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WSP11688
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Last modified
1/26/2010 3:18:31 PM
Creation date
10/12/2006 5:06:38 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.104.I
Description
Flaming Gorge
State
UT
Basin
Yampa/White/Green
Date
11/25/1992
Author
USDOI-USFWS
Title
Final Biological Opinion on the Operation of Flaming Gorge Dam - (Part 1 of 2)
Water Supply Pro - Doc Type
Biological Opinion
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<br />,,~~ <br /> <br />12 <br /> <br />Miaration <br /> <br />The initiation of spawning migration is an important companent of the <br />reproductive cycle of the Colorado squawfish. Based on radio-tracking data <br />(Wick et al. 1983: Tyus and McAda 1984: Tyus 1990), fish in the Green and <br />Yampa Rivers initiated spawning migrations around the summer sa1stice: Green <br />River fish initiated migrations about June 21 (range: May 23-Ju1y 22) and <br />Yampa River fish migrated about June 15 (range: May 26-Ju1y 13). These <br />mavements included downstream migratians in the Yampa and White Rivers and <br />upstream and downstream migratians in the Green River (Tyus et a1. 1987; <br />Tyus 1990). <br /> <br />Flaws and water temperatur.es were highly variable during Calorado squawfish <br />spawning migrations, and migratians were initiated earlier in low-water years <br />(e.g., 1981) and later in higher water years (e.g., 1983). The earlier the <br />spring peak flow occurred, the longer the interval before migration began <br />(Tyus 1990). Initiation of spring migration occurred about 28 days after peak <br />flow in the Yampa and Green Rivers (Tyus and Karp 1989). Migration was <br />associated with water temperatures of at least 9 'C (average 14 'C). <br /> <br />Haming behavior in Colorado squawfish is suggested by long-distance movement <br />patterns and repeated recaptures of the same fish on spawning graunds in <br />subsequent years (Wick et a1. 1983; Tyus 1985 and 1990). Fish use of mare <br />than one spawning area was not detected (Tyus 1990), supporting the idea of <br />spawning fidelity in Colorada squawfish. Colorado squawfish spawning areas <br />thus should be protected as unique habitats that are essential ta the <br />canservation of the species. <br /> <br />The migrations and homing behaviar .of Colorado squawfish mandates pratection <br />of known migration routes. Migrations of Colorado squawfish are vulnerable to <br />stream b1ackage (Tyus 1984) as evidenced by the recent loss of 50 miles of <br />occupied habitat in the White River due to blockage (Martinez 1986) at Kenny <br />Reservoir. lack of access to spawning grounds was implicated in the decline <br />of Co10rada squawfish (Joseph et a1. 1977; Tyus 1984). <br /> <br />SDawnina <br /> <br />Males generally mature at age 5 or 6 and females at age 6 or 7 (Hamman 1981b; <br />Vanicek and Kramer 1969; Seetha1er 1979). Mast mature fish in the Green and <br />Yampa Rivers migrate in spring to two locations identified as spawning areas. <br />These include riffle and pool habitats in Yampa Canyon on the lower Yampa <br />River and Gray Canyon on the Green River (Tyus and Karp 1989; Tyus.1990). <br /> <br />The annual spawning period (as indicated by the presence of migrating radio- <br />tagged fish on spawning grounds, collections of ripe fish, or calculated dates <br />of larval emergence in spawning reaches) lasts about 4 to 5 weeks. An optimum <br />spawning period also was calculated by averaging the dates in which radio- <br />tagged fish and ripe fish were present in the spawning reach and back- <br />calculated dates of egg deposition. The length of the estimated optimal <br />spawning period (about 26 days) was similar in both spawning areas for all <br />years. Spawning generally occurred earlier in low-water years (1981, 1987, <br />and 1988) and later in high-flow years (1983 and 1984). Discharge was <br />
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