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are ice jams, which typically form in specific locations, rather than appearing throughout the length <br />of the river. Ice jams typically start at diverging river reaches, or places where the river slope changes <br />from steep to mild, and surface transport rate decreases as flow slows and the river deepens. Ice jams <br />often accumulate in narrow, constricted regions, giving the false impression that they originate in <br />these areas. <br />Many types of ice jams have been classified, with considerable literature describing the subject, <br />but there are few quantitative measurements detailing their development. Fundamentally, ice floating <br />downstream arrives at an upstream ice edge or a constricted channel region, and either accumulates <br />on the surface or, at higher velocities (>0.6 m/s), submerges and overturns beneath the ice edge <br />(Ashton 1979). Ashton (1980) described two of the more common types of ice jams. The first occurs <br />when a flow discharge wave fractures, displaces, and moves the ice cover, which then clogs a <br />downstream section of river. The resulting rise in water level may dislodge the ice jam, releasing <br />large blocks of ice further downstream to repeat the jamming process. The second common type of <br />jam forms when a discharge of ice encounters either an intact ice cover or a change to a lesser river <br />slope. As transport capacity decreases with reduction in river slope, the ice piles and may block the <br />stream. <br />Ice masses below reservoir tailwaters undergo several phases of formation, jamming, and <br />destruction, depending on flow volume, magnitude, and variation in discharge. Increased discharges <br />initially thicken shoreline ice cover, which results in increased current velocity (Donchenko 1978). <br />Further rise in water level invokes deformation and a dynamic destruction of the ice field. <br />Fluctuations in discharge, such as releases from large hydropower projects, will break the ice cover <br />and deteriorate associated ice jams when water level fluctuations are three to four times greater than <br />ice thickness (Donchenko 1978). <br />Effects of Winter Conditions on Riverine Fishes <br />Physiological Effects <br />Fish are cold-blooded or poikilothermic animals. They cannot internally regulate their body <br />temperature like warm-blooded animals or homeotherms. Body temperature, metabolic rate, activity, <br />and nutritional requirements of fish are, above all, dependent on temperature of the surrounding <br />water. Fishes in seasonally warmed and cooled waters of temperate regions undergo lowered <br />metabolism and growth rates during the coldest months. <br />Fish exposed to subfreezing conditions can succumb to frozen body fluids and tissues, but the <br />first effect of severely lowered temperature is inhibited water diffusion pressure that prevents free <br />36 <br />