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Last modified
1/26/2010 12:25:52 PM
Creation date
10/11/2006 9:43:19 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.101.10.D
Description
Colorado River-Water Projects-Glen Canyon Dam/Lake Powell-Glen Canyon Adaptive Management-
Basin
Colorado Mainstem
Water Division
5
Date
6/17/2005
Author
Korman-Hazel-Melis
Title
Effects of the Experimental Fluctuating Flows from Glen Canyon Dam in 2003 and 2004 in the Early Life History Stages of Rainbow Trout in the Colorado River
Water Supply Pro - Doc Type
Report/Study
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<br />were significantly lower than in the previous (0.91 and 0.95) and following intervals (0.87 and <br />0.90). This change may have been caused by the reduction in the daily minimum flow from 10 <br />to 5 kcfs in early-September. However, it is also possible that the decrease in survival we <br />estimated was a natural occurrence, possibly driven by a normal ontogenetic habitat shift <br />and/or density-dependent mortality. In steep habitats, weekly survival rates dropped from 0.90 <br />for the period spanning early-September to early-November, to 0.59 for the period between <br />November and December. This change was likely related to the 42.5 kcfs Beach Habitat- <br />Building Flow (BHBF), although it could also have been caused by a natural or flow-induced <br />habitat shift rather. Uncertainty in survival rate estimates were generally larger in low angle <br />habitats because of lower sample size. Hatch timing-patterns estimated from the model were <br />highly uncertain when survival rates were allowed to vary among sample periods. The <br />juvenile stock synthesis modeling approach we have developed represents a potential advance <br />in monitoring the response ofsalmonid populations to habitat alterations. However, we <br />caution that it does not replace the need to track trends in the adult population. Without this <br />supporting data, it will be uncertain whether a measured change in the mortality at an early <br />juvenile stage will be compensated by a subsequent change in density-dependent mortality. <br /> <br />Exposed gravels and cobbles above 8 kcfs were generally much too coarse and poorly <br />sorted to support spawning between Lees Ferry and the confluence with the Little Colorado <br />River. We observed a handful of very small areas (10-400 m2) that contained appropriate <br />grain sizes for spawning, however no redds were obseJVed at any of these locations. Due to <br />high turbidity we were unable to survey for spawning habitat or redds in Marble Canyon <br />below the daily minimum flow elevation of 8 kcfs on the April 2004 trip. In June 2004 water <br />clarity was adequate and suitable spawning substrate below 8 kcfs was found at a number of <br />locations in Marble Canyon, with the majority oflarger sites located between the confluence <br />ofNankoweep Creek and Kwagunt rapid (river miles 52 and 56, respectively). The vast <br />majority of these sites were located at the downstream end of rimes or small rapids at depths <br />of3-10 m at a discharge ofca. 9 kcfs. Nankoweep Creek was accessible to fish in the <br />Mainstem Colorado River in 2004 and could support at least a few thousand spawners <br />between January and early-February when water temperatures are suitable. We did not catch <br /> <br />IV <br /> <br />" <br /> <br />. <br /> <br />. <br /> <br />. <br />
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