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ARCHIVED REPORTS_XR0002671
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545259
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ARCHIVED REPORTS_XR0002671
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Entry Properties
Last modified
1/31/2020 4:46:14 PM
Creation date
1/31/2020 3:34:00 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002671
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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GROUNDWATER TECHNOLOGY GROUNDWATER MONITORING AND SAMPLE <br /> COLLECTION PROTOCOL <br /> Groundwater Monitoring <br /> Groundwater monitoring Is accomplished using a INTERFACE PROBEE" Weil Monitoring System The <br /> INTERFACE PROBEE" Well Monitoring System is a hand held, battery operated device for measuring the <br /> depth to separate-phase hydrocarbons and depth to water The INTERFACE PROBE'" Well Monitoring <br /> System consists of a dual-sensing probe which utilizes an optical liquid sensor and electrical <br /> conductivity to distinguish between water and petroleum products <br /> Monitoring is accomplished by measuring from the surveyed top of well casing or grade to groundwater <br /> and separate-phase hydrocarbons If present The static water elevation Is then calculated for each well <br /> and a potentiometric surface map Is constructed It separate-phase hydrocarbons are detected the <br /> water elevation is adjusted by the following calculation <br /> (Product thickness) x (0 8) f (Water elevation) = Corrected water elevation <br /> Groundwater monitoring wells are monitored in order of wells with lowest concentrations of volatile <br /> organic compounds to wells with the highest concentrations, based upon historical concentrations If <br /> separate-phase hydrocarbons are encountered In a well, the product Is visually Inspected to confirm and <br /> note color, amount, and viscosity Monitoring equipment Is washed with laboratory grade detergent and <br /> rinsed with distilled or delonized water before monitoring each well <br /> Groundwater Sampling <br /> aBefore groundwater samples are collected, sufficient water is purged from each well to ensure <br /> representative formation water Is entering the well Wells are purged and sampled in the same order as <br /> monitoring, from wells with the lowest concentrations of volatile organic compounds to wells with the <br /> highest concentrations Wells are purged using either a polyvinyl chloride (PVC) bailer fitted with a <br /> check valve or with a stainless steel submersible Grundfos pump The purge equipment is <br /> decontaminated before use In each well by washing with laboratory grade detergent and tripled rinsing <br /> with delonized or distilled water A minimum of 3 well-casing volumes of water are removed from each <br /> well while pH, electrical conductivity, and temperature are recorded to verify that 'fresh' formation water <br /> Is being sampled and the parameters have stabilized If the well Is low yielding, it may be purged dry <br /> and sampled before 3 casing volumes are purged The wells are then allowed to recharge to <br /> approximately 80 percent of the Initial water level before a sample Is collected <br /> Groundwater samples are collected from each well using a new, prepackaged disposable bailer and <br /> string. The water-kample is decanted from the bailer Into laboratory-provided containers (appropriate for <br /> the analyses required) so that there is no headspace in the containers Samples collected for benzene, <br /> toluene, ethylbenzene, xylene, and total petroleum hydrocarbons (TPH)-as-gasoline analyses are <br /> collected In 40-milliifter vials fitted with Teflon® septum lids Samples are preserved with hydrochloric <br /> acid (HCL) to a pH of less than 2 Dissolved metals samples are filtered through a 0 45-micron paper <br /> filter In the field and preserved as required before submitting to the laboratory for analyses All samples <br /> are labeled Immediately upon collection and logged on the chain-of-custody record Sample label and <br /> chain-of-custody recorded Information Includes the project name and number, sample identification, date <br /> and time of collection, analyses requested, and the sampler's name. Sample bottles are placed In <br /> plastic bags (to protect the bottles and labels) and on Ice (frozen water) In an insulated cooler and are <br /> shipped under chain-of-custody protocol to the laboratory <br /> i <br /> The chain-of-custody record documents who has possession of the samples until the analyses Is <br /> performed Other pertinent Information Is also noted for the laboratory use on the chain-of-custody <br /> record. <br /> Trip blanks (f BLEs) are used for each project as a quality assurance/quality control measure The <br /> TBLBs are prepared by the laboratory and are placed in the Insulated cooler and accompany the field <br /> samples throughout the sampling event <br />
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