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On site sources of nitrogen: <br /> Feed storage areas: <br /> The feed storage area has been paved with asphalt paving. There is no drain system at this point. The <br /> runoff simply collects at the low point to evaporate and percolate into the upper soil layers. 1 recommend <br /> that this area be tied into a future tail water system. <br /> Domestic septic systems: <br /> The human waste septic systems are considered to be insignificant. Reference soil suitability study <br /> submitted by Valley Ag Research. <br /> Corral runoff: <br /> Corral runoff at this time flows to evaporative areas. <br /> Agricultural liquid waste storage pond: <br /> This existing waste storage lagoon is approximately 30 feet deep. The soil boring and subsequent soil <br /> tests indicate that there has been lateral percolation of the manure water, but no movement downward <br /> towards the ground water. Moreover,the ground water depth in the area is approximately 80 feet below <br /> grade. In consideration of the soil type, rainfall and irrigation application rate,there is no threat to the <br /> ground water. <br /> Agricultural solids storage areas: <br /> There are several areas where manure from cattle lanes is being scraped to shallow collection lagoons. <br /> These areas have had no special preparations to prevent percolation into the upper layers of the soil. My <br /> evaluation is that there is no threat to the ground water from percolation. There may be a slight possibility <br /> that surface runoff from a heavy rainfall event could reach the areas' drainage system which will <br /> eventually reach the Lone Tree Creek. <br /> Impact to Underlying Groundwater/Impact to downgradient wells: <br /> In all considerations to the groundwater,the conclusion from the soil borings demonstrate that the <br /> soil profile has layers of clay that have prevented the downward movement of surface water. Moreover, the <br /> depth to static water table is beyond the penetration of surface water. The chemical analysis of the nitrate <br /> content of the soil profile from boring MDS-1 indicates that the nitrates have not penetrated beyond the <br /> 35' depth. <br /> Three water supply wells were sampled to determine the baseline nitrate concentration. Two of the <br /> wells were located on the property at the Manuel Da Silva residence and at the dairy. The third well <br /> sampled was the John Da Silva dairy well which is situated approximately one half mile southeast of the <br /> Manuel Da Silva dairy. This third well is upgradient from the two wells on the subject property. <br /> Water samples from these three wells were transferred under chain of custody to Geo Analytical <br /> Laboratories in Modesto. They were analyzed for nitrate, using EPA method 300, with a detection limit of <br /> 1.0 mg/liter. The results show that nitrate is present in all of the samples,ranging from a low of 18 <br /> mg/liter in the John Da Silva well to a high of 21 mg/Liter in the Manuel Da Silva residence well. <br /> Although the presence of nitrate in the ground water indicate that there may be some agricultural <br /> contribution contamination, all of these values are well below the maximum contaminant level for <br /> drinking water established for nitrate of 45 mg/Liter. Furthermore,the consistent level of nitrate in the <br /> ground water indicates that the nitrate in these waters is more a result of a regional infiltration into the <br /> water table,rather than contribution from the local source of the Manuel Da Silva dairy operation. <br /> It is concluded that the proposed dairy expansion will not impact the downgradient ground water. <br /> There is a possibility that there could be surface contamination of Lone Tree Creek via the site <br /> drainage system. The source would be from field, feed storage areas and or corral runoff. It is important <br /> that this facility have a construction program that prioritizes the timing of a drainage system at a time that <br /> will prevent such offsite runoff. <br /> 11 <br />