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seasonal fluctuation. In the early 2000s, seasonally high groundwater levels in deep zone wells South <br /> i Tracy#1, Brown's#1,and Brown's New Well declined by up to about 60 feet and, although substantial <br /> ` recovery occurred in recent years,seasonally high water levels are currently lower than during the 1990's. <br /> These lower groundwater levels are likely due to an increased demand(pumpage)on the deep aquifer <br /> zone from local agricultural interests and industrial operators. For example, a number of deep wells are <br /> reported to have been installed in the area south and east of the Teichert Vernalis plant(Liese Schadt <br /> personal communication with P. Mercurio, Teichert, October 2002),and increased aggregate production <br /> in the early 2000s resulted in increased groundwater production. Further, reduced usage of local surface <br /> k water supplies by local interests, which may have caused a corresponding increase in local groundwater <br /> v pumpage, has been reported(Liese Schadt personal communication with J. Muller, Teichert, October <br /> 2002). <br /> LWater levels in the South Tracy#I production well typically recovered to an elevation between 20 and 40 <br /> feet(mst)each winter until 2001, when increased pump operation made the measurement of static water <br /> levels difficult. Upon Teichert's initiative, plant staff measured static and pumping water levels in the <br /> South Tracy#1 well more frequently from late 2001 to 2008,and these supplemental data are tabulated in <br /> Attachment 2. Water levels in the South Tracy#3 production well were also monitored at a higher <br /> frequency. However, the sounding of water levels below a depth of approximately 273 feet has not been <br /> successful due to an obstruction at this depth; likely due to a problem with the well's access port. As a <br /> 6. result, any water levels below a depth of approximately 273 feet(i.e., -28 feet, msl)erroneously appear as <br /> a constant water level on this well's hydrograph(see Figure 6 and the well's hydrograph in Attachment <br /> 1). <br /> The Petz irrigation well, which is located west of the Teichert Vernalis plant, is completed in both the <br /> shallow and deep zones of the underlying aquifer system, and its water level hydrograph reflects a <br /> composite of these shallow and deep zones(see Attachment 1). The early water level record of this well <br /> (prior to 2000)shows groundwater level elevations between those observed in the discussed shallow and <br /> deep wells in the area. Similarly, seasonal fluctuations prior to 2000 appear to be a composite of <br /> observations made in the shallow and deep network wells. Specifically, seasonally high water levels in <br /> this well rose from 72.46 to 86.58 feet(msl)between March 1994 and 1998,with seasonal fluctuations of <br /> almost 15 feet. Since then, water levels have been very similar to those observed in the shallow network <br /> ` wells. <br /> LContours of equal groundwater elevations prepared with data from the shallow network wells show that <br /> the general direction of groundwater flow during times of seasonally high water levels was typically to <br /> Lthe east-southeast and east. This includes the first monitoring event in spring 1994 with comparatively <br /> high water levels(Figure 7)and the period of the highest historically recorded groundwater elevations in <br /> spring 1998 (Figure 8). The water level elevations in spring 2000 were relatively low compared to <br /> groundwater conditions observed in previous spring seasons, however,the predominant direction of flow <br /> was also to the east-southeast(Figure 9). In spring 2002, overall groundwater elevations were very <br /> similar to the spring 2000 elevations, but the groundwater flow direction was east-northeasterly as <br /> tinfluenced by a relatively high groundwater level in the Koster irrigation well(Figure 10). <br /> y <br /> Seasonal groundwater level fluctuations have been small in recent years and overall groundwater <br /> ` elevation differences across the monitored area have decreased(see Figure 5). This is exhibited by <br /> F contours of equal groundwater elevation prepared for February 2012 (Figure 11)and November 2012 <br /> (Figure 12). During these periods, a southeasterly direction of groundwater flow is indicated. The recent <br /> contours(including 2009-2012)represent conditions of the lowest water levels on record to date. <br /> L <br /> L ©LLA­VIJPF S SCALMA INF <br /> CONSULTING ENGINEERS 5 <br /> L <br />