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.y <br /> "f <br /> Claytart <br /> - E�'1'IHOY.StENTAL <br /> CONSULTANTS <br /> screens and casings used are in a contaminant-free condition when placed in the ground. No <br /> thread lubrication is used, other than teflon tape, for connecting the casing segments. <br /> Wells extend at least 10 feet into the upper saturated zone, but do not extend through any <br /> clay layers greater than S feet that are below the shallow water table. Factory-slotted casing <br /> •- is used throughout and extends at least 2 feet above the permeable water-bearing zone. The <br /> top of the well is solid casing. The annular space of the borehole is backfilled with washed, <br /> kiln-dried sand to a point at least 1 foot above the slotted screen. A seal above the filter <br /> pack is formed by placing a 1- to 2-foot layer of bentonite pellets on top of the sand. The <br /> bentonite pellets are moistened by pouring clean tap water down the hole so that they 5-an <br /> expand and seal the annulus. A neat cement grout is placed above the bentonite seal and <br /> brought to the ground surface. <br /> Well casings are protected from surface contamination, accidental damage, and „ authorized <br /> entry or tampering with water-tight locking caps on the well casings. The caps are usually <br /> ssurrounded by a concrete vault. Wells are clearly identified with a metal tag or other device <br /> where the following information is recorded: well number, depth to water, depth of well, <br /> casing data including Iocation of screened interval. <br /> The well seal in newly developed wells must set up for 48 to 72 hours prior to development. <br /> i Since development of the well can volatilize contaminants present, the well must also settle <br /> for at least 48 to 72 hours between development and the first purging/sampling incident. <br /> All monitoring wells are initially developed to clean the well and stabilize sand, gravel, and <br /> disturbed aquifer materials around the screened internal perforations. Wells are developed <br /> by pumping (or bailing) and surging until water turbidity and specific conductance stabilize: <br /> In some cases,where wells are installed iLrl low permeability formations and the wells purge <br /> ' <br /> dry, the well is allowed to recover er and is purged dry three times. Clean tap water is <br /> introduced into the well if it does not°recover rapidly enough. <br /> Pending results by laboratory analysis, purge water from well development and sampling is <br /> placed into DOT-approved drums, labeled with the name of the site, address, well number, <br /> iE and left at the site. 'Uncontaminated water may be disposed of by the client. Water found to <br /> contain levels of contaminants above local or state action levels requires that the client <br /> i dispose of it in accordance with hazardous waste requirements. At the client's request, we <br /> can assist with the disposal of contaminated purge water. <br /> ... ........... <br /> a � To collect a representative sample of the groundwater,stagnant water within the well casing <br /> € and filter <br /> � material must be burped and fresh aquifer water allowed to replace it. The water is <br /> purged from the well by pumping or bailing at least three well volumes. Well volumes a-e <br /> calculated by measuring depth to groundwater to the nearest 0.01 Fant upon arrival at the <br /> well before any purging has begun. Groundwater samples are collected only after purging has <br /> 3 <br /> am"dnv <br />