Laserfiche WebLink
<br />Results <br /> <br />Growth response <br /> <br />Growth of Colorado squawfish larvae was not sig- <br />nificantly different in constant and fluctuating re- <br />gimes (p = 0.93), so data for the same temperatures <br />were pooled in subsequent analyses. Response sur- <br />face analysis indicated Colorado squawfish larvae <br />achieved maximum growth at the highest food <br />abundance and temperature (Fig. 1, Table 1). Mal- <br />lows Cp selected a model that included the main ef- <br />fects of temperature and food abundance, their re- <br />spective squared terms, and their interaction (Table <br />2). The final model had an R2 = 0.976 and RMSE = <br />0.0125. Food abundance explained most growth <br />rate variation (partial R2 for food abundance, its <br />squared term and food x temperature interaction = <br />0.916). The LOF test was highly significant (p <br />< 0.0001), but residual analysis did not indicate <br />model LOP. The regression growth model F-value <br />of 933.7 far exceeded the Box-Wetz criterion of <br />31.8, which suggested adequate model fit. <br />Optimization suggested a maximum growth rate <br />of 0.305 mm TL d-I at 310 C and food abundance of <br /> <br />201 <br /> <br />345 nauplii fish-I day- 1, both of which are just out- <br />side of the upper range of values tested in this ex- <br />periment (300 C and 320 nauplii fish-I day-I). Thus, <br />optimization and the data showed growth of Col- <br />orado squawfish larvae was highest between 26 and <br />310 C and at 320 to 342 nauplii fish-I day-I. Model <br />solutions showed that growth of Colorado squaw- <br />fish larvae declined 4.5-7% for each degree drop in <br />temperature from 22 to 180 C at maximum food <br />abundance. <br />A significant food x temperature interaction (p <br />< 0.0001) was likely due to reduced growth rates of <br />Colorado squawfish larvae in treatments at 180 C <br />and food abundance of 142 and 320 nauplii fish-I <br />day-\ when compared to growth rates of larvae in <br />the same food abundance levels for 22, 26, and <br />300 C (Fig. 2). Growth rates at 180 C with food <br />abundance of 142 and 320 nauplii fish-I day-I were <br />20 and 31 % less than growth rates averaged for the <br />three higher temperatures with the same food <br />abundance. Growth rates at 12.5, 28, and 64 nauplii <br />fish-I day-I at 180 C were comparable to those <br />achieved at higher temperatures. Significant inter- <br />actions may invalidate interpretation of model <br />main effects unless interactions are orderly (au <br /> <br />Table 2, Least squares (growth model) and maximum-likelihood (survival model) estimates and significance probabilities for coefficients <br />from quadratic response surface regression models relating growth and survival responses to water temperature and food abundance, <br />Response variable or df Coefficient estimate SE <br />interaction p R' <br />Growth' <br />Intercept 1 - 0,2627170 0,041603 < 0.0001 0.976 <br />Temperature (T) 1 0.0286770 0.003491 < 0.0001 <br />Food (F) 1 0,0007160 0,000071 < 0,0001 <br />T' 1 - 0,0006370 0.000072 < 0.0001 <br />F' 1 - 0,0000024 0,000001 < 0.0001 <br />TxF 1 0,0000313 0,000002 < 0.0001 <br />Survivalb <br />Intercept 1 - 6.5160000 3,527200 0,0647 <br />Temperature (T) 1 0.2953000 0.256300 0.2511 <br />In (Food) (InF) 1 2.0144000 0,749800 0.0086 <br />T' 1 - 0,0169000 0.005300 0,0012 <br />lnF' 1 - 0.4452000 0,074900 < 0,0001 <br />TxlnF 1 0,1084000 0.018800 < 0,0001 <br /> <br />, Growth model statistics: df = 5, 114, model F = 933,7 (F = 3.18 at p '" 0,01), lack of fit p < 0,0001, root mean square error = 0.012553; <br />response in mm d-1. <br />b Survival response is logit (survival). Food abundance is natural log (food), Deviance/df (n = 114) = 1.9194, inflation factor for standard <br />errors was the square root of deviance/df = 1.3854, <br />