Incinerator Burn Rate Screening
Separates two numbers that are routinely, and expensively, treated as one:
Declared (regulatory) throughput — the rate the unit is operated at:
m˙declared=tcyclembatchwhere tcycle is the complete cycle: loading, active burn and final burndown to ash. Using only the active burn period inflates the figure, often by a factor of two.
Engineering screening ceiling — the lowest rate the entered equipment can support. Each populated limit is inverted into a maximum burn rate and the smallest one governs:
- secondary-chamber residence time at the required hot-zone volume;
- combustion-air capacity to hold the target wet O₂;
- maximum permitted or nameplate thermal input;
- primary-chamber loading (volume × fill fraction × bulk density ÷ dwell time);
- the auxiliary-burner heat balance at the secondary set point.
Blank equipment fields are excluded, so the ceiling only ever reflects data you actually entered.
Method
Waste composition is entered as received and must total 100% ±0.5%. The tool runs a Dulong-style HHV/LHV estimate, stoichiometric oxygen demand for C, H, O, N, S and Cl, auxiliary natural gas approximated as methane, combustion air solved to the entered wet O₂ target, and a species mass balance with an automated closure check. Flue-gas volume is evaluated at the actual secondary temperature and absolute pressure. Normal volumes are at 0 °C and 101.325 kPa.
Regulatory context
50 kg/h is the UK boundary between the low- and high-capacity incineration routes. Animal by-product plant is commonly operated on either the 850 °C for 2 s or the 1100 °C for 0.2 s secondary route; both are selectable.
What it does not model
Refractory warm-up, batch-release peaks, combustion kinetics, CO and unburned carbon, fan pressure, air leakage, detailed radiation and convection, ash burnout and emissions. Those need a dynamic design model and commissioning data — this is a screening tool, not a certified capacity statement.