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Last modified
8/11/2009 11:32:58 AM
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UCREFRP
UCREFRP Catalog Number
9702
Author
Petersen, J.H., and C.P. Paukert.
Title
Development of a bioenergetics model for humpback chub and evaluation of water temperature changes in the Grand Canyon, Colorado River.
USFW Year
2005.
USFW - Doc Type
Transactions of the American Fisheries Society
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968 <br />PETERSEN AND PAUKERT <br />TABLE 5.-Final parameter values used in the bioenergetics model of juvenile and subadult humpback chub. Except <br />for SDA, the consumption and respiration parameters, were based on Monte Carlo filtering of humpback chub growth <br />at 24°C. The parameters for SDA, FA, and UA are from other species, so no variance was associated with these values. <br />Parameter <br />abbreviation <br />Description <br />Mean (SD) Coefficient of <br />variation (%) <br /> Consumption <br />CA Intercept 0.154 (0.027) 17 <br />CB Slope -0.251 (0.028) 11 <br />CQ Consumption Q10 2.39 (0.19) 8 <br />CTO Optimum temperature 28.1 (2.3) 8 <br />CTM Maximum temperature 31.5 (2.5) 8 <br /> Respiration <br />RA Intercept 0.0049 (0.0026) 53 <br />RB Slope -0.084 (0.039) 47 <br />RQ Respiration Q10 2.42 (0.17) 7 <br />RTO Optimum temperature 28.2 (2.3) 8 <br />RTM Maximum temperature 31.6 (2.4) 8 <br />ACT Activity 1.16 (0.41) 36 <br />SDA Specific dynamic action 0.15 <br /> Excretion and egestion <br />UA Proportion of excretion 0.1 <br />FA Proportion of egestion 0.1 <br />(Figure 3). Regardless of food availability, pre- <br />dicted growth rates for juvenile and subadult <br />humpback chub were zero or negative at temper- <br />atures above approximately 31°C. <br />For juvenile humpback chub, the predicted <br />growth rate was fairly constant across a broad <br />range of temperatures (-5-25°C) when food avail- <br />ability was in the range of 0.4-0.6 (Figure 3A). <br />For example, with a food availability of 0.5, <br />growth rate varied little from 5 to 27°C. When food <br />availability was relatively low (p < 0.3) growth <br />rate was negative for all temperatures. For subadult <br />humpback chub, growth rates were negative or <br />zero when food availability was low (p < 0.5) for <br />all temperatures examined (Figure 3B). The spe- <br />cific growth rates predicted across a fairly broad <br />range of food availability and temperature is con- <br />sistent with observed growth rates from laboratory <br />and field studies (compare Figure 3 and Table 3), <br />suggesting the model is operating within the ex- <br />pected range. <br />Bioenergetic Simulations of a Potential <br />Temperature Control Device Scenario <br />Before the completion of Glen Canyon Dam in <br />1963, average monthly water temperature through <br />the Grand Canyon ranged from about 5°C to 27°C <br />(Figure 2). Since the dam was constructed, water <br />temperature has varied across a narrow range (9- <br />12°C; Figure 2). Bioenergetic model simulations <br />suggest that before the dam was built, juvenile <br />humpback chub may have grown from 4 to 22 g <br />during 1 year; since the dam, 4-g juveniles grow <br />to only 12 g (Table 6). Over twice as much food <br />was required to achieve the high rate of growth <br />under high temperatures prior to dam construction <br />(Table 6). When we assumed an increased summer- <br />fall temperature from a TCD and average (p = <br />0.65) food availability, juvenile size at the end of <br />1 year increased 33% compared with the size pre- <br />dicted with post-dam temperatures (12 g versus 16 <br />g; Table 6). Juvenile humpback chub would have <br />to eat about 76 g of food (+58% relative to post- <br />dam average conditions) to achieve this increase <br />in size. With a slight increase in prey availability <br />(p = 0.75), juvenile humpback chub grew to 24 g <br />(+100%), requiring 106 g of prey (+121%; Table <br />6). Predicted growth of subadult humpback chub <br />differed little between pre-dam, post-dam, and in- <br />creased temperature scenarios. The food required <br />to maintain this constant size varied from 378 g <br />for post-dam conditions to 516 g (+37%) and 709 <br />g (+88%) in the increased temperature and pre- <br />dam conditions, respectively, due to the higher <br />temperatures in these simulations. If prey avail- <br />ability increased (p = 0.75) during a TCD appli- <br />cation, subadult humpback chub grew to 158 g <br />(+28% relative to post-dam average conditions), <br />requiring 657 g of prey (+74%; Table 6). <br />Discussion <br />Bioenergetics Model Development <br />Estimating bioenergetic parameters using the <br />Monte Carlo sampling procedure was relatively <br />A <br />4 g start <br />15 <br />B <br />119 g -tart <br />0.4 <br />0.2 P? "I <br />15 <br />FIGURE 3.-El <br />range, 0.1-1.0) a <br />growth of a (A) <br />subadult (starting <br />a bioenergetics <br />over 365 d. Grov <br />simple, and thi <br />tions for other <br />periled species, <br />ing collecting p <br />ple size becaus. <br />individuals that <br />appropriate size <br />tions. Laborato <br />may also be su <br />types of experin <br />tality rate for e <br />gered, or imper <br />great concern 1
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