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Last modified
7/14/2009 5:02:34 PM
Creation date
5/17/2009 11:53:12 PM
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UCREFRP
UCREFRP Catalog Number
9315
Author
Harvey, M. D. and R. A. Mussetter.
Title
Evaluation of the Required Frequency of Bar Forming Events and 2-Dimensional Hydrodynamic Modeling at Colorado Squawfish Spawning Sites in the Lower Yampa Canyon, Colorado.
USFW Year
1996.
USFW - Doc Type
Fort Collins.
Copyright Material
NO
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<br />V. <br />Lower Yampa River (just upstream of the Yampa-Green River confluerice, Echo <br />Park, Dinosaur National Monument), Colorado, and lower Green River <br />(possibly near the town of Green River), Utah. <br />Study Methods/Approach: <br />Passive drift-net sampling is an effective and proven method for capturing <br />Colorado squawfish larvae. In properly conducted, results can provide a <br />reasonable estimate of annual reproductive output from spawning agrees <br />without over-sampling larvae. <br />Drift-net sampling in the Yampa and Green rivers, as part of FGFRI, was <br />started in 1990 and will be conducted again in 1991. In 1991, two drift- <br />net stations were established, i.e., lower Yampa River at Echo Park and <br />Green River just below the Split Mountain boat ramp. At each station, <br />three flow-metered plankton nets were set near the shore, daily at dawn <br />for 1-2 h, from end of June through early August. The objectives of this <br />sampling were to document timing and duration of spawning by Colorado <br />squawfish in the lower Yampa River, determine peaks in abundance of <br />transported Colorado squawfish larvae transported from the lower Yampa <br />River spawning area into nursery habitats in the Jensen-Ouray area; <br />nursery-habitat sampling conducted by Utah DWR (SDCR Task 2) in fall 1990 <br />was intended to subsequently determine abundance of young Colorado <br />squawfish in backwater habitats. Results of the 1990 drift-net sampling <br />were provided in an annual progress report submitted to the U.S. Bureau of <br />Reclamation. After discussions with the cooperative FGFRI team in <br />December 1990, the drift-net sampling scheme used in 1990 was changed in <br />favor of the design proposed here (this new study design will be employed <br />in 1991). <br />Reproductive output will be measured by daily captures of drifting <br />Colorado squawfish larvae at two sites, one at mouth of the Yampa River <br />and one below Grey and Desolation canyons in the lower Green River. Both <br />of these sites are below known spawning grounds, and data from sampling at <br />these sites will provide estimates of relative abundance of Colorado <br />squawfish larvae being transported from spawning areas and into potential <br />nursery habitats. <br />Colorado squawfish in the Yampa River spawn on the descending limb of the <br />hydrograph, often associated with abrupt increases (flow spikes) in base <br />flow (Nesler et al. 1988; Tyus and Karp 1989). Sampling for Colorado <br />squawfish larvae will be initiated based on those data and stream-flow <br />conditions prior to sampling (probably start in mid-late June). Duration <br />of the sampling period will depend on number of larvae collected in late- <br />season samples, past data, and stream-flow conditions probably end early- <br />mid August). <br />Colorado squawfish larvae are most abundant in drift-net samples at dawn <br />and nearshore and midstream nets capture roughly equivalent numbers of <br />fish/unit volume of water sampled (Haynes et al. 1984; Nesler 1986). This <br />was supported by results of out nearshore sampling during summer 1990; <br />catch rates of three nearshore drift nets were similar (one-way ANOVA). <br />Results of the 1990 sampling showed that about 60% of drifting Colorado <br />'period on only four sampling days; we determined that daily sampling over <br />a 6-8-week period was necessary to detect and measure peaks in larval <br />abundance and bracket the period of larval transport. <br />At each station, three 4-m-long conical plankton nets (560 micron mesh) <br />will be set daily at dawn. Nets will be attached to rectangular steel <br />frames (0.15 mZ) and staked into the stream substrate adjacent to the shore <br />in water 0.5-1.0 m deep. A removable collection bucket for trapping <br />filtered material and fishes will be attached to the cod end of each net. <br />C3
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