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• field sampling, equipment surfaces that were placed in the well or came into contact with <br /> groundwater during field sampling were steam cleaned with deionized water before the next well <br /> was purged or sampled <br /> Water Leel, 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 /> level 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 foot 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 (PVC) 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 /> sAC1D\QMR\3RDQTR-1\2130Q398 DOC-9ftg 1 A-2 peK au& <br /> Rev 4,518198 <br />