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4. ENVIRONMENTAL ANALYSIS <br /> 4.8 HYDROLOGY AND WATER QUALITY <br /> ` exceeds estimated annual safe yield by approximately 200,000 acre-feet(AF). Exceedence of the <br /> safe annual yield can lead to overdraft of a groundwater basin. All of the sub-basins within the <br /> San Joaquin River Region have experienced some overdraft(DWR, 1994). <br /> The network of water supply aqueducts in the Central Valley is sufficient to provide for over one- <br /> half of the water needed for irrigation in years of average or above-average rainfall. In dry years <br /> .. when rainfall is below normal,reliance on ground-water supplies is greater. During times of <br /> severe drought, groundwater could be removed from the regional aquifers in excess of recharge, <br /> as they were during the 1976-77 drought(USGS,2003). Although gains have been achieved by <br /> importing surface water from areas of surplus,projected water needs in the San Joaquin Valley <br /> may require tem�orar withdrawal of Around water ins=e �:::�lxirecirlte future <br /> The DWR estimates that by 2010, demand for water in the San Joaquin Valley,exclusive of the <br /> Tulare Basin, would be 8 percent greater than the groundwater demand in 1980. Without <br /> increased surface-water imports,the San Joaquin Valley might require groundwater withdrawals <br /> ` of 150,000 AF per year in excess of recharge to meet agricultural demand until at least 2010. <br /> Those estimates probably underestimate additional increased demand that would result from <br /> sustained drought periods. Occasional large withdrawals from an aquifer are a viable solution to <br /> the problem of reduced surface-water supplies in dry periods,provided the aquifer is replenished <br /> during wet years. However, continual withdrawal of ground water in excess of recharge can <br /> ` increase the cost of pumping,reduce water availability,and, in certain hydrogeologic settings, <br /> can lead to overdraft and possibly cause land subsidence(USGS,2003). <br /> ` A detailed groundwater budget is not available for the Tracy or Delta-Mendota Sub-basin. <br /> However, groundwater demand for the Delta-Mendota Sub-basin is estimated by the DWR based <br /> on land and water use. DWR estimates for the Delta-Mendota Sub-basin considered overall <br /> applied water demands, agricultural groundwater pumping,urban pumping demand,and other <br /> extraction data. Natural recharge to the groundwater aquifers is estimated at 8,000 AF, and <br /> applied water recharge is approximately 74,000 AF. Annual urban and agricultural groundwater <br /> extraction is approximately 17,000 AF and 491,000 AF,respectively. Overall, the difference <br /> between aquifer recharge and rates of extraction from that aquifer results in a net negative water <br /> budget of 440,000 acre feet per year within the Tracy-Mendota Sub-basin(DWR, 2003a). <br /> Well Characteristics and Well Yields <br /> ++ The total depth of municipal and irrigation wells range from 60 feet to 1,020 feet and the average <br /> depth is 352 feet. Total depths of domestic wells range between 44 feet and 665 feet and average <br /> depth is 188 feet. Well yields and specific capacities for the domestic wells in the Tracy Sub- <br /> basin are not available. Well yields for Delta-Mendota Sub basin municipal and irrigation wells <br /> range from 20-to 5,000-gpm and average 800- to 2,000-gpm. Total depths for these wells range <br /> from 50 feet to 800 feet with an average depth of 400 feet to 600 feet. <br /> RMC Pacific Vernalis Quany Mining and Reda don Project 4.8-15 ESA/203015 <br /> Admin mdve Draft Eai Math 2004 <br />