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340 <br />McADA AND KAEDING <br /> UTAH ? COLORADO <br />N i <br /> <br /> Black Rocks Grand Palisade <br /> Junction d <br /> Westwater <br />6 297 <br />7 <br />0 40 80 Canyon . <br />K <br /> 201.1 275.1 7 <br />Kllometere <br />5 i <br />8 4.0 <br /> 1840 <br />Gunnison <br /> Colorado 154.5 I River <br /> River 4 <br /> Dolores <br /> 3 River <br /> 114.2 1 <br />Gree 75.6 ? 1 Flaming Gorge <br />n \M oab Reservoir <br />River Yam a Ri <br /> 2 1 Green to River <br /> River Colorado <br />Cataract River Gunnison <br />Canyon I <br />River <br /> 0 <br />1 <br />1 Dolores <br />-26.0 River <br />Lake <br />Powell -52.0 I Lake study Area <br /> Powell <br />FIGURE 1.-Colorado River study area. Bold numbers designate reaches; decimal numbers are distances in river <br />kilometers from the confluence of the Green and Colorado rivers or Gunnison and Colorado rivers. <br />TL is total length (mm) at time of collection and <br />AGE is accumulated days since hatching. We used <br />only larvae smaller than 22 mm TL in these anal- <br />yses. Marsh (1985) reported that the median in- <br />cubation period for Colorado squawfish embryos <br />held at 20°C was about 102 h; therefore, we esti- <br />mated the spawning date by subtracting 4 d from <br />each hatching date. Nesler et al. (1988) have con- <br />firmed the validity of this technique. Because <br />sample sizes were small, we pooled Colorado <br />squawfish larvae from paired, consecutive reaches <br />when estimating spawning dates. Water temper- <br />ature and discharge data were taken from a U.S. <br />Geological Survey stream gauge at the Utah-Col- <br />orado border. <br />Radiotelemetry.-Movements of adult Colora- <br />do squawfish were followed by radiotelemetry. Fish <br />were collected from each of the study reaches by <br />electrofishing and with gill and trammel nets. No <br />sampling was conducted in reach 2. Most collec- <br />tions were in April or May before the onset of <br />spawning. Because sex of nonbreeding adult Col- <br />orado squawfish is difficult to determine by ex- <br />ternal characters, we were unable to sex most fish. <br />After total length and weight were measured, we <br />anesthetized Colorado squawfish longer than 440 <br />mm and surgically implanted radio transmitters <br />(9-20 g; battery lives, 6, 10, or 18 months), fol- <br />lowing procedures outlined by Tyus and McAda <br />(1984). Radio-tagged fish were released near their <br />capture sites within 2 h of implantation. Hatch- <br />ery-reared Colorado squawfish stocked into the <br />Colorado River in 1980 (Valdez et al. 1982) were <br />identifiable by their Carlin dangler tags; none of <br />the four hatchery fish we encountered were given <br />a radio transmitter. <br />Searches for radio-tagged fish were made by boat <br />about every 2 weeks from April to October and <br />weekly during the presumed spawning season. <br />Tracking was not conducted from November to <br />March. Fish locations were determined to the <br />nearest 0.1 km along the river. Maximum fish dis- <br />placement from the release point during the esti- <br />mated spawning period (spawning displacement), <br />maximum displacement from the release point <br />during the entire monitoring period (maximum <br />displacement), and displacement from the release <br />point at last contact (final displacement) were <br />compared among river reaches and among fish in <br />100-mm size-classes by analysis of variance <br />(ANOVA). When a fish occupied more than one <br />reach during the estimated spawning period, the <br />