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Last modified
1/26/2010 4:14:23 PM
Creation date
10/12/2006 5:28:41 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8240.200.10.B
Description
UCRBRIP - Riverine Fish Flow Investigations
Basin
Colorado Mainstem
Date
6/1/2004
Author
CDOW
Title
Riverine Fish Flow Investigations 2004
Water Supply Pro - Doc Type
Publication
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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 />METHODS <br /> <br />Fish sampling was performed by electro-shocking from a IS ft Achilles raft from <br />1998 to 2000 and from a 16-ft Hyside self-bailer raft in 2001 and 2003, A Smith-Root <br />electro-tisher, SOOO-watt generator and anode array mounted on a forward boom was used in <br />all years. The raft was maneuvered by either oars or by a battery powered 40- to 7S-pound <br />thrust trolling motor, Two netters caught as many fish as they could while the shocker was in <br />operation. All fish were measured to the nearest millimeter. Density estimates were made <br />for each study site on the Yampa, Colorado and Dolores rivers, Only fish over 150 mm were <br />marked, and therefore used for mark and recapture population estimates. <br /> <br />The Darroch multiple mark method (Everhart and Youngs 1981) was used to make <br />the population estimate with ninety-five percent confidence intervals. A total fish estimate <br />was made for all species and for each species, Recapture rates generally varied between <br />species and size-groups, In our sampling larger suckers had the highest recapture <br />probabilities and the species with appreciably lower recapture probabilities included catfish, <br />bass, pike and carp (the lower group), The total fish estimate represented a blend of <br />recapture probabilities. but were expected to produce reliable comparisons for total fish <br />abundance between years. when species and size composition was consistent. For rare <br />species (pikeminnow, etc) with zero or one recapture in the sample, abundance was estimated <br />by dividing the number in the sample by the mean recapture probability of the lower group, <br /> <br />The z-test, with an alpha of 0,05 (z = 1,96) was used to test for significant differences <br />in density estimates between years at each station, At stations with three or more years of <br />sampling. the Bonferroni inequality was also used to control the overall significance level <br />(,OS) for the simultaneous comparison of all pairs of years (Dr. David Bowden, CSU, pers. <br />communication). At stations with four years of data, (Duffy and Sevens) the z value (2,631) <br />corresponded to an alpha of 0,05 divided by six (O,0083). <br /> <br />RESULTS <br /> <br />This report compares data collected in 2003 (post 2002 !lows) to data from earlier <br />years, A more complete synthesis of fish data from prior years (1998, 1999, 2000 and 200 I) <br />was presented by Anderson (2002), making it unnecessary to re-present all fish data collected <br />prior to 2003, Each annual progress report between 1999 and 2002 compared species <br />composition, size and density data to the prior year or years. Length frequency histograms <br />for each species at each site were presented in prior annual progress reports. Anderson and <br />Stewart (2000) presented length data for fish sampled in 1998 and 1999, Anderson and <br />Stewart (200 I) contained length data for the 2000 sample. The 200 I sample length data was <br />in Anderson (2002). Meso habitat preferences for depths and velocities determined for <br />flannelmouth sucker and bluehead sucker were given in the projects completion report <br />(Anderson and Stewart 2003), <br /> <br />15 <br />
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