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ARCHIVED REPORTS_XR0006621
Environmental Health - Public
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EHD Program Facility Records by Street Name
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YOSEMITE
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1012
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3500 - Local Oversight Program
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PR0545948
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ARCHIVED REPORTS_XR0006621
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Last modified
9/29/2020 10:19:51 PM
Creation date
8/5/2020 4:02:13 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006621
RECORD_ID
PR0545948
PE
3528
FACILITY_ID
FA0005159
FACILITY_NAME
FILL-EM FAST
STREET_NUMBER
1012
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21903024
CURRENT_STATUS
02
SITE_LOCATION
1012 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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• approximately 25 feet below grade (or 10 feet below the water <br /> table) . Soil borings will be advanced at locations indicated on <br /> Figure 1 using hollow-stem auger drilling techniques. Soil samples <br /> will be collected as the borings are advanced at 5-foot intervals <br /> and/or changes in lithology. The samples will be screened in the <br /> field for the presence of organic vapors with a photoionization <br /> detector (PID) . Soil cuttings will be stored on site on plastic <br /> pending receipt of analytical results and characterization for <br /> disposal. <br /> One soil sample collected above the water table from each soil <br /> boring will be submitted to a state-certified laboratory for <br /> analysis of BTEX and TPHg. All analyses will be done using <br /> established state and federal EPA methodology. Drilling and <br /> sampling protocols are described in Appendix A. <br /> Monitoring Well Construction, Depth to Water <br /> Measurements, and Ground Water Sampling <br /> Proposed monitoring wells will be constructed with 15 feet of 2- <br /> inch diameter polyvinyl chloride(PVC) well screen with 0. 020-inch <br /> wide (#20) slots. Blank 2-inch diameter PVC will extend from the <br /> top of the screen to the surface. The annular space opposite the <br /> screened portion of the well will be backfilled with a gravel pack <br /> consisting of #3 Monterey sand or equivalent. The gravel pack will <br /> . extend 2 feet above the top of the screened interval. In the <br /> annular space above the gravel pack, a 2-foot thick bentonite seal <br /> will be installed. Above the bentonite seal, a cement grout with <br /> approximately 5 percent bentonite will be emplaced and will serve <br /> to inhibit movement of surface water downward through the well <br /> annulus. The well riser will be cut off below grade and a flush- <br /> grade, watertight, well box will be installed at the surface. A <br /> watertight, locking, expansion well cap will be used to secure the <br /> well riser. A diagram of typical well construction specifications <br /> is included as Figure 2 . <br /> After installation, the casing riser on each well will be surveyed <br /> relative to the existing on-site monitoring wells. Depth to water <br /> in each well will then be measured, and each monitoring well will <br /> be developed, purged, and sampled as described in Appendix A and in <br /> accordance with (Santa Barbara) County requirements. Purge water <br /> wi be stored on site in approved 55-gallon drums pending <br /> disposal. The groundwater samples will be submitted to a state- <br /> certified laboratory for analysis of BTEX and TPHg. <br /> Report Results <br /> After field activities are complete and after receipt of laboratory <br /> results, ,a report of� the results will be prepared to,document field <br /> activities, present the ` analytical Iresults�,, 'and recommend ' <br /> I 1 1 I II I• <br /> additional work, l if warranted. The report will include soilh boring ' <br /> logs, soil sample analytical results, subsurface; soil descriptions, <br /> f depth tolwater lImeasurements, and groundwater sample 'analytical <br /> results. I The final report will be signed and sealed by a <br /> I <br /> ' I I <br /> 1'1 , I'I 111 Esq''' <br />
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