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ARCHIVED REPORTS_XR0002903
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_XR0002903
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Last modified
1/31/2020 3:21:39 PM
Creation date
1/31/2020 2:00:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002903
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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�r <br /> r <br /> indicators for assessing sufficient purging. The purging parameters are measured to <br /> observe stabilization to a range of values typical for that aquifer and well. Stable field <br /> parameters are recognized as indicative of groundwater aquifer chemistry entering the <br /> ' well. Specific conductance (conductivity) meters are read to the nearest ±10 umhos/cm <br /> and are calibrated daily. pH meters are read to the nearest t0.1 pH units and are <br /> calibrated daily. Temperature is read to the nearest 0.1 T. Calibration of physical <br /> ' parameter meters will follow manufacturer's specifications. Collected field data during <br /> purging activities will be entered on the Well Sampling Field Data Sheet. <br /> ' Following purging, the well is allowed to recharge prior to sampling. When recovery <br /> to 80% of the static water level is estimated or observed to exceed two hours, a sample <br /> ' will be collected when sufficient volume is available to fill all sample containers. The <br /> well will be purged slowly enough to minimize the volatilization of organic <br /> contaminants during well recharge. <br /> In wells where free-phase hydrocarbons are detected, the free-phase portion will be <br /> bailed from the well and its volume recorded. If free-phase hydrocarbons persist <br /> through bailing, a groundwater sample will not be collected. <br /> Volatile organic groundwater samples are collected so that air passage through the <br /> sample does not occur or is minimal (to prevent volatiles from being stripped from the <br /> samples). Sample bottles are filled by slowly running the sample down the side of the <br /> ' bottle until there is a positive convex meniscus over the mouth of the bottle. The teflon <br /> side of the septum (in cap) is then positioned against the meniscus, the cap is screwed on <br /> tightly, the sample is inverted, and the bottle is lightly tapped. If a bubble is evident, <br /> ' the cap is removed, more sample is added, and the bottle is resealed. <br /> Chain-of-Custody <br /> Groundwater sample containers are labeled with a unique sample number, location, and <br /> ' date of collection. All samples are logged into a chain-of-custody form and placed in a <br /> secure, chilled ice chest for shipment to a laboratory certified by the State of California. <br /> ' Sample Storage <br /> Groundwater samples collected in the field are stored in an ice chest cooled to <br /> ' approximately 4 °C while in transit to the office or analytical laboratory. Samples are <br /> stored in a refrigerator overnight and during weekends and holidays. The refrigerator <br /> is set to 4 °C and is locked with access controlled by a designated sample custodian. <br /> ' RESNA INDUSTRIES INC. <br /> Groundwater Sampling Protocol <br /> Latest Revision: March 18, 1492 <br /> 1 <br />
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