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<br />Service in 1979-1981 (Tyus et al. 1982; Valdez et al. 1982). The SSP utilized <br />a sampling design that divided the Green;. and Colorado rivers into relatively <br />homogeneous sections on the basis of river morphology. Within each section, <br />two 0.8-km reaches were randomly selected for sampling during a 24-hr period. <br />Sampling was with seines, trammel nets and electrofishing in suitable <br />habitats. Each river section was sampled during pre runoff, runoff and <br />post runoff periods. Our data analyses were limited to the seine samples taken <br />during postrunoff period, the season when age-0 Colorado squawfish are <br />available. In addition, analyses were limited to 1980 data. Data were <br />combined among sections within rivers. <br />Samples were taken within individual habitat types using 0.3- or 0,6-cm- <br />mesh seines. Habitat types were categorized as backwater, eddy, pool, <br />shoreline, run or riffle; deep-water habitats could not effectively be <br />sampled. Fishes were identified, grouped into size classes, enumerated and <br />released alive. The areal extent of each seining effort was quantified, and <br />water depth and water velocity (at 0.6 total depth) were measured at two <br />equidistant points along a transect that passed through the center of the area <br />sampled. Dominant substrate size was estimated visually and given a numeric <br />code according to a modified Wentworth Scale--silt (1), sand (2), gravel (3), <br />rubble (4), boulder (5), bedrock (6) (Bovee and Cochnauer 1977). <br />Multiple discriminant analysis (Green 1979; Klecka 1984) was used to <br />compare habitats used by age-0 Colorado squawfish with those used by each of <br />six sympatric species (red shiner Notropis lutrensis, sand shiner N. <br />stramineus, channel catfish Ictalurus punctatus, speckled dace Rhinichthys <br />