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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 />Table 13. Mean lengths of all species collected at Lily Park, Yampa River 2000 to 2003, <br /> <br />YAMPA RIVER Mean length for all fish collect in cm <br />Lily Park 2000 2001 2003 <br />Flannelmouth sucker 41.5 38,3 37,8 <br />Bluehead sucker 34.2 33,5 32,5 <br />Colorado pikeminnow 59.4 64,3 52,6 <br />Roundtail chub 40.3 18,0 6,0 <br />White S. + hybrids 26.6 28.0 35,8 <br />Channel catfish 34,7 32,9 27.2 <br />Carp 42,1 44,6 43.1 <br />Small mouth bass 12.0 15,1 16,7 <br />Northern pike 64,6 66,7 63,7 <br /> <br />Channel catfish biomass was much greater in 2000, Not only was channel catfish <br />density and biomass highly variable between years, but length distribution was also highly <br />variable between years. This variability in size distribution was another aspect of a migrating <br />population, In 2000, 72% of the channel catfish captured at Lily Park were between 30 and <br />39 em in length. In 2001, 48% of the channel catfish measured from 30 to 39 em, Only 13% <br />were of this size in 2003, Only 13% of the channel catfish were less than 30 em in 2000, but <br />78% were less than 30 em in 2003. The large shift in size structure at Lily Park between <br />years likely indicated improved spawning and survival of small channel catfish in 200 I and <br />2002 compared to 1998 and 1999, <br /> <br />Survival of small channel catfish may be more a function of habitat conditions than <br />predation rates. Higher and cooler flows during the Spring and Summer of 1998 and 1999 <br />could mean that channel catfish spawning was located further downstream. In 1998 and <br />1999 younger channel catfish may not have been available or capable of moving into the Lily <br />Park site by 2000. The presence of smaller channel catfish in 2003 would result if their <br />spawning and nursery habitat was much closer to Lily Park. This was indicated by the <br />capture of a 5 em fish (YOY) at Lily Park in 2003 and two yearling fish, 14 em and 16 em, <br />not observed in prior years. <br /> <br />The most common channel catfish size-group (mode from 30 to 40 em) in 2000 was <br />missing in 2003, This could be a result of poor survival in 2002 for channel catfish over 30 <br />em. The very strong mode offish from 20 to 30 em in 2003 (Figure AI-4S) coincided with <br />the drought flows of 2002 which suggested habitat for channel catfish less than 30 em was <br />improved given those flow conditions. <br /> <br />White sucker and carp had their highest biomass estimates in 2003. Smallmouth bass <br />biomass was fairly similar for all three years in spite of the fact that bass density increased in <br />each year. <br /> <br />Age-O smallmouth bass were not collected at Lily Park in 2003 (Figure A I-52), but <br />were common in both 2000 and 2001, The lack ofYOY bass meant that the mean length of <br />smallmouth bass (Table 16) was higher in 2003 compared to prior years, By far the <br /> <br />24 <br /> <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 />
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