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REGIONAL GROUNDWATER FACILITIES PROJECT <br />FEASIBILITY STUDY <br /> <br /> 17 Zone 7 Water Agency <br />December, 2025 <br /> <br />3.3. Project Alternative Production Rates <br />Each of the four project alternatives is capable of producing a range of instantaneous and annual volumes, <br />with actual groundwater production influenced by both hydrogeologic setting/conditions and engineered <br />well materials and pump equipment design features. <br />Hydrogeologic setting/conditions include the thickness and continuity of water-bearing sands <br />and gravels relative to less permeable materials, which determine aquifer transmissivity, defined <br />as the aquifer’s ability to yield water when pumping induces drawdown. Seasonal water level <br />fluctuations and long-term basin trends further affect available drawdown and, therefore, <br />sustainable production. Siting of a production well site a significant distance from the test well <br />site may result in different hydrogeologic conditions (e.g. yield and/or water quality). <br />Well construction characteristics also play a critical role. Production capacity depends on drilling <br />contractor performance/efficiency, selection and placement of well screens, screen length, and <br />gravel pack design. The position of the uppermost screen interval is particularly important for <br />accessing available drawdown in the well (defined as the difference between the static water level <br />and the top of the well screen). Collectively, these factors establish the specific capacity (Q/s) and <br />ultimately the production rate of the well, defined as the pumping rate achieved per unit of <br />drawdown (expressed in gpm/ft). <br />Pump equipment design must then be optimized in consideration of site-specific hydrogeologic <br />and well construction conditions. Properly sized bowls, column, shaft, and motors allow the pump <br />to utilize the full drawdown range from static water levels down to the top of the screen. <br />If any one of these system components (hydrogeologic setting/conditions, well design/construction, or <br />pumping equipment) is suboptimal, the overall capacity of the well is constrained. Conversely, when all <br />three are optimized together, wells can reliably achieve their design production rates and sustain long- <br />term groundwater development. <br />Table 4 summarizes the estimated production capacities for each project alternative under drought-year, <br />average-year, and wet-year conditions. Annual production estimates assume an 18-hour daily runtime <br />(6,570 hours per year), consistent with Zone 7’s 75-percent reliability factor for facility operation and <br />provide a common basis for comparison against Zone 7’s 7,000 AFY drought-year production objective. <br />Results indicate that Alternatives 1 and 3 cannot meet the 7,000 AFY target while operating within the 18- <br />hour limit and therefore are not considered viable for Zone 7’s production goals, though they are carried <br />forward for informational and comparative purposes. <br />At the upper end, Alternative 4 is capable of producing approximately 9,800 AFY under drought <br />conditions; however, Zone 7 does not intend to produce more than 9,000 AFY during drought years, as <br />groundwater sustainability impacts have not been modeled beyond this annual production total for <br />drought years. As a result, the additional production capacity represented by Alternative 4 would not be <br />utilized under normal operating conditions, effectively increasing capital cost without a proportional <br />supply benefit leaving Alternative 4’s only primary advantage of enhanced operational flexibility and <br />reliability beyond Zone 7’s standard policy requirements.