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fgQl ~ u~ <br />666 N <br />in efficiencies of thrs~ sampling techniques for es- <br />timating fish populations in small streams. Pro- <br />gressive Fish-~tilturist 46:180-.184. <br />Northcote, T. Cy ;"and D. W. Wilkie. 1963. Underwater <br />census yf stream fish populations. Transactions of <br />the Pl.lnerican Fisheries"Society 92:(46-151. <br />Watke~;" C. R., R. E. Lennon, and B. L. Berger. 1964. <br />reliminary observations on the toxicity of anti- <br />mycin A to~ish and other aquatic animals. U.S. <br />Trnnsactions ojthe Amerfcnn Fisheries Society 120:666-668, 1991 <br />® Copyright by the American Fisheries Society 1991 <br />OTES <br />g1H~ <br />Bureau of Sport Fisheries and Wildlife, Investiga- <br />tions in Fish Control 2, Washington, D.C. <br />Werner, E. E., D. J. Hall, D. R. Laughlin, D. J. Wagner, <br />L. A. Wilsmann, and E C. Funk. 1977. Habitat <br />partitioning in a freshwater fish community. Jour- <br />nal of the Fisheries Research Board of Canada 34: <br />360-370. <br />Received October 1, 1990 <br />~. <br />h Accepted March I, 1991 <br />A <br />Effect of Sunlight on Tetracycline Marks in Otoliths of <br />Colorado squawfish Larvae <br />ROBERT T. MUTH ANa KEVIN R. BESTGEN <br />Department ojFishery and Wildlife <br />Biology and Larval Fish Laboratory <br />Colorado State University <br />Fort Collins, Colorado 80523, USA <br />Abstract. -Embryos and newly hatched larvae of Col- <br />orado squawfish Ptychocheilus Lucius were immersed in <br />tris-buffered solutions of 350 mg tetracycline hydro- <br />chloride (TC)/L of distilled water for 24 h (embryos) or <br />12 h (larvae). Larvae from both treatments were held <br />indoors prior to swim-up and indoors or outdoors for 7 <br />d afer swim-up. Exposure to sunlight under simulated <br />natural conditions had no detectable effect on quality or <br />retention of fluorescent TC marks in otoliths. Marks in <br />all otoliths examined were distinct and lucid to bright. <br />Mark-recapture studies on age-0 Colorado squawfish <br />could facilitate research needed for applied management <br />and population recovery. Tetracycline marks in otoliths <br />appear to be suitable for this purpose. <br />Research on early life stages is a principal focus <br />of the recovery program for the Colorado squaw- <br />fish Ptychocheilus Lucius, which has been listed <br />federally as an endangered species. Areas of in- <br />vestigation include dispersal patterns of larvae, <br />environmental requirements of age-0 fish, rela- <br />tionships between abundance of larvae and re- <br />cruitment to juvenile and adult stocks, and causes <br />of early mortality (e.g., Kaeding and Osmundson <br />1988; Nesler et al. 1988; Tyus and Karp 1989; <br />Haines and Tyus ] 990). Mark-recapture studies <br />could be used in many of these investigations if <br />adequate methods were adapted or developed for <br />marking early life stages (Wydoski and Emery <br />1983; Tsukamoto 1985). <br />Tetracycline antibiotics are in vivo bone tissue <br />markers that bind to calcium ions at sites of bone <br />proliferation. These compounds, once deposited <br />in bone, fluoresce yellow when illuminated by ul- <br />traviolet (UV) light, particularly at 360 rim (We- <br />ber and Ridgway 1967). Incorporation of tetra- <br />cycline marks in otoliths by immersion of fish <br />embryos or early larvae in a tetracycline solution <br />is one technique for mass-marking young fish <br />(Hettler 1984; Tsukamoto 1985, 1988; Tsuka- <br />moto and Kajihara 1987). In preparation for fu- <br />ture field experiments, Muth et al. (1988) and Muth <br />and Nesler (1989) established procedures for suc- <br />cessful application of this marking technique to <br />early life stages of Colorado squawfish. <br />The possibility that exposure to the UV portion <br />of sunlight will reduce the quality or retention of <br />tetracycline marks in otoliths remains a concern <br />(Hettler 1984; Brothers 1985). Once excited to a <br />higher energy level by absorption of UV light, tet- <br />racyclinemolecules are unstable and decay through <br />fluorescence almost instantaneously (Lehninger <br />1975). I,orson and Mudrak (1987) examined ef- <br />fects of sunlight on fluorescent marks in otoliths <br />of young American shad Alosa sapidissima that <br />had been treated with tetracycline 15 to 18 d after <br />hatching. However, UV degradation of tetracy- <br />cline marks in otoliths could be most severe in <br />embryos or newly hatched larvae released into the <br />wild soon after marking. Although the UV spec- <br />trum is rapidly attenuated in water (Koller 1965), <br />recently hatched larvae of many fishes, including <br />Colorado squawfish, are nearly transparent, have <br />little protective melanophore pigmentation, and <br />often swim near the water surface. Within the first <br />few days of marking, tetracycline deposited in oto- <br />liths would be covered by only a few new layers <br />of calcium carbonate. This study addressed the <br />question of tetracycline mark degradation due to <br />