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ARCHIVED REPORTS XR0000628
Environmental Health - Public
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EHD Program Facility Records by Street Name
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BENJAMIN HOLT
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3128
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3500 - Local Oversight Program
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PR0544112
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ARCHIVED REPORTS XR0000628
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Last modified
2/7/2019 4:41:01 PM
Creation date
2/7/2019 3:32:28 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000628
RECORD_ID
PR0544112
PE
3528
FACILITY_ID
FA0005145
FACILITY_NAME
EXXON COMPANY USA
STREET_NUMBER
3128
Direction
W
STREET_NAME
BENJAMIN HOLT
STREET_TYPE
DR
City
STOCKTON
Zip
95207
APN
09523002
CURRENT_STATUS
02
SITE_LOCATION
3128 W BENJAMIN HOLT DR
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Artesian Environmental Consultants, Inc. <br /> .». Standard Operating Procedures <br /> GROUNDWATER LEVEL MEASURING, PURGING AND SAMPLING <br /> Prior to groundwater sampling,static water level measurements are recorded for <br /> each well using a battery-powered sounder with a precision of plus or minus 0.0 1 <br /> feet. All measurements are recorded as depth-to-water from the surveyed <br /> measuring point at the top-of-casing. Depth-to-water readings are converted to <br /> water level elevations referenced to the USGS mean sea level datum. - <br /> Then each well is purged by evacuating a minimum of three to five well-casing <br /> volumes of <br /> » susing <br /> dedicated <br /> punrchloride <br /> e unpfesterile dispoable bailer or stainless steel pup. Dr gpigigoa h well <br /> and prior to sampling,discharge water temperature, specific conductivity, and pH <br /> measurements are recorded and are allowed to stabilize. Stabilized measurements <br /> indicate that formation water has entered the well. The groundwater sample is <br /> taken when the water level in the well recovers to 80% of its static level. <br /> Following purging,a groundwater sample is collected in accordance with <br /> " California Regional Water Quality Control Board(RWQCB)Procedures described <br /> in the Leaking Underground Fuel Task(LUFTj Field Malural, the Tri-Regional <br /> Board Staff Recommend for Prelimi naryEvaluation ord ltii�estigation of <br /> Underground Tank Sites, and local regulatory guidelines. <br /> A groundwater sample is first collected and checked for the presence of free <br /> product in the sampling bailer. Thickness of possible free product is measured <br /> rrd <br /> using an electronic interface probe with a plus or minus 0,01 foot detection Ii <br /> Groundwater. are collected using a pre-cleaned teflon or stainless steel <br />�w bailerui <br /> eq pped with a ball-check valve, and sample containers are filled directly <br /> from the bailer as soon after purging as possible. <br /> Agitation is minimized during sample retrieval and sample transfer to laboratory <br /> Prepared sample containers in order to minimize sample aeration. Groundwater- <br /> samples to be analyzed are carefully decanted into laboratory-prepared,40- <br /> , .milliliter volatile organic analysis(VOA)vials. The VOA vials are filled <br /> completely, leaving no headspace,and are capped and sealed with 'Teflon-lined <br /> lids. Additional groundwater samples may be collected in 1 liter bottles. All <br /> samples are labeled and stored in an ice chest with crushed ice to maintain a <br /> constant temperature of 4 degrees Celsius. A thermometer is kept in the ice chest <br /> to ensure that the proper temperature is maintained. The samples are then <br /> delivered under chain-of-custody to a state-certified hazardous materials testing <br /> laboratory. <br /> N Monitor well purge water is properly stored on-site pending off-site disposal. <br />
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