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The soil in the boring was within the range of what would be anticipated based on the <br /> Soil Survey data reviewed. Sandy silt was encountered to approximately 2.5 feet below <br /> ground surface, followed by silty sand with clay to the full depth of the boring. The log <br /> for the soil boring is presented in Plate 10. <br /> Discussion of Soil Lithology <br /> Based on the soils observed in the boring, there appears to be moderate potential for <br /> percolation. Sandy soils generally have a much greater potential for percolation than <br /> fine-grained or cemented soils. However, a percolation test is the only accepted <br /> method for determining the suitability of the soils for a septic disposal area. Percolation <br /> test results are discussed in the following section. <br /> One shallow percolation test was conducted on thete; the stlallow soil boring <br /> discussed above was used for the percolation test htile (Plate 2). I Percolation test <br /> procedures conformed to San Joaquin County Environmental Health Department policy. <br /> Preparation and Presaturation of Percolation Test Holes <br /> After the boring was advanced by hand auger and the soils logged, the test hole was <br /> completed for the percolation test. Approximately 2 inches of pea gravel were placed in <br /> the bottom of the open soil boring, followed by a 1.5-inch diameter PVC pipe with <br /> perforations on the bottom. Pea gravel was then used to backfill a few inches of the <br /> annular space. <br /> Live Oak presaturated the percolation test hole approximately 24 hours prior to the <br /> percolation test. The hole was filled with water to a height of 12 inches above the <br /> bottom of the boring for the presaturation. On the day of testing, the percolation test <br /> hole was found to be intact and dry. <br /> Percolation Test Procedure <br /> Live Oak conducted the percolation test for the boring on August 31, 2011. Due to soil <br /> conditions present, a four-hour test was selected. Water Level measurements were <br /> taken every half hour during this four-hour period. Ted Tasiopoulos, Senior Registered <br /> Environmental Health Specialist at the San Joaquin County Environmental Health l <br /> Department, observed the last half hour of the test. <br /> An electronic well sounder with a depth accuracy of 1/100`h foot was utilized for the <br /> water level measurements. The water level was measured against a fixed reference <br /> point on the well casing. Measurements were recorded on the data sheet in decimal <br /> feet. When necessary after measuring the water level, the hole was refilled with water <br /> to a level of six inches or more above the bottom of the hole. <br /> LOGE 1123 Page 5 <br />