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ARCHIVED REPORTS_XR0002905
EnvironmentalHealth
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HAMMER
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3500 - Local Oversight Program
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PR0545252
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ARCHIVED REPORTS_XR0002905
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Last modified
1/31/2020 3:26:07 PM
Creation date
1/31/2020 2:01:11 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002905
RECORD_ID
PR0545252
PE
3528
FACILITY_ID
FA0002232
FACILITY_NAME
QUIK STOP MARKET #3132*
STREET_NUMBER
3555
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
071-180-20
CURRENT_STATUS
02
SITE_LOCATION
3555 W HAMMER LN
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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,• Tracer Research Corporation <br /> contamination. <br /> ' Groundwater samples were collected in 40 nil VOA vials that were filled to <br /> exclude air and capped with Teflon-lined septa caps. Approximately half of the liquid <br /> Iin the bottle was decanted, the vials were shaken vigorously, and a sample of the <br /> headspace from the container was injected into the gas chromatograph (GC). <br /> IHeadspace analysis is the preferred technique when a large number of water <br /> samples are to be performed daily. The method is more time efficient for the <br /> measurement of volatile organics than direct injection of the water sample into the GC <br /> because there is less chance of semi-volatile and non-volatile organics contaminating <br /> the system Depending upon the partitioning coefficient of a given compound, the GC <br /> may be more sensitive to headspace analysis than to direct injection analysis. The <br /> precision and accuracy of both methods are similar. <br /> 5.0 ANALYTICAL PARAMETERS <br /> The GC was calibrated for headspace analysis by decanting 20 ml of the <br /> known standard, leaving approximately the same amount of headspace as in the water <br /> I headspace samples. The standard bottle was resealed and shaken vigorously for 30 <br /> seconds. An analysis of the headspace in the bottle determined the Response Factor <br /> I (RF) which was then used to accurately estimate the standard concentrations. <br /> The GC was also calibrated for soil gas analysis by comparing the detector's <br /> response to a known aqueous standard to the detector's response to the soil gas vapor. <br /> The instrument calibrations were checked periodically throughout each day to monitor <br /> the response factor and retention time. <br /> I <br /> 5.1 Analyte Class <br /> ' The soil gas and groundwater samples were analyzed for the following <br /> analyte class and compounds: <br /> I <br /> Analyte Class: Hydrocarbon <br /> benzene, toluene, ethylbenzene, and xylenes (BTEX) <br /> total volatile hydrocarbons (TVHC) <br /> I - <br /> May�..2� 1992 Page 3 1-92-358 <br />
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