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CORRESPONDENCE_1990-1993
Environmental Health - Public
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4400 - Solid Waste Program
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PR0440005
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CORRESPONDENCE_1990-1993
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Last modified
4/17/2023 4:13:34 PM
Creation date
10/17/2022 1:45:46 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
1990-1993
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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o Well screen sections are perforated with 0.010- or .02 -inch factory -cut slots. <br />This parameter is assessed (and modified if required) after the boring logs <br />and, if warranted, a sieve test has been performed and the results received. <br />Well screen will be stainless steel wire -wrapped screen. <br />o The well will be screened from 5 feet above to 20 feet below the screened <br />interval of MW -14. The screen length is reduced if an aquitard with a <br />minimum thickness of 5 feet is encountered. If an aquitard is encountered <br />the well is usually terminated 1 to 2 feet into the aquitard. Effort is made not <br />to screen across two aquifers. <br />o The well pipe and end caps are steam cleaned prior to installation. <br />o 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 <br />to approximately 2 feet above the top of the perforated sections. Based on <br />soil logs or a sieve test, modifications may be made regarding the size of sand <br />to be used. Installation of the 0/30 sand may require that the sand be <br />tremmied, using clean water. In this event, a sample of the tremie water is <br />collected, unless the source is known to be clean. <br />o A 3- to 5 -foot bentonite plug is placed above the sand pack to provide a seal <br />against surface water infiltration. <br />o The remaining annular space is filled to the surface with tremmied <br />cement/bentonite grout to the surface. <br />o The wells are secured in a locking stovepipe. The well heads may be <br />enclosed in a cement utility box set flush to the ground surface located in a <br />traffic area. <br />A-3.2 Monitoring Well Development <br />The wells are developed to reduce the effects of drilling on the formation and to increase <br />the effective hydraulic radius of the well. <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 acrylic bailer to visually inspect for <br />hydrocarbon layer or sheen. If no product layer or sheen is observed on the water, the well <br />is developed by surging, pumpin*, or bailing. Surging along the screened interval of the <br />well is performed to draw the sediment from the formation into the filter pack and the well <br />and to set the sand pack. The sediment laden water is purged from the well at a rate of <br />between 0.75 to 10 gallons per minute (gpm) depending on recharge rate and casing size. <br />Development continues until the discharge runs relatively clear of fines. Approximately 5 <br />to 10 well volumes are generally removed from each monitoring well. Discharge water is <br />stored in 55 -gallon drums and left on site for later discharge or disposal by the client, <br />depending on laboratory results. <br />A-3.3 Well Survey <br />The locations of soil borings and monitoring wells and the elevation of the top of the PVC <br />casings is usually surveyed and tied into permanent markers, if readily available. Survey <br />accuracy is 0.1 foot for the "x" and "y" coordinates and .01 foot for the "z" coordinate. The <br />FWR-92-04 Page A-3 <br />Copyright 1992 HIeinfelder, Inc. <br />
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