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CLEARWATER GROUP,INC. <br /> Groundwater Monitoring and Sampling Protocols <br /> Prior to begmning,a decontamination area is established Decontamination procedures consist of scrubbing downhole <br /> equipment in an Alconox®solution wash(wash solution is pumped through any purging pumps used),and rinsing in a <br /> fust rmse of potable water and a second rmse of potable water or delonized water if the latter is regtured Any non- <br /> dedicated down hole equipment is decontaminated prior to use <br /> Prior to purging and sampling a well, the static water level is measured to the nearest 0 01 feet with an electronic <br /> water sounder Depth to bottom is 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 w1uch 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 in the bailer SPH may alternatively be measured <br /> with an electronic interface probe Any morutonn&well contammg a measurable tluckness 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 thepprotfect manager Field observations such as well mtegnty as well as <br /> water level measurements and floating product thiclmesses are noted on the Gauging Data/Purge Calculations form <br /> Well Ej= <br /> Each monitoring 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 aquifer If required,parameters such as dissolved oxygen,turbidity,salinity <br /> etc.are also measured Samples are considered representative if parameter stability is achieved Stability is defined as <br /> a change of less than 0 25 pH units, less than 10%change in conductivity in rrucro mhos, and less than 10 degree <br /> centigrade(18 degrees Fahrenheit)change in 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 dunng 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,may be sampled <br /> after fewer than three well volumes have been removed Well purging information is recorded on the Purge Data sheet <br /> All meters used to measure parameters are calibrated daily Purge water is sealed, labeled, and stored on site in <br /> D O T-approved 55-gallon drums After being chemically profiled,the water is removed to an appropriate disposal <br /> facility by a licensed waste hauler <br /> Groundwater Sample Collection <br /> Groundwater samples are collected immediately after purging or,if urgm$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 repurged Samples are collected using 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 n <br /> appro ate laboratory-supplied containers,labeled,documented on a chain of custody <br /> form and placed on ice in a cooler for transport to a state-certified analytical laboratory Analytical detection hmits <br /> match or surpass standards required by relevant local or regional guidelines <br /> 01aal,ty Assurance Procedures <br /> To prevent contamination of the samples,CGI personnel adhere to the followmg 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 degree of <br /> contamination based on histoncal analytical results <br /> • All purging equipment will be thoroughly decontaminated between each well,using the procedures previously <br /> described at the beginning of this section <br /> • During sample collection for volatile organic analysis,the amount of air passinthrough the sample is minimized <br /> This helps prevent the air from stripping the volatiles from the water Sample bottles are filled by slowly running <br /> the sample down the side of the bottle until there is a convex meniscus over the mouth of the bottle The hd is _ <br /> carefully screwed onto the bottle such that no air bubbles are present within the bottle If a bubble is present,the <br /> cap is removed and additional 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 /> I <br /> I[ E <br /> 1 I I I <br /> E CLEARWATFR GROUP,NC 1 E v 96-1 <br /> r' 4 it EI E <br /> Ili <br />