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Last modified
1/26/2010 2:15:17 PM
Creation date
10/12/2006 12:32:29 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8240.200.48.D.3
Description
Wolford Mountain
State
CO
Basin
Colorado Mainstem
Water Division
5
Date
2/7/1990
Title
Wolford Mountain Biological Opinion - (Muddy Creek)
Water Supply Pro - Doc Type
Publication
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<br />. <br /> <br />", <br /> <br />6 <br /> <br />BioloQV <br /> <br />The life-history phases that appear to be most critical for the Colorado <br />sQuawfish include spawning, egg fertilization, and development of larvae through <br />the first year of life. These phases of Colorado sQuawfish development are tied <br />closely to specific habitat requirements. Natural spawning of Colorado <br />sQuawfish is initiated on the descending limb of the annual hydrograph as water <br />tefllleratures approach 200 Celsius (C). Spawning, both in the hatchery and in <br />the field, generally occurs in a 2-month timeframe between July 1 and <br />September 1, although high-flow water years may suppress river temperatures and <br />extend spawning in the natural system into September. <br /> <br />Teflllerature also has an effect on egg development and hatching. In the <br />laboratory, egg mortality was 100 percent in a controlled test at 130 C. At 160 <br />to IBo C, development of the egg is slightly retarded, but hatching success and <br />survival of larvae was higher. At 200 to 260 C, development and survival <br />through the larval stage was up to 59 percent (Hamman 1981). Juvenile <br />teflllerature preference tests showed that preferred temperatures ranged from <br />21.90 to 21.60 C. The most preferred temperature for juveniles and adults was <br />estimated to be 24.60 C. Temperatures near 240 C also are needed for optimal <br />development and growth of young (Miller et al. 1982). <br /> <br />Only two Colorado sQuawfish confirmed spawning sites, as defined by the Upper <br />Colorado River Coordinating Committee, have been located in the Upper Colorado <br />River BasiR--river mile 16.5 of the Yampa River and river mile 156.6 of the <br />Green River. These areas have the common characteristics of coarse cobble or <br />boulder substrates forming rapidS or riffles associated with deeper pools or <br />eddies. It is believed that a stable, clean substrate is necessary for spawning <br />and incubation. Substrates are swept clean of finer sediments by high flows <br />scouring the bed prior to the spawning period. <br /> <br />O'Brien (1984) studied the hydraulic and sediment transport dynamics of the <br />cobble bar within the Yampa River spawning site and duplicated some of its <br />characteristics in a laboratory flume study. Based on field observations, he <br />reported: <br /> <br />On the rising limb of the hydrograph, sands are deposited in the cobble <br />interstices. These sands are interchanged between the bed and the <br />suspe~ zone for discharges less than bank.full. Depending on the supply- <br />capacity relationship, either deposition or scour could be occurring. When <br />the cobbles move, the sand, of course, is washed from the interstices and <br />may be completely removed from around the cobbles. Rearrangement of the <br />cobbles will result in more stability of the armor layer. On the falling <br />limb, the armor layer becomes a trap for sands until finally, the sand <br />reservoir is again filled. Without cobble movement. sand will be scoured <br />only to a depth of one-half to one median cobble diameter below the cobble <br />bed surface. <br />
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