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i` L , <br /> i <br /> (§ 4.0) LOCAL GROUNDWATER AND SURFACE WATER INFORMATION <br /> 4.1 The 1999 Lines o Equal Depth Ma published b the San Joaquin Count Flood Control <br /> � {§ ) ,f q P p p Y q Y <br /> illustrates the groundwater depth to be 122 feet below ground surface (b.g.s.). The 1999 Lines of <br /> Equal Elevation Map illustrates the groundwater elevation and the directional flow to be in a west, <br /> southwesterly direction. <br /> Unfortunately, no Well Driller's Log exists for the on-site domestic well. Consequently, <br /> underground lithology specific to the subject property cannot be discerned. The property is not <br /> subject to 100-year flooding. Therefore, it is highly unlikely there would be surfacing of effluent <br /> from inundated conditions. Surface water will be managed by on-site retention basins. <br /> (§ 4.3,4.4 and 4.5) A water sample was obtained from a hose bibb next to the pressure tank of the <br /> Welch's domestic well after the well was allowed to cycle three times to ensure the sampling of <br /> aquifer formation water. (§ 4.6) The sample was placed in a cooled ice chest and transported <br /> under the attached Chain of Custody to A&L Labs in Modesto, California to be analyzed for <br /> f <br /> nitrate and DBCPIEDB. <br /> Water analysis reveals a low nitrate concentration of 9 ppm. The Maximum Contaminant Level <br /> (MCL) for NO, in drinking water is 45 ppm. This 9 ppm concentration may be considered a <br /> background concentration that has accumulated over eons and can be attributed to the deep <br /> groundwater, high clay content intervening strata, very low septic system density and no intense <br /> (fertilized) agriculture surrounding the property(until recently). <br /> i <br /> (§ 7.0) CONCLUSIONS <br /> The perc test results for proposed Parcels 1, 2, 3 and 4 show acceptable percolation for the <br /> management of septic system effluent flows. For Parcels 1 and 2, effluent management will occur <br /> at the deeper depths representative of sumps, and not necessarily under the leachlines. For Parcels 3 <br /> and 4, effluent management will mostly occur at the shallow leachline depths and only marginally in <br /> k the deeper sump depths. Although the deep perc tests for Parcels 3 and 4 were run at simulated <br /> sump depths due to the encountered material which was the most favorable material at the highest <br /> elevations, seepage pits should be installed on these two Parcels. Seepage pits will give the highest <br /> capacity(volume) for effluent management. <br /> As noted for the shallow tests on Parcels 1 and 2, there will be some effluent percolation at <br /> leachline depth, but if the soil becomes saturated, percolation will cease and the sumps will manage <br /> effluent flows. <br /> A new law that is to be implemented may restrict the installation of seepage pits (Assembly Bill <br /> 885). Before this law is implemented, EHD may require the installation of seepage pits on Parcels <br /> 1 (for a second unit dwelling), 2, 3 and 4 of this project for a number of reasons: 1.) They are the typical <br /> and principle effluent management structure installed in this area, 2.) There is a significant distance <br /> of approximately 100 feet between the bottom of a seepage pit at 25 feet b.g.s. and the current <br /> groundwater depth of 122 feet, 3.) Seepage pits allow head pressure buildup to force effluent into <br /> Page -4- <br /> Chesney Consulting <br /> I <br />