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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 delomzed water before the next well was purged or <br /> 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 /> unmersed In a nonconductive fluid, such as oil or gasoline, and an uiterrluttent tone when <br /> immersed in a conductive fluid, such as water The floating hydrocarbon thickness and water level <br /> were measured by lowering the probe into the well Liquid levels were recorded relative to the <br /> tone enutted 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, signaling <br /> when water had been contacted A sensitivity control compensated for highly saline or conductive <br /> water The electric sounder was decontaminated by being rinsed with deionized water after each <br /> use The bailer was lowered to a point dust below the liquid level, retrieved, and observed for <br /> 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 casing <br /> (Every attempt was made to measure depth to water for all wells on the same day) Total well <br /> depth was then measured by lowering the sensor to the bottom of the well Total well depth, used <br /> to calculate purge volumes and to detem-une whether the well screen was partially obstructed by <br /> silt, was recorded to the nearest 0 1 foot on the depth to water/floating product 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, low- <br /> flow submersible pump, or Teflon bailer was used to purge standing water in the casing and <br /> 40gravel pack from the monitoring well Monitoring wells were purged according to the protocol <br /> presented in Figure A-1 In most monitoring wells, the amount of water purged before sampling <br /> sACNN\PM,080"8051140 8CS 97\r-bell 1 A-2 Rev 0, 12/29/97 <br />