Reduce landfill methane
Food and other organics generate methane when they decompose without oxygen in landfill. Diverting suitable material to well-managed aerobic composting avoids much of that methane-forming pathway.

Organic waste is a resource
Composting keeps food scraps and other suitable organics out of landfill, returns carbon and nutrients to soil, and turns a disposal problem into a useful soil amendment—onsite at homes, farms and smaller commercial or institutional operations.
The environmental advantage depends on good management: oxygen, moisture, carbon balance, temperature and curing all matter.
Benefits of composting
Organic material contains carbon, nutrients and water. Composting manages its biological breakdown so that a stable soil amendment can be recovered and used locally.
Food and other organics generate methane when they decompose without oxygen in landfill. Diverting suitable material to well-managed aerobic composting avoids much of that methane-forming pathway.
Mature compost adds organic matter, supports soil organisms and can improve soil structure, water infiltration and moisture retention.
Instead of burying nutrients, composting returns suitable organic material to gardens, farms, landscapes, sports fields and restoration projects.
Keeping organics out of disposal sites reduces the material placed in landfill and can help extend landfill service life.
Compost can help soils absorb rainfall, resist erosion and retain water during dry periods. Results vary with soil, compost quality and application.
Finished compost can displace some purchased soil amendments and support gardens, grounds, landscaping and agricultural production.
What happens during decomposition?
Microorganisms break down organic matter in both pathways. The availability of oxygen determines which communities dominate, which intermediate compounds form and which gases are released.
Aerobic bacteria and fungi use oxygen while consuming readily degradable carbon. Their activity releases heat and progressively converts a mixed organic feedstock into more stable material.
Important: aerobic composting still releases biogenic CO₂ and can form some methane or nitrous oxide if wet, compacted or poorly managed. “Aerobic” describes the intended process—not a guaranteed condition throughout every part of the material.
Once buried and oxygen is depleted, microbial communities break organics down through a sequence of reactions. In landfill, the resulting gas may be partly captured, but collection is not complete and generation can continue for years.
Anaerobic digestion is different: a purpose-built sealed digester intentionally captures biogas for energy and can be a beneficial diversion route. Uncontrolled anaerobic decay in landfill does not provide the same process control or capture efficiency.
Anaerobic gases and by-products
Produced mainly by methanogenic archaea using acetate or hydrogen and CO₂. Methane traps much more heat per unit mass than CO₂ over a 100-year period, making fugitive landfill methane a major climate concern.
Produced during fermentation and conversion reactions and present with methane in landfill gas. Biogenic CO₂ is part of the shorter carbon cycle, but the landfill pathway also delays nutrient recovery and can release fossil-derived trace compounds.
Produced when sulfur-containing material is reduced under oxygen-poor conditions. It has a strong rotten-egg odor, causes corrosion and is hazardous at elevated concentrations.
Released as microbes break down nitrogen-rich proteins and amino acids. It contributes pungent odor and represents a loss of nitrogen that might otherwise be retained in a managed compost mix.
Volatile organic compounds and other non-methane constituents can form or volatilize. Their type and concentration depend on the waste received and landfill conditions; some contribute odor, air pollution or health concerns.
Water moving through waste can carry dissolved organic acids, ammonium, salts, metals and other contaminants. Engineered landfills collect and treat leachate, but it remains a long-term management responsibility.
Economic benefits
Composting economics are site-specific, but homes, farms and smaller organizations may find value on both sides of the ledger: reducing disposal needs and producing an amendment that can be used onsite.
Estimate size and potential valueOnsite diversion may reduce the weight or frequency of organic waste collection where hauling and tipping fees apply.
Compost used in gardens, landscaping or grounds may offset a portion of purchased soil amendments.
Processing close to where material is generated can reduce dependence on distant disposal or processing infrastructure.
A well-run program can support waste-diversion goals, staff or student engagement and sustainability reporting.
Savings are not guaranteed. Evaluate labour, carbon amendments, space, equipment, curing, contamination control, local collection contracts and regulations when assessing a program.
Composting versus landfill
Source reduction and edible-food rescue should come first. For unavoidable suitable organics, managed composting generally provides a more productive pathway than burial.
Choosing an approach
No method is universally best. Site volume, feedstock, labour, climate, space, regulations and the intended use of finished material should guide the choice.
| Approach | Main advantage | Primary limitation | Best fit |
|---|---|---|---|
| Static backyard pile or bin | Low equipment cost and simple setup | Mixing, aeration, pests and temperature can be difficult to manage | Lower-volume garden material with attentive operation |
| Open pile or farm windrow | Can process larger volumes with relatively simple infrastructure | Needs land, turning equipment, runoff planning and odor control | Farms and sites with adequate space, equipment and operating oversight |
| Vermicomposting | Creates a valuable worm-derived amendment | Worms need moderate conditions and suitable feedstocks; not a hot process | Smaller, controlled programs and education |
| Anaerobic digestion | Captures methane-rich biogas and produces digestate | More complex infrastructure; digestate still requires responsible management | Centralized or farm-scale projects with suitable wet feedstocks and energy-recovery infrastructure |
| Insulated rotary hot composting | Frequent mixing and heat retention can accelerate active decomposition while supporting contained aeration and monitoring in a compact footprint | Requires correct recipe, loading, rotation, moisture control, monitoring and curing | Homes, farms and small-to-midsize onsite programs at breweries, restaurants, resorts, schools, institutions and community sites |
Scale matters: Durvela’s standard range is 120–2,000 L. It is intended for onsite household, agricultural and small-to-midsize commercial or institutional composting—not as a substitute for an industrial composting facility, municipal windrow operation or large anaerobic digester.
Rotation and internal mixing features redistribute wet and dry material, moisture, heat and air more consistently than an undisturbed pile.
Purpose-built vents, regular rotation and optional active aeration help operators maintain aerobic conditions and limit odor-forming anaerobic pockets.
An insulated drum reduces heat loss. The microorganisms—not the equipment—generate heat, so feedstock balance, mass and operating conditions remain essential.
An enclosed, latched stainless steel drum helps contain material and deter rodents while presenting a cleaner installation for homes, guests, staff and campuses.
Monitoring ports make it easier to check temperature and adjust the operating routine. They do not replace observation, recordkeeping or material testing.
304 stainless steel provides a cleanable, corrosion-resistant structure for frequent outdoor use, with replacement parts and technical support available.
Potential drawbacks
A good system improves control, but every composting method still requires an appropriate feedstock, an operating routine and a plan for the finished material.
Too much wet, nitrogen-rich material or too little air can create volatile fatty acids, ammonia and sulfur compounds.
Mechanical mixing, engineered vents, insulation and optional active aeration support oxygen-rich conditions. Operators must still balance feedstocks and moisture.
Exposed food scraps can attract pests, particularly when fresh material remains accessible.
A contained stainless steel drum and latched access points reduce exposure. Good housekeeping and correct loading remain important.
Open piles may require lifting, turning and repeated correction; programs can fail when routines are unclear.
Integrated rotary mixing makes regular agitation more manageable and supports a repeatable loading, rotating, monitoring and unloading workflow.
Biological activity slows when heat is lost or the microbial population lacks adequate food, moisture or oxygen.
75 mm polyurethane insulation helps retain biologically generated heat. It cannot create heat when the compost mix is inactive.
Plastic, treated materials, chemicals and unsuitable food-service items can compromise finished compost.
The controlled loading point supports clear material rules, but source separation, staff training and inspection are still the operator’s responsibility.
Equipment requires capital, a stable foundation, safe access and room to unload and cure material.
Four standard sizes support right-sizing, while a contained footprint can be easier to plan than multiple small bins. Curing space is still required.
A practical operating cycle
Frequently asked questions
These answers describe the general science. Site conditions, approved feedstocks and regulatory requirements vary.
For unavoidable suitable organic material, well-managed composting generally avoids the methane-forming landfill pathway and produces a useful soil amendment. The actual result depends on collection distance, energy use, process emissions, contamination, compost quality and whether the compost is beneficially used. Preventing wasted food and rescuing edible food should come before composting.
Yes. Aerobic decomposition produces mainly biogenic carbon dioxide and water, and composting can also emit smaller amounts of methane and nitrous oxide—especially where oxygen, moisture or nitrogen are poorly managed. Good aeration, structure and moisture control help limit these emissions.
Methane is a powerful greenhouse gas. It forms when methanogenic microorganisms break down organic material without oxygen. Landfill gas systems can capture and flare or use some methane, but collection is incomplete and often begins after readily degradable food waste has already started producing gas.
No. Both occur without oxygen, but an engineered anaerobic digester controls the process in a sealed vessel so methane-rich biogas can be captured and used. Landfill decomposition is less controlled, gas capture is incomplete and nutrients are harder to recover.
No composter can guarantee zero odor. A contained rotary system makes mixing and aeration easier, but odors can still develop if the material is too wet, too dense, overloaded or short of carbon. Prompt correction of the recipe and operating conditions is essential.
No. Microbial activity generates the heat. Insulation slows heat loss and can help maintain active conditions, but the feedstock mix, moisture, oxygen, mass and ambient weather determine whether temperatures rise.
This educational page is informed by the following public resources. Environmental outcomes vary by feedstock, climate, transport, equipment, process management and end use.
Turn organics into an asset
Compare 120–2,000 L capacities, estimate your weekly mix and plan a controlled onsite composting workflow for your home, farm or organization.