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C) 1 + <br /> The Banta area has always had a significantly higher number of repair permits due to the clayey soil <br /> and shallow groundwater, and may also be due to inadequate systems originally installed, in addition <br /> to the age of the systems. <br /> The project site has level terrain; conse uentl there will be no need to incorporate design <br /> p J � q Y� <br /> rP <br /> considerations for slopes within a disposal area. Under EHD requirements and regulations, a mound <br /> system for effluent disposal can be required in this locale due to the clayey soils and more <br /> particularly, the high groundwater table. Mound systems are sensitive to sloping, and changes in <br /> design must be taken into consideration when natural ground sloping is present. However, based <br /> upon the findings of these Studies, particularly with respect to depth to groundwater and the <br /> theoretical rise in the water table, a mound system may not be required. A filter bed system and <br /> disposal parameters will be discussed in a design report for any future project on this property. <br /> B. SOIL PHYSICAL CHARACTERISTICS AND ANALYTICAL TEST RESULTS <br /> The United States Department of Agriculture - Soil Conservation Service (USDA-SCS) indicates the <br /> property soils are on the edge between Stomar clay loam (#252) and Willows clay(#274). The Soil <br /> Survey of San Joaquin County states that permeability is slow and very slow in these two soils, <br /> although this was not observed in the percolation tests conducted. <br /> SSS§ 5.2.The surface and subsurface soil investigation and testing began on May 16, 2007 with <br /> hand drilling a 24-inch and 40-inch percolation test boring in the extreme north corner of the <br /> property. This test location was chosen for two reasons: First, a required distance of 100 ft had to be <br /> maintained between the test locations and the on-site well, and the two wells on adjoining properties. <br /> Secondly, it is probable that a wastewater disposal area for any future commercial development of <br /> the property would take place in the"back"of the property, near this north corner. The test locations <br /> are denoted on the San Joaquin County Site maps found in Appendix A. Soil cutting samples from <br /> the bottom of these two borings were retrieved for physical and chemical analysis. <br /> On May 24, 2007, a backhoe became available from Santos Backhoe Service to sample soil at deeper <br /> depths. Samples from 72 inches and 92 inches in depth were retrieved. At the 17-inch depth, very <br /> moist soil conditions were encountered which was representative of the capillary fringe. At e 92- <br /> inch depth, saturated soils conditions were encountered and groundw er seeped into the test�it. <br /> After one hour, the depth to standing water within the test pit was17.2 feet below the ground sur ace, <br /> then a water table sample was retrieved with a stainless steel bailer--T e test pit was then <br /> subsequently closed-in. <br /> NLS§ 1.1, 1.2. As the noted on the A&L Laboratory Soil Analysis Reports, chemical analyses of the <br /> four soil samples quantify several constituents that influence nitrate loading from this project. The <br /> important parameters for nitrate loading assessment are the organic matter, pH, cation exchange <br /> capacity(CEC), clay content percentage, along with nitrate-nitrogen content of the soil. <br /> As noted, the organic matter in the surface soils is actually lower than in the deeper soil samples. <br /> The nitrate-nitrogen concentrations are again low at 4 ppm and 3 ppm at the 24" and 40" depths,but <br /> increases to 6 ppm at both the 72" and 92" depths. <br /> t <br /> 3 <br /> Chesney Consulting <br />