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ARCHIVED REPORTS_XR0002653
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545259
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ARCHIVED REPORTS_XR0002653
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Last modified
1/31/2020 4:29:55 PM
Creation date
1/31/2020 3:04:41 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002653
RECORD_ID
PR0545259
PE
3528
FACILITY_ID
FA0004966
FACILITY_NAME
CHEVRON USA (INACT)
STREET_NUMBER
45
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12707037
CURRENT_STATUS
02
SITE_LOCATION
45 E HARDING WAY
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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February 14, 1997 <br /> Page 9 <br /> . State Water Board December 8, 1995 Interim Guidance on Requited Cleanup at <br /> Low-Risk Fuel Sites, RWQCB, January 5, 1996) <br /> Groundwater monitoring well completions between November 1988 and January 1989 <br /> (Wells MW-I through MW-8) were performed by screening across groundwater at <br /> approximately 36 feet bgs The wells varied in total depth of screen from approximately <br /> 39 to 48 feet bgs Groundwater elevations then decreased resulting in all wells becoming <br /> 'dry by October 1991 through approximately October 1994 <br /> Groundwater monitoring well completions between July 1991 and January 1994 (MW-9 <br /> through MW-14, and MW-2R) were constructed by screening between approximately 40 <br /> and 65 (to 75) feet bgs reflecting the decreased groundwater conditions With the + <br /> exception of Well MW-12 (completed between 30 and 65 feet bgs), rising groundwater <br /> 'resulted in the screen intervals of these wells becoming submerged, but also resulted in <br /> gauging and sampling previously dry Wells MWA, and MW-3 through MW-8 <br /> I <br /> The SJCEHD commented that wells with gr eater than 20 feet of scl eel) through the <br /> g7oundwate7 have prohlenis with drhitlon as do wells with screened nitervals below fn st <br /> + wate7 For example, [Well]MW-11 which 1 s scl eened between 43 and 73 feet bgs <br /> currently has a gl oundwate7 level c,,f 37 74 feet hgs, thelefole this well not only has 30 <br /> feet of sc7 eened interval but its screened interval i s approximately 6 feet below the <br /> current groundwater level, representing ilgf7ificant dihition prohlen7s <br /> It is true that with the protocol of purging a well prior to sampling dilution occurs with <br /> increasing screen length No well standard has been maintained which stipulates the <br /> length or diameter of the screen interval Therefore with increased screen lengths, purge <br /> volumes increase, resulting in increased mixing and diluting of contaminant <br /> concentrations during purging <br /> If the source of dissolved contaminants is soil contamination at or <br /> above the water table, then a downward decrease in dissolved <br /> concentration is expected in the formation When a well screened <br /> across such a concentration gradient is purged, ground water with <br /> varying contaminant concentrations will flow into the well throughout <br /> the screen interval Some of the groundwater entering the well may <br /> contain high concentrations of contaminants, some may contain <br /> non-detectable concentrations As a result of mixing within the well <br /> during the recovery period following purging, the concentration at the <br /> top of the water column will consequently be lower than it was before <br /> purging (Ground Water Sarnpling�a Pilot Study of the Effects of <br /> Well Purging, Williams et at , 1995) <br /> 5 <br /> 1 <br /> JI <br /> 1 320133781CLOSCIRE3 <br /> 1 <br />
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