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Treated Nater Disposal <br /> Typical methods of treated water disposal include recharging the <br /> groundwater to the aquifer, discharge to a sanitary sewer system or <br /> discharge to a surface drainage system. No sanitary sewer system is <br /> presently in place at the Sebastiani Vineyards/Woodbridge cellars site. <br /> Conveyance distances to the nearest surface drainege system are considered <br /> prohibitive and may require lengthy negotiations to obtain construction <br /> access and rights-of-way. <br /> Groundwater recharge has been selected as the treated water disposal <br /> method for this remedial action plan. Two alternatives for recharge are <br /> considered feasible for reintroduction of treated water to the local <br /> groundwater system. The primary approach to recharge will be a <br /> groundwater infiltration, gallery. Discussion of a contingency recharge <br /> option, groundwater recharge wells, is included for consideration in this <br /> remedial action plan. <br /> Infiltration Gallery <br /> A treated groundwater infiltration gallery is considered the most <br /> r, appropriate method for shallow groundwater recharge at this site. As <br /> shown on Figure 9, the infiltration gallery would be located approximately <br /> 75 feet northeast of the proposed soil and groundwater treatment facility. <br /> The infiltration trench would be located in an area which will be <br /> minimally affected by the proposed Sebastiani facility expansion. <br /> Groundwater recharge at this location would have no potential adverse <br /> effects on the groundwater controls established by the downgradient <br /> groundwater extraction system. <br /> As shown on Figure 11, the infiltration gallery would consist of a trench <br /> approximately 12 inches wide. Ideally, the trench would extend <br /> approximately 5 feet into the silty sand unit which is commonly <br /> encountered at about 16 to 18 feet below ground surface at the site. <br /> �. However, total depth of the trench may be limited due to soil stability. <br /> The length of the gallery trench has been determined based upon the <br /> projected infiltration capacity of the silty sand unit and the projected <br /> flow rate of treatment plant effluent. A plant effluent of 8 gpm was used <br /> to determine the proposed trench length. At 8 gpm (1.1,500 gallons per <br /> day) the trench would need to be approximately 12 feet long, However, a <br /> safety factor of 1.5 was used in designing the length of the infiltration <br /> gallery trench, resulting in an 18-foot long trench. <br /> The infiltration gallery trench would be backfilled from its total depth <br /> to approximately 18 inches below existing grade with clean, washed, <br /> rounded, 1/4- x 1/8-inch stream gravel, free of fine-grained sediments and <br /> 22 <br />