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Last modified
1/26/2010 2:17:29 PM
Creation date
10/12/2006 12:55:23 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.106
Description
Animas-La Plata
State
CO
Basin
San Juan/Dolores
Water Division
7
Date
2/26/1996
Title
Final Biological Opinion - 1996
Water Supply Pro - Doc Type
Biological Opinion
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<br />11 <br /> <br />nonnative cyprinids (red shiner, sand shiner, and fathead minnow) in the <br />Colorado River were much lower following high-flow years and increased three <br />to four times in a 2-year period during normal- and low-water years. <br />Platania (1990) noted that, during the 3 years of studies on the San Juan <br />River, spring flows and Colorado squawfish reproduction were highest in 1987. <br />He further noted catch rates for channel catfish were lowest in 1987. <br />Appendix A, Figure 20, compares the 1987 flow of record to historical <br />conditions for dry, average, and wet years. Recent studies also found catch <br />rates for young-of-year Colorado squawfish to be highest in high water years, <br />such as 1993 (Buntjer et al. 1994, lashmett 1994). <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 <br />through the first year of life. These phases of Colorado squawfish <br />development-are tied closely to specific habitat requirements. Natural <br />spawning of Colorado squawfish is initiated on the descending limb of the <br />annual hydrograph as water temperatures approach 20. Celsius (C). Spawning, <br />both in the hatchery and in the field, generally occurs in a 2-month timeframe <br />between July 1 and September 1, although high flow water years may suppress <br />river temperatures and extend spawning in the natural system into September. <br />Conversely, during low flow years when the water warms earlier, spawning may <br />occur in late June. <br /> <br />A natural hydrograph with a large spring peak; a gradually <br />declining/descending limb into early summer; and low, stable flows through <br />summer, fall, and winter are thought to create the best habitat conditions for <br />endangered fishes while maintaining the integrity of the channel <br />geomorphology. Tyus and Karp (1989) pointed out the importance of peak flows <br />(spring runoff) associated with reproductive activities of Colorado squawfish. <br />They further stated that alteration of this hydrological event may affect <br />initiation of Colorado squawfish migration and spawning. Additionally, <br />maintenance of low stable flows in summer and fall are necessary for growth <br />and survival of young Colorado squawfish. <br /> <br />Temperature also has an effect on egg development and hatching. In the <br />laboratory, egg mortality was 100 percent in a controlled test at 13. C. At <br />16. to 18. C, development of the egg is slightly retarded, but hatching success <br />and survival of larvae was higher. At 20. to 26. C, development and survival <br />through the larval stage was up to 59 percent (Hamman 1981). Juvenile <br />temperature preference tests showed that preferred temperatures ranged from <br />21.9. to 27.6. C. The most preferred temperature for juveniles and adults was <br />estimated to be 24.6. C. Temperatures near 24. C also are needed for optimal <br />development and growth of young (Miller et al. 1982). <br /> <br />Miller et al. (1982) concluded from collections of larvae and young-of-year <br />below known spawning sites that there is a downstream drift of larval Colorado <br />squawfish following hatching. Extensive studies in the Yampa and upper Green <br />Rivers have demonstrated downstream distribution of young Colorado squawfish <br />from known spawning areas (Archer et al. 1986; Haynes et al. 1985). Miller <br />et al. (1982) also found that young-of-year Colorado squawfish, from late <br />
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