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Recycling Treated Municipal Wastewater for Industrial Water Use

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Section 3: 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 />

Section 3: Recycled <strong>Wastewater</strong> System Components and<br />

Costs<br />

This section presents the third area of inquiry into the feasibility of Minnesota’s industries using recycled<br />

wastewater by addressing the question: Is wastewater recycling an economical practice? The answer<br />

begins with identification of the system components which include treatment facilities <strong>for</strong> a range of<br />

treatment requirements and potential facilities to meet those requirements. After establishing a basis <strong>for</strong><br />

the system components, a system of cost curves was developed <strong>for</strong> varying system sizes and transmission<br />

distances. Costs are presented by industry category as cost of service, on a dollar per gallon basis, to<br />

compare a recycled wastewater supply to traditional supplies. Appendix II-3 provides background<br />

in<strong>for</strong>mation and more detail on the treatment requirements, treatment technologies, and cost assumptions<br />

used in the analysis.<br />

3.1 Recycled <strong>Wastewater</strong> System Overview<br />

Recycled wastewater systems can be configured in many ways. Commonly used components are shown<br />

in Figure 3.1 and are described below. This study assumed certain components, identified as (1) through<br />

(7) and attributes <strong>for</strong> those components to develop costs. These assumptions are also described below.<br />

Treatment of WWTP Effluent (1)<br />

— Additional processes to those currently used by an existing WWTP, if needed.<br />

— New WWTP processes to replace existing processes during a plant upgrade, such as membrane<br />

filtration to replace clarification.<br />

Additional Disinfection (2)<br />

— A residual disinfectant is often used in the transmission system to minimize bacterial growth.<br />

Liquid chlorine (sodium hypochlorite) is assumed <strong>for</strong> this study.<br />

— Additional disinfection is required <strong>for</strong> year-round disinfection and more stringent pathogen limits.<br />

The existing facilities may be able to achieve this, but it is assumed new equipment is required.<br />

Storage (3)<br />

— In some instances, storage will be required to balance the diurnal or other WWTP flow variations,<br />

with the requirements of a specific industrial demand <strong>for</strong> different peak hour, weekly or other<br />

dominant demand patterns.<br />

— Storage will likely be required <strong>for</strong> WWTPs that reclaim over 50 percent of their flow. Smaller<br />

facilities, with less equalization capacity, are more likely to need storage.<br />

— The cost curves developed assume no storage requirements. Appendix II-3 provides storage<br />

system cost in<strong>for</strong>mation.<br />

Pump Station (4)<br />

— A pump station located onsite at the WWTP.<br />

— For cost development purposes, this study assumes delivery of supply to industry at a pressure of<br />

40 pounds per square inch (psi) and the same elevation as the WWTP.<br />

Recycled <strong>Wastewater</strong> Transmission System (5)<br />

— Transmission main and branch transmission lines supplying water to industries.<br />

— Variable flows and distances. This study evaluated flows of 0 to 30 mgd and distances of 1 to 10<br />

miles.<br />

Booster Pumps (6)<br />

— Some industries may require booster pumps depending on their location and delivery pressure<br />

requirements.<br />

— Industries A-D shown on the schematic represent potential configurations <strong>for</strong> pumping and<br />

treatment facilities not located on the WWTP site (either at the industry or in the transmission<br />

system).<br />

Metropolitan Council Environmental Services 37

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