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2900 - Site Mitigation Program
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PR0527568
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Last modified
7/3/2019 1:52:22 PM
Creation date
7/3/2019 1:30:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0527568
PE
2950
FACILITY_ID
FA0018677
FACILITY_NAME
SIMMS GRUPE MANAGEMENT CO
STREET_NUMBER
800
STREET_NAME
DOUGLAS
STREET_TYPE
RD
City
STOCKTON
Zip
95207
APN
09746339
CURRENT_STATUS
01
SITE_LOCATION
800 DOUGLAS RD
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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€ L E i N F E L D E R <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. <br /> The well heads may be enclosed in a water tight cement utility box set flush to <br /> the 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 <br /> water, the well is developed by surging, pumping or bailing. Surging along the <br /> screened interval of the well is performed to draw the sediment from the formation into <br /> the filter pack and the well, and to set the sand pack. Development continues until the <br /> discharge runs relatively clear of fines. Approximately 5 to 10 well volumes are <br /> generally removed from each monitoring well. Discharge water is stored in 55-gallon <br /> drums and left on site for later discharge or disposal by the client, depending on <br /> laboratory results. The drums are labeled with the date, well number, and a contact <br /> person and phone number. <br /> 02001 PROP.ENV/ST07P271/DGD:ly/ra Page B-4 <br /> ©2007 Kleinfelder October 31,2007 <br />
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