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<br />Hatching dates for individual larvae were estimated by back-calculation <br />using an equation developed by Haynes et ale (1985): <br /> <br />AGE = - 76.71 + 17.50 TL - 1.06 TL2 + 0.0221 TL3 <br /> <br />~here TL is total length (mm) at the time of collection, and AGE is the number <br />of days since hatching. This equation ~as derived from the gro~th rate of <br />Colorado squawfish in a hatchery (Hamman 1981b). The median incubation period <br />for eggs held in 20 C water ~as 102 hr (Marsh 1985); therefore, 4 days were <br />subtracted from hatching date to determine spawning (egg deposition) date. <br />The peak spawning period ~as considered to be when the median 501 of the <br />Colorado squa~fish larvae were estimated to have been spawned. Estimated <br />spa~ning dates from the upper reach (Reach 4) were compared ~ith ~ater- <br />temperature and discharge data from the USGS gage at the Colorado-Utah border. <br />Similar comparisons were not made for Reaches 1-3 because gage data are not <br />available for these areas. <br /> <br />Fall Dost-larval_ aqe-O samolinq (Obiective 2) <br /> <br />The annual reproductive success of Colorado squa~fish ~as estimated by <br />systematic sampling of the small fishes in reaches 2-4--the riverine part of <br />the study area. Investigators began at the upstream end of the reach and <br />sampled the first backwater or embayment encountered in each 5-mi interval as <br />they moved do~nstream. Sampling at each site consisted of t~, non- <br />overlapping seine hauls in the back~ater and two similar seine hauls in nearby <br />shoreline habitats. Each haul ~as treated as a separate sample. The size of <br />each area seined ~as quantified and the mean depth and velocity of the ~ater, <br />as well as the dominant substrate size, were measured at two equidistant <br />points along a transect through the center of the area seined. water <br />temperature was recorded. Area seined ~as dependant on back~ter size and thus <br />varied among sample sites, but generally did not exceed 250 m. Samples were <br />taken ~ith 1/4-in-mesh (6-mm-mesh) seines in 1982 and 1/8-in (3-mm) seines in <br />1983 and 1984. All fish were identified in the field, enumerated, and released <br />alive in 1982. In 1983 and 1984, fish smaller than about 40 mm long ~ere <br />preserved in 101 formalin and later identified in the laboratory under a <br />binocular microscope. These changes in gear and identification procedure <br />between 1982 and subsequent years resulted from our belief that small Colorado <br />squawfish were escaping the 6-mm-mesh seine and that many of those captured were <br />too small to be accurately identified in the field. River~ide surveys ~ere <br />conducted once in 1982 (September). However, because we were also interested in <br />the temporal effect of sampling on the relative abundance of these young <br />squawfish, two surveys were conducted in 1983 (September and October) and three <br />in 1984 (August, September and October). Data are summari2ed as the number of <br />Colorado squawfish captured in back~ater habitats per 10 m swept ~ith the <br />seine. Data are pooled ~ithin ID-mi-long reaches for graphical presentation and <br />~ithin the four study reaches for statistical analysis. <br /> <br />Statistical analysis <br /> <br />Total displacement (distance between the most upstream and the most <br />downstream locations) of radio-equipped Colorado squa~fish ~as compared among <br />years and river reaches, as well as among fish size groups. Preliminary <br />analyses ~ere conducted to determine ~hether fish size ~as related to distance <br />moved. Three separate comparisons ~ere made, ~ith fish grouped into one of t~o <br /> <br />9 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />