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<br /> <br /> <br /> <br /> <br />1 <br /> <br /> <br /> <br /> <br /> <br />n <br />1 <br />Growth of northern pike was estimated by aging, measuring (total and fork lengths, mm), and <br />weighing (g) specimens collected during October 1993, May and -June 1994 in the Green River. <br />Fish were captured with electroshockers and trammel nets. Ages were interpreted by counting <br />annuli on magnified projections of scales mounted between microscope slides. Annuli were <br />clearly defined, because rapid growth during the warm season was followed by severe winter <br />conditions. Although the sample size was small (N=26), the pattern of weight-at-age was clear <br />(Table 1) and compared favorably with growth patterns from a neighboring population upstream <br />in the Yampa River (T. Nesler pers. comm.). In model simulations, spawning losses (7.7% wet <br />on the difference in length-weight regression in June versus those in May and October. <br />body mass) were subtracted from pike larger than 660 mm on 15 June (simulation day 45), based <br />The proportional contribution of different prey species in the diet was estimated from stomach <br />samples collected from two sub-populations within the upper basin. Fish were sampled during the <br />spring and fall, 1987-89 in the Yampa River, and in May 1993 -June 1994 in the Ouray reach, <br />Green River. Stomach contents were identified to species or the lowest possible taxonomic level. <br />We measured total or standard prey lengths (mm) and wet weights (mg). Diet composition was <br />computed separately for each age class of northern pike, and was used to partition daily rations <br />into estimated consumption rates on Colorado squawfish and other prey in the bioenergetic <br />simulations. Since nearly all prey items in the stomachs were cyprinids, we <br />6 <br />