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Last modified
7/14/2009 5:02:36 PM
Creation date
5/22/2009 5:25:12 PM
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UCREFRP
UCREFRP Catalog Number
9596
Author
Ayers Associates.
Title
Yampa River Basin Research Final Synthesis Report.
USFW Year
1999.
USFW - Doc Type
Fort Collins, CO.
Copyright Material
NO
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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />7. ISSUES IDENTIFICATION AND DISCUSSION <br /> <br />The Yampa Management Team believes most of the relevant technical data needed for the PBO <br />have been collected or are readily available (e.g., USGS stream flow records). However, several <br />issues need to be resolved before a PBO can be developed. Significant issues raised during the <br />Synthesis Conference or identified in comments on the draft Synthesis Report are listed below. <br />Each bullet includes a consensus as to issue resolution, where a consensus was reached, or the <br />substance of issues still in dispute. <br /> <br />. Geographic extent of PBO: The Little Snake River is the largest tributary to the Yampa, <br />encompassing half of the watershed area and contributing 28 percent of the flow upstream <br />from Deerlodge Park. Its benefits to the Yampa and potential impacts of water development <br />on the Little Snake must be considered. Impacts downstream on the middle Green River due <br />to depletions from the Yampa River Basin must be addressed, also. The Yampa PBO also <br />must coordinate with the related PBOs (e.g., Flaming Gorge, Duchesne). However, the <br />Yampa PBO must not be required to mitigate the impacts of Flaming Gorge and Duchesne. <br /> <br />. Year-round flow recommendations: Instream flow requirements for fish were determined <br />for mid-summer through early fall (August-October). The flow needs of fishes also must be <br />identified for the balance of the non-peak flow period (November-March), especially if these <br />flows are used to augment low flows during August-October. The USFWS is evaluating its <br />past year-round flow recommendations to determine if they are still appropriate or should be <br />modified in light of more recent research. <br /> <br />. Role of the Aquatic Management Plan: This plan includes removing nonnative fish from <br />the Yampa River and placing them in ponds and reservoirs in the basin, which are isolated <br />from the river. Because competition and predation by nonnatives represent a significant <br />challenge to the recovery of the endangered fishes, the PBO should incorporate this element <br />of the RIPRAP. <br /> <br />. Incidental take protection for anglers: Anglers are concerned that they could be held <br />liable for mortality they inflict on endangered fishes by capturing and handling them while <br />sport fishing. Can incidental take by anglers be covered by the PBO? Anglers can be <br />protected for their participation in nonnative fish control activities covered by the PBO. <br /> <br />. Future demand horizons: Should measures to protect fish be implemented based on the <br />expectation of future water demands before the need for water exists? Or should recovery <br />actions be phased in as depletions increase over time? Since the ultimate goal of the RIP is <br />to recover the endangered fishes, it may be appropriate to implement some measures as <br />soon as possible, while other measures specifically intended to offset the impacts of <br />depletions could be phased in, commensurate with depletions. <br /> <br />. Conservation alternatives: Water conservation measures have been dismissed as viable <br />alternatives for several reasons. Agriculture accounts for most of the water consumed in the <br />Yampa Valley. Implementing conservation measures, such as sprinkler irrigation systems, <br />would be costly for agriculture, and the potential be~fits of such measures are illusory. <br />Conservation measures would have little effect on consumption; water diversions and return <br />flows would be reduced, resulting in only a marginal net increase in stream flow. Locally, <br />however, stream flows could increase immediately below diversion structures. But the <br />potential benefits to endangered fishes due to increased stream flows through relatively short <br />river reaches may not justify the cost of these measures (also see Section 4). <br /> <br />19 <br />
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