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<br />18 <br /> <br />WESTERN NORTH AMERICAN NATURALIST <br /> <br />[Volume 68 <br /> <br />TABLE 2. Parameters for a response sUlface model to <br />estimate total length as a function of water temperature <br />(1'), time (D, days post-hatch; fish were 9 days post-hatch <br />when experiments began and 37 days post-hatch at the <br />end), and the squared and interaction tellns for those <br />effects. The main effect fi)r T was not included (P = 0.39), <br />The overall model was statistically significant (F 4,23 = <br />174.2. P < 0,0001, R2 = 0,968). <br /> <br />Parameter Estimate s:;: t-value Pr > t <br />Intercept 13,055 2.768 4.72 <0,0001 <br />D -0,591 0.207 2.85 0,009 <br />T'T -0,010 0.005 2.02 0.055 <br />D'D 0,008 0,003 2,99 0,007 <br />D'T 0,038 0,007 5,16 <0.0001 <br /> <br />regression relationship suggested that time <br />(days post-hatch), the sqmu'ed terms for time <br />and temperature, and the time X temperature <br />interaction all importantly affected growth of <br />razorback sucker larvae; the interaction was <br />the most significant effect (Table 2). <br />Based on mean growth rates for each treat- <br />ment, time required for razorback suckers to <br />exceed 25 mm TL was 30 days (post-hatch) at <br />25SC, 33 days at 22SC, 36 days at 19.50C, <br />and 41 days at 16.50C. Time required for slow- <br />growth razorback suckers to exceed 25 mm TL <br />under the simulated 200C temperature (0.29 <br />mm . d-1) was 52 days. <br /> <br />DISCUSSION <br /> <br />Water temperature had a strong, positive <br />effect on growth of early life stages of razor- <br />back sucker, particularly when t~mperatures <br />were 19SC or higher. A threshold was appar- <br />ent, because change in mean length of razor- <br />back suckers reared at 19SC was 50% greater <br />than for those reared at 16.50C over the dura- <br />tion of the experiment; bTfOWth rates at higher <br />temperatures increased at a lower rate. Differ- <br />ences in mean weight were even greater. <br />Razorback suckers reared at 19.50C were more <br />than \:\\.ice as heavy as those reared at 16.50C. <br />I did not test colder temperatures because my <br />main interest was determining more optimal <br />, growth conditions and because some informa- <br />tion describing growth of early life stages of <br />razorback sucker at cooler temperatures \vas <br />already known (Clarkson and Childs 2000). <br />These findings support those of Clarkson and <br />Childs (2000) and others who found faster de- <br />velopment and higher growth rates of early <br />life stages of razorback sucker and other native <br />fishes of the Colorado River Basin at higher <br /> <br />water temperatures (Marsh 1985, Bestgen and <br />Williams 1994, Bestgen 1996). GrO\vth rates of <br />razorback suckers at the highest water tem- <br />peratures tested are relevant because water <br />temperatures of the Green River floodplain <br />exceeded 200C in early June and reached or <br />exceeded 250C by late June (Modde et al. <br />2001, Christopherson et al. 2004, Modde and <br />I-Iaines 2005), a period just after razorback <br />suckers hatch in the. Green River (Modde et <br />al. 2001, Bestgen et al. 2002). <br />Growth rates of razorback sucker larvae <br />observed in this study were generally Ulster <br />than those in most other studies, perhaps due <br />to unlimited food rations or warmer tempera- <br />tures. Laboratorv-reared razorback suckers <br />grew about 0.25 ~m' d-1 (Bundy and Bestgen <br />2001), pond-reared ones grew about 0.21-0.27 <br />mm . d-I (Papoulias and Minckley 1992), and <br />wild fish from the Green River grew about <br />0.27-0.35 mm . d-1 (Muth et al. 2000). The <br />faster growth rate of razorback suckers reared <br />at 19SC in this study (0.58 mm TL . d-1) <br />compared to those reared at 200C (0.29 mm <br />TL . d-1) in Clarkson and Childs (2000) is <br />inexplicable because both studies used the <br />same Artemia diet, food was provided ad libi- <br />tum, and razorback sucker densities in tanks <br />were similar (2.5 fish' L-l in this study, 1.3- <br />2.6 fish' L-I in Clarkson and Childs 2000). <br />High growth rates of the few juvenile razor- <br />back suckers documented in the wild in the <br />Green River Basin suggested that fast growth <br />and survival may be linked (Gutemmth et aL <br />1994, Modde 1996, Modde et al. 2001). <br />Differences in time for razorback sucker <br />larvae to achieve the hypothetical predation <br />threshold of 25 mm TL under different grO\vth <br />rates suggested that water temperature and <br />food resources may playa role in determining <br />intensity of size-dependent mortality processes <br />and survival rates in the wild. I do not imply <br />that survival is assured once razorback suckers <br />reach 25 mm TL but suggest that fast growth <br />may be important when the early life stages of <br />this species are in the presence of large macro- <br />invertebrates or abundant small-bodied preda- <br />ceous fishes known to prey upon cyprinifoml <br />fish larvae in nursery habitats (Minckley 1973, <br />Ruppert et al. 1993, Horn et al. 1994, Bestgen <br />et al. 2006, Markle and Dunsmoor 2007). <br />Increased availability of nursery areas for <br />razorback sucker larvae that promote fast <br />growth and are relatively free of predators <br />