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ARCHIVED REPORTS XR0001633
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3500 - Local Oversight Program
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PR0544513
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ARCHIVED REPORTS XR0001633
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Last modified
6/14/2019 12:12:22 PM
Creation date
6/14/2019 10:49:51 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001633
RECORD_ID
PR0544513
PE
3528
FACILITY_ID
FA0024115
FACILITY_NAME
WEST CLAY PROPERTY
STREET_NUMBER
639
Direction
W
STREET_NAME
CLAY
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14707110
CURRENT_STATUS
02
SITE_LOCATION
639 W CLAY ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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,} J <br /> KLEINFELDER <br /> File No. 20-3769-01 <br /> March 16, 1994 <br /> • Well screen sections will be perforated with 0 010-or 0.020-inch factory-cut slots. The <br /> perforation sieve openings are assessed (and modified if required) after the borings are <br /> logged, and if warranted, a sieve test has been performed and the results received. <br /> • The wells are generally screened from 5 feet above to 15 feet below first groundwater. <br /> Due to shallow groundwater at the site, the screen length may be reduced to 10 feet <br /> below first encountered groundwater. If an apparent aquitard is encountered, the well <br /> is usually terminated 1 to 2 feet into the aquitard. Effort is made not to screen across <br /> two aquifers. If confined aquifer conditions or high vadose zone contamination is <br /> encountered, the well screen in usually not set above the depth of first encountered <br /> groundwater. Wells are usually not set in areas of suspected significant soil <br /> contamination. <br /> • The PVC pipe and end caps will be steam cleaned prior to installation. <br /> • The annular space between the screen and the wall of the boring is backfilled with the <br /> appropriate clean Lone Star Industries 0130 or 2112 Monterey sand to approximately 2 <br /> feet above the top of the perforated sections. Based on soil logs or a sieve test, <br /> modifications may be made regarding the size of sand to be used. Installation of the <br /> 0/30 sand may require that the sand be tremmied, using clean water. In this event, a <br /> sample of the tremae water is collected, unless the source is thought to be clean. <br /> • A 3- to 5-foot bentonite plug is placed above the sand pack to provide an annular seal <br /> against surface water infiltration and to reduce the potential for cement grout to infiltrate <br /> into the water. <br /> • The remaining annular space is filled to the surface with tremmied cementlbentonite <br /> grout (surface seal) to the surface. <br /> • The wells will be secured in a below-ground locking stovepipe and the well heads <br /> enclosed in a water-tight cement utility box set flush to the ground surface. <br /> A-3.2 Monitoring Well Development <br /> The wells are developed to reduce the effects of drilling on the formation and to increase the <br /> effective hydraulic radius of the well. <br /> Monitoring wells are generally developed 24 to 48 hours after installation to allow the grout to <br /> set. Each well is first sampled with a clear acrylic bailer to visually inspect for hydrocarbon <br /> layer or sheen. If no product layer of sheen is observed on the water, the well is developed by <br /> surging, pumping, or bailing. Surging along the screened interval of the well is performed to <br /> 40 draw the sediment from the formation into the falter pack and the well and to set the sand pack. <br /> The sediment-laden water is purged from the well at a rate of between 0 75 to 10 gallons per <br /> Copyzight 1994 Kleinfoldsr, Inc Pago 3 of 5 <br />
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