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Equipment Cleaning <br /> Before the sampling event was started, equipment that was used to sample groundwater is <br /> disassembled and cleaned with detergent water and then rinsed with deionized water. <br /> During field sampling, equipment surfaces that were placed in the well or came into <br /> contact with groundwater during field sampling were steam cleaned with deionized water <br /> before the next well was purged 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 <br /> thickness, and the total well depth were measured using an oil/water interface measuring <br /> system. The oil/water interface measuring system consists of a probe that emits a <br /> continuous audible tone when immersed in a nonconductive fluid, such as oil or gasoline, <br /> and an intermittent tone when immersed in a conductive fluid, such as water. The <br /> floating hydrocarbon thickness and water level were measured by lowering the probe into <br /> the well. Liquid levels were recorded relative to the tone emitted at the groundwater <br /> surface. The sonic probe was decontaminated by being rinsed with deionized water or <br /> steam cleaned after each use. A bottom-filling, clear Teflon® bailer was used to verify <br /> floating hydrocarbon thickness measurements of less than 0.02 foot. Alternatively, an <br /> 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, <br /> two-conductor, coaxial cable that connects the control panel to the sensor. Cable <br /> markings are stamped at 1-foot intervals. The water level was measured by lowering the <br /> sensor into the monitoring well. A low-current circuit was completed when the sensor <br /> contacted the water, which served as an electrolyte. The current was amplified and fed <br /> into an indicator light and audible buzzer, signaling when water had been contacted. A <br /> sensitivity control compensated for highly saline or conductive water. The electric <br /> sounder was decontaminated by being rinsed with deionized water after each use. The <br /> bailer was lowered to a point just 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 <br /> water/floating product survey form. The groundwater elevation at each monitoring well <br /> was calculated by subtracting the measured depth to water from the surveyed elevation of <br /> the top of the well casing. (Every attempt was made to measure depth to water for all <br /> wells on the same day.) Total well depth was then measured by lowering the sensor to <br /> the bottom of the well. Total well depth, used to calculate purge volumes and to <br /> determine whether the well screen was partially obstructed by silt, was recorded to the <br /> nearest 0.1-foot on the depth to water/floating product survey form. <br /> R[O A <br /> SAC:\N:\Consulting\data\Shared\Projects\PJ8\809251.aa.doc-00\ta:1 <br /> 809251 <br />