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ARCHIVED REPORTS_XR0010785
Environmental Health - Public
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EHD Program Facility Records by Street Name
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THORNTON
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9321
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3500 - Local Oversight Program
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PR0545729
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ARCHIVED REPORTS_XR0010785
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Last modified
6/4/2020 12:00:50 PM
Creation date
6/4/2020 11:51:26 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010785
RECORD_ID
PR0545729
PE
3528
FACILITY_ID
FA0002890
FACILITY_NAME
QUIK STOP MARKET #2120*
STREET_NUMBER
9321
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
STOCKTON
Zip
95209
APN
080-180-05
CURRENT_STATUS
02
SITE_LOCATION
9321 N THORNTON RD
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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1 <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 umhoslcm <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 °F 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 /> t 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. Generally, if free-phase hydrocarbons <br /> persist through bailing, a groundwater sample will not be collected unless requested by <br />' the client. <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 stnpped 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 September 18, 1992 <br /> 1 <br />
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