Design ManualDisinfection › Chlorine
FREE ENGINEERING TOOL · DISINFECTION

Chlorine Disinfection

Disinfection is the one unit process where the design is a product, not a rate: concentration × time. This tool builds the dose from the water's actual chlorine demand, converts the target log-inactivation into a CT requirement corrected for temperature and pH, and sizes the contact tank from the baffled contact time — because a perfectly sized tank with a poor baffling factor will still fail.

1Effluent quality & duty

Chlorine demand is set by what is in the water, not by the target. Ammonia dominates: oxidising it to the breakpoint costs 7.6 kg of chlorine per kg of ammonia-nitrogen.

2Disinfection target & chemistry

Free chlorine is a far stronger disinfectant than chloramine — but getting to free chlorine means paying the full breakpoint dose. Chloramine costs less chlorine and forms fewer byproducts, and buys it back with a much longer contact time.

Results — dose & contact

Chlorine dose
mg/L
Cl₂ consumption
kg/d
Contact volume
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3CT — the actual design criterion

CT is corrected outward from the 20 °C, pH 7 reference in both directions: cold water needs far more, and high pH does too, because the hypochlorite ion is a weaker disinfectant than hypochlorous acid.
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4Chemical supply & dechlorination

If the receiving water is sensitive, the residual has to come back off before discharge. Dechlorination is a small step that is often forgotten until the permit arrives.
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Operating envelope & risks

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5Instrument schedule

An honest note: residual chlorine is not in our online catalogue. ORP is — and used properly, with periodic DPD checks, it is a workable continuous proxy.
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Quote the disinfection instruments at factory price

ORP, pH, turbidity and flow — all mappable to our catalogue and supplied at the manufacturer's ex-works price (our margin is the export rebate, not a markup on the device).

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Sources & parameter basis

[1]METCALF & EDDY / EPA — wastewater disinfection: dose 5–20 mg/L for secondary effluent, residual 0.5–2 mg/L (up to 5 for chloramine), contact 20–30 min at peak flow.
[2]Breakpoint chlorination: Cl₂:NH₃-N ≈ 7.6:1 by weight to reach the breakpoint and leave free residual; monochloramine formation sits around Cl₂:N ≈ 3–5:1. Other reducing demand taken as ≈0.3·BOD + 1 mg/L.
[3]CT values at 20 °C, pH 7 (mg·min/L) — free chlorine: coliform 2-log ≈1.5, virus 3-log ≈5, Giardia 3-log ≈53. Chloramine: ≈50, ≈750, ≈1100 respectively. Temperature: CT ∝ 1.07(20−T) (matches EPA tables from 5 to 25 °C).
[4]pH: CT scales as ≈1.25(pH−7), reflecting the HOCl/OCl⁻ split (HOCl ≈76 % at pH 7, ≈24 % at pH 8).
[5]Baffling factor T10/τ: unbaffled 0.1, poor 0.3, average 0.5, superior 0.7, plug flow 1.0. Design on T10, not on the nominal HRT.
[6]Turbidity shields pathogens and consumes chlorine; keep effluent below about 2 NTU, ideally under 1 NTU, before disinfection.
[7]Disinfection by-products: THM formation rises with dose and TOC. Watch it above roughly 10 mg/L dose with TOC above 5 mg/L.
[8]Sodium hypochlorite: 5–15 % available chlorine; it decays with age, heat and light — size storage for turnover, not for calendar weeks. Dechlorination: NaHSO₃ ≈1.46 mg per mg Cl₂, SO₂ ≈0.9 mg per mg Cl₂.
Full derivation and worked example: Chlorine-Dosing-Calculation-Sheet.md. Switch the mode from chloramine to free chlorine and watch what happens: the chlorine bill roughly doubles, and the contact tank shrinks. That trade is the whole decision.
© 2026 Nanjing JiuYuHui Environmental Technology Co., Ltd. · jiuyuhub.com · Municipal WWTP design manual — Disinfection (variant).
⚠ Screening values only. Outputs from this tool are engineering screening estimates. Final equipment sizing, and any construction or permit submission, must be confirmed against the manufacturer’s verified performance curves and the applicable local regulation (e.g., Vietnam QCVN 14 / Indonesia PERMENLHK 68).
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