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ARCHIVED REPORTS_XR0003682
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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YOSEMITE
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2072
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2900 - Site Mitigation Program
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PR0505553
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ARCHIVED REPORTS_XR0003682
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Last modified
7/23/2020 4:48:11 PM
Creation date
7/23/2020 4:11:29 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003682
RECORD_ID
PR0505553
PE
2960
FACILITY_ID
FA0006856
FACILITY_NAME
FRANKS FOOD MART
STREET_NUMBER
2072
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
94336
APN
22202001
CURRENT_STATUS
01
SITE_LOCATION
2072 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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y ,e <br /> 4 <br /> . was placed between the well casing and the boring from the bottom of the <br /> boiing to 1-foot above the ,cieened interval A 0 5-toot thick bentonite <br /> layer was placed between the ,andpack and the overlying cement sanitary <br /> seal A Portland cement sanitary seal was placed above the bentonite <br /> layer to prevent surface watei tiom infiltrating into the well The <br /> wellheads are piped directly into an air-sparging manifold, which is piped <br /> directly to the air source (Figure 2) See Appendix C for well completion <br /> logs <br /> 3 -2 Vapor-Extraction WoaL <br /> The remediation system incoiporates the use of seven (7) vapor- <br /> extraction (VE) wells During the dual-phase test conducted in August <br /> 2000, the VE radius of influence was shown to be at least 45-feet based o n <br /> measurements collected during the dual-phase test To be conservative, <br /> ASE assumed a VE influence of 20-feet and thus a spacing of 40-feet foi VE <br /> wells across areas of the site with elevated hydrocarbon concentrations <br /> Based on this spacing, ASE installed seven (7) VE wells (Figure 2) <br /> The VE wells were drilled with a drill rig equipped with S-inch diameter <br /> hollow-stem augers by West Hazmat Drilling Corp of Rancho Cordova, <br /> California between November 27 and 29, 2001 The wells were <br /> constructed with 2-inch diameter, flush threaded schedule 40, 0 020-inch <br /> factory slotted PVC well screen and blank casing The VE wells were <br /> screened between 4 and 12-feet bgs The depth of 12-feet was chosen <br /> because that depth is dust above the shallowest depth of groundwater <br /> measured historically in on-site monitoring wells Blank casing was <br /> installed above this screened interval Lonestar #2112 sand was placed <br /> between the well casing and the boring from the bottom of the boring to <br /> 05-feet above the screened interval A 0 5-foot thick bentonite layer was <br /> placed between the sandpack and the overlying cement sanitary seal A <br /> Portland cement sanitary seal was placed above the bentonite layer to <br /> prevent surface water from infiltrating into the well The wellheads were <br /> piped individually into a vapor-extraction piping manifold, which is piped <br /> to the abatement device (Figure 2) See Appendix C for the well <br /> completion logs <br /> 3 . 3 Groundwater RecQyery Wells <br /> Two additional groundwater-recovery wells were installed west of RW-1 to <br /> • enhance the recovery of groundwater in areas containing elevated <br /> hydrocarbon concentrations west of the current capture zone (Figure 3 ) <br /> These two additional wells have a spacing of 30-feet, which is consistent <br /> Frank's One Stop ASNE Remediation System Installation Report — February 2002 <br /> -2- <br />
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