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i 74 <br />The Southu~eslern Naftnalisf <br />no a <br /> z~ <br />zc ~ ~ <br />7 <br /> <br />c <br /> 75 I 76 I I 77 III 78 I V 79 V - 00 V I <br /> YEGR OF LIFE <br />vol. 28, no. 2 <br />Frc. 8.-Comparisons of growth of known-age razorback suckers (numbers indicate sample <br />sizes), with growth estimates back-calculated from scale annuli Ior 20 fish sacrificed in 1975. <br />Horizontal lines are means, bars represent tl standard error, and vertical lines represent thr range <br />of lengths (darkened -known-age fish; open -estimated from annuli). <br />investigators could not be achieved for more than the first six apparent <br />annular marks on scales. After [hat point dense circuli were over-lapping, <br />obscure, or obviously lacking, with scales often appearing to have grown <br />uniformly except for random "checks" that could not be interpreted as <br />annuli. Most scales were deeply worn on the margins, and regenerated scales <br />(excluded from further consideration) were common. Minimum estimates for <br />ages of fish with possible annuli were ] 1 to ]4 years, and maxima ranged to <br />>20 years. Estimates of growth rates for the first six years of life mmpare <br />favorably, however, with growth o[ known age fishes under hatchery and <br />laboratory conditions (Fig. 3). <br />Variation in length o[ individuals from the hatchery cohort is remarkably <br />high, and this is shared by estimates of growth made from scales of wild- <br />caught adults. Multiple or protracted spawning in nature may result in a <br />similar size distribution, but the hatchery cohort all were spawned the same <br />day in 1974. A similar size range (7.1 to 13.5 cm TL at 5 months of age) in <br />hatchery produced fish reared in ponds at Dexter, News Mexico, in 1981 (J. <br />E. Johnson, pers. comm.) provides further evidence {or inate variability in <br />this life-history character. Size variation in the 1914 cohort resulted in some <br />hatchery individuals becoming sexually mature at six years of age and 35.39 <br />crtt TL, white siblings <35 cm TL had no sexual development. <br />McAda and L1'ydoski (1980) similarly found little relationship between <br />scale radius and body lengths of razorback suckers. They assigned ages of 4 <br />to 9 years to fish 49 to 61 cm TL, but doubted accuracy of their determina- <br />tions. Evidence against validity of their data was a report by James St. <br />Amant (in McAda and t•'1'ydoski, 1980) of a 66.2 cm TL male from the lower <br />Colorado River estimated to be 22 years old and another large fish (length <br />unknown) that was 17 years old, both on the basis of sagitta analysis. <br />b4cAda and Wydoski also noted a fish recaptured 1.5 years alter original <br />tagging in the upper river had not grown at all, and a second specimen <br />(50.8 cm TL) had grown only 8 mm when recaptured 3.5 years later. <br />I am of the opinion that razorback suckers currently in Lake Mohave <br />hatched when the reservoir was filling in the early 1950s. If this is so, mean <br />growth between 1956 and 1963 would have slowed from ca. 7.0 cm in their <br />seventh year o[ life (Fig. 3) to less than a cm per year in 1964 (Fig. 2). Males <br />May 1989 Mintkley-Stains of Razorback Sucker 175 <br />may have essentially ceased to grow after 1968 or before (Fig. 2), tending to <br />suppress the apparent growth rate of the over-al! population. Death of <br />larger, faster growing fish, and slow growth by smaller fish toward the mean <br />[or the cohort(s), might also serve to explain the remarkably slow average <br />growth rate in recent years. An average o[ 7.3 carcasses;'km o[ large (>50 cm <br />TL) razorback suckers were along the shoreline of Lake Mohave in spring <br />1979. Sagittae have now been obtained from a representative sample of <br />razorback suckers from Lake Mohave, so accurate aging will hopefully soon <br />be accomplished. <br />Reproduction.-McAda and Wydoski (1980) recently summarized informa- <br />tion on reproduction by razorback suckers. Before large dams, razorback <br />suckers migrated in early spring, evidently to spawn (Hobbs and Miller, <br />]953). Jordan (1891) reported such a migration info the Animas River, Colo- <br />rado, and Chamberlain (1904) cited early repoxts that they congregated in <br />tributaries to larger streams. Minckley and Carothers (1979) collected a <br />gravid female razorback sucker and observed two other individuals in the <br />Paria River, Arizona, in June ]978. Concentrations in the Salt River of Ariz- <br />ona in the 1920s (Ellison, 1980) were presumably spawning aggregations. <br />Douglas (1952) specifically described spawning by razorback suckers in <br />shallow coves of Lake Havasu in March ]950. Water depths ranged from <br />0.25 to 1.5 m and temperatures were between 14° and 16°C. lndividua] <br />females were accompanied by 2 to 6 males as they swam in small circles over <br />the bottom. Mates remained close to responsive females and the fish occa- <br />sionally settled to the bottom and vibrated their bodies rapidly. Gamete <br />emission was not visible because of silt disturbed by the fish. Jonez and <br />Sumner (1959) observed razorback suckers spawning in Lake Mead between <br />1 March and 15 April 1953, and described extensive shoreward movements at <br />that time. There was a tendency [or the fish to concentrate near in[lowing <br />rivers. Water temperatures were between 12° and 18°C. Spawning was <br />widespread along grave] shorelines in water 0.6 to 5 m deep. My extensive <br />observations corroborate those o[ Douglas (1952). I have most often observed <br />spawning razorback suckers in shallow (<5 m) waters along gravelly, sub- <br />merged terraces in bays and inlets, and once along canyon walls and on a <br />gravel-cobble bar among boulders in current about 1.6 km below Hoover <br />Dam. The last fish were concentrated in an area of inflowing hot springs <br />(Gustafson, 1975a). <br />McAda and Wydoski (1980) collected razorback suckers in spawning con- <br />dition from water about 1 m deep and at the upstream ends of gravel bars in <br />the upper Colorado River basin. Substrate was predominately cobble, and <br />water velocity was about 1 m/sec. Females captured over bars were ripe, but <br />those from other places were not; al] males over or near bars were ripe. They <br />also observed behavior resembling that described by Douglas (1952) in the <br />gravel pit at Walker Wildlife Area, but no successful reproduction was indi- <br />cated. Linda Ulmer and Loudermilk (pers. comm.) have confirmed spawn- <br />ing activity and hatching of eggs on small, gravelly, wave-cut terraces of <br />Senator Wash Reservoir, California. <br />Holden (in McAda and Wydoski, 1980) collected a few subadult fish in the <br />upper Colorado River basin before 1977, and Holden (1978) reported tenta- <br />