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Recycling Treated Municipal Wastewater for Industrial Water Use

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3.4 Storage and Transmission<br />

Overview<br />

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 />

An integral part of the planning, operation, and maintenance of recycled wastewater systems is the<br />

transmission of the recycled wastewater to the customer. Transmission costs, both capital and O&M, are a<br />

significant cost component of recycled wastewater projects. Transmission systems typically include onsite<br />

storage, pump station(s), piping, off-site storage, diversion structures to off-site storage ponds, service<br />

connections, and metering. <strong>Wastewater</strong> recycling regulations and guidelines generally include standards<br />

<strong>for</strong> the design, installation, operation, and maintenance of the transmission systems. In addition, there are<br />

very specific guidelines and requirements <strong>for</strong> any cross-connections to other systems, use of backflow<br />

preventions devices and other plumbing features.<br />

Storage<br />

The conceptual recycled wastewater system, presented previously in Figure 3.1, provides <strong>for</strong> storage<br />

facilities on the WWTP site to meet a range of storage volumes. The base recycled wastewater system<br />

assumes that no storage is required, which is valid <strong>for</strong> a larger WWTP serving smaller industrial demands.<br />

The cost curves developed <strong>for</strong> this study do not include storage requirements, but cost in<strong>for</strong>mation was<br />

developed to asses the impact of storage on system costs and is detailed in Section 5.5 of Appendix II-3.<br />

For purposes of this study, it is assumed that where storage is needed, it is <strong>for</strong> diurnal, daily, or weekly<br />

industrial demand patterns that the WWTP cannot meet with their continuous supply. Storage<br />

requirements <strong>for</strong> industrial applications can vary widely. Some industries may have adequate storage to<br />

meet peak hour requirements, but most would not have storage to handle significant volumes. Storage<br />

would likely be needed with smaller WWTPs where the diurnal flows could drop below the required<br />

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

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 supply. Seasonal storage<br />

would be required <strong>for</strong> WWTPs that incorporate reuse practices to reduce their discharges to waterways<br />

and supply seasonal customers. These facilities would need to store and/or dampen peak flows to meet<br />

NPDES limits during periods when the seasonal recycled wastewater customers do not use water.<br />

Seasonal storage may also be required to meet a seasonal water demand, where peak demands cannot be<br />

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

demands. Some exceptions include: agricultural processing industries, which may depend on seasonal<br />

crops; industries that use recycled wastewater <strong>for</strong> landscape irrigation; and some cooling water<br />

applications. Seasonal storage facilities are common in recycled wastewater systems <strong>for</strong> irrigation<br />

practices.<br />

Recycled wastewater storage can also provide system reliability with a short-term supply if there is a<br />

process disruption as well as additional contact time <strong>for</strong> chlorine disinfection.<br />

Pumping<br />

This study assumes a pump station is located on the WWTP site and is owned by the municipality. The<br />

pump station is assumed to include standby and reliability features consistent with state water supply<br />

requirements. The pump station is sized <strong>for</strong> peak flow and a residual pressure at the end of the pipe line of<br />

40 psi, assuming delivery at the same elevation as the WWTP.<br />

Transmission Pipelines<br />

The majority of recycled wastewater transmission piping is polyvinyl chloride pipe (PVC) or ductile iron<br />

pipe (DIP) meeting specific industry standards. For this study, the transmission system is assumed to be<br />

all <strong>for</strong>ce main with the following characteristics: pipe with a diameter of 24 inches or less is PVC, DR 18,<br />

Class 150 and greater than 24 inch diameter pipe is DIP, Class 51 with push-on joints. Pipelines are sized<br />

to carry the peak hour demand of a given industry at a target velocity of 5 to 7 feet per second (fps).<br />

Details assumed <strong>for</strong> the cost analysis are provided in Appendix II-3.<br />

Metropolitan Council Environmental Services 49

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