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<br />4? <br />ments of fin rays in all fins (35 mm). Specimens <br />examined all had attained active swimming capa- <br />bility (middle prolarvae), most were early postlar- <br />vae, and the largest were middle postlarvae (termi- <br />nology for razorback suckers from Minckley & <br />Gustafson 1982). Jaws were formed and mouth and <br />anus were open, all were thus presumed capable of <br />feeding. However, yolk had not been completely <br />assimilated by the smallest individuals, which may <br />not yet have begun to feed. <br />Adjacent to Arizona Bay is a backwater (Fig. 1) <br />separated from the reservoir by a wave-formed spit <br />of coarse gravel. This protected habitat was se- <br />lected for rearing razorback sucker in isolation to <br />preclude potential destruction of eggs or larvae by <br />introduced fishes, indications of which had been <br />observed in Lake Mohave and elsewhere (see be- <br />low). <br />The backwater had maximum depths of 1.7 to <br />3.7 m and surface areas of 0.85 to 2.10 ha at respec- <br />tive reservoir elevations of 193.5 to 195.5 m, and <br />was fed by reservoir water that freely exchanged <br />through the porous berm. Water temperature par- <br />alleled that of the reservoir, but averaged slightly <br />cooler (-1.1° C) in winter and warmer in summer <br />(+1.8°C); thermal differences were most pro- <br />nounced on early winter mornings and late summer <br />afternoons. Substrates were coarse gravel around <br />margins and organic silt in deeper areas. Shallow <br />regions were occupied by dense stands of water- <br />milfoil (Myriophyllum spicatum) interspersed with <br />curly leaf pondweed (Potamogeton crispus). Fishes <br />which initially inhabited the backwater were <br />threadfin shad (Dorosoma petenense), common <br />carp (Cyprinus carpio), channel catfish (Ictalurus <br />punctatus), mosquitofish (Gambusia affinis), <br />largemouth bass (Micropterus salmoides), green <br />sunfish (Lepomis cyanellus), and bluegill (L. mac- <br />rochirus). All are non-native. These were removed <br />by ichthyocide in autumn 1984, and the backwater <br />stocked in January-February 1985 with 30 female <br />and 150 male adult razorback suckers collected <br />from Arizona Bay. These spawned successfully <br />and produced larvae that were first captured on 7 <br />March 1985 and subsequently monitored through <br />their disappearance in early April (see below). <br />Larval sampling in shallow littoral areas of both <br />the reservoir and backwater was generally at night, <br />when the small fishes were attracted to a spotlight, <br />captured by dipnet, and preserved in 5% buffered <br />formalin. Zooplankton in Lake Mohave was col- <br />lected in duplicate Clarke-Bumpus samples (8011. <br />mesh) towed for 5 min at 1.3 km hr-' and 0-3m <br />depth throughout habitats occupied by larval <br />suckers. Backwater samples were duplicate, com- <br />posite 38-L grabs concentrated through 80 µ mesh. <br />Zooplankters were preserved in 5% formalin and <br />later identified, enumerated (Sedgwick-Rafter <br />chamber), and measured (greatest body length and <br />width) at 35-450x with a light microscope. Linear <br />dimensions were converted to individual volume <br />on the basis of similarity to regular geometric sol- <br />ids. Foods of larval suckers were treated in a simi- <br />lar manner after removal from digestive tracts. <br />Selection of foods by taxon and size class (volume) <br />was evaluated by a linear index: L = r; - p;, where <br />r; and pi are relative abundances expressed as pro- <br />portion of prey item i in the gut and habitat, respec- <br />tively (Strauss 1979, 1982). The index ranges from <br />-100 to +100. Positive values indicate preference, <br />negative values avoidance or inaccessability, and <br />values near zero indicate random feeding. We con- <br />sidered /L/ <10 not different from L = 0. <br />Results <br />Lake Mohave <br />Razorback sucker larvae were first captured from <br />Lake Mohave in Hammerhead Cove on 9 Febru- <br />ary, approximately 3 weeks after initial observa- <br />tions of spawning at that location. Larvae became <br />abundant within the next few days and remained <br />common into April. Larvae averaged 10.6 ± 0.3 <br />(SE) mm TL (n = 410) throughout the period, in- <br />dicating continuous spawning and larval produc- <br />tion. There was no evidence of larval growth since <br />neither mean nor maximum TL increased; the <br />largest individual captured from the reservoir was <br />12.2 mm. Comparisons with known-age fish reared <br />experimentally at similar temperatures (Marsh <br />1985, Papoulias unpubl. data) indicated maximum <br />age of the largest specimens was at most a few <br />weeks. <br />1