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Last modified
7/14/2009 5:02:31 PM
Creation date
5/18/2009 12:26:50 AM
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UCREFRP
UCREFRP Catalog Number
7769
Author
McAda, C. W., J. W. Bates, J. S. Cranney, T. E. Chart, W. R. Elmblad and T. P. Nesler.
Title
Interagency Standardized Monitoring Program
USFW Year
1994.
USFW - Doc Type
Summary of Results, 1986-1992 - Final Report.
Copyright Material
NO
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substituting the trapping technique, (2) maintaining the current sampling protocol and adding <br />additional sampling (trapping or electrofishing, whichever is most effective) on a regular or as-needed <br />basis, (3) mark-recapture population estimates, (4) age analysis of captured fish, and (5) collecting <br />abundance and biological data on the entire fish community. <br />Humpback Chub <br />Both Black Rocks and Westwater Canyon continue to support large populations of humpback <br />chub. Size of the adult population in Black Rocks (the only part of the population measurable with <br />trammel-net data) appears basically unchanged from 1988 to 1991, although CPE was somewhat <br />higher in 1991. However, the population structure appears to have shifted towards larger fish by <br />1991. In Westwater Canyon, catch rates for humpback chub increased somewhat during the course of <br />ISMP, with highest catches reported in 1991. The most obvious change in Westwater Canyon is <br />increased abundance of roundtail chub in the upper canyon. CPE for roundtail chub was about six <br />times higher in 1991 than it was earlier and their relative proportion of the Gila community increased <br />from about 33 % in 1988 to 62 % in 1991. The size structure in Westwater Canyon and Black Rocks <br />indicates continued recruitment to adult populations of both roundtail and humpback chubs. A large <br />number of juvenile humpback chub were collected from Westwater Canyon, but relatively few were <br />collected from Black Rocks. <br />The sampling schedule as currently outlined for ISMP may not be adequate to monitor the two <br />populations of humpback chub. The 3-year sampling intervals could allow substantial population <br />changes to occur without being detected. Further, using only trammel nets restricts sampling to the <br />adult population. Monitoring should also include gears expected to capture juvenile and YOY chubs <br />such as seines, traps, and small-mesh trammel nets. The additional sampling gear would allow <br />monitoring all age classes of chubs in the two populations. In addition, sampling frequency should be <br />increased to every 2 years. However, ISMP in Westwater Canyon should be temporarily suspended <br />because a more intensive study of that population is currently underway. ISMP should be reinitiated <br />after that study is completed. ISMP can be.considered for other humpback chub populations as well <br />when intensive studies of those populations are completed. <br />ix <br />
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