Aerobic treatment works by feeding organic matter to bacteria that need oxygen, and supplying that oxygen is expensive. Aeration typically consumes half or more of a biological treatment plant’s electricity. On top of that, aerobic bacteria convert a large share of the organic load they consume into new bacterial mass — sludge — which then has to be dewatered and disposed of at further cost.

Anaerobic digestion inverts both problems. It treats organic load without oxygen, so there is no aeration bill. It produces roughly a tenth of the sludge, because anaerobic organisms grow slowly. And the carbon that would have become carbon dioxide in an aerobic system becomes methane instead — a fuel you can burn.

For facilities producing high-strength organic effluent, this changes the economics of wastewater treatment fundamentally. The stream stops being purely a cost and becomes partly a resource.

How anaerobic digestion works

Four microbial stages happen in sequence, in the same vessel.

Hydrolysis breaks complex organic polymers — carbohydrates, proteins, fats — into soluble sugars, amino acids and fatty acids. For particulate-heavy feedstocks this is the rate-limiting step.

Acidogenesis converts those soluble compounds into volatile fatty acids, alcohols, hydrogen and carbon dioxide, driven by fast-growing acid-forming bacteria.

Acetogenesis converts the volatile fatty acids into acetic acid, hydrogen and carbon dioxide.

Methanogenesis is where methanogenic archaea convert acetic acid and hydrogen into methane and carbon dioxide. These organisms grow slowly, are sensitive to pH and temperature, and are the reason anaerobic systems must be operated with care.

The critical dynamic is the balance between stages two and four. Acid formers grow fast; methanogens grow slowly. Overload the system and acids accumulate faster than the methanogens can consume them, pH falls, the methanogens are inhibited further, and the reactor sours. Recovery from a soured digester takes weeks. This is why anaerobic systems reward steady, well-buffered operation and punish shock loading — and why adequate equalisation ahead of the digester is not optional.

The technology options

UASB — upflow anaerobic sludge blanket. Wastewater flows upward through a blanket of granular anaerobic biomass. The granules — dense, settleable aggregates of the microbial consortium — retain biomass in the reactor while treated water passes upward through a three-phase separator that captures gas and returns solids. UASB is proven, widely deployed, and efficient on soluble high-strength effluent from breweries, distilleries, starch and sugar processing. UASB digesters achieve COD removal of 70 to 85 percent with retention times of hours rather than days.

EGSB and IC reactors. Expanded granular sludge bed and internal circulation designs increase upflow velocity for better mixing and higher loading rates in a smaller footprint — relevant where land is constrained.

Anaerobic digesters for sludge and solids. Where the feedstock is particulate — waste activated sludge, food waste, agricultural residue — completely stirred digesters with retention times of 15 to 30 days handle material that granular systems cannot. Anaerobic advanced digesters are the standard approach for sludge stabilisation, reducing volatile solids by 40 to 60 percent and cutting the mass requiring disposal correspondingly.

Anaerobic MBR. Combining anaerobic biology with membrane separation retains biomass completely, allowing operation at high loading with excellent effluent quality — at higher capital and operating complexity.

What the biogas is worth

Raw biogas is typically 55 to 70 percent methane, 30 to 45 percent carbon dioxide, with traces of hydrogen sulphide, moisture and siloxanes. Its calorific value is roughly 20 to 25 MJ per cubic metre — around 60 percent that of natural gas.

There are three common uses.

Direct combustion in a boiler is the simplest and usually the most economical. Minimal treatment is required beyond moisture removal and hydrogen sulphide reduction, and most industrial sites already have a boiler burning purchased fuel. Displacing that fuel is straightforward value.

Combined heat and power generates electricity and recovers waste heat, typically used to maintain digester temperature. It requires more gas cleaning, since hydrogen sulphide and siloxanes damage engines, and it makes sense at larger gas volumes.

Upgrading to biomethane removes carbon dioxide to produce gas of natural gas quality for grid injection or vehicle fuel. Capital-intensive and only viable at scale with supportive commercial arrangements.

Hydrogen sulphide removal matters in every case. It is corrosive and combusts to sulphur dioxide, so biogas utilisation systems always include some form of gas conditioning.

Where it makes sense — and where it does not

Anaerobic treatment suits high-strength, warm, biodegradable effluent. Practical thresholds are around 2,000 mg/L COD minimum, with the economics improving steeply above that. Distilleries, breweries, dairy, starch and sugar processing, palm oil mills, pulp and paper, and municipal sludge digestion are all well-established applications. Palm oil mill effluent in particular is close to an ideal feedstock — very high organic strength, warm, and produced in large volumes.

It does not suit dilute effluent, where there is insufficient organic load to sustain the biology or generate useful gas. It struggles with high sulphate, because sulphate-reducing bacteria compete with methanogens and produce hydrogen sulphide instead of methane. Toxic or inhibitory compounds — heavy metals, biocides, certain solvents — will suppress the culture. And cold effluent requires heating, which erodes the energy benefit.

The most important qualification: anaerobic treatment alone rarely meets discharge standards. It removes the bulk of organic load efficiently but leaves residual COD, ammonia and suspended solids. It is a first stage, followed by aerobic polishing — commonly MBBR, SBR or MBR — to reach compliance. Presented correctly, anaerobic treatment shrinks the aerobic stage required and pays for itself through avoided aeration energy as much as through gas.


Frequently Asked Questions

What COD strength justifies anaerobic treatment? As a working guide, above roughly 2,000 mg/L COD anaerobic treatment becomes worth evaluating, and above 5,000 mg/L it is usually the clearly better option. Below 1,500 mg/L, the biology is difficult to sustain and gas yield rarely justifies the capital.

How much biogas will my effluent produce? Theoretical yield is approximately 0.35 cubic metres of methane per kilogram of COD removed. Real systems achieve somewhat less. A plant removing one tonne of COD per day might therefore produce in the region of 250 to 300 cubic metres of methane daily — enough to displace a meaningful share of boiler fuel.

Is anaerobic treatment difficult to operate? It demands more understanding than aerobic treatment but is not unmanageable. The key disciplines are steady loading, temperature stability, alkalinity maintenance and monitoring volatile fatty acids. Well-run digesters operate for years without incident; poorly run ones sour and take weeks to recover.

What happens to the sludge from anaerobic digestion? Far less is produced than in aerobic treatment, and what remains is more stable and less odorous. It still requires dewatering before disposal, but the reduced volume is one of the significant economic advantages of the approach.

Can anaerobic digestion handle variable production schedules? Within limits, and only with buffering. Anaerobic biology dislikes shock loads and extended starvation. Adequate equalisation upstream, and where necessary supplementary feedstock during low production, keeps the culture stable through production swings.


Turn your effluent load into an energy asset

If your facility is paying to aerate a high-strength organic effluent, there is a reasonable chance you are spending energy to destroy something you could be burning instead.

World Technologies designs and delivers anaerobic treatment systems, digesters and biogas utilisation for industrial clients, together with the aerobic polishing stages needed to meet discharge standards, backed by in-house process engineering and long-term operational support. To explore waste-to-energy and anaerobic wastewater treatment in Singapore, speak to World Technologies.