Laserfiche WebLink
<br /> <br />~ <br /> <br />Hamman <br />,q<6q <br /> <br />'" <br /> <br />al. <br />i'ety <br />~hal <br />~ of <br />~at- <br />sful <br />=ig- <br />;ase <br />"lod <br />js. <br /> <br />The Progressive Fish-Cul/urisl 51 :27-29, 1989 <br /> <br />COMMUNICA nONS <br /> <br />()7/{,L <br /> <br />-- <br /> <br />Survival of Colorado Squawfish Cultured in Earthen Ponds <br />. . <br /> <br />ROGER L. HAMMAN <br /> <br />U.S. Fish and Wildlife Service <br />Dexter National Fish Hatchery <br />Post Office Box 219 <br />Dexter, New Mexico 88230, USA <br /> <br />W. <br />rial <br />J.S. <br />85- <br /> <br />Abstract. -Swim-up fry and fingerlings of Colorado <br />squawfish (Ptychocheilus lucius) were successfully reared <br />in earthen ponds at the Dexter, New Mexico, National <br />Fish Hatchery. Swim-up fry (95,340-104,420/1b) were <br />stocked in 0.89-O.98-acre ponds at the rate of 105,316- <br />137,438 fry/acre; fingerling fish (980-I,088/Ib) were <br />stocked in 0.98-1.08-acre ponds at the rate of 52,978..,. <br />55,424 fingerlings/acre. Ponds were treated initially with" <br />organic and inorganic fertilizers in addition to periodic <br />applications of alfalfa pellets. Swim-up fry were supple- <br />mentally fed a formulated trout feed. Survival ranged <br />from 27.7 to 36.0% for swim-up fry and averaged 92.2% <br />for fingerlings: <br /> <br />fish <br /> <br />lon, <br /> <br />use <br />ies. <br />:"'R- <br /> <br />po- <br />tas- <br />-rIal <br /> <br />The Colorado squawfish (Ptychocheilus lucius) <br />is presently being cultured at Dexter National Fish <br />Hatchery, New Mexico. The largest native cypri- <br />nid in North America, it formerly reached lengths <br />up to 6.0 ft and weights of 80 Ib (USFWS 1978), <br />but specimens larger than 15 Ib have rarely been <br />found in the past 15 years. Considered endemic <br />to the Colorado River basin, it is one of the na- <br />tive fishes that have undergone population de- <br />clines in the past century (Behnke and Benson <br />1980; Holden and Wick 1982). The Colorado <br />squawfish is believed to be extirpated in the lower <br />basin (Minckley 1973); although it is stiIl present <br />in much of the upper basin (Joseph et al. 1977), <br />it is considered in danger of extinction. Deacon et <br />al. (1979) listed the Colorado squawfish as an en- <br />dangered species in the states of Arizona, Califor- <br />nia, Colorado, New Mexico, Nevada, Utah, and <br />Wyoming. It is also listed as endangered by the <br />U.S. Department of the Interior (1980; see also <br />Johnson and Rinne 1982). <br />In 1974, a propagation program was started at <br />Willow Beach National Fish Hatchery, Arizona, <br />to test and develop techniques for spawning and <br />rearing the Colorado squawfish (Toney 1974). The <br />program was transferred, in 1981, to Dexter Na- <br />tional Fish Hatchery. Although the species' repro- <br />ductive biology (Hamman 1981, 1986) and early <br />Iife.,b~Sfory (Marsh 1985) have become better <br />un~od, little has been documented concern- <br /> <br />A. <br />10- <br /> <br />:lrs. <br />ere, <br /> <br />mic <br />for <br />ler- <br /> <br />1l1d <br />24- <br /> <br />Jer- <br />:ul- <br /> <br />ups <br />md <br />sh- <br /> <br />ing its survival under culture conditions from fry <br />to fingerling size (Hamman 1981). The purpose of <br />this paper is to present data on the survival of <br />Colorado squawfish cultured during 1987 at Dex- <br />ter National Fish Hatchery. <br /> <br />Methods <br /> <br />Spawning techniques used during this study were <br />those described by Hamman (1981,1986). Twen- <br />ty-five Colorado squawfish females (1974 year <br />class) were induced to spawn by injecting them <br />with acetone-dried carp pituitary. Average weight <br />of females was 4.7 Ib; mean fecundity was 82,576 <br />eggs. <br />Fry culture. -Colorado squawfish swim-up fry <br />(337,620) were stocked in June 1987 in three 0.89- <br />0.98-acre earthen ponds of 3-ft average depths. <br />Stocking densities were 105,316-137,438 fry/acre. <br />At stocking, the fry ranged from 95,340 to 104,420/ <br />Ib among the three ponds. No substantial handling <br />mortality was observed. <br />Approximately 10 d before swim-up fry were <br />stocked, ponds were treated with organic and in- <br />organic fertilizers. Ponds received alfalfa pellets at <br />300 Ib/acre and superphosphate at 50 Ib/acre. Af- <br />ter the initial treatment, ponds received six weekly <br />fertilizations of alfalfa pellets at 100 lb/acre. <br />Chemical and physical characteristics of incoming <br />water supply to ponds is shown in Table 1. <br /> <br />TABLE I.-Water analysis summary for water well 1 <br />at Dexter National Fish Hatchery, New Mexico. <br /> <br />Variable <br /> <br />Sodium (Na) <br />POlassium (K) <br />Calcium (Ca) <br />Magnesium (Mg) <br />Chloride (CI) <br />Sulfale (S04) <br />Bicarbonate (HC03) <br />Total iron (Fe) <br />Silica (Si02) <br />Total solids <br />Total hardness (CaC03) <br />Alkalinity (CaC03) <br />Nitrate (N03) <br />Conductivity (250C) <br />pH <br />Temperature <br /> <br />Concentration <br />or measure <br /> <br />317 ppm <br />5 ppm <br />513 ppm <br />199 ppm <br />340 ppm <br />1,955 ppm <br />158 ppm <br />0.01 ppm <br />27 ppm <br />3,680 ppm <br />2,100 ppm <br />260 ppm <br />2.5 ppm <br />3,900 "S/cm <br />7.35 <br />640F <br /> <br />27 <br />