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<br />20 <br /> <br />water temperatures from Maybell downstream ranged above 19C. In 1984, <br />peak spawning activity occurred from July 8-18. During this period flows <br />decreased from 179 m3/s to 163 m3/s on July 8-9, then increased to 229 <br />m3/s by July 11. Spawning activity diminished considerably as flows <br />again decreased below 105 m~15. Water temperatures at Maybell during <br />this time ranged above 17C. In 1985, spawning activity was described by <br />two peaks. The first peak occurred from June 25-29, and was associated <br />with a sharp resurgence in flows from 108 m3/s to 136 m3/s over June <br />25-27. Spawning activity dropped off equally as sharp when flows again <br />declined below 55 m3/s on July 6. On July 19-21, flows increased from <br />31 m3/s to 67 m3/s, which appears to initiate another small peak in <br />spawning activity from July 23-26. As with the first peak, spawning <br />declined considerably as flows dropped below 55 m3/s. Water temperature <br />data indicated that spawning began as the Yampa River reached l8C maximum <br />at Maybell~ and continued despite a significant drop in temperature of 4C <br />on July 24-27. Water temperatures quickly climbed above l8C again for the <br />remainder of the spawning season. <br />In summary, the past three years' data suggest that the peak in <br />Colorado squawfish spawning activity occurred when Yampa River flows <br />increased sharply (approx. 30 m3/s or more within 1-2 days) from the <br />declining pattern of spring runoff. Spawning activity declined when flows <br />dropped below the 55-60 m3/s range. <br /> <br />DISCUSSION <br /> <br />f;:r~J..::~:ti v~~..__sPuncL2I.n..s.g_ - No c:l. ear 2I.nnuc:3.1 trends were .::.:\ppc\rE.mt in the <br />relative abundance of fish species collected in drift samples since 1983. <br />With reference to drift samples, relative abundance may be equated with <br />yearly reproductive success rather than population abundance trends. <br />Within the Cyprinidae, Colorado squawfish, speckled dace, and Gila spp. <br />were most prevalent, though larvae of the latter two species remained <br />lower in abundance in 1984-85. Within the Catostomidae, abundance of <br />larval bluehead suckers increased in 1984, then declined in 1985 to a <br />level similar to that of 1983. Flannelmouth sucker exhibited a relative <br />increase in numbers of larvae in 1985. Channel catfish reproductive <br />success remained fairly stable over the 1983-1985 period. <br /> <br />Drift s~mp-=linq methodoloqv/General - An,:11yses of wCl.ter volumes sa.mpled <br />show each net functioning as an independent sampler ~ith variability in <br />the volume of water sampled connected to position in the stream and <br />duration of sampling effort. Statistical results show surface drift-net <br />sampling in a line perpendicular to streamflow could be considered <br />triplicate sampling for efforts of 1 hr or less, but 2 hr sampling <br />magnifies differences in the river conditions experienced by each net, <br />causing significant differences in the water volumes sampled. Timing of <br />sample effort based on flow and suspended debris load becomes important in <br />this case with regard to assumptions used in sample design and data <br />analyses. These results should be applicable as cautionary guidelines to <br />any further drift-net sampling conducted in the Upper Basin. It cannot be <br />e:-;pected that the differences noted here will be generally consistent <br />between different years or sampling sites, so it is recommended that <br />analyses of water volumes sampled between drift-nets become standard for <br />quality control. <br />