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3-10 <br />recognized that the area's heavy reliance on groundwater associated with significant <br />population growth and agricultural needs, has resulted in the basin being overdrafted for at <br />least the past 40 years, and water levels have continued to decrease throughout the region. <br />3.7.2 Local Aquifers <br />The uppermost groundwater beneath the Forward Landfill occurs in the unconfined Victor <br />Formation. Historical groundwater measurements in monitoring wells at the Forward Landfill <br />indicate that groundwater occurs at a depth of approximately 50 to 70 feet below the ground <br />surface with seasonal variations in the groundwater depth of as much as 10 feet; the highest <br />groundwater elevations are observed during the winter/spring and lowest levels in the <br />summer/fall. Groundwater elevations typically range from about -10 feet relative to mean sea <br />level on the southern (Forward Unit) portion of the landfill and about -25 feet relative to MSL <br />on the northern (Austin Road Unit) portion of the landfill. Data acquired by GLA between 2003 <br />and 2009 indicates that, with rare exceptions, the groundwater flows in a north to <br />northeasterly direction at a gradient between 0.001 and 0.003 ft/ft. Although a broad range <br />of hydraulic conductivity values have been assigned to the formational materials (e.g., clay, silt <br />and sand) within the Victor Formation, slug tests performed in four wells at Forward Landfill <br />resulted in hydraulic conductivity values of 2E-02 to 2E-03 cm/sec for the uppermost aquifer <br />beneath the landfill. Based on the maximum hydraulic conductivity of 2E-02 cm/sec, a <br />hydraulic gradient of 0.003, and an estimated effective porosity of 0.2, the maximum <br />groundwater velocity beneath the Forward Landfill is estimated to be approximately 0.85 feet <br />per day. <br />3.7.3 Local Wells <br />Water supply (non -potable) to the landfill is provided by three on-site wells. The water is used <br />for dust control, compaction, and irrigation. One well, located near the main entrance facility <br />was drilled to a depth of approximately 135 feet and groundwater occurs at a depth of <br />approximately 70 feet. The well was likely installed before the opening of the landfill, having <br />been previously used for agricultural purposes. It is pumped at a rate of approximately 1500 <br />gallons per minute (gpm) at a maximum frequency of approximately 27 times in a 12 -hour day. <br />Another well is located south of the South Branch of Littlejohn's Creek and has a capacity of <br />500 gpm. The third well is located along the northern boundary of the former Austin Road <br />Landfill. This well was installed in 1972 and has a production of approximately 60 gpm. The <br />fact that groundwater flow near the existing Forward Landfill is not modified by pumping from <br />this well suggests that it is screened in a confined unit below the uppermost groundwater units <br />that are monitored at the site. <br />The sedimentary formations underlying the Victor formation have many productive confined <br />aquifers. In order to develop adequate flow, most of the agricultural irrigation wells in the area <br />are at least 500 feet. The unconfined aquifers are recharged by rainfall and local stream <br />Forward Landfill SWT Engineering <br />Joint Technical Document - April 2014 <br />z:\projects\allied waste\forward\five year permit rvw 2013\jtd-5 yr pr 2013\text\sec 3_final.doc <br />