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Last modified
7/14/2009 5:01:47 PM
Creation date
5/22/2009 6:24:36 PM
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UCREFRP
UCREFRP Catalog Number
8104
Author
Modde, T. and D. B. Irving
Title
Use of Multiple Spawning Sites and Seasonal Movement by Razorback Suckers in the Middle Green River, Utah
USFW Year
1998
USFW - Doc Type
North American Journal of Fisheries Management
Copyright Material
YES
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1 <br /> <br />MODDE AND IRVING <br />547 <br />515 <br />483 <br />450 <br />418 <br />386 <br />L <br />N <br />O <br />Y <br />N <br />fY <br />547 <br />515 <br />483 <br />450 <br />418 <br />386 <br />547 <br />515 <br />483 <br />450 <br />418 <br />386 <br />547 <br />515 <br />483 <br />450 <br />418 <br />386 <br />547 <br />515 <br />483 <br />450 <br />418 <br />386 <br />547 <br />515 <br />483 <br />450 <br />418 <br />386 <br />321 <br />94 95 94 95 <br />FIGURE 2.-Seasonal movement patterns of six male razorback suckers in the middle Green River between April <br />1993 and June 1995. Horizontal lines represent the Escalante spawning area (RK 442-501) and the Yampa River <br />spawning site (RK 555). <br />te). Fish 177D1B returned to Split Mountain Can- <br />yon in October and 180B26 returned sometime <br />before March. In late July 1993, approximately 2 <br />months after implantation, the transmitter from <br />one adult razorback sucker was found in a shallow <br />inlet near Stewart Lake. The fish was presumed to <br />be dead. <br />Fish implanted with transmitters either ex- <br />pressed milt or were heavily tuberculated at cap- <br />ture, suggesting they were probably involved or <br />preparing for spawning activity at the time of cap- <br />ture. We assumed that these fish engaged in spawn- <br />ing activity in 1994 and 1995 when they returned <br />to identified spawning sites in the spring, although, <br />because of high flows and turbidity, it was not <br />possible to confirm actual spawning. <br />Maximum downstream movement of the six fish <br />implanted with transmitters ranged between 0.0 <br />and 112.7 km (Table 1). Most movement occurred <br />just before, or following, congregations at spawn- <br />ing locations (Figure 2 and as reported by Tyus <br />and Karp 1990). During both years of study, mean <br />downstream movement exceeded upstream dis- <br />tance traveled, although two fish in 1993 and one <br />in 1994 moved further upstream than downstream. <br />Maximum downstream movement averaged 33.1 <br />(SD = 21.8) and 61.8 km (SD = 43.8) during <br />1943-1994 and 1994-1995, respectively (Table 1; <br />Figure 2), In 1993-1994, two fish underwent ex- <br />tensive downstream movements (55.5 and 68.0 <br />km) compared with three fish between 1994-1995 <br />(93.3, 99.0, and 112.7 km). In 1994, two of the <br />six transmitter-implanted fish moved to a different <br />spawning area than the one they were captured at <br />the previous year. Fish 180B2C was collected on <br />the Yampa River spawning bar in 1993 but moved <br />94 95 <br />94 95 <br />94 95 <br />94 95 <br />
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