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ARCHIVED REPORTS XR0000322
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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BENJAMIN HOLT
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2905
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3500 - Local Oversight Program
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PR0544110
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ARCHIVED REPORTS XR0000322
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Entry Properties
Last modified
2/6/2019 5:09:01 PM
Creation date
2/6/2019 4:58:26 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000322
RECORD_ID
PR0544110
PE
3528
FACILITY_ID
FA0003712
FACILITY_NAME
CHEVRON STATION #94275*
STREET_NUMBER
2905
Direction
W
STREET_NAME
BENJAMIN HOLT
STREET_TYPE
DR
City
STOCKTON
Zip
95207
APN
09760004
CURRENT_STATUS
02
SITE_LOCATION
2905 W BENJAMIN HOLT DR
P_LOCATION
01
P_DISTRICT
002
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 PROBER Well Monitoring System The <br /> INTERFACE PROBE`" 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 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 delonized 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 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 sample Is decanted from the bailer Into laboratory-provided containers (appropriate for <br /> the analyses required) so that there is no headspace in the container;. Samples collected for benzene, <br /> toluene, ethylbenzene, xylene, and total petroleum hydrocarbons (TPH)-as-gasoline analyses are <br /> collected in 40-milliliter 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-0f-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-of-custody <br /> 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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