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I <br /> 10 <br /> use The baler will be lowered to a point just below the liquid level. <br /> Iretrieved, and observed for floating hydrocarbon <br /> Vquwd measurements will be recorded to the nearest 0.01 foot in the field <br /> I logbook. The ground-water elevation at each monitoring well will be cal- <br /> culated by subtracting the measured depth to water from the surveyed <br /> elevation of the top of the well casing (Every attempt will be made to mea- <br /> sure depth to water for all wells on the same day ) Total well depth vAil <br /> then be measured by lowering the sensor to the bottom of the well. Total <br /> well depth, used to calculate purge volumes and to determine whether the <br /> well screen is partially obstructed by silt, will be recorded to the nearest <br /> 0 1 foot in the field logbook. <br /> Well Purging <br /> I Before the sampling event, a polyvinyl chloride baler, low-flow sub- <br /> mersible pump, or Teflon baster will be used to purge standing water in the <br /> casing and gravel pack from the monitoring well. Monitoring wells will be <br /> purged according to the protocol presented in Figure B-1. In most morn- <br /> tonng wells, the amount of water purged before sampling will be greater <br /> than or equal to three casing volumes. Some monitoring wells are <br /> expected to be evacuated to dryness after removing fewer than three cas- <br /> ing volumes These low-yield monitoring wells will be allowed to recharge <br /> for up to 24 hours Samples will be obtained as soon as the monitoring <br /> wells have recharged to a level sufficient for sample collection If insuffi- <br /> cient water has recharged after 24 hours, the monitoring well %nil be <br /> recorded as dry for the sampling event <br /> Ground water purged from the monitoring wells will be contanenzed :n <br /> 55-gallon drums for subsequent disposal. Drums will be stored on site at a <br /> Shell-designated location. <br /> EMCON will arrange for the disposal of the purged ground water and the <br /> removal of drums through Crosby and Overton During storage, drums will <br /> be properly labeled with a Shell drum label <br /> Field measurements of pH, specific conductance, temperature, turbidity <br /> and dissolved oxygen (when requested) will be recorded in a waterproof <br /> field logbook. Figure B-2 shows an example of the Water Sample Field <br /> Data Sheet on which field data are recorded Feld data sheets will be <br /> reviewed for completeness by the sampling coordinator after the sampling <br />�• event is completed. <br /> PRA P91 K022 AOw Rev 0 February 7, 1992 <br />