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The soil in the boring was similar to, but sandier than, that described by the Soil Survey. <br /> Sandy clay with roadbase was encountered to approximately 0.5 feet below ground <br /> surface, followed by clay to 2.5 feet below ground surface, followed by sandy clay to 3.3 <br /> feet, followed by medium to coarse sand with clay to the full depth of the hole. The soil <br /> log is presented on Plate 14. <br /> Discussion of Soil Litho/ogy <br /> Based on the soil observed in the boring, there appears to be moderate potential for <br /> percolation in the shallow soil zone. Sandy soils generally have a much greater <br /> potential for percolation than fine-grained or cemented soils. However, a percolation <br /> test is the only accepted method for determining the suitability of the soils for a septic <br /> disposal area. Percolation test results are discussed in the following section. <br /> Percolation Test <br /> A shallow percolation test was conducted in the proposed septic disposal area of the <br /> Site. The soil boring discussed above was used for the percolation test hole. <br /> Percolation test procedures conformed to San Joaquin County Environmental Health <br /> Department policy. <br /> Preparation and Presaturation of Percolation Test Holes <br /> After the boring was advanced by hand auger and the soil logged, the test hole was <br /> completed for the percolation testing. Approximately two inches of pea gravel were <br /> placed in the bottom of the open soil boring, followed by a 2.0-inch diameter PVC pipe <br /> with perforations on the bottom. Pea gravel was then used to backfill a few inches of <br /> the annular space. <br /> Live Oak presaturated the percolation test hole approximately 24 hours prior to the <br /> percolation testing. 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 hole was found to <br /> be intact and dry. <br /> Percolation Test Procedure <br /> Live Oak conducted the percolation test for the boring on June 23, 2020. Due to initial <br /> percolation rates observed, a one-hour test was selected. Water level measurements <br /> were taken every 10 minutes during the one-hour period. The last 30 minutes of the <br /> test were observed by Sukhreet Kaur, Registered Environmental Health Specialist at <br /> the San Joaquin County Environmental Health Department. <br /> An electronic well sounder with a depth accuracy of 1/100th 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 /> LOGE 20-24 Page 7 <br />