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. Quarterly Report - Third Quarter 2005 <br /> RIVER CITY PETROLEUM- CONNELL MOTOR LIFT TRUCK <br /> 2211 North Wilson Way, Stockton, California <br /> 1.0. INTRODUCTION <br /> At the request of Ms. Kerry Heckman,Advanced GeoEnvironmental, Inc. (AGE)has prepared this <br /> quarterly report for the property located at 2211 North Wilson Way, Stockton, California(the site). <br /> The site setting is illustrated on Figure 1. Site structures,soil borings,monitoring well locations and <br /> soil-vapor extraction well locations are shown on Figure 2. <br /> The scope of work included the following: l)the installation of eleven monitoring wells 2)operation <br /> and monthly monitoring of the interim soil-vapor extraction (SVE) remediation system <br /> 3)performance of a quarterly ground water monitoring event in June 2005;and 4)preparation of this <br /> report. The procedures for the site remediation were outlined in the AGE-prepared Soil-Vapor <br /> Extraction and Site Assessment Work Plan,dated 15 November 2003, and approved by the Central <br /> Valley Regional Water Quality Control Board(CVRWQCB)letter dated 30 December 2003.Ground <br /> water monitoring&well installation was performed in accordance with procedures outlined in the <br /> AGE-prepared Monitoring Well Installation Work Plan, dated 01 June 2004, Monitoring Well <br /> Installation - Site Assessment Work Plan Addendum, dated 05 May 2005, Monitoring Well <br /> Installation Location and Specification dated 02 June 2005 and approved by the CVRWQCB <br /> electronic letter dated 14 June 2005. <br /> Currently,there are forty-eight monitoring well locations at the site.Eighteen wells(MW-1 through <br /> MW-17 and MW-41)are shallow-water wells screened from 40 to 60 feet bsg;the remaining wells <br /> are either intermediate or deep, depth-discrete, monitoring wells. Based on field and laboratory <br /> analytical data,the screened intervals of these wells were set within eight, depth-discrete intervals <br /> (hydrogeologic units) to monitor vertical and lateral changes in hydraulic gradient, contaminant <br /> concentrations and migration directions within each unit. Each hydrogeologic unit was previously <br /> defined based on lithologic information provided by laboratory analyses, soil sample descriptions, <br /> and cone penetrometer testing. The above referenced monitoring wells and hydrogeologic units are <br /> as follows: <br /> • Shallow-screened(40 to 60 feet bsg)monitoring wells MW-1 through MW-17 are screened <br /> through the first hydrogeologic unit(HU1); <br /> • Upper intermediate-screened(75 to 85 feet bsg)wells MW-18 through MW-21 are screened <br /> in the second hydrogeologic unit(HU2); <br /> • Lower intermediate-screened (90 to 105 feet bsg) wells MW-22 through MW-29 are <br /> screened in the third and fourth hydrogeologic units (HU3/HU4); <br /> • Deep-screened(125 to 135 feet bsg)wells MW-31 through MW-33 are screened in the fifth <br /> hydrogeologic unit(HU5); <br /> • • Two deep-screened (145 to 150 feet bsg) depth-discrete wells in the former UST and the <br /> Advanced GeoEnvironmental,Inc. <br />