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2900 - Site Mitigation Program
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PR0524190
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Last modified
4/3/2020 2:07:24 PM
Creation date
4/3/2020 1:45:09 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0524190
PE
2965
FACILITY_ID
FA0016241
FACILITY_NAME
STOCKTON REGIONAL WATER CONTROL FAC
STREET_NUMBER
2500
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16333003
CURRENT_STATUS
01
SITE_LOCATION
2500 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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+/ KLEINFELDER <br /> EXPECT MORE <br /> • The well casing are 2- or 4-inch inside diameter, flush threaded joint, schedule 40 <br /> PVC pipe. <br /> • The wells are constructed in 8- or 10-inch diameter borings. <br /> • Well screen sections are perforated with 0.010- or 0.020-inch factory-cut slots. <br /> • The wells are generally screened from 5 feet above to 15 feet below first <br /> groundwater. The screen length is reduced if an aquitard with a minimum <br /> thickness of 5 feet is encountered. If an apparent aquitard is encountered, the <br /> well is usually terminated 1 to 2 feet into the aquitard. Effort is made not to <br /> screen across two aquifers. If confined aquifer conditions or high vadose zone <br /> contamination are encountered, the well screen is usually not set above the <br /> depth of first encountered groundwater. Wells are usually not set in areas of <br /> suspected significant soil contamination. <br /> • The PVC pipe and end caps are steam cleaned prior to installation. <br /> • The annular space between the screen and the wall of the boring is backfilled <br /> with the appropriate clean sand to approximately 2 feet above the top of the <br /> perforated sections. Based on soil logs or a sieve test, modifications may be <br /> made regarding the size of sand to be used. Installation of the sand may require <br /> that the sand be tremmied, using clean water. <br /> • A 3- to 5-foot bentonite plug is placed above the sand pack to provide a seal <br /> against surface water infiltration and to reduce the potential for cement grout to <br /> infiltrate into the water. <br /> • The remaining annular space is filled to the surface with cement/bentonite grout. <br /> • The wells are secured in an aboveground or underground locking stovepipe. The <br /> well heads may be enclosed in a water tight cement utility box set flush to the <br /> ground surface when located in a traffic area. <br /> B-3.2 Monitoring Well Development <br /> The wells are developed to reduce the effects of drilling on the formation and to <br /> increase the effective hydraulic radius of the wells. <br /> Monitoring wells are generally developed 24 to 48 hours after installation to allow the <br /> grout to set. Each well is first sampled with a clear disposable bailer to visually inspect <br /> for a hydrocarbon layer or sheen. If no product layer or sheen is observed on the water, <br /> the well is developed by surging, pumping or bailing. Surging along the screened <br /> interval of the well is performed to draw the sediment from the formation into the filter <br /> pack and the well, and to set the sand pack. Development continues until the discharge <br /> runs relatively clear of fines. Approximately 5 to 10 well volumes are generally removed <br /> from each monitoring well. Discharge water is stored in 55-gallon drums and left on site <br /> 02002 PROP.ENV/ST07P083R Page B-4 <br /> 0 2007 Kleinfelder May 17,2007 <br />
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