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<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 />
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