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TABLE 4 <br /> AVERAGES OF EAST AND WEST PERCOLATION TEST RESULTS <br /> CORRESPONDING APPLICATION RATE AVERAGES <br /> 24 INCH DEEP PERC TEST BORING PYFRCOLATION RATE / INFILTRATION RATE <br /> PERCOLATION RATE/APPLICATION RATE <br /> 34.#min/inch / 0.544 gallons/ft'/day <br /> 36 INCH DEEP PERC TEST BORING 19.2/min/inch / 0.769 gallons/ft'/day <br /> PERCOLATION RATE/APPLICATION RATE ` / <br /> 42 INCH DEEP PERC TEST BORING 14.$ min/inch / 0.686 gallons/ft'/day <br /> PERCOLATION RATE/APPLICATION RATE / <br /> 60 INCH DEEP PERC TEST BORING PERCOLATION 81min/inch 1 0.908 gallons/ft'/day <br /> RATE/APPLICATION RATE J <br /> AVERAGE SOIL PROFILE PERC RATE: 24"-60" 19.2 min/inch / 0.727 gallons/ft'/day <br /> AVERAGE SOIL PROFILE APPLICATION RATE: 24"-60" <br /> D. GROUNDWATER INFORMATION <br /> NLS§.1. Groundwater depths and elevations throughout San Joaquin County are illustrated on <br /> maps pub 'shed by the County Flood Control and Water Conservation District. However, due to <br /> the hi egree of variability in groundwater elevations in the Tracy area, groundwater lines of <br /> equal depth and equal elevation are not drawn for this area. The last map denoting lines of equal <br /> elevation for the Tracy area was published in 1992, and show the general groundwater flow to be in <br /> a northeasterly direction, toward the San Joaquin River. This is regarded as the generalized <br /> groundwater directional flow,primarily based on highly accurate groundwater studies at the Tracy <br /> Defense Depot. <br /> SSSi 2. . The site has been under agricultural production for the last several decades,but has not <br /> farm or the last five years. This may explain why the soil nitrate-nitrogen and soil organic <br /> matter concentrations were comparatively low. <br /> NLS'2. 33. , SS 4.2. As noted in the Prim gpory the underlying water table has been <br /> impact with nitra almost 2x the MCL at 88 p Since there are no septic systems <br /> upgradient to the sample location, and the s is s ems nearby can be considered crossgradient, <br /> this nitrate source can almost assuredly be associated with agricultural inputs, such as nitrogen <br /> fertilizers, in addition to natural nitrate formation. Decomposition of crop residues has probably <br /> also contributed to nitrate production through mineralization and nitrification. <br /> NLS2. , SSS§L3,4.4 . There are no domestic or irrigation wells on the property. TgsL,j <br /> results r the nitrate concentration of the water table, as discussed above are found on Page 9 of / <br /> the Primary Report. The domestic well location for the Multipurpose Building, and subsequent <br /> Church development is unknown as of the date of this Report. Proper setbacks for a publi!:j ll <br /> must be followed. The well location should be installed to the south of the proposed fi <br /> area which would place the well upgradient to the disposal area. <br /> Page -7- <br /> Chesney Consulting <br />