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ATC Associates Inc. <br /> \v/ 1117 Lone Palm Avenue,Suite 201 <br /> Modesto,California 95351 <br /> 209-579-2221 <br /> fax:209-579-2225 <br /> The proposed groundwater monitoring wells will be constructed of 2-inch inside diameter, <br /> Schedule 40 PVC casing-,with five-feet_of_O..01.O.inch..slotted.screen. A s nd=pack willbe`placed <br /> in the annulus of each well extending from 6-bottom of the well screen to approximately three <br /> feet-above the top of the screen. Approximately three feet of bentonite will beplaced,-ontop of <br /> the sand pack and hydrated with potable water. The remamrng annulus-will""be completed to <br /> surface with,cement grout. To protect theintegrity of the wells, locking, watertight well plugs <br /> will bei sn talled ori each well and a watertight wellhead labeled ':monitoring well" will be set in <br /> concrete over each well. <br /> The proposed monitoring well locations are shown on Figure 3. Well construction diagrams <br /> associated with the Zone B and C groundwater zones are provided as Attachment 1. <br /> Well Survey,Development, and Groundwater Monitoring <br /> Once the proposed monitoring wells are installed, the top of each well casing will be surveyed to <br /> sub-meter accuracy relative to a known benchmark. The surveying activities will include location <br /> and elevation of each well casing. The survey data will be used to tie in to the existing <br /> groundwater monitoring well network. <br /> At least 48 hours after installation, the new wells will be developed using surging and bailing <br /> techniques until the purged groundwater is relatively sediment free. The wells will be sampled at <br /> least 48 hours after they are developed. Prior to the collection of groundwater-samples,the depth <br /> to groundwater will be measured in each well and a minimum of three well volumes of <br /> groundwater will be purged from each well. Temperature, electric conductivity (eH), pH, <br /> dissolved oxygen (DO), and oxidation-reduction potential (ORP) will be monitored and allowed <br /> to stabilize. Groundwater samples will be collected using disposable bailers, one dedicated to <br /> each well. <br /> Sample Analyses <br /> Selected soil samples collected during installation of the proposed groundwater monitoring wells <br /> and subsequent groundwater samples collected from these wells will be submitted under chain- <br /> of-custody procedures to a California State-certified analytical laboratory. The groundwater <br /> samples will be analyzed for TPHg or gasoline range organics (GRO) utilizing EPA Method <br /> 801513; and BTEX, MTBE, tertiary butyl ether (TBA), ethyl tertiary butyl ether (ETBE) di- <br /> isopropyl ether (DIPE), tertiary amyl ether (TAME), 1,2-dichloroethane (1,2-DCA), and 1,2- <br /> dibromoethane(EDB)utilizing EPA Method 8260B. �-- <br /> Report Preparation <br /> Upon completion of the field activities, a report will be prepared describing the field activities <br /> and laboratory analytical results. The report will include a detailed summary of the subsurface <br /> investigation and contaminant distribution, both in soil and groundwater. The report will be <br /> S:\Environmenta1\25847\37 Tracy\Repom\wkp-addendum 2009.doc 7 <br />