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• The soil in the borings was similar to that described by the Soil Survey. At location P1, <br /> silty, fine to medium sand was encountered to a depth of 2.5 feet, followed by sandy silt. <br /> At location P2, fine to medium sand with silt was encountered for the full depth of the <br /> hole. The soil logs are presented on Plates 10 and 11. <br /> Discussion of Soil Lithology <br /> Based on the soil observed in the borings, there appears to be good potential for <br /> percolation at the test locations. Sandy soils generally have a much greater potential <br /> for percolation than fine-grained or cemented soils. However, a percolation test is the <br /> only accepted method for determining the suitability of the soils for a septic disposal <br /> area. Percolation test results are discussed in the following section. <br /> Percolation Test <br /> A shallow percolation test was conducted on each proposed parcel of the Site. The soil <br /> borings discussed above were used for the percolation test holes (Plate 9). Percolation <br /> test procedures conformed to San Joaquin County Environmental Health Department <br /> policy. <br /> Preparation and Presaturation of Percolation Test Holes <br /> • After the borings were advanced by hand auger and the soils logged, the test holes <br /> were completed for the percolation tests. Approximately one inch of pea gravel was <br /> placed in the bottom of each 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 holes approximately 24 hours prior to the <br /> percolation testing. Each 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 holes were found <br /> to be intact and dry. <br /> Percolation Test Procedure <br /> Live Oak conducted the percolation tests for the borings on July 14, 2017. Due to rapid <br /> percolation rates observed, one-hour tests were selected. Water level measurements <br /> were taken every 10 minutes during this one-hour period. The tests were observed by <br /> Ted Tasiopoulos, Senior Registered Environmental Health Specialist at the San Joaquin <br /> 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 /> feet. When necessary after measuring the water level, the holes were refilled with water <br /> • to a level of six inches or more above the bottom of the hole. <br /> LOGE 1718 Page 6 <br />