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Last modified
7/14/2009 5:02:32 PM
Creation date
5/20/2009 10:54:46 AM
Metadata
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UCREFRP
UCREFRP Catalog Number
8033
Author
Lentsch, L. D., et al.
Title
Endangered Fish Interim Management Objectives for the Upper Colorado River Basin Recovery And Implementation Program -Final Report.
USFW Year
1998.
USFW - Doc Type
55,
Copyright Material
NO
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<br />1 <br />11 <br />t <br />LI <br />1 <br /> <br /> <br />1 <br /> <br />t <br /> <br />Ir ? <br />u <br />1 <br /> <br /> <br /> <br />1 <br />the Green River (LTDWR, unpublished; Modde et at. 1996), however significant recruitment to the <br />adult population is doubtful, because few young fish have been found and adults were considered <br />rare (Modde et aL 1996; Chart et al. 1997). Razorback sucker was declared endangered by the <br />USFWS in 1991 due to declining numbers and lack of documented recruitment of natural <br />populations (USFWS 1997). <br />Demographic information in the UCRB is sketchy. Sex ratios have been reported from relict <br />populations in Lake Mojave at 3 males to 2 females (Bozek et al. 1984) and in lotic environments <br />as 2 males to 1 female (Tyus and Karp 1990). Minckley (1983) and McAda and Wydoski (1980) <br />reported from 1812 and 1166 eggs/cm of total length. When translated to an average sized female <br />(500 mm TL), fecundity is approximately 82,500 eggs/female. No specific estimates on <br />survivorship are available. <br />Lanigan and Tyus (1989) estimated a population size of 948 individuals in the Green river above <br />Desolation Canyon but felt the number of captures in the lower Green River was too low to <br />estimate population size. Current population estimates suggest approximately 500 mature <br />individuals exist in the Green River (including middle and lower) Modde et al (1996). It is not <br />clear whether this discrepance represents a population decrease or differences in estimation <br />techniques. Crowl and Bouwes (1998) assume an initial population of 50 for the Yampa River <br />based on reports of very low numbers, because no estimate exists for the Yampa River population. <br />Humpback Chub The USFWS has recognized five populations of humpback chub in the Colorado <br />River Basin (Valdez and Clemmer 1982; USFWS 1990). Presently, populations are found in <br />canyon reaches of the Colorado River system. The largest and most stable population is also the <br />only population remaining in the Lower Colorado River Basin and resides in Grand Canyon in and <br />near the confluence of the Little Colorado River (LCR). The other populations are in <br />WestwaterBlackrocks Canyons and Cataract Canyons of the Colorado River, Desolation/Gray <br />Canyon of the Green River and in Yampa Canyon of the Yampa River. In addition, aggregations <br />of humpback chub or roundtail/humpback hybrids occur sporadically throughout the basin within <br />confined canyon reaches. <br />Humpback chub have been difficult to study because of their rarity and residence in swift, turbid <br />and inaccessible riverine environments. The only sex ratios reported suggest they are <br />approximately equal and that fecundity averaged 3, 677 eggs/ female in the Grand Canyon of the <br />lower Colorado River basin (Valdez and Ryel 1995). Egg survival is optimal between 16 °C and <br />22 °C and significantly reduced below temperatures of 12 °C which could affect reproductive <br />success of mainstem spawning in the Grand Canyon (Marsh 1985). In Grand Canyon studies, age- <br />s fish were noted to disperse one to three months after emergence (Valdez and Ryel 1995). <br />Survivorship in years 0, 1 and 2, collectively was 10% but most likely later life stages survived <br />better. Adult survivorship has been reported as 60% in the upper Colorado River basin and 75% <br />in the Grand Canyon (Kesler 1992; Valdez and Ryel 1995). Humpback chub mature in two to <br />three years (approximately 200 mm in total length), and they may five 20 to 30 years (Valdez et al. <br />1992). <br />12 <br />IJ
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