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Last modified
8/11/2009 11:32:56 AM
Creation date
8/10/2009 3:24:30 PM
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UCREFRP
UCREFRP Catalog Number
7346
Author
Wick, E. J. and J. A. Hawkins.
Title
Colorado Squawfish Winter Habitat Study, Yampa River, Colorado 1986-1988.
USFW Year
1989.
USFW - Doc Type
Fort Collins, Colorado.
Copyright Material
NO
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<br /> <br />Depti, velocity, and substrate utilization <br />Number of observations for total depth, effective depth, and velocity ' <br />were normalized for each year within each habitat type during the winter. <br />Total depth reflected distance from the river bottom to the top of the ice; <br />this measurement included solid ice, packed non-moving frazil, and water <br />(effective depth). <br />Backwater habitats showed the narrowest range of depths used, and pool <br />habitat showed the broadest range and deepest depths. Generally, the <br />; <br />difference between total depth and effective depth reflected surface ice <br />thickness except in run and pool habitat where effective depth was <br />substantially less due to very thick (packed) frazil ice. Highest frequency <br />of use for total depths was 2.0-3.5 feet in backwater, embayment, run, and <br />shoreline habitats. Frequency of effective depth use was highest between 1.0 <br />to 2.0 feet. 'Dotal depths used most frequently in eddy habitat ranged 5.0 to <br />9.5 feet. Effective depths used most frequently in eddy habitat ranged <br />between 3.5 to 9.0 feet. In pool habitat the most frequently used total depth <br />the most frequently used effective depth was 3.0 feet, <br />was 10.0 feet; however <br />, <br />showing the effect of packed frazil ice (Figures 11 and 12). <br />The predominant velocity within backwater, embayment and eddy habitats <br />during the winter was 0.0 ft/s, but a few velocities over 0.0 ft/s indicated <br />fish locations along the interface with the main channel. The positive <br />velocities within eddy habitat indicate fish within the eddy-run interface. <br />The greatest range and highest velocity were found in run habitat. Velocities <br />used most in run and shoreline habitat were 0.0 to 0.4 ft/s. The most <br />frequently used velocity in pool habitat was 0.6 ft/s (Figure 13). These <br />velocities are not fish nose velocities but are mean column velocities taken <br />at 0.6 effective depth. Fish may be utilizing micro-habitats that provide <br />lower velocities. Depth and velocity summaries over extended periods can be <br />misleading because a large number of observations on any given trip or period <br />can heavily influence the over-all frequency. Therefore, depth and velocity <br />are presented below on a trip by trip basis to better reflect habitat use aver <br />time. <br />Most depth mats during the fall period were in ice-free water. <br />Depth measurements which included ice are identified within the appropriate <br />figures. Ice thickens during this time was 0.1 foot. Water depth in <br />backwaters during the fall were between 3.0 and 4.0 feet. Embayment use was <br />similar except for use of shallower 1.5 foot depth. Fish use of the <br />shallowest depths in each habitat may have been facilitated by ice that <br />provided overhead cover. Depth of eddy habitat was greatest at 4.0 and 4.5 <br />feet. Pool depths showed a bimodality at 5.0 and 13.0 feet. lam and <br />shoreline depth utilizations ranged between 3.0 and 4.5 feet (Figure 14). Fall <br />velocities. were mostly 0.0 ft/s in backwater, embayment, eddy, and pool . <br />habitats and 0.5 ft/s in run habitat and 0.3 ft/s in shoreline habitat (Figure ? <br />15). <br />Winter substrate use was segregated by habitat type for each year of the <br />study (Table 7 and 8). of the 36 possible combinations of clay, silt, sand, <br />gravel, cobble, boulder, and bedrock substrates, 21 were observed throughout <br />the 2 years of the study. Sand (SASA) was the most commonly used substrate <br />type in both years of the study. It was the dominant substrate used in run <br />habitat during Winter 1 and in run and pool habitat in Winter 2. During <br />28 <br />
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