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r./ k'g KLEINFELDER <br /> PRESENT USE OF THE SITE <br /> At the time of our field exploration, the project site was an active cucumber field. <br /> Topographically, the site was essentially level. <br /> HISTORICAL GROUNDWATER DEPTH <br /> In accordance with groundwater reports published by the San Joaquin County Flood Control and <br /> Water Conservation District (Spring 1972 to Spring 1999), high groundwater in the project area <br /> has been recorded at depths in the range of about 90 to 100 feet below ground surface. <br /> FIELD EXPLORATIONS AND TESTING <br /> The subsurface conditions at the site were initially explored on September 12 and 13, 2001, by <br /> drilling eight borings to depths of about 16.5 to 25.8 feet below existing grade. At this time, two <br /> percolation tests were performed on the west side of the facility within the proposed leach field <br /> area. The borings were drilled using a Simco 2400 truck-mounted drill rig equipped with 4.5- <br /> inch O.D. solid-stem auger. Due to relocation of the proposed leach field area to the east side of <br /> the proposed facility, two additional percolation tests were performed on January 31, 2002, <br /> ranging from about 3.5 to 8 feet below existing site grade. The approximate percolation test <br /> locations are shown on the attached plate. <br /> Based on our findings, the subsurface soils encountered consisted predominately of stiff to hard, <br /> moderately-plastic silty to sandy clays to depths ranging from about 2.5 to 11 feet below site <br /> grade. These soils were underlain by loose to very-dense silty to clayey sands, stiff to hard silty <br /> to sandy clays, and very-stiff to hard sandy silts to the maximum depths explored. <br /> The percolation tests were performed in accordance with accepted guidelines using clear potable <br /> water. The procedure calls for first placing about 2 inches of fine gravel at the bottom of the <br /> bore hole, installing a perforated PVC casing, and then placing additional gravel. The holes were <br /> then pre-soaked with water at least 24 hours prior to performing the tests. The tests are <br /> performed by first adding about 6 inches of water above the gravel. From a fixed reference point, <br /> the drop in water level was measured in approximate 10-minute intervals, refilling as necessary <br /> to maintain the original head of water over the gravel. Under the observation of a sanitarian <br /> from the San Joaquin County Public Health Department, the last 10 minute reading of the <br /> monitoring period was recorded and used to calculate the percolation rate in minutes per inch <br /> and gallons per square foot per day(gfd). <br /> Test Number Approximate Depth, ft. Percolation Rate min./inch <br /> P-1 3.5 26.3 <br /> P-2 8 7.7 <br /> A soil percolation rate of 60 minutes per inch or faster is generally required within the upper 3.5 <br /> feet of subgrade for county approval. At deeper depths, a soil percolation rate of 30 minutes per <br /> inch or faster is required. Based on our findings, the upper soils yielded an acceptable <br /> percolation rate. The sandy soils encountered in our test borings beneath the near-surface soils <br /> 20-2080-19.GOI/2002R083 February 4,2002 <br /> ©2002 Kleinfelder,Inc. Page 2 of 4 <br />