🧪 ClO₂ · Legionella · Cooling

Chlorine Dioxide (ClO₂) Dosing Calculator

Calculate ClO₂ dose for Legionella control, cooling-tower disinfection or food-industry water treatment. Input cooling-tower flow + target residual.

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In short — chlorine dioxide (clo₂) generation & dosing formula

Chlorine Dioxide (ClO₂) Generation & Dosing rate is the volume of stock chemical that must be injected per unit time to achieve a target concentration in the main flow. The exact formula:

Dose (L/hr)  =  (Q × C_target) ÷ C_stock

Worked example: Q = 100 m³/hr cooling water, target = 0.5 ppm ClO₂ residual, generator output = 0.3% ClO₂ solution (SG ~1.00, C_stock = 3 g/L)  →  Dose = (100 × 0.5) ÷ 3 = 16.7 L/hr ≈ 278 mL/min.

Used for: chlorine dioxide is the gold standard for legionella control in cooling towers and hot-water systems — it does not form trihalomethanes, works across ph 4–10, and penetrates biofilm.

🧪 Chlorine Dioxide (ClO₂) Dosing — Quick Estimator

Required Dosing Rate

Chlorine Dioxide (ClO₂) Generation & Dosing Equation

Chlorine dioxide is the gold standard for Legionella control in cooling towers and hot-water systems — it does not form trihalomethanes, works across pH 4–10, and penetrates biofilm. ClO₂ is generated on-site from sodium chlorite + acid (or chlorine) and dosed at 0.1–0.8 ppm residual.

ClO₂ dose (L/hr generator output)
Rate = (Flow × Dose_PPM) / (Strength_% / 100 × SG × 1000)

Where:

  • Flow = Main flow rate in m³/hr
  • Dose_PPM = Target concentration in mg/L or ppm
  • Strength_% = Percentage active ingredient of the stock chemical
  • SG = Specific Gravity (density relative to water) of the stock

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Frequently Asked Questions

What is the typical ClO₂ dose for Legionella control?

0.3–0.8 mg/L continuous residual in cooling towers per ASHRAE 188 and HSE L8. For potable hot-water systems, 0.2–0.5 mg/L. ClO₂ is 2.6× more potent than chlorine on a mass basis for biofilm penetration, but residual decays in 6–24 hours so continuous dosing is required.

How is ClO₂ generated on site?

Two-precursor systems: sodium chlorite (NaClO₂, 25%) + hydrochloric acid (HCl, 9%) → ClO₂ in a reactor. Three-precursor systems add sodium hypochlorite for higher yield. Generator outputs are typically 1–500 g/hr ClO₂ as a 0.2–0.5% solution. Bulk ClO₂ cannot be transported (Class 5.1 explosive at >10%).

Why use ClO₂ instead of chlorine?

ClO₂ does not form trihalomethanes (THMs) or haloacetic acids (HAAs), works at high pH where Cl₂ loses potency, penetrates biofilm 100–1000× better, and oxidises iron and manganese without lowering pH. Downside: more expensive, requires on-site generator, must monitor chlorite (ClO₂⁻) by-product (<1.0 mg/L EPA limit).

What is the ClO₂ to ClO₂⁻ conversion?

30–70% of ClO₂ reduces to chlorite ion (ClO₂⁻) in normal water-treatment use — chlorite is a regulated by-product (EPA MCL 1.0 mg/L for drinking water). Apply enough ferric or ferrous iron (Fe²⁺/Fe³⁺) to scavenge excess chlorite if approaching the limit.

Can I dose ClO₂ in food and beverage water?

Yes — ClO₂ is FDA-approved (21 CFR 173.300) at up to 3 mg/L for food washing and 5 mg/L for poultry chiller water. EU regulation (EC 1935/2004) allows ClO₂ for water in contact with food at up to 0.5 mg/L residual. Lower-than-chlorine taste threshold makes it preferred for bottled water and breweries.

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