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7/14/2009 5:02:29 PM
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UCREFRP
UCREFRP Catalog Number
7065
Author
Behnke, R. J. and D. E. Benson.
Title
Endangered and Threatened Fishes of the Upper Colorado River Basin.
USFW Year
1983.
USFW - Doc Type
Bulletin 503A,
Copyright Material
NO
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reproduction for the past several years in any of the <br />locations where adult squawfish are found. Most <br />specimens have been at least 6 years old or older. <br />Causes of Decline <br />The most obvious and clearly identifiable factor <br />contributing to the decline of squawfish is the large <br />dams and reservoirs that converted hundreds of miles <br />of large-river habitat into great impoundments. The <br />preservation of native fishes was not considered in <br />the planning and operation of these projects. Squaw- <br />fish and other native fishes do not reproduce success- <br />fully in large reservoirs. The adults present in the <br />river when a dam is constructed may continue to live <br />in a reservoir, and may thrive and grow, but the popu- <br />lation-consists of fewer, larger, and older fish each <br />successive year until they all die of old age. The <br />largest known squawfish caught in relatively recent <br />times (34 pounds) was taken in Lake Mead about 35 <br />years ago. Thus, there is no doubt that squawfish <br />can live in reservoirs but they have not maintained <br />themselves by natural reproduction. <br />Reservoirs release cold water (400 - 500) from <br />great depths. These cold tailwaters below dams sup- <br />port trout fisheries but they are avoided by squaw- <br />fish. Releases of cold water from Flaming Gorge Dam <br />effectively eliminated squawfish from 65 miles of the <br />Green River below the dam. Only after the Green <br />River is warmed by the flow from the Yampa River do <br />temperatures reach 700 F or more in the summer and <br />make reproduction possible. Cold-water releases from <br />Glen Canyon Dam apparently eliminated the last squaw- <br />fish from the Grand Canyon area of the Colorado River. <br />Land-use practices, irrigation, and channeliza- <br />tion drastically alter flow patterns and river channel <br />characteristics, and eliminate the quiet backwater <br />nursery areas to a point that suitable squawfish habi- <br />tat is no longer present. Evidently, this sequence <br />of events led to the elimination of squawfish from the <br />Gila River of Arizona. These gradual, cumulative im- <br />pacts on habitat are much less dramatic and not as <br />obvious as the more sudden changes created by a large <br />dam and reservoir, but the end result can be similar <br />in relation to the continued existence of squawfish. <br />In other instances, such as in the Yampa River, <br />squawfish have declined in abundance, and virtually <br />no young squawfish have been found for several years. <br />Yet, no large dams are directly involved nor have any <br />great changes occurred in the flows, temperatures, or <br />water quality of the Yampa River. That is, for the <br />Yampa River, no physical or chemical changes can be <br />pointed to as suggesting a cause-and-effect relation- <br />ship acting against the squawfish. After 1968, <br />the increasing volume of cold water from Flaming <br />Gorge Reservoir became an effective block to squaw- <br />fish moving up the Green River and into the Yampa <br />River for spawning. This must be taken into account <br />when considering the causes of squawfish decline <br />in the Yampa River. However, there is good habitat <br />for adult squawfish in certain deepwater sections <br />of the Yampa River such as Cross Mountain Canyon and <br />Juniper Canyon. Adult squawfish (6 to 10 years old) <br />are found throughout the year in the Yampa River. <br />No indication of successful reproduction and recruit- <br />ment of young squawfish into the Yampa River popula- <br />tion has been found despite intensive search. In <br />this case, a biological change must be considered -- <br />namely, the influence of non-native fishes. <br />Inasmuch as non-native fishes have lived with <br />the squawfish in the Yampa River for a long time and <br />the squawfish formerly reproduced successfully there, <br />one possible cause of reproductive failure in recent <br />years might be attributable to a non-native <br />species that has become established in the Yampa <br />River in relatively recent times -- the redside <br />shiner. This species was introduced from the Colum- <br />bia River basin and was first recorded in the Yampa <br />River in 1961. It rapidly proliferated to become a <br />dominant species by the 1970's. It prefers waters <br />of low velocity -- the quiet side channels and back- <br />water habitat that are required as a nursery area <br />for newly hatched squawfish. Because the redside <br />shiner spawns earlier in the year than the squawfish, <br />the young shiners get a head start and quickly <br />saturate the habitat needed by young squawfish. The <br />redside shiner is absent from the Desolation Canyon <br />area of the Green River, where the most consistently <br />successful reproduction of squawfish still occurs. <br />However, the cause-and-effect relationship of <br />the redside shiner on squawfish is actually not as <br />clear-cut as it might appear. Squawfish reproduction <br />has been severely limited in the Colorado River above <br />and below Grand Junction for several years; yet the <br />redside shiner does not occur in the Colorado River. <br />Redside shiners provide an abundant food supply for <br />Yampa River squawfish. Previous studies in the Green <br />River revealed that the redside shiner was the major <br />component in the diet of squawfish. The key to <br />restoring a viable, self-perpetuating squawfish <br />population in the Yampa River appears to be a matter <br />of finding ways to favor reproduction and survival <br />13
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