Laserfiche WebLink
<br />intolerant of tUlbidity, which may interfere with reproduction and growth. Instream cover of 40- <br />60% of pool area is optimal. Optimal current velocities are ~ 6 em/see and velocities exceeding <br />20 cm/ see are unsuitable. Optimal spawning substrate for largemouth bass is gravel; silt bottoms <br />are unsuitable. Current velocities> 10 cm/sec are avoided by spawning bass and stable water <br />levels are considered best due to characteristic shallow nest depths. Bass fry cannot tolerate <br />current velocities exceeding 0.27 cm/see and optimal temperatures for growth are 27-3OC. These <br />temperatures were not reached in the Colorado River mainchannel between Cameo and Stateline <br />in 1989 or 1990. Instream vegetative cover is considered important for fry survival. Spawning <br />by largemouth bass is negatively affected by the predominance of silt substrate, fluctuating water <br />levels, and rapid water temperature changes (Carlander 1977). <br /> <br />Based on these habitat suitability criteria, the presence of flowing, cold, turbid water with <br />rising spring water levels and storm-induced summer flow spikes in the Colorado River would <br />likely not favor adult largemouth bass reproduction, and could disrupt all centrarchid species <br />attempting to spawn in main-channel habitats, including backwaters. A change in side-channel <br />backwaters to flowing channels and fluctuating water levels would make many backwaters unstable <br />and unsuitable spawning habitats. Backwaters, as low-velocity habitats may provide higher water <br />temperatures for centrarchids and other fish species. McAda et al. (1994) found a significant <br />difference in water temperatures between the mainchannel and backwaters containing Colorado <br />pikeminnow young-of-year in the Colorado and Green rivers in only 3 of 22 comparisons from <br />1986-1992, but suggested Colorado pikeminnow used backwaters during the warmest part of the <br />day and left during nighttime cooling. Trammell and Chart (1999c) reported monthly mean water <br />temperatures in the Green River mainchannel for May through October were higher than in <br />backwaters in all but one occasion. They found the average backwater temperature was <br />significantly lower than the mainchannel temperature and backwater maximum temperature was <br />signifteantly higher than mainchannel maximum. These authors found degree day accumulation <br />in backwaters based on maximum daily temperature was higher the mainchannel, but degree day <br />accumulation in backwaters was lower than the mainchannel based on average daily temperature. <br />Results of Trammell and Chart (1999c) suggest the thermal advantage of backwaters resides <br />largely in being able to achieve higher daily maximum temperatures than the mainchannel, but this <br />advantage may be mitigated by daily temperature fluctuations resulting in average backwater <br />temperatures lower than the mainchannel. To exploit the thermal advantages of backwaters and <br />mainchannel habitat, fish species must be adapted to move freely between and exploit both. <br /> <br />Offchannel, standing water habitats that are infrequently affected by Colorado River flows <br />and can maintain stable water levels and more optimal water temperatures suitable for centrarchids <br />would be the most conducive to centrarchid reproductive success. This suggests that off -channel <br />ponds and reservoir act as centrarchid sources to riverine habitats. The incidental presence of <br />bluegill and black crappie collected in backwaters as well as the catch rate and length frequency <br />data for largemouth bass support this hypothesis. This contn"bution may occur during high spring <br />flows when floodplain ponds are breached by high water, or by simple escapement in outlet <br />streams. While largemouth bass samples collected in backwaters are comprised of many young- <br />of-year or juvenile fish, the length frequency distributions do not demonstrate recruitment of these <br /> <br />32 <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 />