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by gravel with silty sand to a depth of 16 feet, followed by sand to the full depth of the <br /> boring. The logs for the soil borings are presented in Plates 11 and 12. <br /> Discussion of Soil Lithology <br /> Based on the soil observed in the borings, there appears to be poor potential for <br /> percolation in the shallow soil zones but good potential for percolation in the deep soil <br /> zones at the test locations. Sandy soils generally have a much greater potential for <br /> percolation than fine-grained or cemented soils. However, a percolation test is the only <br /> accepted method for determining the suitability of the soils for a septic disposal area. <br /> Percolation test results are discussed in the following section. <br /> Percolation Test <br /> Shallow and deep percolation tests were conducted on both proposed parcels of the <br /> Site. The soil borings discussed above were used for the percolation test holes (Plate <br /> 10). Percolation test procedures conformed to San Joaquin County Environmental <br /> Health Department 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 1.5-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 tests. 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, both deep holes were <br /> found to be intact and dry; the shallow holes were intact, but standing water was <br /> present. <br /> Percolation Test Procedure <br /> Live Oak conducted the percolation tests for the borings on July 10, 2014. Due to soil <br /> conditions observed, four-hour tests were selected. Water level measurements were <br /> taken every 30 minutes during this four-hour period. The tests were observed by Ted <br /> 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 hole was refilled with water <br /> to a level of six inches or more above the bottom of the hole. <br /> LOGE 1415 Page 6 <br />