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Last modified
8/11/2009 11:32:56 AM
Creation date
8/10/2009 3:42:40 PM
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UCREFRP
UCREFRP Catalog Number
7610
Author
Wick, E. J. and J. A. Hawkins.
Title
Colorado Squawfish Winter Habitat Study, Yampa River, Colorado, 1986-1987
USFW Year
1987.
USFW - Doc Type
Final Report Year 1.
Copyright Material
NO
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r- <br />(Table it and Figures 24-26). The majority of shallow depths less than 1 foot <br />were from embayment habitat. In the backwater habitat at RMI 95.7 the most <br />commonly used depth was 2 feet. All depths greater than 6 feet were from eddy <br />habitat used by fish B07 at RMI 76.2 (Table 6). The high use of shale;Lhs <br />less than 1 foot c`uld have been due to ice cover. As previously mentioned the <br />overhead ice was probably a security facter allowing fish to venture into more <br />shallow water. Throughout most of the study the ice thickness ranged from 1 <br />to 1.8 feet. If total water and ice depths (water elevation) were considered, <br />the averages would be at least a foot greater. Depth distributions f_U the <br />inner and outer holes were similar to the main a (Table 11 and Figures 27- <br />32). Inner hole depths were slightly shallower (X = 2.3) and outer hole depths <br />were deeper at 2.9 feet than main hole depths. The deep outer hole depths over <br />8 feet are all attributable to fish B07 in the eddy at RMI 76.2. <br />Velocity <br />Velocity histograms were based on measurements taken at 0.6 depth from <br />the bottom-of the ice (Figures 2a and 2b) and were made for the main, inner, <br />and outer holes. Main hole mean velocity was 0.21 feet/second and ranged from <br />0.0 to 1.9 feet/second (Table 12 and Figures 33-35). Inner hole velocity was <br />0.17 feet/second while outer hole velocity averaged 0.26 feet/second. The <br />range of short term data was from 0.0 to 2.2 feet/second while the highest <br />long term velocity was only 0.9 feet/second (Table 12 and Figures 36-41). <br />Substrate <br />Of the 36 possible combinations of clay, silt, sand, gravel, cobble, and <br />boulder substates, 19 were observed throughout the study (Figures 42-50). <br />Gravel-gravel (GRGR) was the most frequently utilized substrate followed by <br />sand-sand (SASA). The dominance of gravel-gravel (GRGR) is interesting since <br />many of the habitats in which it was dominant were 0.0 velocity backwater <br />areas (Table 8). The dominance of sand substrate in the short term data set is <br />probably related to the.dominance of run habitat. <br />26 <br />41 <br /> <br /> <br />• <br />0 <br />0 <br />Habitat <br />Overall, backwater was the most <br />run. Run was the most frequently used <br />(Figures 51-53). <br />commonly used habitat type followed by <br />habitat in the short term data set <br />40 <br />Comparison of 2.5 vs 24 hour data <br />Long and short term data were often different. This could be due to <br />either differences in the sample designs or possibly fish reacting to observer <br />presence. <br />Short term observations would tend to create more data points, creating <br />smoother distributions for final analysis where long term observations tend to <br />stack data over a few data intervals, especially if fish remained at one site <br />for an extended time. Long term data is more subject to compounding observer <br />error. For instance, if a triangulation to a fish location is done incorrectly <br />it could lead to a heavy weighting of incorrect micro-habitat variables in the <br />0 <br />0 <br />0
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