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Kennedy/Jenks Consultants <br /> the calculated "stagnant water" volume include the water contained in the pores space of the <br /> wetted portion of the monitoring well filter pack in addition to the casing/screen. If this is a <br /> requirement, it should be defined in the project-specific sampling requirements. <br /> d. If light non-aqueous phase liquid (LNAPL) is potentially present, measure the depth and <br /> thickness of the LNAPL and the static water level using a multiphase interface monitoring <br /> probe. Use one of the following devices for purging: <br /> (1) Bladder pump: adjust the pump intake at a depth approximately equal to the middle or <br /> just slightly below the middle of the well screen interval or water column unless another <br /> position is justified based on site-specific conditions. <br /> (2) Peristaltic pump: place the pump intake at a depth equal to the approximate middle or <br /> just slightly above the middle of the well screen interval or water column unless another <br /> position is justified based on site-specific conditions. Note: If degassing of water is <br /> occurring when sampling with a peristaltic pump, alternative types of sampling <br /> equipment should be used for volatile organic compound (VOC) or volatile petroleum <br /> hydrocarbon (VPH) sample collection. <br /> (3) Inertial pump: place the pump intake at a depth approximate to the middle or just <br /> slightly below the middle of the well screen interval or water column unless another <br /> position is justified based on site-specific conditions. Note: Some studies suggest that <br /> the use of inertial pumps for purging and/or sampling may produce a low bias when <br /> collecting samples for VOC and VPH analyses. This should be considered along with <br /> regulatory requirements when selecting an inertial pump for purging and/or sampling. <br /> (4) Submersible pump: place the pump intake at a depth approximate to the middle or just <br /> slightly below the middle of the well screen interval unless another position is justified <br /> based on site-specific conditions. <br /> (5) Pre-cleaned or disposable bailers. Note: The use of bailers for low-flow <br /> purging/sampling is not appropriate. <br /> (6) Another suitable purging/sampling device may be selected for use depending upon <br /> project requirements. <br /> 2. Monitoring Well Purging and Sampling. When purging of a monitoring well prior to sampling <br /> is appropriate and/or required, purge the well using either (a) wetted-casing-volume-based <br /> purging or (b) low-flow purging as described in the following sections. If a well exhibits evidence <br /> of slow recharge, or produces excessively silty water, etc., the well may need to be <br /> redeveloped. <br /> a. Wetted-casing-volume-based purging. <br /> (1) Establish a purging rate to pump or bail approximately three wetted-casing volumes of <br /> groundwater without dewatering the well. <br /> (2) If using a pump, set-up the discharge tubing, flow-through cell, water quality meter, and <br /> purge water collection container. If turbidity is measured, collect the sample for turbidity <br /> measurement after groundwater passes through the flow-through cell in the vial <br /> provided with the turbidity meter. If using a bailer, maintain a clean plastic container <br /> next to the well for collecting observation samples. Begin purging the well. <br /> Monitoring Well Installation Work Plan, D-3 <br /> Barrel Ten Quarter Circle Land Company, Escalon, California <br /> \1SFO\Groups\I S-Group\Admi n\Job\03\0301 18.27_BTQ CLC\09-Reports\M W-Install-W Pln\Appendi x\.;PP_D.doc <br />