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<br /> <br />Effects of ice on habitat use <br />Ice formation occurred on low-velocity habitats as early as November 11, ' <br />1986, and November 17, 1987. Squawfish were observed by radiotelemetry to <br />move under the ice at the large backwater at RMI 95.7, at the large embayment <br />at RMT 81.1, and along large ice pads in pool and eddy habitat at initial ice <br />formation both years. On the first scheduled trip in December 1986, the main <br />river channel was clogged with floating ice and slush during early morning <br />hours. low-velocity shoreline areas were frozen over. All nine squawfish <br />located on that trip were in habitat areas that were iced over although the <br />main channel would clear of ice by late afternoon. The initial ice over <br />pattern outlined and identified habitat types that were used by squawfish <br />throughout the rest of the winter. Because lower velocity waters were the <br />first to freeze, ice served as a velocity indicator. Squawfish were apparently <br />attracted to these frozen-over law-velocity areas for the cover and security <br />they provided. In addition, large schools of small fish were observed through <br />the thin clear ice near shore, so food may have been an additional attraction. <br />Except for a few open riffle areas the river was completely covered by ice <br />throughout most of the winter (mid December through early March) both years. <br />Ice-out occurred March 7 in 1987 and March 21 in 1988. <br />The initial attraction squawfish have for ice-covered habitats at first <br />ice formation suggests that surface ice provides a protective cover which <br />permits utilization of habitat areas seldom used during other times of the <br /> <br />year. Ice may provide needed security from overhead predators such as hawks , <br />and eagles, allowing squawfish to move into clear, shallow waters to forage <br />with little danger. Ice insulates the water in backwater and embayment <br />habitats maintaining temperatures slightly above freezing while allowing light <br />penetration for photosynthesis. The importance of embayment habitat as a <br />source of primary productivity was indicated by high dissolved oxygen levels <br />of 17 parts per million (ppm) compared to 12 ppm saturation (Table 6). , <br />Schools of small fish were seen through the clear ice swimming along <br />shorelines of shallow embayments and backwaters. Maintenance of these <br />nutrient-rich embayment and backwater areas could be critical to the overall <br />productivity of the winter ecosystem. <br />Oxygen measurements were taken during midwinter the second year to <br />determine if heavy ice and snow cover affected oxygen levels. Some depression <br />of oxygen levels was noted in upstream study areas (Table 6). Reductions in <br />oxygen levels in the main channel may have been due to oxygen demand from <br />sewage inputs from upstream towns. The river recovered to saturation levels <br />at the lower Lily Park study area. Recovery to oxygen saturation was probably <br />assisted by open water in canyon areas (Juniper and Cross Mountain) and by <br />mixing with supersaturated water in embayment habitats similar to the one <br />measured at RU 81.1. <br />Ice cover insulates the river from extremely cold air eratures that <br />occur frequently along the Yampa River. Ice cover reduces formation of <br />excessive amounts of frazil ice which can o=W large volumes of run and pool <br />habitat and when moving in the water column may damage fish gills. <br /> <br />26 1 <br />t