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WORK PLAN AND TIME SCHEDULE <br /> FOR ANALYSES OF BACKGROUND <br /> GROUNDWATER QUALITY <br /> City of Stockton <br /> Regional Wastewater Control Facility <br /> 1.0 INTRODUCTION <br /> This Work Plan has been prepared by Condor Earth Technologies,Inc. (Condor)at the request of the City <br /> of Stockton Municipal Utilities District(MUD)to comply with Provision VI.C.2.c of California Regional <br /> Quality Control Board, Central Valley Region (Regional Water Board) Order No. 115-2008-0154 for <br /> municipal sewage discharges at the Stockton Regional Wastewater Control Facility (RWCF). This work <br /> plan and time schedule describes the installation of additional monitoring wells and other testing needed <br /> to effectively and fully characterize background groundwater quality conditions to evaluate compliance <br /> with Groundwater Limitations V.B.I.b and c. Sections 2.0 through 8.0 include introductory and <br /> background information, the theoretical basis of the approach taken with respect to the use of the <br /> background concept and a needs assessment. Descriptions of the work proposed begin in Section 9.0.The <br /> Time Schedule is included in Section 13.0. <br /> 2.0 FACILITY DESCRIPTION <br /> The location of the RWCF is shown on Figure 1. Effluent treatment and disposal practices at the facility <br /> have been on-going for decades. The RWCF consists of a primary and secondary treatment facility on the <br /> east side of the San Joaquin River(SJR)including primary treatment screening,grit removal, and primary <br /> sedimentation with enhanced treatment through injection of polymer and ferric chloride into the primary <br /> clarifiers. The secondary treatment consists of high rate trickling filters and secondary clarifiers. Treated <br /> effluent is piped under the SJR to the tertiary treatment facilities west of the river. Tertiary treatment <br /> facilities west of the SJR include oxidation ponds, recirculation canals and interceptor ditches, a <br /> constructed wetland treatment area,treatment plants, chlorination facilities and the river outfall discharge <br /> system.A Flow Schematic is provided in Appendix 6. <br /> Groundwater monitoring at the facility was initiated in 2003 and has continued on a quarterly basis. MUD <br /> maintains a network of 17 active monitoring wells around the RWCF that are sampled quarterly or semi- <br /> annually. The locations of the facility's monitoring wells east and west of the SJR are shown on the <br /> topographic map on Figure 2. Also shown on Figure 2 are December 2008 groundwater surface contours <br /> with groundwater flow direction indicated by arrows. Table 1 lists completion details of the monitoring <br /> wells. Of particular note is the well screen submergence in 16 of 18 monitoring wells. The tops of well <br /> screens range from 2.87 feet above the mean static water level at well MW-18 to 15.08 feet below the <br /> mean static water level at MW-5. The average screen submergence of all wells is 6.81 feet below the <br /> respective mean static water level in the wells. Typically the wells were constructed with sand pack <br /> extending 1.5 to two(2)feet above the top of screens. <br /> 3.0 PHYSICAL AND HYDROLOGICAL SETTING <br /> The RWCF site is located in the SJR delta. The oxidation ponds are located at sea level on flat ground <br /> west of the SJR and the primary and secondary treatment facilities are located in a similar setting east of <br /> the river. The Bums Cutoff and the former U.S. Naval Facilities on Rough and Ready Island are located <br /> to the North, a Stockton industrial area is located to the east, and agricultural lands are located to the west <br /> and south. The SJR is subject to daily tidal fluctuations of three (3) feet or more which, periodically, <br /> i.�i1 t;ON�/)R <br />