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ARCHIVED REPORTS_XR0006696
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ARCHIVED REPORTS_XR0006696
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Last modified
5/5/2020 10:18:27 AM
Creation date
5/5/2020 9:35:57 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006696
RECORD_ID
PR0543479
PE
2960
FACILITY_ID
FA0024679
FACILITY_NAME
CANEPA'S CAR WASH
STREET_NUMBER
6230
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95204
APN
081360030
CURRENT_STATUS
01
SITE_LOCATION
6230 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
Scanner
LSauers
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EHD - Public
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Additional Soil and Groundwater Investigation Report <br /> Canepa's Car Wash(Pacific Avenue) <br /> January 21,2002 <br /> Page 3 <br /> ISoil samples collected from the monitor well borings were logged in accordance with the Unified Soil <br /> Classification System (USCS). Descriptions of the soil types encountered and other pertinent field <br /> observations were recorded on geological boring logs. The geological boring logs prepared by Condor <br /> for the soil and monitor well borings, and the CPT boring logs provided by Gregg, are included in <br /> Appendix C. <br /> 3.3 MONITOR WELL CONSTRUCTION <br /> Monitor wells MW-9 and MW-10 were constructed using 20 feet of 2-inch outside diameter, Schedule <br /> 40, flush-threaded, machine-slotted PVC screen (slot size 0.020). Monitor well MW-11 was constructed <br /> using 20 feet of 4-inch outside diameter, Schedule 40, flush-threaded, machine-slotted PVC screen (slot <br /> size 0.020). MW-12d was constructed using 10 feet of 2-inch outside diameter, Schedule 40, flush- <br /> threaded, machine-slotted PVC screen (slot size 0.020). A flush-threaded PVC bottom cap was placed at <br /> the bottom of the screen sections. Blank PVC casing was installed above the screens to the ground <br /> surface. A well construction graphic is included as part of the geological boring logs for each well <br /> (Appendix Q. Table 1, on the next page, includes construction details for the monitor wells, including <br /> the calculated quantity of annular seal materials and the approximate quantities used. <br /> For each well, a filter pack of#3 Monterey sand was emplaced through the augers into the well annulus <br /> from the bottom of the boring to approximately one foot above the screened interval. The depth of the <br /> sand in the well annulus was monitored with a weighted tape measure while the sand was being placed, <br /> and the auger gradually retracted to avoid bridging. Following emplacement of the sandpack to the <br /> desired depth, a surge block was used to settle the sandpack.After surging, the depth to the sandpack was <br /> measured and sand was added to bring the sandpack back to the desired level as necessary. To form a <br /> protective seal, approximately two feet of bentonite chips, hydrated using potable water, was installed <br /> above the sandpack as the augers were retracted. Monitor well MW-12d was completed to a depth of 110 <br /> feet bgs and, due to a substantial water column above the sandpack, coated bentonite pellets, instead of <br /> bentonite chips, were tremied to the top of the sandpack to form the seal in order to minimize the <br /> possibility of bridging. The pellets were allowed to hydrate for approximately thirty minutes following <br /> emplacement. A surface seal of neat cement was then pumped through a tremie pipe into the annulus <br /> extending from the bentonite seal to the ground surface. To verify the stability of the borehole, the augers <br /> were gradually retracted during emplacement of the grout. The grout hose retrained near the top of the <br /> bentonite seal until the pumped grout was near the surface. The remainder of the grout was pumped into <br /> the annulus from the top of the borehole. The monitor wells were then completed using traffic rated flush <br /> Imount protective covers set in concrete. <br /> 1 <br /> i CONDOR <br />
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