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2900 - Site Mitigation Program
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PR0506460
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Last modified
5/14/2020 1:22:09 PM
Creation date
5/14/2020 12:30:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0506460
PE
2950
FACILITY_ID
FA0007440
FACILITY_NAME
ATHERTON KIRK/SPRECKELS
STREET_NUMBER
18800
STREET_NAME
SPRECKELS
STREET_TYPE
RD
City
MANTECA
Zip
95336
CURRENT_STATUS
01
SITE_LOCATION
18800 SPRECKELS RD
P_LOCATION
04
QC Status
Approved
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EHD - Public
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i � • <br /> File No. 20-3978-O1.Wr6 KLEINFELDER <br /> February 24, 1997 <br /> • The wells are generally screened from 5 feet above to 20 feet below first <br /> ground water. The screen length is reduced if an aquitard with a minimum <br /> thickness of 5 feet is encountered. If an aquitard is encountered the well is <br /> usually terminated 1 to 2 feet into the aquitard. Effort is made not to screen <br /> across two aquifers. If confined aquifer conditions or high vadose zone <br /> contamination is encountered, the well screen is usually not set above the depth <br /> of first encountered ground water. 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 Lone Star Industries 0/30 or 2/12 Monterey sand to <br /> approximately 2 feet above the top of the perforated sections. Based on soil <br /> logs or a sieve test, modifications may be made regarding the size of sand to be <br /> used. Installation of the 0/30 sand may require that the sand be tremmied, <br /> using clean water. In this event, a sample of the tremie water is collected, <br /> unless the source is known to be clean. <br /> • A 3- to 5-foot bentonite plug is placed above the sand pack to provide a seal <br /> against surface water infiltration. <br /> • The remaining annular space is filled to the surface with tremmied <br /> cement/bentonite grout to the surface. <br /> • The wells are secured in a locking stovepipe. The well heads may be enclosed <br /> in a cement utility box set flush to the ground surface located in a traffic area. <br /> A-3.2 Monitoring Well Development and Sampling <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 <br /> to set. Each well is first sampled with a clear acrylic bailer to visually inspect for <br /> hydrocarbon layer or sheen. If no product layer or sheen is observed on the water, the well is <br /> developed by surging, pumping, or bailing. Surging along the screened interval of the well is <br /> performed to draw the sediment from the formation into the filter pack and the well and to set <br /> the sand pack. The sediment laden water is purged from the well at a rate of between 0.75 to <br /> 10 gallons per minute (gpm) depending on recharge rate and casing size. Development <br /> continues until the discharge runs relatively clear of fines. Approximately 5 to 10 well <br /> volumes are generally removed from each monitoring well. Discharge water is stored in 55- <br /> 10-3978-01.WR61107RE074.doc Page No.A-4 0 199 7, Kleinfelder,Inc. <br />
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