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csj ii <br /> a1 <br /> • 24 July 2000 <br /> AGE-NC Project No 99-0654 <br /> Page 3 of 6 <br /> 25 REGIONAL GROUND WATER DEPTH AND FLOW DIRECTION <br /> The estimated depth to ground water at the property is approximately 30 to 40 feet below surface <br /> grade (bsg), based on the map titled Lanes of Equal Depth to Groundwater Fall 1998 published by <br /> the San Joaquin County Flood Control District and Water Conservation District (FCD&WCD) It <br /> is inferred from the map titled Lanes of Equal Elevation of Groundwater Fall 1998, also published <br /> by the FCD&WCD, that ground water flows toward the northeast in the general area of the site, but <br /> this may be modified by changing recharge and discharge patterns Ground water is considered to <br /> be of beneficial use and is used for domestic, industrial and commercial purposes <br /> The closest surface water feature to the site is San Joaquin River and Walker Slough located <br /> approximately 4,500 feet southwest of the site Water from the site drains into the San Joaquin River <br /> Deep Water Channel and is primarily used for commercial and recreational boating Based upon well <br /> information obtained from nearby saes, ground water flow direction is northeasterly and is currently <br /> estimated to occur at a depth of approximately 30 to 40 feet below surface grade (bsg) <br /> • 3.0. PROCEDURES <br /> An Interim Remediation Work Plan, dated 22 March 2000, for the excavation and disposal of <br /> hydrocarbon-impacted soil, was prepared by AGE and approved by PHS-EHD The objective of the <br /> interim remediation was to remove hydrocarbon-impacted soil from the floor and sidewalls of the <br /> former underground storage tank (UST) excavation prior to installation of new USTs <br /> 3 1 EXCAVATION OF HYDROCARBON-IMPACTED SOIL <br /> On 20 Apnl 2000, approximately 175 cubic yards of petroleum hydrocarbon-impacted soil were <br /> excavated from the former UST area Excavation was performed by Stockton Service Station <br /> Equipment Company using a Holt excavator <br /> Excavated soil was screened for the presence of organic vapor using a using an organic vapor meter <br /> (OVM) equipped with a photo-ionization detector (PID Thermo Environmental 580A, 10 0 eV, <br /> calibrated to isobutylene) Based on OVM readings and field observations, excavated soil was <br /> segregated into clean soil and impacted soil, only soil exhibiting hydrocarbon odor or measurable <br /> OVM readings were stockpile for transportation and final disposal <br /> 3 2 EXCAVATION SOIL SAMPLE COLLECTION AND ANALYSIS <br /> • Soil samples were collected from the floor and sidewalls of the excavation and stockpiled soil by <br />