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WORK PLANS_CASE 1
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WORK PLANS_CASE 1
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Last modified
3/6/2020 3:53:57 PM
Creation date
3/6/2020 3:00:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
CASE 1
RECORD_ID
PR0506313
PE
2950
FACILITY_ID
FA0000514
FACILITY_NAME
MAIN STREET SHELL*
STREET_NUMBER
1071
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21707011
CURRENT_STATUS
02
SITE_LOCATION
1071 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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PRE-TANK REPLACEMENT SITE ASSESSMENT WORK PLAN. <br /> %W 1071 North Main Street,Manteca,California <br /> Yr <br /> 3.0 PROPOSED WORK PLAN <br /> 41.0 <br /> A total of thirteen soil borings will be advanced according to San Joaquin County <br /> guidelines at the locations shown in Figure 2. Four soil borings will be advanced to an <br /> •- estimated minimum depth of 20 feet below grade in the area of the existing and proposed <br /> underground fuel storage tanks. Eight soil borings will be advanced to estimated depths <br /> of 10 feet below grade around the four dispenser islands. One soil boring will be drilled <br /> adjacent to the existing product line locations. Soil borings will be advanced using a 8- <br /> inch diameter hollow stem auger. All soil borings, upon completion, will be grouted to <br /> surface with a cement bentonite slurry. Soil samples will be collected using brass liners <br /> in a California-Modified split-barrel sampler. Proposed methods are attached in Appendix <br /> A. <br /> ;" Soil samples will be collected from each 13 borings at initial depths of 2.5 feet bgs. Soil <br /> samples will then be collected at a maximum vertical spacing of approximately 5 feet. The <br /> samples will be screened in the field with a portable photoionization detector (PID) to <br /> tow determine organic vapor content. Selected soil samples will by sent to a state-certified- <br /> laboratory for analysis. Samples will be analyzed for benzene, toluene, ethlybenzene, <br /> aw xylenes (BTEX), total petroleum hydrocarbons (fPH) as gasoline and total lead. The <br /> samples will be analyzed, following the SJCPHSD's "Sampling Protocol for Routine Tank <br /> Removals," using GCFID/MS, EPA Method 8260, and Total Lead by Flame AA, EPA <br /> Method 7420. <br /> The estimated volume of soil cuttings removed from the borings is expected to be <br /> between one and two cubic yards. All drill cuttings will be stored temporarily at the site <br /> on top of and covered by plastic sheeting. Additional sampling and testing of the <br /> stockpiled soil may be required in order to meet local landfill disposal criteria. Following <br /> .r receipt of the laboratory results, the drill cuttings will be transported from the site by a <br /> state-licensed hauler to an appropriate disposal facility. <br /> .. t according to the health and safe rocedu s <br /> All work described herein will be completed a g safety p <br /> outlined in the site health and safety plan included in Appendix B. A copy of the health <br /> and safety plan will be available on site during all field operations. <br /> Upon completion of drilling, the bore holes will 'ted with a cement bentonite slurry. <br /> The slurry will not free fall more than twen (20) feet. The slurry will be pumped with a <br /> tremie pipe to depths greater than twenty fe <br /> l� ,pro � <br /> %, r -� <br /> 91-013A.RPT 6 <br /> •r <br /> it <br />
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