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CLEARWATER GROUP, INC <br /> Groundwater Manitonng and Sampling Protocols <br /> w t t P <br /> Prior to beguvrungg,a decontamination area is established Decontamination procedures consist of scrubbing downhole <br /> giiprtient in an Alconox®solution wash(wash solution is pumped through any purling pumps used),and nnsmg in a <br /> first raise of potable water and a second rinse of potable water or deioruzed water if the latter is required Any non- <br /> dedicated down hole equipment is decontarrunated prior to use <br /> Prior to purging and sampling a well, the static water level is measured to the nearest 0 Ol feet with an electronic <br /> water sounder Depth to bottom ss typically measured once per year,at the request of the project manager,and during <br /> Clearwater's first visit to a site If historical analytical data are not available, with which to establish a reliable <br /> order of increasing well 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 clear, open-ended <br /> product bailer,and the thickness is measured to the nearest 0 01 feet irn the bailer SPH may alternatively be measured <br /> with an electronic interface probe Any monitoring well contairung a measurable thickness of SPH before or during <br /> purging is not additionally purged and no sample is collected from that well Wells containing a hydrocarbon sheen <br /> are sampled unless otherwise specified by the project manager Field observations such as well integrity as well as <br /> water level measurements and floating product thicknesses are noted on the Gauging Data/Purge Calculations form- <br /> Well Pur—�� <br /> Each monitorirng well to be sampled is purged using either a PVC bailer or a submersible pump Physical parameters <br /> (pH, temperature and conductivity)of the purge water are monitored during purging activities to assess if the water <br /> sample collected is representative of the aqucfer If required,parameters such as ddissolved oxygen, turbidity,sah uty <br /> etc are also measured p Samples are considered reresentative if parameter stability is achieved Stability is defined as <br /> a change of Iess than 025 pH units, less than 10F,a change un conductivity in micro mhos, and less than 10 degree <br /> centigrade(1 8 degrees Fahrenheit)change un temperature Parameters are measured in a discreet sample decanted `from <br /> the bailer separately from the rest of the purge water Parameters are measured at least four times during purging, <br /> initially, and at volume intervals of one well volume Purging continues until three well casing volumes have been <br /> removed or until the well completely dewaters Wells which dewater or demonstrate a slow recharge,maybe sampled <br /> after fewer than three well volumes have been removed Well purging information is recorded on the Purge Data sneer <br /> All meters used to measure parameters are calibrated daily Purge water is sealed, labeled, and stored on site m <br /> D O T-approved 55-gallon drurns After being chemically profiled, the water is removed to an appropriate disposal <br /> facility by a licensed waste hauler <br /> Groundwater Sample,Collec ion <br /> Groundwater samples are coLlecred immediately after purging or,if purging rate exceeds well recharge rate,when the <br /> well has recharged to at least 80% of its static water level If recharge is extremely slow, the well is allowed to <br /> recharge for at least two hours, if practicable,or until sufficient volume has accumulated for sampling The well is <br /> sampled within 24 hours of purging or re purged Samples are coLlected usuag polyethylene bailers,either disposable or <br /> dedicated to the well Samples being analyzed for compounds most sensitive to volatilization are collected first <br /> Water samples are placed in ap ropnate laocratory-supplied containers, labeled, documented on a chain or custody <br /> form and placed on ice in a cooler for transport to a state-certified analytical laboratory Analytical detection limits <br /> match or surpass standards required by relevant local or regional guidelines <br /> u <br /> To prevent contamination of the samples,CGI 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 are collected in the expected order of increasing deg ee of <br /> contarnmation based on historical analytical results <br /> • All purging equipment will be thoroughly decontaminated between each well, using the procedures previously <br /> described at the begiruung of this section <br /> • During samole collection for volatile organic analysis,the amount of air passuag through the sample is aururrized <br /> This helps prevent the air from stripping the volatiles from the water Sample bottles are filled b slowLv runrurng <br /> the samole down the side of the bottle until there is a convex meniscus over the mouth of the bottle The lid is <br /> carefully strewed onto the bottle such that no air bubbles are present within the cattle If a bubble is present, the <br /> cap is removed and additronal water is added to the sample container After resealing the sample container, if <br /> bubbles still are present inside, the sample container is discarded and the procedure is repeated with a new <br /> Container <br /> CLAxwATER(aror_ip,INC 1 v 96-1 <br />