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Evaluation of Groundwater Supply Alternatives Within Bernal Subbasin
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Evaluation of Groundwater Supply Alternatives Within Bernal Subbasin
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4/14/2026 10:07:54 AM
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CITY CLERK
CITY CLERK - TYPE
AGENDA REPORT
DOCUMENT DATE
4/21/2026
DESTRUCT DATE
15Y
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Page 3 <br />along with the typical 24-hour specific capacity value used in most well yield calculations. Available <br />drawdown relates to regional groundwater elevations and varies seasonally and year to year, depending <br />on how wet or dry the recent and preceding years have been. Well capacities were estimated for relatively <br />high and low available drawdown estimates. Well efficiency can be highly variable and is heavily <br />dependent on well engineering design considerations (e.g., screen slot size, filter pack quality and <br />gradation, well drilling/development specifications) and drilling contractor performance (e.g., driller <br />efficiency, driller adherence to drilling specifications). Each of these three key inputs is described in more <br />detail below. <br />Data from the constant rate aquifer tests were reviewed to calculate the 24-hour specific capacity by <br />extending the trend of water level declines (on a semi-log time-drawdown plot) from the 8-hour test out <br />for a 24-hour period. The 24-hour specific capacity was calculated by dividing the average pumping rate <br />during the 8-hour constant rate test by the total estimated drawdown over a 24-hour period. In addition, <br />specific capacity values were determined in a similar manner (extending the semi-log plot time-drawdown <br />line from 8 hours to 30 daysand 90 days) for 30-day and 90-day continuous pumping scenarios to evaluate <br />the difference in assumptions regarding specific capacity values. The specific capacity values for different <br />time periods are summarized in Table 3. <br />Table 3. Summary of Test Well Specific Capacity Values <br />tĞůů/Pumping <br />Rate (gpm) <br />24-Śƌ <br />;ĨƚͿ <br />24-Śƌ <br />Q/s <br />(gpm/ft) <br />30-ĂLJ <br />;ĨƚͿ <br />30-ĂLJ <br />Q/s <br />(gpm/ft) <br />90-ĂLJ <br />;ĨƚͿ <br />90-ĂLJ <br />Q/s <br />(gpm/ft) <br />Tennis Park 549 9.6 57.2 10.3 53.3 10.6 51.8 <br />Hansen <br />Park 594 19.5 30.5 21.5 27.6 22.5 26.4 <br />Del Prado <br />Park 252 15.6 16.2 16.2 15.3 17.2 14.7 <br />As summarized above Tennis Park specific capacity ranges from 57 to 52 gpm/ft, Hansen Park specific <br />capacity ranges from 30.5 to about 26.5 gpm/ft, and Del Prado Park ranges from 16.2 to 14.7 gpm/ft for <br />24 hours to 90 days of pumping. <br />Given the relatively high groundwater elevations at the time of the pumping tests, the measured <br />groundwater level at the start of testing was used as the basis for the high-end well capacity estimate. <br />The difference between the measured groundwater level and the top of the uppermost screen was used <br />as the available drawdown for the well capacity estimate. As described above, historical groundwater <br />elevation contour maps (for critical dry years) and municipal pumping were reviewed to determine an <br />appropriate regional groundwater elevation to use at the test well sites as the basis for low-end well <br />capacity estimates. The water years considered for the low-end estimate were 2021 and 2022. The <br />difference between groundwater elevations in these dry years and the top of the well screen were used <br />as available drawdown for low-end estimates. <br />Well efficiency relates to the difference between the pumping water level inside a production well casing <br />and the groundwater level in the aquifer formation just outside the well filter pack. In theory, a well would <br />be 100% efficient if these water levels are the same; in practice, this rarely occurs for high-capacity
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