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ARCHIVED REPORTS_XR0004371
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2900 - Site Mitigation Program
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PR0506313
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ARCHIVED REPORTS_XR0004371
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Last modified
3/9/2020 7:44:10 PM
Creation date
3/9/2020 9:20:02 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004371
RECORD_ID
PR0506313
PE
2950
FACILITY_ID
FA0000514
FACILITY_NAME
MAIN STREET SHELL*
STREET_NUMBER
1071
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21707011
CURRENT_STATUS
02
SITE_LOCATION
1071 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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CAMBRIA <br /> Water Sampling <br /> • Water samples, if they are collected from the boring, are either collected using a driven Hydropunch® type <br /> sampler or are collected from the open borehole using bailers The ground water samples are decanted into <br /> the appropriate containers supplied by the analytic laboratory Samples are labeled, placed in protective foam <br /> sleeves, stored on crushed ice at or below 4°C, and transported under chain-of-custody to the laboratory <br /> Laboratory-supplied trip blanks accompany the samples and are analyzed to check for cross-contamination <br /> An equipment blank may be analyzed if non-dedicated sampling equipment is used <br /> Grouting <br /> If the borings are not completed as wells,the borings are filled to the ground surface with cement giout poured <br /> or pumped through a tremie pipe <br /> MONITORING WELL INSTALLATION, DEVELOPMENT AND SAMPLING <br /> Well Construction and Surveying <br /> Ground water monitonng wells are installed to monitor ground water quality and determine the ground water <br /> elevation, flow direction and gradient Well depths and screen lengths are based on ground water depth, <br /> occurrence of hydrocarbons or other compounds in the borehole, Stratigraphy and State and local regulatory <br /> guidelines Well scieens typically extend 10 to 15 ft below and 5 ftabove the Static water level at the time <br /> of do(ling However, the well screen will generally not extend into or through a clay layer that is at least three <br /> . Ft thick <br /> Well casing and screen are flush-threaded, Schedule 40 FVC Screen slot size varies according to the <br /> sediments screened, but slots are generally 0 010 or 0 020 inches wide A rinsed and graded sand occupies <br /> the annular space between the boring and the well screen to about one to two ft above the well screen A <br /> two ft thick hydrated bentonite seal separates the sand from the overlying sanitary surface seal composed of <br /> Portland type I,II cement <br /> Well-heads are secured by locking well-c,aps inside traffic-rated vaults finished flush with the ground surface <br /> A stovepipe may be installed between the well-head and the vault cap for additional security <br /> The well tap-of-castng elevation is surveyed with respect to mean sea level and the well is surveyed for <br /> horizontal location with respect to an onsite or nearby offsite landmark <br /> Well Development <br /> Wells are generally developed using a combination of ground water surging and extraction Surging agitates <br /> the ground water and dislodges fine sediments from the sand pack After about ten minutes of surging ground <br /> water is extracted from the well using bailing, pumping and/or reverse air-fitting through an eductor pipe to <br /> remove the sediments from the well Surging and extraction continue until at least ten well-casing volumes <br /> of groundwater are extracted and the sediment volume in the groundwater is negligible This process usually <br /> occurs prior to installing the sanitary surface seal to ensure sand pack stabilization If development occurs <br /> after surface seal installation,then development occurs 24 to 72 hours after seal installation to ensure that the <br /> Portland cement has set up correctly <br /> Page 2 of 3 <br />
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