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`. .� <br /> am (0 The EHD will make a determination on the feasibility of connecting the new milk barn effluent to <br /> this existing septic system. Sewer connections will be dependant upon the final elevations of the <br /> invert of the milk barn sewer outlet and the invert of the existing septic tank. This is in accordance <br /> with Item "H" in the Conditions of Approval from EHD. <br /> It is imperative that a 100%replacement area be set-aside for eventual repair. This replacement area <br /> may be used while the primary leachfield area"rests and rehabilitates." Effluent management can <br /> then be converted back to the primary field with this cycle continuing indefinitely. Sufficient <br /> replacement area exists to the south of the existing disposal area that serves the referenced mobile <br /> home. <br /> C. ON-SITE WELL WATER AND IRRIGATION WATER INFORMATION <br /> Currently, there are four wells at the de Snayer Dairy facility: 1.) The irrigation well at the west end <br /> of the freestall barns, 2.) A domestic well west of the existing office, 3.) Another domestic well near <br /> the shade corrals, and 4.) A new domestic well drilled in July 2001, that is west of the actual dairy <br /> facility. The only well log available for these wells was the Well Permit from EHD for the new well. <br /> A minimal lithology description on the Well Permit for the west well illustrates the underlying strata <br /> to consist predominately of clay from the surface to 125 below ground surface (bgs) and sand strata <br /> from 125 feet to 162 feet. The well has a grout seal to 100 feet consisting of 9 sack grout. <br /> The irrigation well and the domestic well near the shade corrals are scheduled for destruction when <br /> construction of the milk barn commences. Only the new west well and the north well will provide <br /> domestic water for the de Snayers', their employees, and water for the dairy cows. <br /> The EHD stipulated the domestic well west of the office and the new domestic well be tested for <br /> the agrichemical Dibromochloropropane (DBCP), Ethylenedibromide (EDB) and nitrate. <br /> However, several other constituents were also tested as noted on the Analysis Reports, to establish <br /> baseline concentrations. In addition, the domestic well serving the two single family residences at <br /> the Acampo Ranch was sampled from a sample port at the wellhead for several constituents. The <br /> irrigation well west of the freestalls was also sampled from the overhead for several constituents. <br /> The well water test results indicate that nitrate concentrations are a function of well screening <br /> depth. The new well is 140 feet deep. While the exact depths of the other tested wells are <br /> unknown, they are known to be less than 140 feet deep. Consequently,the shallower wells have <br /> higher nitrate concentrations, with the North well and the Acampo well exceeding the Maximum <br /> Contaminant Level (MCL) for nitrate. The de Snayer employees who use water from these two <br /> _ wells are supplied with bottled water for drinking and cooking purposes. <br /> Both DBCP and EDB were Below Detection Limit (BDL), which is equivalent to non-detect(ND) <br /> _ in the West well,North well and the Acampo Ranch well. Given that the acreage surrounding <br /> these wells have been planted in vineyards for a number of decades, detecting these two <br /> agrichemicals in the groundwater was a possibility. A summary of the water analysis test results <br /> are as follows: <br /> -16 �jj <br /> - <br /> Chemq Consuhing <br />