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• r u <br /> CLEARWATER <br /> G R O U P [ \ C <br /> frro vurtrarntat Srrr itis <br /> Prior to purging and sampling a well, the static water level is measured to the nearest 0 01 feet <br /> with an electronic water sounder Depth to bottom is typically measured once per year, at the <br /> request of the project manager, and during Clearwater's first visit to a site If historical <br /> analytical data are not available, with which to establish a reliable order of increasing well <br /> contamination, the water sounder and tape will be decontaminated between each well If <br /> floating separate-phase hydrocarbons (SPH) are suspected or observed, SPH is collected using a <br /> clear, open-ended product bailer, and the tluckness is measured to the nearest 0 01 feet in the <br /> bailer SPH may alternatively be measured with an electronic interface probe Any monitoring <br /> well containing a measurable thickness of SPH before or during purging is not additionally <br /> purged and no sample is collected from that well Wells containing a hydrocarbon sheen are <br /> sampled unless otherwise specified by the project manager Field observations such as well <br /> integrity as well as water level measurements and floating product thicknesses are noted on the <br /> Gauging Data/Purge Calculations form <br /> Well Purziri <br /> Each monitoring well to be sampled is purged using either a PVC bailer or a submersible pump <br /> Physical parameters (pH, temperature and conductivity) of the purge water are monitored <br /> during purging activities to assess if the water sample collected is representative of the <br /> aquifer If required, parameters such as dissolved oxygen, turbidity, salinity etc are also <br /> measured Samples are considered representative if parameter stability is achieved <br /> Stability is defined as a cnange of less than 0 25 pH units, less than 10% change in conductivity <br /> i in micro mhos, and less than 1 0 degree centigrade (1 8 degrees Fahrenheit) change in <br /> temperature Parameters are measured in a discreet sample decanted from the bailer <br /> separately from the rest of the purge water Parameters are measured at least four tunes during <br /> purging, initially, and at volume intervals of one well volume Purging continues until three <br /> well casing volumes have been removed or until the well completely dewaters Wells which <br /> dewater or demonstrate a slow recharge, may be sampled after fewer than three well volumes <br /> have been removed Well purging information is recorded on the Purge Data sheet All meters <br /> used to measure parameters are calibrated daily Purge water is sealed, labeled, and stored on <br /> site in D O T-approved 55-gallon drums After being chemically profiled, the water is <br /> removed to an appropriate disposal facility by a licensed waste hauler <br /> roundwa er Sample Collection <br /> Groundwater samples are collected immediately after purging or, if purging rate exceeds well <br /> recharge rate, when the well has recharged to at least 80% of its static water level If <br /> recharge is extremely slow, the well is allowed to recharge for at least two hours, if <br /> practicable, or until sufficient volume has accumulated for sampling The well is sampled <br /> within 24 hours of purging or repurged Samples are collected using polyethylene bailers, <br /> either disposable or dedicated to the well Samples being analyzed for compounds most <br /> sensitive to volatilization are collected first Water samples are placed in appropriate <br /> laboratory-supplied containers, labeled, documented on a chain of custody form and placed on <br /> ice in a cooler for transport to a state-certified analytical laboratory Analytical detection <br /> limits match or surpass standards required by relevant local or regional guidelines <br /> CLEARWATER GROUT',INC 4 August 26, 1996 <br />