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lie CLEARWATER GROUP, INC <br />' Groundwater Monitoring and Sampling Field Procedures <br /> Groundwater Monitorin* <br />' Prior to beginning a decontamination area is established Decontamination procedures consist of scrubbing downhole <br /> cquipmcnt in an Alconox0 solution wash (wash solution is pumped through any purging pump, used) and rinsing in a first <br /> antic of potable water and a second rinse of potable water or dwonized water if the latter is required Any non-dcdicated down <br /> hole equipment is decontammated prior to use When using a peivtaltic pump new or dedicated silicon head tube and <br />' polyethylene tubing is used <br /> Piior to purging and sampling a well, the static water level is measured to the nearest 0 0f lett with an electronic watu <br /> sounder Depth to bottom is typically measured once per yeai at the request of the prod"( manager, and during Clearwater~ <br /> lint visit to a site It historical analytical data are not available, with which to eslabltsh a reliable aider of increasing well <br />' contamination the water sounder and tape will be decontaminated between each well it floating separate-phase <br /> Itydroc.vbons (SPH) are suspected or observed SPH is collected using a clear, open-ended product bailer, and the thickness <br /> is mcasuied to the nearest 0 01 feet in the bailer SPH may alternatively he measured with an electronic interface probe <br /> Any monitoring well containing a measurable thickness of SPH before or during purging is not additionally purged and no <br />' sample is collected from that well Wells containing a hydrocarbon sheen are sampled unless otherwise specilted by the <br /> piuJcct manager Field observations such as well integrity as well is water level measurements and floating product <br /> fhtcknesses tic noted on the Gauging Data/Purge Calculations loan <br />' Well Puiginc <br /> Fach monitoring well to be sampled is purged using either a PVC baiter, submersible primp or i peristaltic pump Physical <br /> parameters (pH, temperature and conductivity) of the purge water are monitored during purging activities to assess if the <br /> water sample collected is representative of the aquifer If required parameters such as dissolved oxygen, turbidity salinity <br /> I etc are also measured Samples are considered representative it parameter stability is achieved Stability is defined as a <br /> ch Inge of less than 0 25 pH units less than 10% change in conductivity in micro mhos and less than 1 0 degree centigrade <br /> (1 B degrees Fahrenheit) change in temperature Parameters aic measured in a discreet sample decanted train the bailer <br /> separately horn the rest of the purge water or in a in-line flowthrough cell Parmmeters are measured at least tour times <br /> duimg purging initially, and at volume intervals of one well volume Purging continues until three well casing volumes <br /> h ive been removed or until the well completely dewater Wells which dewater or demonstrate a slow recharge may be <br /> snnpled aftei Ic,wci than three well volumes have been removed Well purging information is recorded on the Purge Data <br /> sheet All meters used to measure parameter are calibrued daily Purge water is scaled, labeled ind stored on site in <br /> D O T-appioved 55-gallon drums Atter being chemically prattled, the water rs removed to in appropriate disposal f icility <br /> by i licensed waste hauler <br /> Gioundwatei Sample Collection <br /> Groundwater samples are collected immediately alter purging or if purging rate exceeds well iecharge rate when the well <br /> has techargcd to at Icist 90% of its static water level It icchaige is extremely slow the well is allowed to iecharge for at <br /> lc ist two hours it practicable, or until sufficient volume has accumulated for sampling The well is sampled within 24 <br /> hours 01 putging or rcpurged Samples are collected using polyethylene bailers, either disposable or dedicated to the well <br /> Samples may also he collected from the pcirstaltic pump tubing Samples being analyzed for compounds most scmrtive to <br /> volatilvation arc collected first Water samples are placed in appropriate laboidtoty-supphcd containers labeled, <br /> documented on a ch tin of custody foim and placed on ice in a cooler for transport to a state-certified anilytical laboratory <br /> Analytical detection limits match or surpass standards required by relevant local or regional guidelines <br /> I <br /> Qu ility Assurance Piocecluics <br /> To prevent contamination of the samples, CCI personnel adhere to the following procedures in the field <br /> A new clean pair of latex gloves are put on prior to sampling each well <br /> Wells are gauged, purged and groundwater samples tic collected in the expected oider of increasing degree of <br /> contamination based on historical analytical results <br /> I All purging equipment will be thoroughly decontaminated between each well, using the procedures previously <br /> cicscrihed at the beginning of this section <br /> • Duung ,ample collection for volatile organic analysis, the amount of air passing through the sample is minimized <br /> This helps pievent the air lrom stripping the volatiles from the water Sample bottles are filled by slowly running the <br /> • sample down the side o1 the bottle until there is a convex meniscus over the mouth of the bottle The lid is carefully <br /> suewecl onto the bottle such that no air bubbles are prescnt within the bottle It a bubble is present the c ip is removed <br /> I <br /> C1 FARwAIERGROUP INC (GWS) I revised November R <br /> I <br />