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a. <br /> Monitoring Well Installation and Development <br /> The monitoring wells will be installed in each borehole by inserting 4-inch-inside- <br /> diameter, Schedule 40 polyvinyl' chloride (PVC) casing''with approximately 20 feet of <br /> 0.020-inch machine-slotted well screen beneath the blank casing. The slotted casing will <br /> extend 15 feet below the water table, .in order to accommodate for seasonal fluctuations. <br /> Screw-on bottom caps will be installed the bottom of each 'well.' The wells will be <br /> designed in the field by.the.on-site geologist.. <br /> To gravel pack each -well, No.. I.sand will be poured directly through the auger as <br /> are being gradually removed from .the borehole. The sand will extend to <br /> the augers Y <br /> g l� <br /> approximately 2 feet above the screen. A, 2-foot -bentonite pellet seal will be placed <br /> immediately above the gravel. pack and -the augers will then be totally- removed. The <br /> remaining annular space of' each well will be filled with cement. Each well will be <br /> completed with an at grade locking box. Typical monitoring well design is illustrated on <br /> Figure 4. <br /> Following installation of each well, the. well will be developed using a centrifugal <br /> pump. The well will be developed until relatively sediment-free water is .produced. <br /> m nt time will field conditions. Water. <br /> The length of develop vary depending a e y p g Aon <br /> produced during development and sampling will be contained' on site. ARCO will be <br /> responsible for the disposal of water .and any recovered petroleum product. Prior to and <br /> following development, the thickness of free product, if any, will be gauged. <br /> When the lead investigating agency deems that monitoring .groundwater quality is no <br /> longer necessary, ARCO will be responsible for .abandonment of the wells. The wells will <br /> be abandoned according to state water well codes (Bulletin 74-81, December 1981). <br /> Groundwater Sampling <br />` Following development of each well, a nitrogen gas-driven bladder pump, stainless <br /> steel bailer, or Teflon bailer will be used to evacuate at least three well volumes of water <br /> before samples are taken. A well volume is defined as the water in the well casing plus <br /> the water in the sand pack with an assumed porosity of 35 percent. The pH; electrical <br /> i <br /> conductivity (EQ, p EC), and temperature -of the water will be measured periodically during the <br /> evacuation of water. Samples will be taken when pH, .EC, and temperature measurements <br /> are stable. Stable measurements do not vary by. more than. 0.1 units. ' Samples will be . <br /> collected in 40-milliliter glass volatile organic- analysis '(VOA) bottles. Sample bottles will <br /> be filled directly from the discharge line of the bladder; pump or from the bailer, and will <br />' be filled to minimize any aeration of the :water. ' A Teflon-lined cap (septa) will be placed <br /> on the bottles, and the VOA bottles will be checked to ensure that no air bubbles remain <br /> within. <br /> All water samples will be labeled and stored as previously described in the soil <br /> samples section, and transported to the.laboratory. . <br />