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ARCHIVED REPORTS XR0009968
Environmental Health - Public
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EHD Program Facility Records by Street Name
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EL DORADO
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7906
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2900 - Site Mitigation Program
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PR0540858
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ARCHIVED REPORTS XR0009968
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Last modified
8/1/2019 12:32:23 PM
Creation date
8/1/2019 10:59:51 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009968
RECORD_ID
PR0540858
PE
2960
FACILITY_ID
FA0023360
FACILITY_NAME
ARCO SERVICE STATION #2130
STREET_NUMBER
7906
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95210
CURRENT_STATUS
01
SITE_LOCATION
7906 N EL DORADO ST
QC Status
Approved
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EHD - Public
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sampling, equipment surfaces that were placed in the well or came into contact with groundwater <br /> during field sampling were steam cleaned with deionized water before the next well was purged <br /> or sampled <br /> Water Level, Floating Hydrocarbon, and Total Well Depth <br /> Measurements <br /> Before purging and sampling occurred, the depth to water, floating hydrocarbon thickness, and <br /> the total well depth were measured using an oil/water interface measuring system The oil/water <br /> interface measuring system consists of a probe that emits a continuous audible tone when <br /> immersed in a nonconductive fluid, such as oil or gasoline, and an intermittent tone when <br /> immersed in a conductive fluid, such as water The floating hydrocarbon thickness and water <br /> Ievel were measured by lowering the probe into the well Liquid levels were recorded relative to <br /> the tone emitted at the groundwater surface The sonic probe was decontaminated by being rinsed <br /> with deionized water or steam cleaned after each use A bottom-filling, clear Teflon bailer was <br /> used to verify floating hydrocarbon thickness measurements of less than 0 02 foot Alternatively, <br /> an electric sounder and a bottom-filling Teflon bailer may have been used to record floating <br /> hydrocarbon thickness and depth to water <br /> The electric sounder is a transistorized instrument that uses a reel-mounted, two-conductor, <br /> coaxial cable that connects the control panel to the sensor Cable markings are stamped at 1-foot <br /> . intervals The water level was measured by lowering the sensor into the monitoring well A low- <br /> current circuit was completed when the sensor contacted the water, which served as an <br /> electrolyte The current was amplified and fed into an indicator light and audible buzzer, <br /> signaling when water had been contacted A sensitivity control compensated for highly saline or <br /> conductive water The electric sounder was decontaminated by being rinsed with deionized water <br /> after each use The bailer was lowered to a point dust below the liquid level, retrieved, and <br /> observed for floating hydrocarbon <br /> Liquid measurements were recorded to the nearest 0 01 toot on the depth to water/floating <br /> product survey form The groundwater elevation at each monitoring well was calculated by <br /> subtracting the measured depth to water from the surveyed elevation of the top of the well <br /> casing (Every attempt was made to measure depth to water for all wells on the same day ) Total <br /> well depth was then measured by lowering the sensor to the bottom of the well Total well depth, <br /> used to calculate purge volumes and to determine whether the well screen was partially <br /> obstructed by silt, was recorded to the nearest 0 1 foot on the depth to water/floating product <br /> survey form <br /> Well Purging <br /> If the depth to groundwater was above the top of screens of the monitoring wells, then the wells <br /> were purged Before sampling occurred, a polyvinyl chloride (FVC) bailer, centrifugal pump, <br /> low-flow submersible pump, or Teflon bailer was used to purge standing water in the casing and <br /> gravel pack from the monitoring well Monitoring wells were purged according to the protocol <br /> Cp1D 1Q MRIARCOIISTQ9912130Q199 DOC-98\Esg 1 A-2 <br />
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