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ARCHIVED REPORTS_XR0011469
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545174
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ARCHIVED REPORTS_XR0011469
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Last modified
1/13/2020 3:20:45 PM
Creation date
1/13/2020 2:26:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011469
RECORD_ID
PR0545174
PE
3528
FACILITY_ID
FA0004965
FACILITY_NAME
CHEVRON USA (INACT)
STREET_NUMBER
3246
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
14341001
CURRENT_STATUS
02
SITE_LOCATION
3246 E FREMONT ST
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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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 PROBI_" Well Monitoring System. The <br /> INTERFACE PROBE" Well Monitoring System is a haul 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. If separate-phase hydrocarbons are detected the <br /> water elevation is adjusted by the following calculation: <br /> (Product thickness) x (0.8) + (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 deionized water before monitoring each well. <br /> Groundwater Sampling <br /> Before 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 deionized 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 sample 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-miliilfter vials fitted with Teflon® septum(ids. 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 /> 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-.6f-custody <br /> i� record. <br /> Trip blanks (TBLBs) 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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