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<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 /> <br />instead wait for appropriate spawning temperatures to initiate migration into these areas. <br />The water temperatures and the presence of large numbers of adults congregating in the <br />backwaters in early April suggest that the primary spawning period in the Yampa River <br />occurs during this period. We continued to collect sexually mature northern pike <br />throughout May, which was similar to the findings of Nesler (1995). These results <br />suggest that the entire spawning period may last for about a month, as has been reported <br />elsewhere (Farrell 2001; Miller et al. 2001). The presence of more males than females <br />during the primary spawning period is consistent with other studies of northern pike <br />spawning activity (Billard 1996). <br />The dynamic nature of lotic systems makes identifying spawning habitats <br />challenging. For example, spawning habitat that may look suitable during April may be <br />negatively affected by the spring runoff in May and areas that look good during May <br />might not have water during the early April spawning period. From year to year the <br />quality of nursery habitat can change because of different spring runoff levels. Initial <br />counts of backwater habitats in the river indicated that they were widespread, but closer <br />observation revealed that good spawning and nursery habitat is limited. Backwater <br />orientation to the river was a major indicator of whether the backwater would be <br />protected or not from spring runoff flows and thus serves as good nursery habitat. <br />Backwaters that are parallel to the main river channel have the possibility of experiencing <br />direct flow through the backwater if it connects to the main channel during spring runoff, <br />thus lowering the value of these areas as nursery habitat. In contrast, backwaters that are <br />more or less perpendicular to the main channel are less likely to receive direct flow <br />through them during spring runoff. Large backwaters of this type were relatively <br />uncommon in our study area. <br /> <br />The amount of spawning habitat available does not seem to differ greatly from <br />year to year, regardless of the magnitude of spring runoff, but spring runoff could <br />seriously impact the recruitment of age-O northern pike during the nursery period. Our <br />analysis of backwaters indicated that a large majority showed signs of being connected to <br />the main channel during a typical spring runoff. During a runoff of large magnitude, <br />similar to 2003, we observed that most backwater nursery habitats became part of the <br />main channel or at least experience increased flows. During a spring runoff of low <br />magnitude, as in 2002, backwater nursery habitat is less likely to connect to the main <br />channel, but has the added threat of being dewatered. On these occasions some age-O <br />pike are able to find suitable nursery habitat in low velocity areas of the main channel, <br />which can serve as de facto backwater habitat. While the spring runoff appears to create <br />abundant backwater nursery habitat, these habitats may in fact be unsuitable for age-O <br />pike because of flushing flows. <br /> <br />Based on our observations, the primary spawning period on the Yampa River is <br />from April 1-15. Egg incubation may last between 12 and 17 days at water temperatures <br />between 7.80 and 100 C (Swift 1965) at which point larvae attach to vegetation for 5-12 <br />days (Billard 1996) after which they become free-swimming (Figure 6). Based on this <br />age-O northern pike timeline for development, we suspect that spring runoff flows in May <br />and June could be detrimental to age-O northern pike recruitment. Most backwaters <br />available for spawning and nursery habitat experience strong currents during spring flows <br /> <br />9 <br />