Effluent disinfection: chlorine contact tank

Input data

Average flow

Peak flow

Contact time at peak flow

Water depth

Chlorine residual at the outlet

Chlorine demand

Chlorine dose (blank = demand + residual)

Influent coliforms (optional)

Target effluent coliforms (optional)

Channel length-to-width ratio

Baffle factor (t10/t)

Hypochlorite available chlorine

Hypochlorite density

Storage time

Collins-Selleck b

Collins-Selleck n

Output data

Contact volume

Contact time at average flow

Plan area

Channel width

Total channel length

Channel velocity at average flow

Effective contact time at peak flow

Chlorine dose

Chlorine consumption (as Cl2)

Hypochlorite solution consumption

Hypochlorite solution volume

Dosing pump flow at peak

Hypochlorite storage volume

Residual times effective time (CT)

Coliform log reduction

Effluent coliforms

Residual for the target coliforms

Description

Chlorine contact tank for a treated effluent, with sodium hypochlorite dosing. Sized for the contact time at the peak flow, as a serpentine channel long and narrow enough to behave as plug flow:

V=Qmax tcb=AL/bL=A⋅L/bV = Q_{max} \, t_c \qquad b = \sqrt{\frac{A}{L/b}} \qquad L = \sqrt{A \cdot L/b}

A length-to-width ratio of 40 or more keeps short-circuiting small; the effective contact time is the theoretical one times the baffle factor, t10=BF tct_{10} = BF \, t_c. The channel velocity at average flow is checked against the minimum that keeps the remaining solids from settling.

Chlorine dose as the demand plus the residual to keep at the outlet, unless the dose is given, and the hypochlorite it takes:

D=Dcons+CRVhip=D QChip ρhipD = D_{cons} + C_R \qquad V_{hip} = \frac{D \, Q}{C_{hip} \, \rho_{hip}}

When the influent coliforms are given, the kill at the residual and effective time follows Collins-Selleck, and a target gives the residual it needs:

NN0=(CR t10b)−n(CRt10>b)\frac{N}{N_0} = \left( \frac{C_R \, t_{10}}{b} \right)^{-n} \quad (C_R t_{10} > b)

b=4.0b = 4.0 mg.min/L and n=2.8n = 2.8 are typical values for coliforms; site data is better. Hypochlorite loses strength in storage, so the storage time is kept short.

References

METCALF & EDDY. Wastewater Engineering: Treatment and Resource Recovery. 5th ed. McGraw-Hill, 2014. Chapter 12 (disinfection).

U.S. EPA. Design Manual: Municipal Wastewater Disinfection. EPA/625/1-86/021, 1986.