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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 />

smaller WWTPs where the diurnal flows could drop below the required demand of<br />

an industry or group of industries. Weekly demand patterns of industry could also<br />

change and should be accounted <strong>for</strong> when establishing storage requirements.<br />

This study does not consider any seasonal storage requirements <strong>for</strong> a reclaimed<br />

supply. Seasonal storage would be required <strong>for</strong> WWTPs that incorporate reuse<br />

practices to reduce their discharges to waterways and supply seasonal customers.<br />

These facilities would need to store effluent during periods when the seasonal reuse<br />

customers do not use water. These are cases where the WWTP’s NPDES permit limits<br />

are more stringent in the warmer months and rather than upgrade treatment facilities<br />

to meet the lower seasonal mass limits, a portion of the plant effluent is reused and<br />

not discharged to the receiving stream. Seasonal storage may also be required to meet<br />

a seasonal water demand, where peak demands cannot be consistently matched by<br />

the WWTP flow. The majority of Minnesota’s industries have year-round water<br />

demands, with the exclusion of agricultural processing industries that may depend on<br />

seasonal crops, industries that use reclaimed water <strong>for</strong> landscape irrigation, and some<br />

cooling water applications. Seasonal storage facilities are more commonly used in<br />

water reuse systems <strong>for</strong> irrigation practices.<br />

Reclaimed water storage can also provide system reliability with a short-term supply<br />

if there is a process disruption, as well as additional contact time <strong>for</strong> chlorine<br />

disinfection.<br />

4.3 Pumping<br />

The model <strong>for</strong> this study assumes a pump station is located on the WWTP site and is<br />

owned by the municipality. The pump station will include redundancy and reliability<br />

features consistent with state water supply requirements. The pump station is sized<br />

<strong>for</strong> peak flow and a residual pressure at the end of the pipe line of 40 psi, assuming<br />

delivery at the same elevation as the WWTP.<br />

4.4 Transmission Pipelines<br />

The majority of reclaimed transmission piping is polyvinyl chloride pipe (PVC) or<br />

ductile iron pipe (DIP) meeting specific industry standards. For this study, the<br />

transmission system is assumed to be all <strong>for</strong>cemain: pipe with a diameter of 24 inches<br />

or less is PVC, DR 18, Class 150. Greater than 24 inch diameter pipe is assumed to be<br />

DIP, Class 51 with push-on joints. Pipelines are sized to carry the peak hour demand<br />

(peaking factor of 3) of a given industry at a target velocity of 5 to 7 fps.<br />

5.0 Costs<br />

5.1 Overview<br />

This section presents the estimated cost of service <strong>for</strong> a municipal water reuse system<br />

to serve a “base level” water quality and “alternative” water quality supplies to<br />

industries. The base level quality is defined as a hard water that meets regulatory<br />

standards <strong>for</strong> non-contact industrial water uses. The processes needed to produce the<br />

base level water quality define a “base WWTP” <strong>for</strong> water reuse to which other<br />

28 Craddock Consulting Engineers<br />

In Association with CDM & James Crook<br />

TM3-Component&Costs_0707

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