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WSP09475
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Last modified
1/26/2010 2:53:53 PM
Creation date
10/12/2006 3:39:26 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8240.300.10
Description
San Juan Endangered Fish Recovery Program
Basin
San Juan/Dolores
Date
1/1/2000
Author
USDOI/FWS
Title
Adult Fish Community Monitoring on the San Juan River 1991 - 1997
Water Supply Pro - Doc Type
Publication
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<br />Walleye were collected as far upstream as RK 108.3 and striped bass as far <br />upstream as RK 91.2. The upstream limit of threadfin shad distribution <br />appears to be Government Rapid at RK 20.2. <br />Both flannelmouth sucker and bluehead sucker showed declining CPUE <br />between 1991 and 1997 in the core sampling area (RK 158.6-53.0). Declines in <br />flannelmouth sucker CPUE were much more dramatic than those for bluehead <br />eucker. However, during the same time period, the average condition factor of <br />these two fish epecies increased. In addition, CPUE for both of these species <br />increased in Reach 6 (RK 180.0-158.6) collections. The declines in <br />flannelmouth sucker and blue head sucker populations may be cyclical <br />fluctuations in these populations. <br />There does not appear to be a resident, reproducing population of <br />roundtail chub in the San Juan River. The individual roundtail chub collected <br />in the San Juan River during the seven-year research period appear to be <br />originating from upstream tributaries, namely the Animas, La Plata, and Mancos <br />River drainages, that support populations of roundtail chub. <br />Between 1991 and 1993, no wild razorback sucker were collected in the San <br />Juan River.' Razorback sucker that were experimentally-stocked between 1994 <br />and 1997 appear to be surviving and growing in the San Juan River. <br />Adult monitoring has also proven to be efficient in monitoring juvenile <br />Colorado pikeminnow that were experimentally-stocked by the utah Division of <br />Wildlife Resources in 1996 and 1997. Thirty-nine of these fish ranging from <br />44-235 mm total length (TL) were recaptured in 1997. Thirty-eight of these <br />recaptured juvenile Colorado pikeminnow were in the 125-235 mm TL range. Six <br />of which were implanted with PIT tags. The sampling regime presently in place <br />for adult monitoring studies appears to be efficient for monitoring stocked <br />juvenile COlorado pikeminnow greater than 100 mm TL. <br />Between 1991 and 1995, 19 wild Colorado pikeminnow, 17 adults (519-945 mm <br />TL) and two large juveniles (363 and 432 mm TL) were collected via <br />electrofishing. All of these COlorado pikeminnow were captured downstream of <br />CUdei Diversion (RK 142.0). Of the 19 COlorado pikeminnow collected, 16 (all <br />adults) were collected in the section of the san Juan River between CUdei <br />Diversion and the Four Corner's bridge (RK 142.0-199.2). Thirteen wild, adult <br />Colorado pikeminnow were implanted (tagged) with radio transmi~ters (tags). ' <br />All 16 COlorado pikeminnow captured and tagged between RK 142.0 and 119.2 <br />remained in a 33-mile section of river from RK 142.0-109.0. This area of the <br />San Juan River seems to have properties that make it a "preferred" reach for <br />adult COlorado pikeminnow. Adult COlorado pikeminnow appear to have very <br />small home ranges which they occupy throughout most of the year, moving only <br />during pre-spawning (mid-May through June) and spawning (July through mid- <br />August) periods. Only one adult Colorado pikeminnow demonstrated migratory <br />behavior. This individual, a large female fish, moved upstream from her home <br />range downstream of'Bluff, Utah apparently to spawn in the summer of 1994. <br />Of the 13 radio-tagged Colorado pikeminnow, 11 were contacted in area of <br />the San Juan River known as the Mixer (RK133.4-l29.8) during presumed <br />spawning periods. Seven individual adult Colorado pikeminnow were contacted <br />in or at the mouth of the Mancos River (RK 122.6) during pre-spawn periods, a <br />behavior dubbed "staging." Two fish tracked in multiple years used the Mancos <br />during two separate pre-spawn periods. Two fish tracked in multiple years, <br />including one of the fish contacted in the Mancos in two separate years moved <br />to the Mixer during two separate spawning seasons. There appears to be a <br />seasonally-repeated behavior among San Juan River Colorado pikeminnow of <br />staging at the Mancos River, then moving to the Mixer to spawn. <br /> <br />iii <br /> <br />-i <br />"- <br />--, <br /> <br />,-, <br />-,- I <br /> <br />:"r <br />r--,- <br /> <br />. " <br />," , <br />,- 1- I <br /> <br />- <br />-T, <br />,. 1- <br /> <br />,- <br />e 1- <br /> <br />:1- I <br />,- )- <br /> <br />:T <br />r:-r <br /> <br />-', <br />...,: <br />- r- <br /> <br />:-T <br />r: r- <br /> <br />-I: <br />. r- <br /> <br />:1: <br />, l' <br /> <br />-. L: <br />,:.1- <br /> <br />: J~ <br />, J' <br /> <br />'. C <br />'_J- <br /> <br />=--I~ <br />r- <br /> <br />- I: I <br />'.J" I <br />I <br /> <br />~L <br />-" <br /> <br />',J;j I <br />~... <br /> <br />--- <br />:.~ <br />-". . <br /> <br />~ <br />..J." I <br />. )1 <br />~ ' <br />~' <br />- <br />il~ <br />- <br />
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