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Evaluation of Groundwater Supply Alternatives Within Bernal Subbasin
City of Pleasanton
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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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Zone 7 Water Agency – Hansen Park Test Well Summary <br />and Production Well Design Recommendations <br />5 Zone 7 Water Agency <br />December 2025 <br />requirements of the City’s Waste Discharge Permit. Benzo-a-pyrene was not detected in that testing. <br />Based on the fact there have been no detections of benzo-a-pyrene in other wells in Pleasanton area and <br />the non-detect in the initial sample from the well, LSCE believes that sample was contaminated and is not <br />representative of groundwater. <br />Based on a review of water quality data for the City of Pleasanton and Zone 7 wells, iron, aluminum, and <br />manganese concentrations are typically non-detect or below their respective MCLs. Iron and aluminum <br />concentrations can be elevated in a turbid sample. Aluminum has typically been non-detect in the City of <br />Pleasanton and Zone 7 wells. The concentration of aluminum in the Hansen Park well was 0.44 mg/l. The <br />concentration of iron in the well was 0.54 mg/l. LSCE believes that, based on the water quality of other <br />wells in the area and the elevated turbidity of samples, the levels of aluminum and iron are not <br />representative of groundwater. <br />The concentration of manganese was 0.045 mg/l, below its MCL of 0.050 mg/l. It has been our experience <br />that manganese concentrations in monitoring wells and test wells can be higher than observed in <br />production wells. That is, water produced from monitoring wells or test wells will have elevated <br />manganese concentrations, whereas production wells completed in the same formations have lower <br />concentrations or are non-detect for manganese. LSCE has recognized this phenomenon in monitoring <br />and test wells across the state, in different geologic environments, using different drillers and drilling <br />techniques, and different laboratories. In our experience, this only occurs with manganese. <br />The most probable cause for elevated concentrations of manganese in the test well is related to well <br />development techniques and limitations. Due to the size of the well casing, limited screen section lengths, <br />water levels during pump and surge development, pump size limitations, and well yield, the development <br />of a small-diameter well can be less effective than can be achieved in a large-diameter well. The <br />development of a full-size production well can be more vigorous and effective than is possible in a small- <br />diameter well with isolated zones. LSCE believes that the large discharge volumes and development <br />techniques utilized in production wells results in more effective well development and removal of residual <br />drilling fluids and formation material than is possible in small diameter wells. Based on our experience <br />and the water quality of other wells in the vicinity of the Del Prado test well, and the limitations of <br />development of a small-diameter well, we believe that the elevated concentration of manganese is not <br />representative of groundwater. <br />While meeting Title 22 water quality standards, hardness and total dissolved solids values exceed Zone <br />7/City of Pleasanton’s water quality targets. The exceedances are summarized in Table 5. <br />Table 5. Water Quality Targets and Exceedances <br />Parameter Target Result <br />Hardness 150 mg/l 410 <br />Total Dissolved Solids 500 mg/l 542
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