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COMPLIANCE INFO_PRE 2019
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2300 - Underground Storage Tank Program
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PR0231219
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COMPLIANCE INFO_PRE 2019
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Entry Properties
Last modified
2/12/2020 5:53:44 PM
Creation date
11/6/2018 9:19:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0231219
PE
2381
FACILITY_ID
FA0002836
FACILITY_NAME
SAN JOAQUIN DELTA COLLEGE DIST
STREET_NUMBER
5151
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
10816001
CURRENT_STATUS
02
SITE_LOCATION
5151 PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
Scanner
KBlackwell
Supplemental fields
FilePath
\MIGRATIONS\P\PACIFIC\5151\PR0231219\COMPLIANCE INFO 1987-2015.PDF
QuestysFileName
COMPLIANCE INFO 1987-2015
QuestysRecordDate
8/15/2017 3:06:13 PM
QuestysRecordID
3580045
QuestysRecordType
12
QuestysStateID
1
Tags
EHD - Public
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k■ KLEINFELDER <br /> • T#e wells are generally screened from 5 feet above to 20 feet below first groundwater. <br /> The screen length is reduced if an aquitard with a minimum thickness of 5 feet is <br /> encountered. If an aquitard is encountered the well is usually terminated 1 to 2 feet into <br /> the aquitard. Effort is made not to screen across two aquifers. If confined aquifer <br /> conditions or high vadose zone contamination is encountered, the well screen is usually <br /> not set above the depth of first encountered ground water. Wells are usually not set in <br /> ares of 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 with the <br /> appropriate clean Lone Star Industries 0/30 or 2/12 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 0/30 <br /> sand may require that the sand be tremmied, using clean water. In this event, a sample of <br /> the tremie water is collected, 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 against <br /> surface water infiltration. <br /> • The remaining annular space is filled to the surface with tremmied cement/bentonite <br /> grout to the surface. <br /> • The wells are secured in a locking stovepipe. The well heads may be enclosed in a <br /> 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 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 or 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 /> draw the sediment from the formation into the filter 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 /> minute (gpm) depending on recharge rate and casing size. Development continues until the <br /> discharge runs relatively clear of fines. Approximately 5 to 10 well volumes are generally <br /> removed tom each monitoring well. Discharge water is stored in 55-gallon drums and left on <br /> site for later discharge or disposal by the client, depending on laboratory results. <br /> After the wells are developed, the aquifer is allowed to equilibrate for at least 24 to 48 hours. <br /> The wells can then be purged and sampled. Purging and sampling may be accomplished with <br /> 20-0232-01/201181514 Page A-4 <br /> 0 2001,Kleinfelder,Inc. December 6,2001 <br />
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