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<br />I <br />I <br />. <br />I <br />I <br />. <br />I <br />- <br />I <br />- <br />- <br />I <br />- <br />- <br />- <br /> <br />, <br /> <br /> <br />~ <br /> <br /> <br />, <br /> <br />1408 <br /> <br />QUALITY ASSURANCE I QUALITY CONTROL <br /> <br />SAMPLE COLLECTION METHODS <br /> <br />All samples were collected in accordance with the Non-Point Source Task Force protocol <br />for sampling of ground water. Samples were collected from existing wells via outside hydrants or <br />whatever means available prior to any type of treatment (i.e. water softener), As a rule of thumb, <br />three times the volume of water in the well casing plus any volume contained within the <br />associated piping was purged prior to sampling, Rather than attempt to calculate these volumes, <br />a determination of when fresh formation water has reached the point of sampling was verified by <br />measuring pH, conductivity and temperature, A field portable instrument for measuring pH, <br />conductivity and temperature was used for this purpose at each well site, For each well, the pH, <br />conductivity and temperature were measured at periodic intervals (approximately every 5 <br />minutes) while the well was being purged, Water samples were collected when solution chemistry <br />of the ground water had stabilized such that three consecutive readings were within 5 %, It can <br />be reasonably assumed that a stabilization in the values of these parameters indicates that the <br />casing and piping have been purged and fresh formation water had reached the sampling point. <br /> <br />Negative bias (loss of constituent) is of significant concern in sampling for volatile <br />compounds. Therefore, great care was taken in sample collection to minimize degassing by <br />operating the sampling port at a low volume, Samples for volatile constituents and those samples <br />which require field filtration were collected first. Samples for nitrate and inorganic analysis were <br />collected next, Samples collected for dissolved metals analysis were filtered in the field with a <br />0.45 micron size filter, <br /> <br />In addition, the sampling team collected quality assurance samples consisting of field <br />blanks, periodic duplicate samples, and spiked samples, Field blanks were utilized for field <br />QA/QC performance and subjected to all conditions to which the samples were exposed, <br />Duplicate and spiked samples were prepared for lab calibration checks, <br /> <br />The following types of samples were provided for quality assurance: <br /> <br />1, Field Blank <br /> <br />A blank ground water sample was periodically collected to check field <br />decontamination procedures, The blank was prepared by pouring laboratory <br />supplied deionized water through decontaminated sampling equipment <br />following the collection of possible contaminated samples, <br /> <br />2, Duplicates <br /> <br />Random duplicate groundwater samples were collected to compare laboratory <br />analysis procedures as well as sample collection procedure, <br />