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ARCHIVED REPORTS_XR0012454
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ARCHIVED REPORTS_XR0012454
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Last modified
3/4/2020 9:46:12 AM
Creation date
3/4/2020 9:36:10 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012454
RECORD_ID
PR0505714
PE
2950
FACILITY_ID
FA0003590
FACILITY_NAME
M B P
STREET_NUMBER
501
Direction
W
STREET_NAME
LODI
STREET_TYPE
AVE
City
LODI
Zip
95240
APN
03731045
CURRENT_STATUS
02
SITE_LOCATION
501 W LODI AVE
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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a - <br /> 1 . <br /> • <br /> Quarterly Report - Second Quarter 2002 <br /> MEL BOKIDES PETROLEUM, INC. <br /> 501 W. Lodi Avenue, Lodi, California <br /> 1.0. INTRODUCTION <br /> ' At the request of Mr. Nicholas Bokides of Mel Bokides Petroleum Inc., Advanced <br /> GeoEnvironmental, Inc. (AGE) has prepared this quarterly report for 501 W. Lodi Avenue, Lodi, <br /> California (site). The site setting is illustrated on Figure 1. Site structures and monitoring well <br /> locations are depicted on Figure 2. <br /> ' This report documents three soil-vapor sampling events between April and June 2002 and a ground <br /> water monitoring event on 06 June 2002, and presents the results of the laboratory analyses of soil- <br /> vapor and ground water samples. <br /> ' A sununaprevious revious <br /> Investigations at the site was Included in the AGE-prepared Work Plan for <br /> Site Assessment, Mel Bokides Petroleum, 501 West Lodi Avenue, Lodi, California, dated 15 May <br /> 1998. <br /> ' • 2.0. PROCEDURES <br /> ' Field work was conducted in accordance with guidelines issued by the Central Valley Regional Water <br /> Quality Control Board(CVRWQCB)and directives issued bythe San Joaquin County Environmental <br /> Health Department (EHD) for subsurface investigations and sampling of ground water monitoring <br /> ' wells at sites with underground storage tank (UST) system releases. <br /> ' 2.1. WELL MONITORING AND EVACUATION <br /> On 06 June 2002, the depth to ground water in each monitoring well was measured to the nearest <br /> ' 0.01-foot utilizing a•Solinst water level meter. Ground water monitoring wells BMW-1 through <br /> BMW-5 (site wells) and MW-5 (off-site well) were monitored and sampled. The ground water <br /> elevation was then calculated by subtracting the measured depth to ground water from the surveyed <br /> ' casing elevations (Table 1). Ground water elevations were later plotted and contoured on a scaled <br /> site map (Figure 3). <br /> _- <br /> - After water levels -were measured approximately 36 gallons (a minimum of three casing-water <br /> volumes per well) of water were purged from wells BMW-1 and BMW-2 utilizing a Grundfos <br />' submersible pump and approximately 4 to 10 gallons of water were purged from the remaining wells <br /> with dedicated, disposal bailers. <br /> An Oakton water t analyzers were utilized to monitor temperature, H and mP , p conductivity of purged <br /> water at regular purge-volume intervals. Stabilization data and field logs are included in Appendix A. <br /> Purged ground water was containerized in 55-gallon drums and stored on-site. <br />' Advanced GeoEnvironmental,Inc. <br />
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