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ARCHIVED REPORTS_XR0012741
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545337
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ARCHIVED REPORTS_XR0012741
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Last modified
2/11/2020 4:50:47 PM
Creation date
2/11/2020 11:57:32 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012741
RECORD_ID
PR0545337
PE
3528
FACILITY_ID
FA0003629
FACILITY_NAME
ARCO STATION #434*
STREET_NUMBER
501
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
03119028
CURRENT_STATUS
02
SITE_LOCATION
501 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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10711 <br /> d 's'Y- R+--+ •'-ISEE�� �r rl:_,; -"--+ Fwd ''�' _3 e 'a„• ` . �` <br /> r.Y <br /> gmF <br /> %bA <br /> CHAPTER 2 <br /> FIELD METHODS <br /> w <br /> During April 23, 1990, through May 10, 1990, five groundwater monitoring wells, one <br /> groundwater extraction well, and eight vapor extraction wells were installed. In addition, one <br /> groundwater monitoring wall was abandoned and a step-pumping test was performed an the <br /> extraction well. The boreholes were drilled by Wayne Drilling Company, using two CME-55 <br /> li. drilling rigs equipped with hollow-stem augers. Locations of the wells installed, W-1 A, W-9, <br /> i W-10,W-1 I,W-12,E-1, V-1, V-2,V-3,V-4,V-5,V-6, V-7,and V-8,are shown on Figure 2-I. <br /> Table 2-1 describes the construction and purpose of each of these wells. The work was <br /> performed under San Joaquin County special permit numbers 90-866 and 90-867. All grouting <br /> r i was inspected by a San Joaquin County representative. <br /> Groundwater Monitoring Wells <br /> Each monitoring well borehole was advanced to approximately 80 feet, or about 20 feet <br /> below the groundwater surface, using 8-inch hollow-stem augers. For Well W-9, samples for <br /> fr laboratory analyses were collected at 5-foot intervals. For the remaining mcnitoring wells, <br /> W-lA, W-10, W-I1, and W-12, soil samplinb was conducted only if field evidence of <br /> contamination was observed. Each monitoring well borehole was continuously cored for <br /> lithologic classification with the exception of W-lA. The borehole for W-1A was not logged <br /> because it was a replacement for well W-1 which had previously been logged. Drill cuttings <br /> '-' were screened using an organic vapor meter(OVM)or threshold limit value (TLV) meter. <br /> Soil showing evidence of organic vapors of 100 parts per trillion (ppm) or mom were <br /> considered contaminated, and samples were collected every 5 feet, or until no evidence of <br /> contamination was found. Table 2-1 describes the samples taken for each monitoring well. <br /> Soil samples were collected using an 18-inch-long by 2-inch-diameter Modified California- <br /> type sampler with 6-inch-long brass tube liners. The drive sampler was driven ahead of the auger <br /> ., into undisturbed soil. Soil samples were screened in the field for organic vapors using an OVM <br /> or TLV and the measurements recorded. The ends of the tubes were covered with foil and a <br /> plastic cap taped to the tube. The samples were stored on ice from collection through delivery <br /> to Brown and Caldwell's state-certified analytical laboratory in Emeryville, California. <br /> Monitoring wells W-9,.._W-10,.-.W-1.1,-and W.-12_.were-.continuously..cored using-a-5-foot-long. ------ ----- - <br /> 3-inch-diameter core barrel in order to accurately describe the lithnlogy of the borehole. Each <br /> borehole was logged froth the continuous cores and/or the samples taken at 5-foot intervals, and <br /> F the drill cuttings, using the Unified Soil Classification system. Borehole logs are presented in <br /> Appendix A. <br /> 1 U <br /> �e <br />
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