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Last modified
8/16/2009 2:58:24 PM
Creation date
10/4/2006 6:50:25 AM
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Board Meetings
Board Meeting Date
5/23/2005
Description
ISF Section - Spring Creek Instream Flow Appropriation
Board Meetings - Doc Type
Memo
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<br />was recorded by depth. Water levels in wells without loggers were measured several times <br />during the study period. <br />Water chemistrv: Water samples for chemical analysis were collected from each well in the fall <br />of2002. Samples were analyzed at the Soil and Water Testing Laboratory at Colorado State <br />University in Fort Collins, for major cations and anions. Water pH was measured in the field <br />with an Orion Model 250A pH meter, equipped with a combination electrode and calibrated with <br />fresh buffers. <br /> <br />Statistical Analyses: Correlation analysis was used to relate monitoring well water levels to <br />other wells. <br /> <br />Results <br /> <br />Well/StaffGaufJe Installation <br />Well casing lengths are listed in Table I, and their locations are show in the site map <br />(Figure I). Three wells (2,3,4) and the staff gauge (I) had continuous water level loggers. <br />Because the substrate is landslide debris, several wells were constructed from steel well points, <br />driven with a fence post pounder. However, as illustrated later, the hydraulic head was so strong <br />at this site that many driven well points functioned as piezometers. <br /> <br />Table 1. Wells installed at the Spring Creek site. Well numbers (for both PVC and Steel well <br />points), casing lengths, height of casing sticking up above the ground surface, and depth of <br />slotted casing below the soil surface are listed. Weill is the Spring Creek staff gauge. Units are <br />meters. <br /> <br />. <br /> <br />. <br /> <br />Well Casing Length Stick Up Well depth <br />1 <br />2 1.62 0.74 0.88 <br />3(PVC) 1.16 0.84 0.32 <br />3(steel) 2.38 1.16 1.22 <br />4(PVC) 1.48 0.85 0.62 <br />4(Steel) 2.53 1.54 0.99 <br />5 2.38 0.76 1.62 <br />6 1.58 0.67 0.91 <br />7(Steel) 2.38 1.51 0.86 <br />8 2.38 1.58 0.80 <br />9 2.38 1.37 1.01 . <br /> <br />2 <br />
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