Use two separate preliminary design calculators for MBR permeate disinfection: a vendor-validated UV-reactor sizing calculation and a chlorination CT/contact-basin mass balance.
UV and chlorination calculation basis
Documentation revision: 2026-10-02.
Decision-use boundary: Defaults are illustrative examples, not recommended design or compliance values. UV credit requires the selected OEM validation curve/certificate at the entered flow, dose and minimum UVT, with lamp ageing, fouling, sensor calibration, hydraulics, alarms and standby conditions documented. CT is screening only: confirm disinfectant species, organism/log target, pH, temperature, residual decay, contact segments, tracer/T10 evidence and the applicable authority's tables.
Unit basis: 1 mW/cm² × 1 second = 1 mJ/cm²; the fluence display is arithmetic only, not validated RED or pathogen credit. For chemical demand, mg/L × m³/day ÷ 1,000 = kg/day; available-chlorine percentage is a mass fraction and product litres require verified density and assay.
This page documents the calculation basis so an engineer can trace the inputs, units, assumptions, and review needs. Results are preliminary screening estimates; they are not a permit determination, OEM guarantee, or construction/procurement approval.
Method and source basis
UV duty and standby counts use peak flow divided by vendor-validated reactor capacity at the entered dose and UVT. The intensity-time fluence is deliberately illustrative. Chlorination uses dose = demand + outlet residual, CT = residual multiplied by T10, and T10 = theoretical detention time multiplied by the entered baffling factor.
The sources below provide technical context or analytical/design methodology. They do not endorse this calculator's defaults, and any jurisdiction-specific requirement applies only where that authority has jurisdiction.
- U.S. EPA, Ultraviolet Disinfection Guidance Manual (2006)
- U.S. EPA, Wastewater Technology Fact Sheet: Ultraviolet Disinfection
- U.S. EPA, Disinfection Profiling and Benchmarking: Technical Guidance
- Pennsylvania DEP, Tracer Studies and Contact Time (jurisdictional example)
Assumptions, limitations, and review actions
- UV dose credit requires reactor validation at flow, UVT, lamp output/status, fouling/ageing, sensor calibration, hydraulics, and operating conditions. UV does not provide a downstream disinfectant residual.
- CT compliance depends on disinfectant species, organism/log credit, pH, temperature, residual measurement, tracer/T10 evidence, and the applicable authority or permit. The default CT and baffling factor are screening inputs only.
- Chemical storage, decay, mixing, feed turndown, containment, dechlorination, DBP constraints, power reliability, and multiple contact segments require separate review.
Professional review checkpoint
Before using the result for specification or operation, reconcile it with representative site data, the applicable permit and design standard, the selected equipment or membrane supplier's current data, and a qualified wastewater/process engineer. Record the input basis, date, units, and any pilot, bench-test, or comparable full-scale evidence used to select the assumptions.