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ARCHIVED REPORTS_XR0002673
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545259
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ARCHIVED REPORTS_XR0002673
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Last modified
1/31/2020 4:47:14 PM
Creation date
1/31/2020 3:36:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002673
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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EHD - Public
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a <br /> GROUNDWATER TECHNOLOGY GROUNDWATER MONITORING AND SAMPLE <br /> COLLECTION PROTOCOL <br /> Groundwater Monitoring <br />' Groundwater monitoring is accomplished using a INTERFACE PROBE'" 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 /> i conductivity to distinguish between water and petroleum products. <br /> r <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 b adjusted adj y s <br /> 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 delonizedd-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, ethyibenzene, xylene, and total petroleum hydrocarbons (TPH)-as-gasoline analyses are <br /> collected in 40-milliliter vials fitted with TeflonO 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 t <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-of-custody <br /> record. <br /> �a•� 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 /> PROTOCOL <br />
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