilic anaerobic digestion (MAD) reduces pathogens in sewage sludge but typically cannot achieve the stringent pathogen reduction required for Class A biosolids under US regulations.
Common methods for producing Class A biosolids include composting, thermal drying, advanced alkaline stabilisation, pasteurisation, and thermal hydrolysis combined with anaerobic digestion. Certain thermophilic digestion configurations can also achieve Class A pathogen reduction requirements, provided the treatment process meets the applicable time-temperature, monitoring and pathogen criteria.
While mesophilic digestion operates at moderate temperatures, an alternative approach is thermophilic anaerobic digestion (TAD), which typically operates between 50°C and 60°C.
Both approaches rely on the same fundamental biological processes to break down organic matter and produce biogas. However, their different operating temperatures influence the microorganisms involved, the rate of digestion, energy requirements, process stability and pathogen reduction.
The table below summarises the main differences between the two approaches.
|
Parameter |
Mesophilic digestion (MAD) |
Thermophilic digestion (TAD) |
|
Typical temperature |
30–40°C |
50–60°C |
|
Process stability |
Generally more tolerant of operational fluctuations |
Generally more sensitive to operational fluctuations |
|
Heating demand |
Lower |
Higher |
|
Retention time |
Typically longer due to slower digestion |
Potentially shorter due to faster digestion |
|
Pathogen reduction |
Moderate |
Higher |
|
Methane/biogas yield |
Generally reliable and consistent, depends on feedstock and operating conditions
|
Can be higher than MAD in some cases, but depends strongly on stable operation and feedstock |
These two approaches are not mutually exclusive. Multistage anaerobic digestion systems can combine thermophilic and mesophilic stages to leverage the benefits of each. Intermediate-temperature digestion also exists, though mesophilic and thermophilic remain the conventional operating regimes.
Optimising mesophilic anaerobic digestion (MAD) involves improving process stability, increasing biogas production and maximising the breakdown of organic matter. Several established and emerging techniques can enhance digester performance:
When anaerobic digestion is enhanced through additional technologies, the resulting process is commonly referred to in the wastewater industry as advanced anaerobic digestion (AAD). The term also encompasses other enhanced digestion configurations.
Among the various treatment methods, thermal hydrolysis has become a well-established technology for sewage sludge treatment.
Thermal hydrolysis (THP) is an advanced treatment technology that uses high temperatures and pressure to break down cellular structures and make organic matter more accessible to microorganisms, improving biodegradation and biogas production.
THP can be combined with mesophilic digestion in different configurations, depending on the treatment objectives. It may be applied before digestion to all or part of the sludge, between digestion stages, or after digestion.
The combination of THP with MAD provides several benefits compared with conventional mesophilic digestion:
These improvements can be particularly valuable for wastewater treatment plants facing increasing sludge production, limited space for new digesters, or rising sludge management costs.
The widespread use of mesophilic anaerobic digestion reflects its established performance, relatively stable operating conditions and potential for energy recovery.
Although conventional MAD has limitations in treatment efficiency, capacity and pathogen reduction, technologies such as thermal hydrolysis can help address these constraints while retaining the operational advantages of mesophilic digestion.
Understanding the capabilities and limitations of mesophilic digestion can help wastewater treatment plants optimise existing systems to meet evolving demands for efficient, sustainable sludge management.