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This permit indicates that sumps were installed and there apparently have beery no epairs to this � <br /> system. wo other permits were found in the microfiche files in the one-half' e proximity to the <br /> subject el. This can be considered a low number of repairs in the study area. <br /> (§ 5.1 and 6.0) SOIL PROFILE AND PERCOLATION TESTING <br /> (§ 5.4) As noted on the USDA Soil Survey map, the on-site soils consist of Madera sandy am, <br /> #193. Typically, this soil type is moderately well-drained, with a moderately deep an. This <br /> hardpan stratum was encountered during the shallow perc test boring, as indicated by the shallow <br /> perc test results. Madera sandy loam has rapid permeability at depths below the encountered <br /> hardpan stratum, as illustrated by the deep perc test results. <br /> (§ 5.4) The subject property is in an area designated asIardp "by EHD's map denoting the <br /> various soil types and septic system requirements throu Joaquin County. Consequently, <br /> only leachlines and seepage pits are allowed to be installed in this area of the County. However, as <br /> referenced above, sumps have been installed in this area. This will be further discussed in the <br /> Conclusions Section 7.0. <br /> (§ 5.2, 5.3, and 5.4) A Log of Boring using the Unified Soil Classification System (USCS), as <br /> observed from the 23 ft exploratory/deep perc test boring is found in Appendix B. Generally, the <br /> soils show a clayey, silty soil on the space to five ft, then a consistent silty sandy soil under the <br /> referenced hardpan strata down to 23 ft.)At 23 ff, a poorly graded fine silty sand was encountered, <br /> where the boring was terminated'fer--the percolation test. <br /> (§ 6.1) Percolation testing was conducted in the proposed location of the leachfield, as determine <br /> on the Site Schematic. The perc test locations were approximately 60 ft from the west property <br /> line and 275 ft from the Tiffani Lane centerline, and 125 feet north of the existing domestic well, <br /> as all illustrated on the Site Schematic found in Appendix B. <br /> Q 6.2, 6.3 and 6.5) On April 18, 2007, 1245 hrs-,—onehallow perc test boring of 42 inches and <br /> one eep perc test boring of 23 ft (276 inches) were�dnlled with a truck mounted drill rig. The <br /> walls of the shallow boring were scored with a pry-bar and the loose material removed. Two <br /> inches of fine gravel was placed at the bottom and three-inch perforated PVC pipe was inserted in <br /> each test boring. The borings were then pre-saturated after drilling at 1400 hrs. with approximately <br /> 12 inches of water. <br /> (§ 6.4) On April 19, 2007, at 0800 hrs, percolation testing commenced. There w.As no sit ing water <br /> in either boring after the 24-hour soak period, as illustrated in Table 1 below. Co ently, EHD <br /> Perc Test Procedure#2 was conducted for both tests. The last half hour of the four-hour test was <br /> witnessed by Ted Tasiopoulos, R.E.H.S. of the San Joaquin County Environmental Health <br /> Department. Perc test results reveal a failing rate of 83.3 minutes/inch (min/in) for the shallow test, <br /> and a rate of 4.5 min/in for the deep perc test. The maximum acceptable perc rate is 60 min/in for <br /> shallow tests and 30 min/in for deep tests. <br /> (§ 5.4 and 6.8) The following Table illustrates the existing acreage, post soak period status and <br /> perc test results for the respective perc test depth: <br /> Page -2- <br /> Chesney Consulting <br />