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<br />906 <br /> <br />HAINES AND MODDE <br /> <br />ratory studies were age-O Colorado squawfish pro- <br />duced at Dexter (New Mexico) National Fish <br />Hatchery. During the study, the fish were held at <br />temperatures ranging from 190C to 210C and fed <br />BioKiowa diet. <br />Prior to marking, fish were anesthetized with <br />MS-222 (tricane methanesulfonate). A dental in- <br />oculator (Syrijet Mark II) was used to inject red <br />tattoo ink intracutaneously in the caudal peduncle <br />as described by Laufle et al. (1990). After marking, <br />the fish were held in an aquarium for 10-15 min <br />to confirm dye penetration. The elastic polymer <br />(provided by Northwest Marine Technology) was <br />injected subcutaneously on the dorsal surface left <br />of the dorsal fin with a I-mL insulin syringe and <br />28-gauge needle. The polymer was implanted as <br />a liquid and subsequently solidified into an elastic <br />solid. For the third treatment, the fish's left pelvic <br />fin was clipped. <br />Mark longevity and survival.-The study began <br />4 December 1992 when fish averaged 49.8 mm TL <br />(SD = 7.04 mm). Fish with each of the three marks <br />were held in flow-through troughs (2.0 m X 0.5 <br />m X 0.1 m) for 142 d. Three replicate lots con- <br />sisting of 120 fish (40 fish of each mark) were <br />tested. Deaths were recorded daily. Fish were ex- <br />amined for marks on 22 December 1992 and 12 <br />February, 30 March and 22 April 1993. On 22 <br />April 1993, all fish having recognizable elastic <br />polymer marks were placed in a cage in an outside <br />pond and held an additional 104 d. On 4 August <br />1993 the number of fish having a recognizable <br />mark were counted. <br />One-way analysis of variance was used to assess <br />differences in mean length, mortality, and mark <br />retention among marking treatments. Percentages <br />were arcsine-transformed to more closely approx- <br />imate normality. Tukey's honestly significant dif- <br />ference method was used to compare differences <br />among means (Wilkinson 1990). <br />Vulnerability of marked fish to predation.- <br />Marked and unmarked (control) age-O Colorado <br />squawfish were exposed to predation by large- <br />mouth bass Micropterus salmoides. Marking pro- <br />cedures were the same as described in the previous <br />section. Two recovery times (IS and 120 min) were <br />tested; recovery time was defined as the time <br />elapsed between marking and exposure to preda- <br />tion. The experiment was conducted in six circular <br />tanks (1.8 m in diameter and 0.9 m deep) and <br />consisted of two trials. Each tank held two large- <br />mouth bass (205-255 mm TL) that had been placed <br />in the tanks 2 or 3 weeks prior to the experiment <br />and fed fathead minnows Pimephales promelas. <br /> <br />Food was withheld for at least 3 d prior to begin- <br />ning each trial. <br />For each trial, 144 Colorado squawfish were di- <br />vided into six lots of 24 fish (6 fish with each of <br />the three marks and 6 controls); each lot was ran- <br />domly assigned to a tank. Three tanks received <br />fish that had recovered IS min and three received <br />fish that had recovered 120 min. After 3 min, sur- <br />viving Colorado squawfish were counted. Data <br />were transformed to instantaneous mortality rates <br />per min for each largemouth bass and analyzed by <br />means of a two-way analysis of variance (4 marks <br />X 2 recovery times) with three replications, in <br />which the variance assigned to date of trial and <br />tank were blocked (Wilkinson 1990). <br />Field-marking evaluation.-Based on laboratory <br />experiment results, the syringe-injected elastic <br />polymer was selected to determine the feasibility <br />of using mark-recapture techniques to study <br />movement patterns of young Colorado squawfish <br />and estimate abundance and winter survival. Field <br />studies conducted in the autumn of 1992 and <br />spring of 1993 were designed to answer four ques- <br />tions: (I) Can the mark be easily applied and rec- <br />ognized in the field? (2) How much postmarking <br />mortality occurs? (3) How much immigration and <br />emigration occur? and (4) What biases and pre- <br />cision can we expect from an optimally designed <br />mark-recapture study? <br />The study area was a 16.1-km reach of the Green <br />River, beginning 3 km below Jensen, Utah. For <br />each population estimate, three sampling passes <br />were made. With one exception, sampling passes <br />consisted of seining (4.5 X 1.9 m, 4.0-mm mesh) <br />all backwaters over 30 m2 within the study reach; <br />the first pass in autumn consisted of seining only <br />large backwaters (70-800 m2, N = 6). Each seine <br />haul was approximately 8 m in length (range, 4- <br />10 m). Age-O Colorado squawfish received marks <br />unique to each backwater. No fish were marked on <br />the third pass. <br />Captured Colorado squawfish were placed in a <br />20-L bucket filled with river water containing <br />0.5% added salt, anesthetized within 20 min with <br />MS-222 (0.1 g/L), and marked with red elastic <br />polymer. Fish recovered in a 20-L bucket of river <br />water with 0.5% salt for 20-30 min and then were <br />placed in a floating net-pen until the seining and <br />marking of all specimens were completed; elapsed <br />holding time ranged from 0.5 to 3.0 h.No salt was <br />added to the holding buckets the first 2 d of sam- <br />pling. All marked fish were released into the back- <br />water of origin. On five occasions, postmarking <br /> <br />~ <br />