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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />.1 <br />I <br />I <br />I <br />I <br />I <br /> <br />Marsh and Langhorst 1988; Papoulias and Minckley 1990, 1992; Modde 1997), Papoulias and <br />Minckley (1990) suggested that many wild-caught razorback sucker larvae from Lake Mohave <br />are in the "critical period" (sensu Hjort 1914) of transition from dependence on endogenous to <br />exogenous foods (within about the first 3 weeks after hatching), They concluded that mortality <br />related to low abundance of appropriate foods may contribute to year-class failure of razorback <br />suckers in Lake Mohave, Papoulias and Minckley (1992) found that survival of larval razorback <br />suckers reared at 12-170C in earthen ponds fertilized at three levels (low, medium, and high) was <br />independent of invertebrate densities (survival ranged from 67.4% in the low-fertilization <br />treatment to 89.8% in the medium-fertilization treatment), but total larval growth was <br />significantly greater at the two higher invertebrate densities. Based on their observations of mean <br />TL at each fertilization level by 7-d intervals, growth rates oflarvae during the first 56 dafter <br />swimup averaged about 0.17, 0.16, and 0.13 mm TL/d for the high, medium, and low treatments, <br />respectively. By comparison, our estimated mean growth for otolith-aged larval razorback <br />suckers less than 35 d old (posthatching) ranged from 0.27 mm TL/d (1994, lower Green River) <br />to 0.35 mm TL/d (1996, middle Green River). Our estimates of growth on wild-caught fish are <br />likely biased high because many slow-growing individuals had probably already been "removed" <br />from the populations by natural selection (e.g., Miller et al. 1988; Rice et al. 1993; Bestgen et al. <br />1997). Nonetheless, based on observations of larval diet, composition and abundance of <br />invertebrates in quiet-water soft-sediment riverine habitats, and growth and survival of captive <br />larvae, it appears that food abundance in existing razorback sucker nursery habitats on the Green <br />River is adequate to meet the minimum nutritional requirements for larval survival. However, <br />the growth potential of razorback sucker larvae is greater than we observed. Mean growth rates <br />of larval razorback suckers reared in the laboratory for 28 d after the start of exogenous feeding <br />and fed nauplii of Artemia sp. ad libitum twice daily were 0.39, 0.58, 0.65, or 0.72 mm TL/d at <br />constant water temperatures of 16.5, 19.5,22.5, or 25.50C, respectively (K. R. Bestgen, Larval <br />Fish Laboratory, personal communication). Relatively minor differences in growth rates can be <br />biologically significant if size-dependent processes, such as predation by small, gape-limited <br />predators, ;ll"e important regulators oflarval survival. For example, Bestgen et al. (1997) <br />demonstrated through experiments and recruitment-model simulations that the predatory effects <br /> <br />21 <br />