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<br />-26- <br /> <br />The previous report (Nehring 1991) alluded to the dynamic interaction between <br />habitat availability and size specific competition, Living organisms (trout <br />in this case) rarely respond instantaneously to environmental stress. Rather, <br />the impacts of most habitat stress factors have a slow, cumulative effect over <br />an undefined period of time. These effects may be manifested as increased <br />mortality rates among the most susceptible components of the trout population. <br /> <br />I hypothesized that agonistic encounters and aggressive interactions among <br />conspecifics (different sizes of trout of the same species) and between <br />different species would increase in frequency during periods of severe habitat <br />restriction or as density per unit habitat increased. These sorts of <br />interactions have been documented for brown trout (Bachman 1984) as well as <br />between different sa1monid species (Fausch and White 1981, 1986; Fausch 1988). <br />It is reasonable to assume that the competition for physical habitat, i.e., <br />"living space" would be most severe among those size groups of trout with <br />similar habitat requirements. Data presented in the previous report (Nehring <br />1991) clearly demonstrated the largest declines in density and biomass <br />occurred among the 20-40 cm (8-16 inch) size classes in 1990. <br /> <br />Figure 2 shows the habitat suitability index (HSI) curves for brown trout fry <br />(s 50 mm), fingerlings (50-100 mm), juveniles (100-200 mm) and adults (~201 <br />mm) for water depth and velocity. These graphs indicate there should be the <br />least amount of direct competition (or overlap in habitat requirements) <br />between fry and adult brown trout, then fingerlings and adults, and somewhat <br />greater competition between juveniles and adults. However, competition should <br />be the greatest between the small adults (ages 2 and 3) and the largest adults <br />(ages 4-6), since habitat preferences for these two groups would be virtually <br />identical. These brown trout HSI curves are provided for explanatory purposes <br />only. The relationships among the various life stages for rainbow and SRC <br />trout would be similar. <br /> <br />Table 13. Dolores River (below McPhee Dam) rainbow and brown trout age <br />specific mortality rates versus mean age specific mortality rates <br />for Colorado's Gold Medal trout streams. <br /> <br /> Cohort (Age in Years) <br />River <br /> 2 3 4 5 <br /> Brown Trout <br />Dolores 0.57 0.65 0.76 0.85 <br />Gold Medal" 0.32 0.42 0.63 0.79 <br /> Rainbow Trout <br />Dolores 0.54 0.72 0.45 0.56 <br />Gold Medal 0.38 0.33 0.55 0.59 <br /> <br />" <br /> <br />Gold Medal mortality rates taken from Table Al in Espegren, Miller, and <br />Nehring 1990. <br />