What It Really Takes To Enable Organic Waste | Infrastructure news

Paul Jones, director at Lumec

Paul Jones, director at Lumec

South Africa continues to rely heavily on landfill as its primary waste disposal method, a reality driven largely by cost, but one that carries significant environmental and social consequences.

“Landfilling is the dominant method of disposal globally, and in South Africa more so,” explains Paul Jones, director at Lumec, an economic research consultancy, whose recent master’s research compared aerobic windrow composting and anaerobic digestion as alternative technologies for managing organic municipal solid waste.

“One of the reasons is its relatively low cost compared to other alternatives,” he says. “But the external costs of landfilling, the environmental and social impacts, are not internalised.”

According to Jones, an international study suggested that “waste management costs would be between 50 and 100 per cent higher if those external costs were internalised in landfilling”.

This matters particularly for organic waste.

“Landfilling organic waste specifically is quite a challenge because it creates methane,” he explains. “Methane is a very potent greenhouse gas, which is exacerbating climate change. So, there is an urgent need for us to consider how we divert organics from landfill.”

Comparing composting and anaerobic digestion

decomposing organic waste

Organics have value if they are treated as though they have value

Jones’ study focused on two relatively low-cost and widely adopted technologies: aerobic composting (specifically windrow composting) and anaerobic digestion, which produces biogas.

“The objective was to look at these two technologies and compare them to understand what variables essentially make each of these technologies tick,” he says.

Using a cost–benefit analysis model, Jones set out to answer three key questions: why landfill remains dominant, what factors drive diversion from landfill, and which technology offers the highest net benefit to society in a South African context.

“The ultimate aim of a cost–benefit analysis is to say: what’s the highest benefit to society as a whole of a project or a policy?” He explains. “And then further to that, what are the variables that influence the viability of these technologies?”

His methodology combined literature review, stakeholder interviews with government, academia and industry, and detailed surveys of operational composting and anaerobic digestion facilities.

“I got 28 responses in the end,” Jones says. “About 20 were composting facilities, and about eight were from anaerobic digestion facilities and technology providers.”

Participants were asked about capital costs (including machinery and equipment), operational expenses, feedstock volumes, staffing, and outputs, but the data received was inconsistent.

“Some people gave me very detailed answers, exactly how many tonnes of food waste and garden waste are going in,” he recalls. “Others didn’t even know how much feedstock was coming in.”

Every facility is different

What quickly became clear was that no two facilities operate in the same way.

“Every single facility across the different technologies is completely unique,” Jones says. “They have different processes, different locations, different business models and different structures.”

As a result, he adopted what he calls a “generic business model approach,” modelling small, medium, and large commercial facilities processing approximately 5, 20 and 100 tonnes of feedstock per day.

His analysis considered both private costs, what operators themselves pay, and total societal costs, including greenhouse gas reductions and social impacts such as the impact on property values near landfill sites.

When you include those external costs, every scale and technology is considered viable, he says.

The only exception was small-scale anaerobic digestion, which was not considered viable when assessed purely on private financial returns.

“However, these results are not definitive,” he stresses. “You cannot say outright that a small-scale biogas facility of five tonnes a day will not be viable. The results provide an indication of the factors that generally affect viability.”

Gate fees, scale, and feedstock consistency

trays of organic fruit and vegetables at a market

Fruit and veg markets often produce a lot of waste, which can be a reliable feedstock for anerobic digestion and composting

One of the strongest influences across all models was gate fees; the charge paid to accept waste at a facility. “Gate fees affect all scales, across all technologies, quite a lot,” Jones explains.

He also found that smaller facilities are far more sensitive to changes in capital costs, product prices, and operating conditions.

“Small-scale composting was relatively sensitive to a number of variables,” he says. “If compost prices drop, it becomes negative. If they cannot rent out surplus equipment, it becomes negative.”

Anaerobic digestion on a small commercial scale faces even greater challenges.

“A number of specialists confirmed that it’s difficult to be viable on that small commercial scale,” Jones says. “It’s this middle range that struggles; domestic systems work, and large systems work, but the smaller commercial systems are tough.

Feedstock quality and consistency

“Electricity is low value,” he notes. “A lot of biogas facilities in South Africa use biogas to offset expensive energy like diesel, rather than selling electricity to the grid.”

Feedstock quality and consistency are perhaps the most decisive variables of all. “You can’t compare rotten tomatoes with mouldy bread,” Jones says. “You can have the same digester, same capital cost, same operational cost, but a huge variation in gas production depending on the waste stream feeding into the system.”

He cites one example where bakery waste produced more than twenty times the biogas of cow manure. “This is why understanding your feedstock is one of the most critical things.”

A lack of proper feedstock analysis has already caused major failures. “One of the biggest biogas plants in the country, a R400 million facility in Cape Town, initially failed because the actual food waste received was far lower than projected,” Jones explains.

Land access and location

anerbic digestion to work size of the facility and reliability of feedstocks are vital.

For anerbic digestion to work size of the facility and reliability of feedstocks are vital. Copyright Thomas Nugent and licensed for reuse under this Creative Commons Licence.

Composting faces its own structural challenges, particularly land availability.

“Composting requires a lot of land,” Jones says. “In Cape Town, zoning is pushing composting into industrial areas, which forces facilities further from the city, increases transport costs, and makes businesses less viable.”

In a related study conducted by Lumec for the eThekwini Municipality, Jones found that private operators were willing to process greater amounts of organic waste, provided they had access to land close to feedstock sources.

“They said: we’ll bring the machinery, we’ll cover operational costs, just give us access to land and feedstock.”

A case for internalising landfill costs

Jones argues that diverting organic waste could free up 30 to 60 per cent of landfill capacity, generating massive savings for municipalities.

“If we can avoid landfill development and associated operational costs, how does that money filter back into supporting alternative technologies? Well, they often just need a small nudge.”

Ultimately, his conclusion is clear: composting and anaerobic digestion are proven, valuable tools, but only when applied thoughtfully.

“These technologies are great, and they’re widely adopted in other countries,” Jones says. “But you cannot do ‘plug-and-play.’ You must understand your feedstock, know your markets, and apply the right technology.”

He adds: “A lot of people are fooled by technology providers saying, ‘this will work.’ But every facility must be considered in its own unique light.”

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