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Kellogg Garden Products ECOLOGIC Engineering <br /> Groundwater Monitoring Well Installation Work Plan KELG04-001 <br /> 11/10/2004 <br /> locations were chosen to provide one up-gradient and two down-gradient monitoring points,based on inferred <br /> regional groundwater flow(to the southwest) from the Contact Water Pond(Figure 2).Monitoring well MW-4 <br /> will remain and provide a cross-gradient monitoring point from the Contact Water Pond. Table 1 summarizes <br /> the proposed actions and well locations with respect to the Contact Water Pond and the regional groundwater <br /> flow regime. <br /> Table 1: Proposed Well Re lacement Actions <br /> Monitoring Well Action Groundwater Well Location <br /> Monitoring (with respect to <br /> Contact Water Pond <br /> MW-1 Conversion to Piezometer P-I GW Elevation Only Down-Gradient <br /> MW-2 Conversion to Piezometer P-2 GW Elevation Only Down-to Cross- <br /> Gradient <br /> MW-3 Conversion to Piezometer P-3 GW Elevation Only Down-to Cross- <br /> Gradient <br /> MW-IR Proposed Replacement Well MRP Parameters Down-Gradient <br /> MW-2R Proposed Replacement Well MRP Parameters Down-Gradient <br /> MW-3R Proposed Replacement Well MRP Parameters Up-Gradient <br /> MW-4 Existing Well MRP Parameters Cross-Gradient <br /> Hydrological Well Design <br /> In order to provide monitoring of the uppermost saturated zone and maximize water yield for required <br /> laboratory analysis, the monitoring wells should be constructed with the top of the screen about 10 feet below <br /> the top of the water table when drilled in the winter of 2005. In order to achieve maximum well utility, the <br /> water level in each borehole will have to be closely measured during drilling and before the final well design is <br /> chosen. If the wells are drilled at some other time than in the winter, consideration must be given to the <br /> seasonal fluctuations at the time of drilling, <br /> The monitoring wells will be designed and installed according to the California Well Standards and installed <br /> according to the permit conditions of the San Joaquin County Environmental Health Division with the <br /> following details: <br /> Borehole Diameter — Nominal 8 inches; allows a nominal annular space of 3 inches surrounding the well <br /> casing and screen. <br /> Borehole Depth — Estimated to be approximately 130 feet bgs based on site depth to groundwater <br /> measurements and available borehole logs. Well depth should allow for normal seasonal fluctuations <br /> which generally are on the order of approximately+/- 10 feet. <br /> Casing Diameter—Nominal 2 inches. <br /> Casing Materials—ASTM F480 Schedule 40 PVC. Top of casing shall be approximately two feet above the <br /> land surface. <br /> Well Screen—Factory slotted ASTM F480 Schedule 40 PVC. Approximately 15 linear feet of well screen will <br /> be placed 10 feet below the level at which water is first encountered during the spring. <br /> Filter Pack— The wells are proposed using 10-20 mesh Colorado Silica Sand, or equivalent. The proposed <br /> monitoring wells are intended for sensitive water quality determinations, therefore all filter pack <br /> material shall be handled to avoid contact with contaminants as discussed in Section 11 of the <br /> California Well Standards. The filter pack will be extended two-feet above the top of the screen. <br /> Slot Aperture Width—Well screens will be installed with 0.020 inch aperture width. The gradation is based <br /> on the initial selection of the filter pack and is sized to retain the Dyo of the filter pack. <br /> Protective Surface Casing — Six linear feet of nominal 6-inch diameter %-inch wall steel casing, or 6"x6" <br /> square tubing, equipped with lockable, removable cap. Cemented in place from approximately 2.0 <br /> 4 <br />