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WELL INSTALLATION AND INTERIM REMEDIAL ACTION REPORT <br />www.arcadis.com <br />FINAL_Forward CHCF (CDCR) Well Installation Report_10182024 <br /> <br />12 <br />The step test data were also analyzed and included as part of the hydraulic parameter assessment for <br />transmissivity and hydraulic conductivity using the Theis (1935) step test curve solution. Typically, all hydraulic <br />parameters derived using the pumping well were approximately an order of magnitude lower than those derived <br />from the observation wells. This indicated the influence of well losses on the pumping well dataset. The <br />observation well hydraulic results were considered to be most representative of the aquifer parameters and, <br />therefore, were preferentially used for aquifer parameter calculations. <br />Using only the monitoring well data, the hydraulic conductivity was indicated to range between 199 and 247 feet <br />per day (ft/day) (7.0 x 10-2 to 8.7 x 10-2 centimeters per second [cm/s]), with an average hydraulic conductivity of <br />228 ft/day (5.2 x 10-2 cm/s), which is indicative of medium to coarse sand, and/or sand and gravel mixes <br />(Kruseman and de Ridder 2000). Storativity for the monitoring wells was between 7.0 x 10-3 and 2.6 x 10-1 cm/s, <br />with an average of 7.5 x 10-2 cm/s, which is indicative of an unconfined or leaky aquifer system. Based on the <br />monitoring well data, the aquifer transmissivity1 was indicated to range between 5,956 and 7,414 square feet per <br />day (ft2/day), with an average transmissivity of 6,844 ft2/day. <br />Hydraulic conductivity estimates were also calculated for gain size sample data (Appendix G-4) collected from <br />depths adjacent to the screen zones of extraction well CDCR-EW-3. The grain size data were imported and <br />assessed using HydrogeoSieve version 2.1 (Devlin 2015). The hydraulic assessment data are presented in <br />Table 8, the output files from the analysis are presented in Appendix G-4, and the laboratory sieve data that were <br />used are presented in Appendix C. <br />Hydraulic conductivity calculated from the grain size data ranged between 5.0 and 60.1 ft/day (1.8 x 10-3 to 2.1 x <br />10-2 cm/s), with an average of 23.1 ft/day (8.2 x 10-3 cm/s), which is indicative of fine to medium sand and sand <br />and gravel mixes. The hydraulic conductivity estimates calculated using the grain size data are lower than the <br />aquifer testing estimates. The aquifer testing results are considered more accurate because the soil samples are <br />locally derived from the borehole and the aquifer test indicates the entire response of the aquifer. <br />5.2.2 CDCR-EW-4 Hydraulic Testing Data Analysis <br />Step and constant rate tests were conducted on extraction well CDCR-EW-4, which is screened across <br />permeable sections of the shallow and intermediate WBZs on the CDCR property (Table 1, Figures 1 and 2). Step <br />testing was performed by extracting groundwater from extraction well CDCR-EW-4 at incrementally increased <br />flow rates while recording changes in water levels from CDCR-EW-4. The step testing results are presented in <br />Table 3 and on Figure 4, and field data sheets are presented in Appendix D-2. <br />Step testing was conducted at rates of 7.5, 13.0, 15.0, 17.0 and 23.0 gpm. The step test results indicated a <br />specific capacity between 0.5 and 0.9 gallons per foot drawdown (Table 3). The specific capacity trend was <br />consistent (Figure 4) for the first four steps, and the well reached drawdown stabilization. The fifth step, when <br />pumping at a rate of 23.0 gpm, the well did not reach stabilization before the step test was concluded and was <br />indicated to be dewatering the well. This indicates that a maximum well capacity and sustainable yield is between <br />17 and 23 gpm. A pumping rate of 20 gpm could theoretically be achievable but would expose the upper screen <br />interval. <br />Constant rate testing was then conducted with extraction well CDCR-EW-4 pumped at a rate of 16.5 gpm for <br />approximately 8 hours and groundwater recovery monitored overnight. The hydraulic test design is presented in <br />Table 5, and field data sheets are provided in Appendix D-3. A monitoring well network of six wells, located <br /> <br />1 Transmissivity equals hydraulic conductivity multiplied by saturated permeable thickness,