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Last modified
7/14/2009 5:02:29 PM
Creation date
5/20/2009 10:06:44 AM
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UCREFRP
UCREFRP Catalog Number
7203
Author
Osmundson, D. B. and L. R. Kaeding.
Title
Colorado Squawfish and Razorback Sucker Grow-Out Pond Studies as Part of Conservation Measures for the Green Mountain and Ruedi Reservoir Water Sales
USFW Year
1989.
USFW - Doc Type
Final Report.
Copyright Material
NO
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t <br />1 <br /> <br />1 <br />t <br />t <br />1 <br /> <br />1 <br />t <br />t <br />1 <br />11 <br />1 <br />t <br /> <br /> <br />Morgan Fish Disease Control Center in 1984. Thus the incidence of tape- <br />worm infection was assumed to be zero among fishes in T & F Pond. In West <br />Pond, Asian tapeworm was first detected in squawfish on 2 June 1987. The <br />average number of worms per infected fish was low at that time. However, <br />infection intensity rapidly became quite high (Table 4). Squawfish col- <br />lected during 1988 have not yet been examined for Asian tapeworm, but it <br />can be assumed that infection rates and worm burdens were at least as <br />great as in 1987. <br />The effect of Asian tapeworm on Colorado squawfish is not yet known. <br />However, the literature indicates that this parasite is a dangerous patho- <br />gen, particularly to underyearling cyprinids. Scott and Grizzle (1979) <br />report heavily infected golden shiners (Notemigonus crysoleucas) killed by <br />complete intestinal blockage and occasional bursting of the intestine. <br />Heavy infections may cause blockage, inflammation and perforation of the <br />intestine, generalized emaciation, reduced growth rate, and even death <br />(Hoffman 1980, Pool et al. 1984). Infection rates and severe losses of <br />common carp sometimes reach 100% in German pond hatcheries (Korting 1975). <br />Given the high infection rates and intensities in Colorado squawfish from <br />West Pond, B. acheilognathi should be considered a serious problem for <br />squawfish pond culture. <br />Water Quality. Low dissolved oxygen may have caused some problems for <br />fish in late August. In the central region of the pond, where limnologi- <br />cal data were normally collected, DO dropped to 1.0 mg/L on the bottom, <br />0.5 mg/L at mid depth, and 1.5 mg/L on the surface (Fig 4). However, in <br />the north corner of the pond, where fish were rising for mayflies, dis- <br />solved oxygen remained between 3-5 mg/L during this time. Thus, squawfish <br />27
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