Thermophilic composting — commonly called hot composting — relies on heat generated by microbial activity to accelerate organic matter decomposition. Under the right conditions, a well-managed pile can reach internal temperatures between 55°C and 70°C (130°F to 160°F), processing raw materials into finished compost in as few as four to eight weeks.

Layered outdoor compost pile showing green nitrogen-rich materials and brown carbon-rich material

A typical outdoor compost pile showing layered green and brown inputs. Photo: Wikimedia Commons.

The carbon-to-nitrogen ratio

Microbial populations in a compost pile require both carbon (an energy source) and nitrogen (for cell construction). The ratio of carbon to nitrogen in the raw feedstock directly controls how fast decomposition proceeds and whether the pile heats adequately.

A target C:N ratio of roughly 25:1 to 30:1 by weight is widely cited in composting literature, including guidance from Agriculture and Agri-Food Canada. Ratios higher than 35:1 produce a slow, cool pile; ratios below 15:1 tend to generate ammonia and odour.

Approximate C:N ratios of common inputs

  • Straw: 75:1 to 100:1 (high carbon)
  • Dry leaves: 50:1 to 80:1 (high carbon)
  • Wood chips: 100:1 to 500:1 (very high carbon)
  • Fresh grass clippings: 15:1 to 20:1 (nitrogen-rich)
  • Food scraps (mixed): 15:1 to 20:1
  • Coffee grounds: approximately 20:1
  • Manure (cattle): 15:1 to 20:1

Building the pile

A minimum pile volume of one cubic metre is generally needed to insulate the microbial core sufficiently to reach and sustain thermophilic temperatures. Smaller piles lose heat too quickly at their edges.

Layering alternating carbon-rich (brown) and nitrogen-rich (green) materials helps distribute the feedstock evenly, though thorough mixing at the start achieves the same result. Uniform particle size of roughly 1–5 cm accelerates microbial access compared to large, intact pieces.

Moisture management

Microbial decomposition requires moisture. The commonly used target range is 50–60% moisture content by weight — described as feeling like a wrung-out sponge. A pile that is too dry will stall; one that is too wet becomes anaerobic and malodorous.

In practice, a handful of compost material squeezed firmly should release only a few drops of water. During dry summer periods in Prairie provinces, regular watering may be needed. In wetter coastal regions, covering the pile protects against saturation.

Compost bin with visible finished compost at the bottom and fresh material on top

Compost bin with partially finished material. Photo: Wikimedia Commons.

Aeration and turning

Aerobic decomposition requires oxygen. Turning the pile introduces fresh air and redistributes materials so that outer, cooler sections move into the hot core. In an active hot compost system, turning every three to seven days during the thermophilic phase is typical.

Passive aeration — using perforated PVC pipes inserted vertically into the pile — reduces labour but produces lower peak temperatures and longer processing times compared to regular turning.

Temperature monitoring and phases

A long-stem compost thermometer (at least 40 cm shaft) allows measurement at the pile's core. The thermophilic phase ideally maintains 55°C to 65°C for several days before turning. Once temperatures drop and fail to rebound after turning, the pile has entered the curing phase.

The United States Composting Council and parallel Canadian guidance from provincial environment ministries note that sustained temperatures above 55°C for several days are sufficient to reduce common weed seeds and most human pathogens in the feedstock — though this is not guaranteed by temperature alone and depends on thorough mixing.

Canadian climate and seasonal factors

In much of Canada, outdoor composting slows significantly once ambient temperatures drop below freezing. Microbial activity does not stop entirely — mesophilic organisms continue working at low rates down to near-freezing temperatures — but thermophilic composting becomes difficult without insulation.

Practical approaches for cold-weather composting include:

  • Insulated bin designs with thick foam board or straw bales surrounding the pile
  • Building larger piles (1.5–2 m³) that retain core heat longer
  • Continuing to add material through winter and allowing active decomposition to resume in spring
  • Using covered three-bin systems that allow indoor starting materials to be added to an outdoor pile during brief thaws

Alberta Environment and Protected Areas and Ontario's Resource Recovery and Circular Economy Act both reference composting as an accepted household waste diversion activity, with guidance available through regional conservation authorities.

Troubleshooting

Common problems and adjustments:

  • Pile is not heating: likely too dry, too small, or C:N ratio too high. Add nitrogen inputs and water; turn thoroughly.
  • Strong ammonia odour: C:N ratio too low (excess nitrogen). Add dry leaves or straw.
  • Rotten or sulphur odour: pile is anaerobic (too wet or compacted). Turn to introduce oxygen; add dry bulking material.
  • Pests attracted to the pile: meat, cooked foods, or dairy likely present. Bury problem materials deep in the pile or exclude them.
  • Pile composting unevenly: insufficient turning or uneven material distribution. Turn and mix more thoroughly.

Finished compost characteristics

Finished hot compost has an earthy smell similar to forest soil, a dark brown to near-black colour, and a crumbly texture with no recognizable original inputs remaining. It should not feel warm at the core. Curing for an additional four to eight weeks after the active phase stabilizes the material further.