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25I - AGMT - OCWD ASSESSMENT
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25I - AGMT - OCWD ASSESSMENT
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1/15/2015 4:39:07 PM
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City Clerk
Doc Type
Agenda Packet
Agency
Public Works
Item #
25I
Date
1/20/2015
Destruction Year
2020
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CITY OF SANTA ANA <br />Well No. 32 Nitrate Mitigation and Rehabilitation Study <br />3. PROJECT ALTERNATIVES <br />The alternatives consist of a variety of several options that include the following: <br />1. No action <br />2. Blending in the distribution system at the following locations: <br />• Garthe Reservoir <br />• Memory Lane Pressure Reducing Facility (blending Well No. 32 water into the well water from <br />the City's easterly sources) <br />3. Utilizing treatment technologies to reduce the nitrate levels located either on -site at Morrison Park or <br />at Garthe Reservoir <br />3.1 No Action <br />A no action scenario would result in the City operating Well No. 32 as it had in the past. The well would <br />be started and pumped to waste until the nitrate level dropped to acceptable levels before allowing the <br />groundwater to enter the distribution system. The pump to waste time varied based on the concentration <br />of nitrate detected. The City has reported that the pumping time varied as much as 6 to 18 hours. The City <br />would then be discharging anywhere between 900,000 to 2,700,000 gallons of groundwater to waste. <br />Well No. 32 waste flows are piped from the well and discharged to Santiago Creek, located adjacent to <br />Garthe Reservoir. The City must coordinate with Riverview Golf Course located downstream as the City <br />discharges into Serrano Creek which merges downstream with the Santa Ana River. Riverview Golf <br />Course lies within the Santa Ana River and course operations are impacted due to the well discharge. <br />Therefore, the City's operation of Well No. 32 would remain constrained both by the nitrate level in the <br />groundwater and the impacts to the golf course. <br />3.2 Blending in the Distribution System <br />High - nitrate groundwater is largely managed by blending the groundwater with water from other sources <br />that has lower nitrate concentrations. This approach is common for drinking water treatment in larger <br />municipalities and obviously requires a second, low- nitrate water source. <br />3.2.1 Blending in Garthe Reservoir <br />The City prepared a nitrate blending and monitoring plan in 2010 for both Garthe and Walnut Reservoirs. <br />One of the potential alternatives is to blend water from Well No. 32 into Garthe Reservoir. The blending <br />plan was reviewed to determine whether it would be feasible to blend Well No. 32 water into the <br />reservoir. <br />Garthe Reservoir site consists of three reservoirs with a total of 16 million gallon storage capacity, Wells <br />18, 24, 36, and 39 and six booster pumps. The City provides an ongoing nitrate blending treatment <br />process in which high nitrate water from Well No. 18 and Well No. 24 are blended with low nitrate water <br />from Well Nos. 36 and 39. The wells are staged in the SCADA system to utilize the low nitrate wells first <br />(i.e., Well Nos. 36 and 39) followed by the high nitrate wells. The staging of the wells is based on the <br />reservoir level. The control logic in the station's Remote Terminal Unit is programmed to prevent Well <br />18 and Well 24 from coming on alone (i.e., Well Nos. 36 or 39 have to be running first). Table 3 -1 <br />P:V' 00597 \008ylrngineoing\OS\_We11J2- Nitrate - Mitigation \Dian Report \02text dot 51 .13 3 TETRA TECH <br />
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