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Recycling Treated Municipal Wastewater for Industrial Water Use

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TM3: Recycled <strong>Wastewater</strong> System Components and Costs<br />

<strong>Recycling</strong> <strong>Treated</strong> <strong>Municipal</strong> <strong>Wastewater</strong> <strong>for</strong> <strong>Industrial</strong> <strong>Water</strong> <strong>Use</strong><br />

Sodium hypochlorite feed systems provide a unit process that can meet the three<br />

disinfection system improvement requirements: to meet a year-round disinfectant,<br />

provide a higher level of disinfection, and maintain a residual in the transmission<br />

system. A conservative assumption is made that all WWTPs will require new<br />

equipment <strong>for</strong> application of sodium hypochlorite. It is assumed that the chlorine<br />

dose can be elevated sufficiently to meet the disinfection requirements without the<br />

need <strong>for</strong> additional detention time (new contact tanks).<br />

Chlorine doses were assumed as follows <strong>for</strong> the two annual operating practices and<br />

residual disinfection:<br />

April-October months with disinfection practiced by Minnesota WWTPs, where<br />

chlorination provides incremental disinfection from the NPDES pathogen limit to<br />

the reclaimed water pathogen limit.<br />

November-March months with no disinfection practiced by Minnesota WWTPs to<br />

provide disinfection to the reclaimed water pathogen limit.<br />

A chlorine dose of 2.5 mg/L was selected to achieve adequate residual through<br />

the transmission system. This is a dose commonly used by reclaimed systems<br />

across the country.<br />

Chlorination practices at MCES facilities and facilities with reuse systems were<br />

reviewed to identify chlorine doses <strong>for</strong> existing systems to meet NPDES permit limits<br />

and to meet a variety of state reclaimed water criteria. For MCES facilities, average<br />

chlorine doses to meet NPDES discharge limits range from 2-4 mg/L with peak<br />

demands requiring 6 mg/L of chlorine. A reclaimed system in Cary, North Carolina<br />

reported the use of an 8 mg/L dose to meet pathogen kill and residual disinfection<br />

requirements. <strong>Use</strong> of the Refined Collins-Selleck Model to estimate chlorine dosages<br />

<strong>for</strong> disinfection of a nitrified secondary effluent (White, 1999) to meet a 23/100 ml<br />

total coli<strong>for</strong>m limit indicates that <strong>for</strong> a contact time of 15 minutes (the contact tank<br />

design criteria typically used in Minnesota), a dose of 4-15 mg/L is required<br />

depending on the nitrification process (ammonia at concentrations from 0.5 – 2<br />

mg/L).<br />

For this study, it is assumed that a chlorine dose of 6.5 mg/L applied to an advanced<br />

secondary treatment system effluent is required to meet a total coli<strong>for</strong>m limit of<br />

23/100 ml. For the disinfection season months of April through October it is assumed<br />

that WWTPs have a disinfection process equivalent to a chlorination system with an<br />

average dose of 3 mg/L. There<strong>for</strong>e, an additional 3.5 mg/L chlorine is required to<br />

meet the more stringent reclaimed water pathogen limit from April to October. When<br />

the 2.5 mg/L chlorine dose <strong>for</strong> disinfection residual is included, the chlorine doses are<br />

as follows:<br />

April-October (7 months): 3.5 mg/L + 2.5 mg/L = 6 mg/L<br />

November-March (5 months): 6.5 mg/L + 3.5 mg/L = 9 mg/L<br />

Average Annual (based on weighted average, rounded) = 7 mg/L<br />

Craddock Consulting Engineers 21<br />

In Association with CDM & James Crook<br />

TM3-Component&Costs_0707

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