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<br />de-silting ponds. Flow regimes were recommended for releases of water from the dam to <br />' protect trout spawning areas. Requests were made to stop stocking operation of catchable <br />trout in the upper 2.5 miles of the river in order to attempt to establish an area of "wild <br />trout waters". In 1971, rubble was removed by bulldozer from two sections in the <br />' government owned portion of the river to induce trout spawning and recruitment. <br />Invertebrate fauna was said to be abundant in all sections of the river but especially in the <br />' lower reaches. It was suggested that the Fryingpan River would remain one of the most <br />productive trout streams in Colorado. Flows of 100 cfs were recommended to maintain <br />the health of his river. <br />Finnell, L. M. and G. L. Bennet. 1973. Fryingpan-Arkansas Fish Research <br />Investigations. Colorado Division of Wildlife. Project Report No. 2. <br />The objectives of this project were to evaluate the physical, chemical and biological <br />' properties of all streams and reservoirs in the Fryingpan and Arkansas river basins prior <br />to planned water diversion operations and to address problems that may arise during <br />these operations. During the 1972-1973 study period the investigations that were <br />' conducted in Ruedi Reservoir and the Fryingpan River were in three general areas of <br />concern: limnological studies, fish population studies, and special studies of exotic food <br />organisms. <br />' Fryingpan River <br />' The purpose of this portion of the study was to determine the effects of planting of <br />hatchery trout on wild trout populations, study the survival and migration of hatchery <br />trout, and to determine whether or not wild trout are capable of maintaining an adequate <br />' population in the face of increasing fishing pressure. Samples were taken by electro- <br />fishing in three sections of the river. Section one was the upper 3 miles that had been <br />designated "wild trout waters". Section two was between the confluence of Frenchman <br />' Creek and the confluence of Taylor Creek. This section was to receive 5 plants of 1000 <br />catchable rainbow trout each distributed at half-mile intervals between March and <br />August. Section three was between the confluence of Taylor Creek and the confluence of <br />' the Roaring Fork River. Average length of rainbow trout captured in Section I was 7.3 <br />inches. These fish were mostly naturally occurring. Sections II and III contained a <br />' higher percentage of adult and sub-adult rainbow trout. There was a noticeable lack of <br />young trout. Conditions were assumed to be more beneficial for rainbow trout <br />reproduction than for brown trout based on the fact that rainbow trout outnumbered <br />' brown trout 4 to 1. <br />Headwater tributaries of the Fryingpan River were examined for the presence of <br />Colorado River cutthroat trout. Brook trout were observed in Mormon Creek and the <br />Middle Fork of Cunningham Creek. Cutthroat trout taken from North Cunningham <br />Creek were identified as a pure strain of Salmo clarki pleuriticus, the original native trout <br />of the upper Colorado River Basin. <br />' Fryingpan-Roaring Fork Literature Review February 27, 2002 <br />Miller Ecological Consultants, Inc. page 7 <br />