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Last modified
8/11/2009 11:35:00 AM
Creation date
5/22/2009 6:22:48 PM
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UCREFRP
UCREFRP Catalog Number
9650
Author
Mueller, G. A. and e. al.
Title
Factors Influencing Poststocking Dispersal of Razorback Sucker
USFW Year
2003
USFW - Doc Type
North American Journal of Fisheries Management
Copyright Material
YES
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V <br />MANAGEMENT BRIEFS <br />Methods <br />Telemetric transmitters were externally attached <br />to 120 razorback suckers that were stocked at three <br />different locations: (1) areservoir, (2) a small (<1- <br />ha) backwater connected to the Green River, Utah, <br />and (3) a large (30-ha) backwater (Laughlin La- <br />goon, Nevada) connected to the lower Colorado <br />River. Thirty fish were released in both the res- <br />ervoir and small backwater, and 60 were released <br />in the large-backwater test. Their movements were <br />followed for 28 d. <br />Reservoir and small-backwater tests were sub- <br />divided into two 15-fish subgroups; one group was <br />released (reference) after being acclimated to wa- <br />ter conditions and the second was site-acclimated <br />for 3 d behind a barrier net (6-mm mesh) before <br />release. The large-backwater test was divided into <br />four subgroups of 15 fish each: (1) pond-reared <br />and released immediately (reference), (2) pond- <br />reared and acclimated for 7 d at the site, (3) flow- <br />conditioned and released immediately, and (4) <br />flow-conditioned and site-acclimated for 7 d. <br />Sonic transmitters (70 kHz) were used for the <br />reservoir experiment, and radio transmitters (40- <br />41 MHz) were used for the small- and large- <br />backwater tests. Transmitters were individually <br />coded (pulses or frequencies) and similar in shape <br />(conical), size (8 mm diameter, 35-50 mm long), <br />weight (4-7 g), and transmitter life (45 d). Radio <br />transmitters had external trailing antennae. Ra- <br />zorback suckers possess a unique cartilaginous <br />dorsal hump suitable for transmitter attachment. <br />Transmitters were externally attached, a process <br />taking about 30 s, to reduce stress and convales- <br />cence associated with abdominal surgery (Mellas <br />and Haynes 1985). Anesthesia was not used, par- <br />tially because it could have impaired swimming <br />performance. <br />The reservoir test was conducted at Lake Pow- <br />ell, a large (65,000-ha) mainstream reservoir on <br />the Colorado River. Reservoir fluctuations typi- <br />cally exceed 15 m annually, which prevents es- <br />tablishment of submergent vegetation. Under- <br />water cover is limited to rock talus Tamarix sp. <br />and sparse flooded salt cedar. Fish were trans- <br />ported by boat on 3 June 1997 and released in <br />Castle Creek Canyon, a large inundated side can- <br />yon of the San Juan Arm of Lake Powell, Utah. <br />The release site was 16 km down-reservoir of the <br />inflow of the San Juan River. Fish were thermally <br />acclimated (1 h), after which the transmitters <br />were attached. Fish were alternately released in <br />front of (reference group) or behind a barrier net <br />271 <br />enclosure (200 mz), which held the acclimating <br />fish (test group) for 3 d. <br />The small-backwater test was conducted in Mil- <br />lard Canyon, a side canyon of the Green River, <br />Utah, that seasonally floods. Thirty fish were trans- <br />ported by tank truck and raft on 16 June 1998 to <br />the release site located 53 km upstream from the <br />confluence of the Green and Colorado rivers. Both <br />rivers were turbid and confined by steep canyon <br />walls that limited channel widths to typically less <br />than 100 m. Backwater habitat was rare except for <br />small side eddies and side canyon entrances that <br />flood during spring runoff. Water velocities were <br />moderate (about 0.5-1.0 m/s) for both the Green <br />and Colorado rivers upstream of their confluence. <br />However, downstream the Colorado River enters <br />Cataract Canyon, a 26-km white-water reach that <br />extends downstream to Lake Powell. <br />The large-backwater experiment was conducted <br />on the Colorado River downstream of Davis Dam <br />in Arizona and Nevada. Fish were released into <br />Laughlin Lagoon, a 30-ha backwater 12 km down- <br />stream of Laughlin, Nevada. The lagoon is con- <br />nected to the river through a navigational channel <br />and by paired culverts (1 in diameter) located at <br />both ends of the levee. Portions of the lagoon were <br />recently dredged, but 75% of the area is shallow <br />(<1 m) and supports lush stands of submergent <br />pondweed Potamogeton sp. and emergent bullrush <br />Scirpus sp. The river was dredged in the 1950s, <br />and channel widths are typically less than 150 m. <br />Currents appeared similar to those observed in the <br />Green River (<1 m/s), but backwaters and sub- <br />mergent vegetation were more common. <br />Fish for the large-backwater experiment origi- <br />nated from two sources: Willow Beach National <br />Fish Hatchery (WBNFH), where fish are reared in <br />ponded (0.05 m/s recirculating flows) raceways, <br />and Boulder City Municipal Ponds (BCMP), Ne- <br />vada, where fish were maintained in lined earthen <br />ponds (Table 1). Thirty WBNFH fish were placed <br />in a concrete raceway (1.5 X 10 m) on 16 No- <br />vember 2000 and subjected to flow for 2 months. <br />A 10-cm inlet pipe produced flows that varied from <br />0.1 to 1.0 m/s, depending upon location. On 12 <br />January 2001, radio transmitters were attached to <br />these and 30 fish collected from the BCMP. Half <br />of each group was transported and site acclimated <br />in a 0.5-ha netted embayment at Laughlin Lagoon. <br />The remaining half stayed on site until 19 January <br />(after 7 d), when they to were transported to <br />Laughlin Lagoon. The barrier net was removed and <br />all study fish had access to the river at the same <br />time.
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