Laserfiche WebLink
Report.Groundwater-quality Monitoring--October 27,2004, 7500 West Eleventh Street, Tracy, CA. Page 8 <br /> _ 2.0 OCTOBER 2004 GROUNDWATER-QUALITY MONITORING ROUND <br /> On October 27 and 28, 2004, SJC conducted the sixteenth round of groundwater-quality <br /> monitoring at the 7500 West Eleventh Street site. The depth to groundwater was <br /> y measured in all of the 27 extant wells, including floating product monitoring wells <br /> MWFP-1 through MWFP-5,but sampling for groundwater-quality analysis was restricted <br /> to the 22 monitoring wells MW-1 through MW-19, which are at the locations shown on <br /> Figure 2. <br /> 2.1 Groundwater Elevations and Flow Direction <br /> To initiate the October 2004 sampling program, the depth to groundwater in each of the <br /> 27 monitoring wells was measured using a conductivity probe on October 27, 2004. The <br /> jj water table elevations were computed relative to mean sea-level (MSL). Those <br /> measurements and the computed groundwater table elevations are recorded in Table 1. <br /> In the period from July 26, 2004, the date on which the depths to groundwater in the <br /> monitoring wells were last measured, to October 27, 2004, the groundwater table fell <br /> between 0.33 ft. and 0.8 ft in the monitoring wells that are screened in the near-surface <br /> aquifer beneath the site. (See Figures 4 through 9 for aquifers and well screen intervals.) <br /> k <br /> As has been observed previously, the greatest rise in the groundwater table was observed <br /> in the wells in the approximate southern half of the well array, while the rise diminished j <br /> with distance north from there. In the monitoring wells that are screened in the first <br /> aquifer that is located deeper than the near-surface aquifer (i.e., Monitoring Wells MW- j <br /> 3A and 12A), the piezometric head fell, on average,by 0.67 ft. In the deepest aquifer that + <br /> is monitored at the site (by Monitoring Well MW-3B) the piezometric head rose by 2.05 <br /> The observed changes in depths to groundwater in the groundwater-quality monitoring <br /> wells that were observed between July and October 2004 reflect the fact that, as SJC has <br /> noted in previous reports, agricultural irrigation dominates variations in groundwater <br /> elevations in the area around Tracy. When crops are being irrigated, very large volumes <br /> 3 of water are imported to the fields around Tracy via the Delta-Mendota canal, and water <br /> pumped from deep agricultural wells is being discharged to shallow aquifers. This <br /> activity begins in the spring of each year and typically continues through early- to mid- <br /> September, when it stops and groundwater levels in shallow aquifers begin to fall. Except <br /> in unusually wet winters, levels usually continue to fall until some time in February or <br /> r March. Inspection of Table 1 shows that the rise and fall in the groundwater table <br /> elevation beneath the 7500 West Eleventh Street site usually occurs with little or no <br /> relationship to seasonal precipitation in the San Joaquin Valley where little rain falls <br /> between May and September of each year. <br /> The groundwater elevations presented in Table 1 were used to generate the groundwater <br /> contours shown on Figure 2. <br /> i` <br /> SJC <br />