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ARCHIVED REPORTS XR0000406
Environmental Health - Public
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EHD Program Facility Records by Street Name
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BENJAMIN HOLT
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2908
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3500 - Local Oversight Program
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PR0544111
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ARCHIVED REPORTS XR0000406
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Last modified
2/7/2019 12:34:23 PM
Creation date
2/7/2019 11:26:02 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000406
RECORD_ID
PR0544111
PE
3528
FACILITY_ID
FA0003625
FACILITY_NAME
ARCO STATION #83560*
STREET_NUMBER
2908
Direction
W
STREET_NAME
BENJAMIN HOLT
STREET_TYPE
DR
City
STOCKTON
Zip
95207
APN
09763032
CURRENT_STATUS
02
SITE_LOCATION
2908 W BENJAMIN HOLT DR
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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ro <br />• GROUNDWATER MONITORING WELLS <br /> Morutonng Well Drilling. Groundwater monitoring wells will be drilled by the method <br /> described in the section entitled Borehole Dnlling, with the excepuon that they will be dulled <br /> to a depth of 15 or 20 feet below the water table or piezometric surface depending upon known <br /> conditions and upon unanticipated conditions encountered during drilling The borehole will then <br /> be completed as a monitoring well by the method described below <br /> Monitoring Well Completion. Groundwater monitoring wells will be completed with PVC <br /> screen and casing On-site monitoring wells will be completed with 4-inch-diameter PVC screen <br /> and blank casing, while off-site wells will be completed with 2-inch-diameter PVC A PVC cap <br /> will be installed at the bottom of each well <br /> The well screen typically will be 0 020-inch slotted flush-threaded PVC extending from a <br /> depth of approximately 15 or 20 feet below the water table or piezometric surface to 5 to 10 feet <br /> above The well design is intended to accommodate seasonal water-level fluctuations within the <br /> slotted interval The well design may be modified in the field during the drilling operation, <br /> depending upon conditions encountered during drilling In no case does the monitoring well <br /> penetrate clay zones greater than 5 feet thick, which might allow downward migration of <br /> contaminants into lower water-bearing zones. Blank casing extends from the top of the <br /> perforated section to the ground surface (or above, in the case of above-ground completion) <br /> The annular space surrounding the well screen and casing will be packed with No 1120 (or <br /> equivalent) sand, from the bottom of the screen to approximately 2 feet above the top of the <br /> screen The well will then be bailed or surged to settle the filter pack, and more sand will be <br /> added as necessary to return the level to a height of 2 feet above the top of the screen. A 2- to <br /> 3-foot-thick seal of bentonite pellets will be placed above the sand pack. The well will then be <br /> grouted with bentonite-cement slurry or neat cement, from the top of the bentonite seal to the <br /> surface. Groundwater monitoring wells commonly will be completed below grade and protected <br /> with a water-tight locking cover. A typical well constriction is illustrated on Figure 1 <br /> The top of casing (TOC) will be surveyed by a licensed surveyor, and all depths to water <br /> will be measured in relation to the surveyed mark on the TOC <br /> Monitonng Well Development Groundwater monitoring wells will be developed by <br /> surging, balling, or pumping until clean, sediment-free water is produced from the well. The <br /> length of development time vanes, depending upon field conditions Development water is <br /> contained in 55-gallon barrels, which will be stored temporarily on site until disposal. <br />
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