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permeable to a maximum depth of exploration of 42 inches. The soil type allows for infiltration <br /> of water through the top soils. The infiltration rate will limit the natural treatment of the sites soils <br /> as they drain from the surface layers. <br /> The soil survey by US Department of Agriculture (USDA) indicates that the site is composed of <br /> Bruella Sandy Loam soil. The Bruella Sandy Loam is composed of 0-8 inches of loamy sand at <br /> the top layer, then a layer of sandy clay loam 0-60 inches deep. The site is mainly composed of <br /> sandy material. <br /> 4.0 GROUNDWATER ANALYSIS <br /> 4.1 Description of the depth to groundwater, seasonal fluctuations of groundwater depth, <br /> directional flow and gradient: Description of depth to groundwater, seasonal fluctuations of <br /> groundwater,directional flow and gradient are referred to in Section 4 of the Soil Suitability Report <br /> prepared by Dillon& Murphy that is attached in the Appendix. <br /> 4.2 Description/discussion of any existing and/or potential groundwater <br /> contamination issues in the general location of the site: Description of existing or potential <br /> groundwater contamination issues in the general location of the site are referred to in Section 4.2 <br /> of the Soil Suitability Report prepared by Dillon& Murphy (See Appendix). <br /> 4.3 Description of the current use of groundwater at the site and of the future expected use <br /> of groundwater as related to the proposed development project: <br /> Based on the most recent results from San Joaquin County's "Flood Control and Water <br /> Conservation District" report on groundwater from Fall of 2017, the estimated depth to <br /> groundwater was determined to be 100 feet below the surface.This was verified with the California <br /> Department of Water Resource's Water Data Library. The results of the historic depth to ground <br /> water show that the relative depth has not changed drastically throughout the years. It fluctuates <br /> minimally on a yearly basis. The proposed improvements will not have a negative effect on the <br /> current depth to ground water as the proposed usage is less than that of agriculture. See appendix <br /> for the site's depth groundwater tables and diagrams. <br /> 5.0 SOURCES AND CALCULATED IMPACT OF NITRATE TO <br /> GROUNDWATER <br /> 5.1 Description of all current off-site sources of nitrate to soil and groundwater in the general <br /> up gradient area and the contribution of nitrate load from these sources to the project <br /> site: Current off-site source of nitrate to soil and groundwater in the general up gradient <br /> area and the contribution of nitrate loads are agriculture and neighboring sites with septic <br /> systems with minimal to no current impact to the site. The site does have an existing house <br /> and a wine tasting room which were accounted for when determining the capacity for the <br /> proposed improvements. The adjacent site does not pose a significant impact as the nitrate <br /> concentration can be dispersed through the neighboring site that is approximately 79 acres. <br /> The existing site contains a nitrate loading concentration of only 2.8 mg/L-N with the <br /> winery and adjacent facilities being established for more than 10 years, confirming the site <br /> does have capacity for the proposed improvements. <br /> 4 <br />