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ARCHIVED REPORTS_XR0002852
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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HAMMER
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3555
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3500 - Local Oversight Program
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PR0545252
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ARCHIVED REPORTS_XR0002852
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Last modified
1/31/2020 3:09:47 PM
Creation date
1/31/2020 11:50:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002852
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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EHD - Public
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FIELD PROTOCOL <br /> Conventional Sampling Technique <br /> Before the static groundwater level from the Monitoring Wells is measured, wells are opened <br /> and allowed to equilibrate. The Depth To Water (DTW) and floating product level, if present, in <br /> each well that contained water is then measured with a Solonist Water level Indicator and a <br /> KECK Interface Probe — 100', respectively. These instruments are accurate to the nearest 0.01 <br /> foot. If necessary, groundwater depths are subtracted from wellhead evaluations, including <br /> corrections for product thickness, for gradient evaluation by multiplying product thickness (PT) <br /> by a correction factor 0.8 and subtracting from the DTW (Adjusted DTW=DTW— [PT x 0.8]). <br /> Water samples collected for subjective evaluation, i.e. measurable floating hydrocarbon product <br /> (if present), are collected by gently lowering approximately half the length of a new disposable <br /> bailer past the air-water interface (if possible) and collecting a sample from near the surface of <br /> 1 the water in the well. <br /> Prior to collection of groundwater samples, at least three well casing volumes are purged with <br /> either a powered pump or bailers. Temperature, pH and conductivity are measured with a <br /> Horiba Water Quality Monitor Model U-22XD for each well casing volume. When the <br /> measured parameters are stabilized, the groundwater sample is collected. The quantity of water <br /> purged from each well is calculated as follows: <br /> 1 Well Casing Volume (gal) =n x r2 x h x 7.48 <br /> h=Total Well Depth—DTW. <br /> where r is radius of the well casing (feet), h is column of water in the well (feet) and 7.48 is the <br /> conversion factor from cubic feet to gallons. The number of well casing volumes removed=total <br /> gallons of water purged/gallons in 1 well casing volume. <br /> ' After purging, each well is allowed to recharge to at least 80% of the initial water level. Water <br /> samples are collected with a new disposable bailer, and carefully poured into 40-milliliter (ml) <br /> glass vials preserved with hydrochloric acid. The vials are filled so as to produce a positive <br /> meniscus and sealed with a cap containing a Teflon® septum, and examined for air bubbles to <br /> avoid headspace that would allow volatilization to occur. The labeled samples are promptly <br /> transported on ice in a thermally insulated ice chest, accompanied by a Chain of Custody Record, <br /> ' to a California-certified laboratory. <br /> 1 <br />
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