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96 GREAT BASIN NATURALIST [Volume 55 <br />were to (1) describe diets of YOY Colorado <br />squawfish and other small fish in backwaters <br />of the Green River and (2) examine diet overlap <br />and potential for competition with Colorado <br />squawfish. <br />METHODS <br />Samples of small fish were provided by the <br />U.S. Fish and Wildlife Service Field Station at <br />Vernal, UT. These were collected from back- <br />waters of the Green River during summer (30 <br />June-27 August) and autumn (22 September- <br />10 December) 1987. The study area extends <br />from confluence of the Green and Yampa <br />rivers in Echo Park, Dinosaur National Monu- <br />ment, CO, to Turks Head in Canyonlands <br />National Park, UT-river kilometer (RK) 555 <br />to 35 above confluence with the Colorado <br />River. Upper and lower reaches are divided at <br />Sand Wash (RK 346), UT, a convenient access <br />point just above Desolation Canyon. Each <br />river reach began with a rocky, high-gradient <br />(1.3-2.1 m/km) segment and continued with a <br />sand- and silt-laden, low-gradient (0.2-0.4 <br />m/km) segment known for relatively high <br />catches of YOY Colorado squawfish (Haines <br />and Tyus 1990, Tyus and Haines 1991). The <br />river was further divided into 8-km sections <br />starting from a random location within each <br />reach to help assure an even distribution of <br />collection sites. <br />Backwaters were defined as shallow (typi- <br />cally <0.5 in maximum depth), ephemeral <br />embayments with negligible water velocity. <br />Substrates consisted of silt and sand or silt and <br />mud, sometimes overlaying or interspersed <br />with gravel or cobble. Backwaters had little or <br />no rooted aquatic vegetation, but some had <br />dense mats of algae. Two backwaters were <br />sampled weekly in each 8-km section during <br />daylight (1000-1800 h) using 1-m2 seines (0.8- <br />mm2 mesh) in summer and 1-m X 3-m seines <br />(3.2-mm X 4.8-mm mesh) in autumn. Fish <br />were killed and fixed in 10% formalin immedi- <br />ately after collection. <br />Up to five specimens <- 20 mm total length <br />(TL) and five >20 mm TL of each fish species, <br />representing graded size series, were selected <br />from each sample. Each digestive tract (from <br />esophagus to vent) was removed, opened, and <br />visually assessed for percent fullness. Food <br />items were identified to lowest practical taxon, <br />and a visual estimate was made of percentage <br />contributed by each taxon to total volume of <br />food in each digestive tract (Larimore 1957, <br />Mathur 1977). For diet analyses, food-item <br />taxa (total of 124) were grouped into 20 family, <br />order, or broader-based categories, sometimes <br />divided according to habitat (e.g., aquatic or <br />terrestrial). <br />Data for each fish species were stratified <br />according to length (10-mm TL or larger inter- <br />vals) by season (summer or autumn) within river <br />reach (upper or lower). Only subsets with at <br />least six fish containing food were included in <br />analyses. Diet measures calculated for each <br />subset were (1) mean percentage each food <br />category contributed to total volume of food in <br />each digestive tract (mean of volume percent- <br />ages) and (2) percentage of all digestive tracts <br />in which each food category occurred (per- <br />centage of occurrence). Wallace (1981) evalu- <br />ated several diet measures and concluded that <br />mean of volume percentages is the best mea- <br />sure for calculating overlap. However, per- <br />centage of occurrence is useful for describing <br />general variations in diet (Wallace 1981, <br />Bowen 1983). <br />Similarities in diet by subset between Colo- <br />rado squawfish and other fishes were evaluat- <br />ed by Schoener's (1970) resource-overlap <br />index: <br />n <br />«= 1-0.5(Y,I Pxi-Pyi <br />i=1 <br />where n is the number of food categories, Pxi <br />is the proportion of food category i (expressed <br />as mean of volume percentages) in the diet of <br />species x (Colorado squawfish), and Pyi is the <br />proportion of food category i in the diet of <br />species y (other fishes). Values range from 0.0 <br />(no overlap) to 1.0 (complete overlap). When <br />data on resource availability are absent, <br />Schoener's index is one of the best indices <br />available for calculating resource overlap <br />(Hurlbert 1978, Linton et al. 1981, Wallace <br />1981). Diet overlap is useful in helping to elu- <br />cidate food relationships among species and <br />has been considered "biologically important" <br />when values exceed 0.60 (Zaret and Rand <br />1971, Matthews and Hill 1980, Galat and <br />Vucinich 1983). <br />RESULTS <br />Digestive tracts from 2554 fish represent- <br />ing 15 species were examined for food items;