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SPAWNING CUES FOR COLORADO SQUAWFISH <br />E <br />O <br />J <br />LL <br />E <br />O <br />z <br />c ~, <br />3 ~ <br />~ E <br />m <br />D ~ <br />O O <br />~ ~ <br />_T <br />N <br />Si <br />71 <br />z <br />c <br />3 <br />m <br />m <br />x <br />O <br />T <br />T <br />2 <br />2so 1986 so <br />220 Deerlodge 40 <br />z <br />_ c <br />~ 180 ~ <br />E 90 m <br />~ 140 ~~, ~ <br />O Maybell Vn'~. ~ 20 a <br />~ 100 ~ ~ <br />`~. <br />,.,. ~~ ~. _ li <br />20 25 30 5 10 15 20 25 30 5 10 <br />JUN -JUL AUG <br />FIGUxE 3.-Relationships of estimated Colorado squawfish spawning dates (vertical bars) to Yampa River flow <br />regimes (curves) at the U.S. Geological Survey's Maybell and Deerlodge gages for 1983-1986. Number of fish <br />represents number sampled and distributed according to estimated spawning date. <br />Figure 1). Months of record were selected to <br />bracket the known Colorado squawfish spawning <br />seasons as reported in existing literature. The <br />years of record selected represented the available <br />flow data for the Yampa River and were used to <br />characterize the historical flow regime during the <br />spawning season. Water temperatures were also <br />obtained from USGS data collected at the May- <br />bell gage. Precipitation data for the region includ- <br />ing Dinosaur National Monument, Colorado, <br />were compared to the Yampa River flow regime <br />during June-August, 1980-1986, to determine the <br />relationship between rainfall and flow spike <br />events. Daily rainfall data were provided in <br />NOAA (1980-1985, 1986). <br />Results <br />The frequency distribution of Colorado <br />squawfish spawning dates for each year during <br />1983-1986 demonstrated prominent peaks in <br />spawning activity (Figure 3). In 1983, peak <br />spawning activity began July 24-25 and was <br />closely related to the flow spike occurring July <br />22-25. Flows at Deerlodge increased from 89.7 <br />to 122 m~/s. Peak spawning activity in 1984 <br />began July 8, and was associated with the flow <br />spike occurring July 9-11. Flows at Deerlodge <br />increased from 162.1 to 233.5 m3/s. In 1985, two <br />peaks in spawning activity were ,evident and <br />appeared closely related to two major flow <br />spikes. The first peak in spawning activity began <br />June 25, and was associated with the flow spike <br />occurring June 25-27. Flows at Deerlodge in- <br />creased from 108.5 to 136 m3/s. The second peak <br />in spawning activity began July 23, and was <br />associated with the flow spike occurring July 19- <br />22. Flows at Deerlodge increased from 27.6 to 66 <br />m3/s. In 1986, peak spawning activity began July <br />10, following the flow spike occurring July S-7. <br />Flows at Deerlodge increased from 98.9 to 129.2 <br />m'/s. In these five cases, spawning peaks were <br />associated with flow spikes of 27.5-71.4 m3/s <br />occurring over a 2-3-d period. These spikes <br />represented 25-139% increases in river flow. <br />No prominent spawning peaks by Colorado <br />squawfish were evident during 1980-1982 (Figure <br />4). In these 3 years, only 20-46 larvae were <br />collected, compared to 124-455 in 1983-1986 <br />(Table 1). As a result, only the range of spawning <br />dates may be compared to the flow regime. In <br />1980 and 1981, onset of spawning appeared to be <br />loosely associated with the occurrence of flow <br />JUN JUL AUG <br />JUN JUL AUG <br />JUN JUL AUG <br />