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 COTTONWOOD
WATER & SANITATION DISTRICT

Mission Statement

Provide high quality, reliable, sustainable water and ecologically safe wastewater collection and treatment with a commitment to service excellence and cost effectiveness.

 

TABLE OF CONTENTS

Article Summaries / Case Studies

 


INDIRECT POTABLE REUSE (WATER RECYCLING)

In traditional water systems, raw water is diverted from a source, such as a stream, lake, or aquifer, and treated before being distributed to consumers for drinking water. After use by consumers, wastewater is collected, treated and discharged to a receiving water body, often to the same one from which raw water is diverted. The discharge of treated wastewater occurs downstream of the raw water diversion.

In many places in the United States unplanned indirect potable reuse is being practiced. Unplanned potable reuse occurs when treated wastewater discharged from an upstream community is subsequently withdrawn for drinking water use downstream by another community. The fraction of wastewater effluent in the raw drinking water can vary significantly depending upon the relative amounts of native water and effluent. In some cases, more than half of the water in rivers used as a drinking water source comes from wastewater discharges.

In planned indirect potable reuse systems, treated wastewater is intentionally used to augment water supplies. Rather than discharging treated wastewater downstream of the raw water diversion, it is returned upstream. The treated wastewater mixes with native water and then is diverted and treated for potable use.

Fundamental to the practice of planned indirect potable reuse is the concept of multiple barriers to remove contaminants. These barriers include wastewater treatment, dilution and natural cleansing in the water body, effective drinking water treatment, and extensive raw and treated water monitoring to ensure high quality drinking water.

Planned indirect potable reuse systems should incorporate a number of safety measures beyond those normally included in conventional water systems. These barriers to potential contaminants include advanced wastewater treatment, the receiving water, and the water treatment system. Facility redundancy and increased water quality testing enhance system reliability.

There are a number of successful planned indirect potable reuse systems in operation across the country. There are systems in California, Virginia and Texas that provide safe drinking water to citizens every day. Several of these systems have been operating for over 25 years. Studies have shown that there are no health effects, long or short term, as a result of consuming reclaimed water.

The proposed Cottonwood Water and Sanitation District (CWSD) and Arapahoe County Water and Wastewater Authority (ACWWA) planned indirect potable reuse project will have multiple barriers to produce safe water for their consumers. Wastewater is treated at the Lone Tree Creek Wastewater Treatment Plant (LTCWWTP). This advanced treatment plant provides biological nutrient removal followed by membrane microfiltration and disinfection. The plant successfully removes nitrate and phosphorous, as well as pathogens. The highly treated effluent would be discharged into the Cherry Creek alluvium, an aquifer influenced by surface water flow in Cherry Creek. The water will seep through the sandy alluvial material taking about 18 months to reach the supply wells. While travelling through the alluvium, the water will be further filtered and diluted with native flows. After reaching the supply wells, the water will be treated in a new advanced water treatment facility. The treatment will include a reverse osmosis membrane process to remove organic and pathogenic contaminants. The clean water from the membrane process will then be disinfected and distributed to CWSD and ACWWA customers.

Recent articles on the subject of planned indirect potable reuse were researched. The following literature review of these articles includes title, author(s), date, and a summary of the main points.

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Recharge Project Overcoming Impediments to Water Recycling: The San Gabriel Valley Groundwater, Hartling, Earle C., and Margaret H. Nellor, WEFTEC 2000.

  • Initially developed in 1989, the San Gabriel Valley Groundwater Recharge Project is a 25,000 AFY project. Tertiary treated effluent from the Sanitation Districts of Los Angeles County San Jose Creek West WRP is used to surface recharge a potable water aquifer in the San Gabriel Valley. A 10,000 AFY "demonstration" was scheduled for completion in late 2001.
  • California DHS required 450 mg-min/L CT (chlorine residual multiplied by contact time) and a minimum of 90 minutes contact time (peak dry weather flow) for 5-log virus inactivation.

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Use of Recycled Water to Augment Potable Supplies: An Economic Perspective, Potable Reuse Committee, WateReuse Association, Sept. 1999.

  • The East Valley Water Recycling Project, proposed by the City of Los Angeles Department of Water and Power, has an ultimate capacity of 35,000 AFY. The water would be used for industry, irrigation, and groundwater recharge of potable aquifers. The estimated cost of the project is $478 per acre-foot.
  • The Groundwater Replenishment System operated by the Orange County Water District and Orange County Sanitation District employs reverse osmosis and UV disinfection of secondary treated wastewater. The effluent is disposed of at existing spreading basins or injection wells for replenishment of groundwater supply and seawater intrusion control barrier, respectively. The existing capacity will be 68,000 AFY by 2003, and the ultimate capacity is 20,000 AFY. The cost of the project is estimated to be $565 per acre-foot.
  • The City of San Diego Water Purification Project would construct a system with a capacity of 15-20,000 AFY. The system would include microfiltration, reverse osmosis, ion exchange and ozonation to treat North City WRP tertiary effluent. The project would also include the construction of a pipeline to the San Vicente water supply reservoir. The estimated cost of the project is $1,060 per acre-foot.

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Development of Regulations for Potable Water Reuse in Georgia, Hall, Ken C., WEFTEC 2000.

  • The key points of the paper are: the provision of multiple barriers to key pollutants, provision of reliability and redundancy, use of demonstrated technologies, protection of public health, and importance of public perception.
  • In order to reuse treated wastewater to augment the water supply, the draft guidelines would require two barriers for suspended solids, three barriers for pathogens, and one barrier each for both metals and total organic carbon.
  • Biological nutrient removal, nanofiltration, and reverse osmosis are considered barriers for suspended solids, pathogens, metals, and total organic carbon. Microfiltration and ultrafiltration are considered barriers for suspended solids, pathogens, and total organic carbon. Disinfection is considered a barrier for pathogens.
  • Based on this, the proposed project would include three barriers for suspended solids, five barriers for pathogens, two barriers for metals, and two barriers for total organic carbon. This does not include the aquifer, which is not considered in the guidelines.
  • The guidelines also include monitoring and effluent limits for the wastewater treatment plant. Turbidity, TOC, and total coliform limits would be imposed on the wastewater discharge. For discharges to water supplies, Turbidity would be sampled every 4 hours and the maximum limit for any sample would be 5.0 NTU. TOC would be monitored daily and the maximum monthly average would be 10 mg/l. Total coliforms would be sampled daily, and at least 75% of the results shall be less than detect and no sample shall exceed 25 cfu/100 ml.
  • Semiannual samples for giardia and cryptosporidium shall be taken and analyzed for discharge to water supply reuse. Results shall always be less than detect.
  • There would also be finished water quality requirements. Reclaimed water shall not cause violation of water quality standards of the receiving water body in addition to standards set forth in guideline. Priority pollutant and SDWA parameters shall be analyzed semiannually.
  • Indirect potable reuse is the preferred option for potable reuse. It has also been proven safe after years of unintentional practice.

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Developing Indirect Potable Reuse to Increase Water Supply, Improve Water Quality and Manage Wastewater Discharge in Orange County, California, Anderson, Blake P., Thomas M. Dawes, Gregory L. Leslie, Donald F. McIntyre, William R. Mills Jr., J.E. Norman, Wendy Sevenandt, and T.S. Snow, WEFTEC 2000.

  • Three phase, 100,000 AFY Groundwater Replenishment system to recharge local groundwater basin by Orange County Water District and Orange County Sanitation District.
  • System design based on new regulatory guidelines, which include complete treatment with a process designed to reduce the concentration of TOC. Additional treatment with a process to remove TDS might be required to comply with local groundwater quality objectives.
  • The use of ultrafiltration and microfiltration as pretreatment for reverse osmosis is the industry standard for indirect potable reuse.
  • California DHS requires 2,000 foot horizontal separation and a one-year detention time between the point of injection and extraction for indirect potable reuse projects.

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East Valley Water Recycling Project: Challenges of Implementation, Van Wagoner, William T., WEFTEC 2000.

  • City of Los Angeles Department of Water and Power project will ultimately provide 35,000 AFY of tertiary treated recycled water for groundwater recharge, irrigation, and industrial uses.
  • Three-year demonstration project started in September 1995, providing 10,000 AFY for groundwater recharge.
  • Proposed requirements state that water extracted from the ground may not contain more than 20% recycled water over the course of a five-year running average.
  • Groundwater recharge regulations specify that monitoring wells be placed one fourth and half of the distance between the spreading grounds and the closest domestic production well.
  • Extensive public involvement program. Six public hearings, nine press releases, a media open house, 46 newspaper articles, numerous television news reports, project information bill stuffers, a project hotline telephone, numerous project fact sheets, a project description was published on the Department’s website, and two full page color articles in the Los Angeles Times were all part of the program. The program began in 1990 and ran through April 2000.
  • Project currently under review by City Council.

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Microfiltration and Reverse Osmosis Pilot Testing for Indirect Potable Reuse at the University Area Joint Authority, Book, Brian L., Steven M. Siegfried, Stephen T. Welch, and Jason D. Wert, WEFTEC 2001.

  • Pilot testing facility constructed to determine the feasibility of reclaiming 3.0 mgd of secondary effluent for water reuse and streamflow augmentation.
  • Commercial and industrial customers will use effluent, followed by discharge to Slab Cabin Run. The discharge will mix with several State College Borough Water Authority supply wells, and the Pennsylvania Department of Environmental Protection determined the expected treatment level for indirect potable reuse.
  • "Microfiltration/Ultrafiltration is not sufficient alone to completely produce recycled water that meets all established water quality limits." Nitrates, TDS, and TOC are of concern to this project (all of these would be removed by reverse osmosis, BNR would remove nitrate).

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Indirect Potable Reuse and Aquifer Injection of Reclaimed Water, Beverly, Sharon D., William J. Conlon, and David F. MacIntyre, AWWA Water Sources Conference Proceedings 2002.

  • Membranes followed by ultraviolet disinfection provides multiple effective barriers.
  • Pilot study in Orlando, Florida looked at reinjecting water into aquifer or augmenting lakes for potable reuse.
  • Reverse Osmosis is not always necessary to reach desired water quality.
  • All indirect potable reuse projects would have to meet Florida Maximum Contaminant Levels for Direct Aquifer Injection. These MCLs include primary and secondary drinking water standards, TOC less than 3.0 mg/l, total organic halides less than 0.2 mg/l, and total nitrogen less than 10.0 mg/l.
  • Membrane fractionation studies showed that NF removed all contaminants except nitrate. 50 Daltons was the effective molecular weight cutoff for nitrate. This cutoff is designated as an RO membrane.

Thomas, and Tama Snow, WateReuse Association Newsletter, 1998.

  • National Research Council (NRC) report entitled Issues in Potable Reuse: the Viability of Augmenting Drinking Water Supplies with Reclaimed Water in March 1998.
  • Careful, thorough, project-specific assessment that includes contaminant monitoring, health and safety testing, and system reliability evaluation is required for indirect potable reuse projects.

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The Ongoing Evolution of Water Reuse Criteria, Crook, James, AWWA Water Sources Conference Proceedings, 2002.

  • The California Water Recycling Criteria were updated in 2000. The updated criteria include total coliform limits and required treatment for groundwater recharge by spreading are determined on a case-by-case evaluation.
  • Disinfection requirements of 2000 California Water Recycling Criteria include a chlorine disinfection process that provides a residual chlorine concentration times modal contact time (CT) value of at least 450 mg-min/L at all times with a modal contact time of at least 90 minutes where disinfected tertiary treated wastewater is required. This is based on the Pomona Virus Study.
  • The paper summarizes the USEPA Guidelines for Water Reuse. Groundwater recharge of potable aquifers by injection and augmentation of surface water supplies requires secondary, filtration, disinfection, and advanced water treatment. Water quality goals include pH 6.5-8.5, turbidity less than 2 NTU, no detectable fecal coliforms, less than 1 mg/L chlorine residual, and compliance with all drinking water standards.
  • USEPA Guidelines for Water Reuse has different requirements for groundwater recharge of potable aquifers by spreading. It requires site-specific treatment with secondary treatment and disinfection at a minimum. The reclaimed water quality is also site specific, but must be able to meet drinking water standards after percolation through the vadose zone.
  • The paper also presents the World Health Organization guidelines for potable municipal reuse. They include no fecal coliform or virus particles plus no toxic effects on man. Essential treatment processes include primary, secondary, nitrification, and disinfection. In addition, one or more of the following processes will be essential: filtration or equivalent, denitrification, chemical clarification, carbon adsorption, and ion exchange or other means to remove ions.

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Too Much or Too Little: Public Health Perspectives of Water Reclamation Reliability, Riley, Craig L., AWWA Water Sources Conference Proceedings, 2002.

People are Watching: Public Participation in a "Win-Win" Reuse Project, Janga, Ram G., and Richardson, Andrew W., AWWA Water Sources Conference Proceedings.

  • 10-mgd plant called Northwest Water Resource Center began operation in Las Vegas in July 2001. The plant treats municipal wastewater for irrigation use in the summer, and for potable water storage in the aquifer during the winter. Recharge/recovery wells inject/withdraw water from the aquifer based on demand and time of year.
  • Community Relations and Public Involvement Program was developed for the project. They took on a number of tasks including development of audio-visual programs, brochures, fact sheets, project newsletters, and news releases. They also coordinated with the media, organized public information meetings, responded to public inquiries via phone and mail, and organized field trips to similar projects.

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Indirect Potable Reuse: Committee Report, McEwen, Brock, and Tom Richardson, AWWA/WEF Water Reuse Conference Proceedings, 1996.

  • Water supply development policy has shifted from large, trans-basin water conveyance projects to conservation and reuse.
  • More stringent wastewater disposal standards are becoming common. It may be more advantageous to reclaim treated wastewater for potable use than discharge highly treated water to sensitive aquatic systems.
  • Current planned indirect potable reuse in Los Angeles County, CA, Orange County, CA, Fairfax County, VA, and El Paso, TX.

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"Potable use of Reclaimed Water," Crook, James, Jacqueline A. MacDonald, and R. Rhodes Trussell, Journal AWWA, August 1999.

  • Treatment technology is advanced enough that very high quality water can be produced from wastewater effluent.
  • More than two dozen large water utilities use water that receives significant contributions from wastewater discharges.
  • Reuse requirements should exceed drinking water and wastewater discharge requirements.
  • Public health should be protected by providing increasingly effective and reliable treatment and through more comprehensive monitoring in scope and frequency. Projects with less conservative treatment should incorporate more comprehensive monitoring and vice versa.
  • More rigorous pretreatment programs should be considered when indirect potable reuse is planned.
  • Multiple barriers are essential.
  • Aquifer storage appears to be a better buffer for reclaimed water than surface water bodies.
  • The treatment of the water in the aquifer may be considered an additional barrier to certain contaminants.
  • Alternative means of disposing of reclaimed water should be maintained in the event that water quality standards are not met.

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Using Reclaimed Water to Augment Potable Water Resources, Joint Task Force of the Water Environment Federation and the American Water Works Association, 1998.

  • From the WEF water reuse policy statement: "Treated wastewaters already comprise an unplanned, but significant component of our nation’s freshwater supplies through discharge to streams, lakes, and groundwater basins used to supply domestic, industrial, and agricultural water demands."
  • From the AWWA water reuse policy statement: "…whereby reclaimed water is a supplement to existing raw water sources receiving appropriate subsequent treatment."
  • System reliability takes on far greater importance in a potable water reuse project.

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Issues in Potable Reuse, National Research Council Commission on Geosciences, Environment, and Resources Water Science and Technology Board, 1998.

  • Concerns about planned indirect potable reuse also apply to conventional water supplies under the influence of wastewater discharges.
  • Significant health risks have not been identified in communities using reclaimed water. This is confirmed by analytical and toxicological testing as well as epidemiological studies.
  • Indirect potable reuse system requirements should exceed the requirements for conventional water treatment facilities.
  • Every reuse project should have a rigorous and regularly updated monitoring system to ensure the safety of the product water.
  • All major chemical inputs from household, industrial, and agricultural sources should be considered.
  • Stringent industrial pretreatment and pollutant source control programs should be used.
  • Potable reuse systems should continue to employ strong chemical disinfection processes to inactivate microbial contaminants even if they also use physical treatment systems.
  • Barriers for microbiological contaminants should be more robust than convention water treatment.
  • Operators of reuse facilities need training beyond that typically provided.

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Singapore Water Reclamation Study – Expert Panel Review and Findings, June 2002.

  • "NEWater" project in Singapore began in 1998. Project takes effluent from the Bedok Water Reclamation Plant and treats it with microfiltration, reverse osmosis, and UV. The plan is to augment raw water reservoirs with reclaimed water.
  • 2.6 mgd demonstration plant in operation since May 2000. The plant demonstrated that reclaimed water can be consistently and reliably produced on a large scale.
  • Sampling and Monitoring Programme included extensive analysis of many parameters in the following categories: physical, disinfection by-products, inorganic, disinfection by-products, pesticides/herbicides, radionuclides, wastewater signature components, synthetic and natural hormones, and microbes.
  • The report concludes that the physical, chemical, and microbiological data for the reclaimed water are within the requirements of USEPA and the World Health Organization.
  • A health effects study on mice and fish is being conducted.
  • To date, the Health Effects Testing Programme show that exposure to or consumption of reclaimed water does not have carcinogenic or estrogenic effects on fish or mice.
  • Expert Panel findings include: reclaimed water is considered safe for potable use; Singapore should adopt indirect potable reuse because trace minerals are provided, by blending with natural reservoir, that are removed from reclaimed water by treatment, storage provides additional safety, and for public acceptance; Singapore should consider the use reclaimed water for indirect potable reuse as it is a safe supplement to the water supply; and a vigilant and continuous monitoring programme be implemented if indirect potable reuse is used.

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