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Last modified
1/26/2010 12:31:34 PM
Creation date
10/11/2006 10:31:38 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8170
Description
Arkansas Basin Water Quality Issues
State
CO
Basin
Arkansas
Water Division
2
Date
1/1/1996
Author
Bradford Austin
Title
Report to the Commissioner of Agriculture - Colorado Department of Agriculture - Ground Water Monitoring Activities - Arkansas River Valley Alluvial Aquifer - 1994-1995
Water Supply Pro - Doc Type
Report/Study
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<br />I: <br />I <br />, <br />. <br />- <br />- <br />, <br />- <br /> <br />I <br /> <br />I <br /> <br />0299 <br />QUALITY ASSURANCE / 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 oftreatrnent (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 ofthese parameters indicates that the <br />casing and piping have been purged and fresh formation water had reached the sampling point. <br /> <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 />I <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 />QNQC 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 /> <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 />
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