JOURNAL OF EXPERIMENTAL ZOOLOGY 309A (2008) A Journal of Integrative Biology Plasticity of Growth Rate and Metabolism in Daphnia magna Populations From Different Thermal Habitats J. CHOPELET, P.U. BLIER, AND F. DUFRESNE De´partement de Biologie, Université du Que´bec à Rimouski, Rimouski, Que´bec, Canada ABSTRACT The aim of this study was to evaluate the effect of temperature on growth and aerobic metabolism in clones of Daphnia magna from different thermal regimes. Growth rate (increment in size), somatic juvenile growth rate (increment in mass), and oxygen consumption were measured at 15 and 251C in 21 clones from one northern and two southern sites. There were no significant differences in body size and growth rate (increase in length) at both 15 and 251C among the three sites. Clones from southern site 2 had a higher mass increment than clones from the other two sites at both temperatures. Clone had a significant effect on growth (body length) and body size at both temperatures. As expected, age at maturity was lower at 251C (4.5 days) than at 151C, (11.6 days) and body sizes, after the release of the third clutch, were larger at 151C than at 251C. Northern clones had higher oxygen consumption rates and specific dynamic action (SDA) than southern clones at 151C. By contrast, southern clones from site 1 had a higher oxygen consumption and SDA than subarctic clones at 251C. Clones from southern site 2 had high oxygen consumption rates at both temperatures. Our results reveal important differences in metabolic rates among Daphnia from different thermal regimes, which were not always reflected in growth rate differences. J. Exp. Zool. r 2008 Wiley-Liss, Inc. 309A, 2008. How to cite this article: Choplet J, Blier PU, Dufresne F. 2008. Plasticity of growth rate and metabolism in Daphnia magna populations from different thermal habitats. J. Exp. Zool. 309A:[page range]. Phenotypic plasticity of organisms is a highly relevant biological character to study in the face of a changing world and challenged ecosystems. Levins (’69) first introduced the term countergradient variation (CgV) that refers to a geographic pattern of variation in which genetic influences on a trait oppose environmental influences across an environmental gradient, thereby reducing phenotypic change across the gradient. These compensations allow ectotherms from higher latitudes to carry out their life cycle in stressful environments with low temperatures and short growing seasons (Conover, ’90; Conover and Schultz, ’95; Conover et al. ’97). Several physiological studies comparing ectotherm populations from different latitudes support this CgV hypothesis (Wohlschlag, ’60; Holeton, ’74; Clarke, ’83; Guderley and Blier, ’88; Addo-Bediako et al., 2002). For example, in the lugworm Arenicola marina, individuals from colder environments in the White Sea have a higher mitochondrial activity along with higher oxygen consumption rates compared with their counterparts from warmer r 2008 WILEY-LISS, INC. environments in the North Sea (Sommer and Pörtner, 2002). These studies reveal significant levels of plasticity in these phenotypic characters allowing partial compensation to adverse environmental conditions. Investigation of the evolution of phenotypic plasticity requires integration of the different physiological components of an organism (from molecular biology to whole organism physiology) to identify the tools and constraints of adaptation that could be ecologically relevant (for a review, see Pörtner et al., 2006). The first step in the identification of key genetic, metabolic, or physiological attributes allowing adaptations or Grant sponsors: Natural Sciences and Engineering Research Council of Canada (NSERC); Fonds Québécois de la Recherche sur la Nature et les Technologies (FQRNT); Northern scientific training program. Correspondence to: F. Dufresne, Département de Biologie, Université du Québec à Rimouski, 300 Allée des Ursulines, Rimouski, Québec, Canada G5L 3A1. E-mail: [email protected] Received 26 October 2007; Revised 17 March 2008; Accepted 29 June 2008 Published online in Wiley InterScience (www.interscience.wiley. com). DOI: 10.1002/jez.488 2 J. CHOPELET ET AL. acclimations is the identification of divergences among species or populations, which could lead to advantageous phenotypes in specific environments. Growth rates and metabolic rates are good candidates as ecologically relevant characters because they have been associated with life history traits and fitness (Anguilletta et al., 2004), and both can be strongly affected by environmental conditions, offering the grip to selective process to work on. Comparative approach is usually the most convenient one to identify phenotypic changes in different environments but here the choice of animal model is critical to ensure that the observed correlations are not dictated by phylogenetic constraints and therefore could not reflect local adaptations. Therefore, the study of widely distributed and closely related taxon should prevail in such comparative studies. Species of zooplankton are often widespread over large latitudinal distributions. Freshwater populations of the same species may inhabit contrasting environments, from deep permanent lakes to shallow temporary rock pools, experiencing large temperature variations. Differences in developmental rate, size, and growth rate have been measured among copepod species from different latitudes with higher performances at temperatures prevailing in their specific environment (Londsale and Levington, ’85). Clones from Daphnia magna collected in winter have higher survival and fecundity at a low temperature than those collected in summer (Carvalho, ’87; Carvalho and Crisp, ’87). D. carinata collected in summer have a higher tolerance to warm temperatures than D. carinata collected in winter (Wiggins and Frappell, 2000). Lamkemeyer et al. (2003) found that D. magna from Germany acclimated to cold temperatures has a higher aerobic metabolism compared with warm acclimated individuals. Both developmental and metabolic adjustments are involved in adaptation to thermal environments, whereas their relationships and there respective role are still enigmatic. The objectives of this study were to assess intraspecific variation in phenotypic responses (body size, growth rate, and aerobic metabolism) to temperature in populations of D. magna inhabiting different climatic zones (subarctic and temperate). If growth rate adjustments to different thermal regimes are modulated through metabolic adaptations, we expect that differences in growth performance or its thermal sensitivity among populations will be reflected at the metabolic level. Therefore, we hypothesized that J. Exp. Zool. subarctic clones will have higher growth and metabolic rates than clones from more southern sites at 151C and lower rates at 251C. Clonal reproduction (production of genetically identical individuals) and wide distribution in different habitats make D. magna a suitable model to study the physiological mechanisms dictating growth and metabolic plasticity. We herein document for the first time intraspecific variability for aerobic metabolism in a daphniid experiencing different thermal regimes. MATERIAL AND METHODS D. magna origins Subarctic clones were collected from Churchill, Manitoba, Canada (581440 N; 941030 W) in July and August 2004. They were found in small oligotrophic rockbluff ponds in close proximity to Hudson’s Bay. Temperate clones were collected in Gimlet Lake, in the Nebraska Crescent Lake National Wildlife Refuge, Nebraska, USA (411470 19N; 1021260 W). We also obtained Daphnia from a second southern site in Israel. Daphnia was collected in January 2004 and February 2004 in a permanent flooded ditch near Lake Hula (33160 N; 351370 W) and in a temporary rainpool in Dora (321170 N; 341500 W). The climate at this site can be classified as mediterranean i.e. long rainy winters and short dry summers. Clonal identification To identify clones, DNA was extracted with the 6% Chelex method and polymerase chain reaction (PCR) was performed using three microsatellite loci available from Genebank: dma11 (AF291911), dma12 (AF291912), and dma14 (AF291913). PCR products were migrated on 6% polyacrylamide gels and subsequently stained with Syber Green. Gels were then scanned and allele identified on a Hitachi FMBIO III (Yokohama, Japan). As these loci were monomorphic in the Churchill population, four allozymes (PGM, GPI, GOT, MDH) were additionally screened on all populations on cellulose acetate plates according to Hebert and Beaton (’93). Nine multilocus genotypes from Nebraska, five from Israel, and seven from Churchill were identified using both allozyme and microsatellite markers. Maintenance conditions Clones (n 5 21) were raised at 15 and 251C under a 16:8 hr L:D photoperiod for three generations to 3 GROWTH RATE AND METABOLISM IN DAPHNIA MAGNA remove any maternal effect (Lynch and Ennis, ’83; Mousseau and Fox, ’98). Five individuals per clone were grown together in 100 mL of filtered lake water. Algae (Selenastrum capricornotum) were added to the 100 mL of water in order to obtain a concentration of approximately 3 105 cells mL1. We replaced the water of the containers twice a week with water at the right algal concentration. Growth rate We used neonates from the first clutch of newly mature females to measure sizes and growth rates as maternal size and age significantly affect neonate size. Size at birth and at first and third clutches was measured using a BQ nova prime software (Bioquant, Nashville) interfaced to a microscope. Size was measured from the top of the eye to the base of the caudal spine. Growth rate (increment in body length, IBL) was calculated as the difference between sizes at first reproduction and birth divided by the number of days to maturity. Size vs. time was plotted and growth curve was derived by curve fitting. We also measured the somatic juvenile growth rate (Gj), which is defined as Gj 5 (ln W2ln W1)/t2t1 where W1 and W2 are the masses of individual at times t1 and t2 and t1 is the neonate stage and t2 is maturity. This parameter has been shown to be linearly correlated with the per capita rate of increase (r) when differences in food concentration, temperature, and clonal differences are considered (Lampert and Trubetskova, ’96). It is a good proxy for fitness (Lampert and Trubetskova, ’96) and can serve as an index of clonal performance when size may be affected by predation (Hairston et al., 2001). Oxygen consumption Oxygen consumption was measured on five individuals per clone for each population with a spectrophotometer following a modified Winkler titration (Broenkow and Cline, ’69; Peck et al., ’86; Roland et al., ’99; Lemos et al., 2003). A single Daphnia without eggs in the brood chamber (rinsed with sterile water) was introduced for 24 hr in a 1.5-mL eppendorf tube filled with sterile water (no air inside) and streched with parafilm. Another tube filled with the same sterile water but without D. magna was used as control. Preliminary experiments revealed that after 24 hr at 251C, oxygen concentration in eppendorf tubes containing large individuals was well above values leading to oxygen stress in Daphnia (50%; Paul et al., ’97; Hodkinson, 2003). We also controlled for oxygen diffusion inside the tubes during the 24-hr period. Eppendorf tubes were filled with anoxic water and kept at 15 or 251C for 24 hr. Oxygen content was measured before and after the 24-hr period. No significant diffusion was observed. The water was subsequently sampled with a syringe (without opening the eppendorf) and mixed with reagent solutions : 7 mL of MnCl2 (3 M), 7 mL of NaOH (8 N) and INa (4 M), and with 7 mL of H2SO4 (10 N). The absorbance of the final yellow solution was read at a 440 nm wavelength with a Perkin Elmer spectrophotometer (lambda 11, Waltham). The relationship between absorbance of the solution and oxygen concentration was determined with the following equation: O2 ðmg L1 Þ ¼ 13:682 Absorbance 0:5769 ðr2 ¼ 0:998; Po0:001Þ: The relationship between absorbance at 440 nm of the yellow solution and the oxygen concentration was constructed by thiosulfate titration. Solutions with different oxygen concentrations were obtained by bubbling water with nitrogen. The previous reagent solutions (7 mL of MnCl2 (3 M), 7 mL of NaOH (8 N) and INa (4 M), and with 7 mL of H2SO4 (10 N)) were then added to 1.5 mL of water. The volume of thiosulfate added to ensure that the solution became translucid (absorbance null) is proportional to the oxygen concentration: O2 ðmg L1 Þ ¼ ð5; 600Nthio ðVthio Vblk ÞÞ=ð0:7ðV sample Vreagent ÞÞ: Vthio (mL) is the volume of thiosulfate added and Vblk (0.2 mL) a correction to subtract the volume of thiosulfate used to titrate oxygen introduced by reagents, 5,600 cm3 is the volume of oxygen corresponding to 1 equivalent of thiosulfate at standard temperature pressure (STP), and 0.7 cm3 is the volume of 1 mg of oxygen. Vsample and Vreagent are, respectively, the volume of sample (1.5 mL) and reagents (0.021 mL) added. The exact normality of the thiosulfate solution (Nthio 5 0.159) was evaluated by titration with 0.02 N potassium iodate. In order to measure the apparent specific dynamic action (SDA), oxygen consumption was measured on fed (3 105 cells mL1) and unfed individuals. Measures were first taken on fed individuals. These were subsequently starved for 24 hr at 251C and 48 hr at 151C (Schmocker J. Exp. Zool. 4 J. CHOPELET ET AL. and Hernandez-Leon, 2003) and oxygen consumption measurements were therefore taken on the same individuals. Oxygen consumption rates were measured on a wide range of individual body sizes for each clone. The dry weight of each individual was measured to the nearest 0.1 mg on a microbalance following a 24-hr desiccation period at 601C. Because it is not possible to measure standard metabolic rate in Daphnia as limb movements are required for respiration, we measured oxygen consumption of unfed animals, which reflects the sum of maintenance plus activity costs (SMRA). The apparent SDA is defined as the energy used during digestion, assimilation, and storage in active organisms and is calculated as the arithmetic difference between fed and unfed oxygen consumption rates (Fry, ’47). As we were unable to calculate the true factorial scope, which is usually defined as the ratio of maximal oxygen consumption to standard metabolic rate, we calculated an ‘‘apparent factorial scope’’ that we defined as the ratio between fed and unfed oxygen consumption rates. The aerobic scope provides a good estimation of the aerobic capacity available for either activities, growth processes, or reproduction, whereas the factorial scope indicates the proportion of maximal aerobic capacity that is devoted to life maintenance processes. The later parameter can be a good metabolic indicator of the stress faced by an organism in a given environment. Statistical analyses Comparisons of neonate size, size and age at first reproduction, juvenile and somatic growth rates were carried out using a mixed-model nested analysis of variance. Terms of the model were temperature, population, clone nested in population, their interaction, and error. When normality and homogeneity of variances of nontransformed and log-transformed data residuals were rejected, nonparametric tests were used. When parametric and nonparametric statistical conclusions were similar, only parametric results were presented. Tukey post hoc tests were used to identify groups showing the significant differences. Comparisons of oxygen consumption–mass and SDA–mass regressions were carried out using analysis of covariance followed by pairwise comparisons. Interactions of covariate term (mass) with temperature, population, and feeding status were tested in the first model then removed when not J. Exp. Zool. significant to compare elevation of regressions. All statistical analyses were performed using general linear model procedure of SYSTAT 9.0 (SPSS Inc., ’99). RESULTS Body size and growth rate No significant differences in somatic juvenile growth rates (Gj) were found among Churchill, Nebraska, and Israel populations at 15 and 251C (F2; 44 5 1.13, P 5 0.332) (Fig. 1). There was a significant effect of clone on growth rate (IBL) at 151C (F 5 10.79, df 5 18, P 5 0.001) and at 251C (F 5 12.31, df 5 18, P 5 0.001). At birth, clones from Nebraska had larger sizes, whereas Churchill clones had smaller sizes (F2; 160 5 7.09, P 5 0.023) (Fig. 1). Although all populations had similar sizes at first (F2; 160 5 0.83, P 5 0.452) and third clutches (F2; 39 5 0.35, P 5 0.706), Israel clones had higher growth rates (length) than clones from Churchill and Nebraska (F2; 160 5 893, P 5 0.002) owing to their shorter time to reach the first clutch (age at first clutch, F2; 167 5 9.58, P 5 0.001) (Fig. 1). Sizes at birth did not differ at both temperatures but were significantly smaller at 251C than at 151C at first (F1; 18 5 27.2, Po0.001) and third reproduction (F1; 39 5 13.786, P 5 0.001) (Fig. 1). Age at first reproduction decreased with increasing temperature from an average of 11.6 days at 151C to 4.5 days at 251C (Figs. 1 and 2). D. magna had a higher somatic juvenile growth rate (Gj) at 251C than at 151C (F1; 44 5 28, Po0.001) (Fig. 1). Significant differences among clones were found for the following parameters: size at birth with significant interactions between clones and temperature (F18; 160 5 6.45, Po0.001), size at first reproduction (F18; 160 5 3.38, Po0.001), age at first reproduction with significant interactions between clones and temperature (F18; 167 5 10.1, Po0.001), and growth rate (IBL) with significant interactions between clones and temperature (F18; 160 5 9.85, Po0.001). No significant interactions between population and temperature were found for Gj (F2; 44 5 1.2, P 5 0.3), growth rate in length (F2; 18 5 1.8, P 5 0.194), size at birth (F2; 18 5 0.5, P 5 0.643) and at first maturity (F2; 18 5 3.1, P 5 0.068), and age at first maturity (F2; 18 5 2.3, P 5 0.130). We pooled all individuals at each temperature to plot body size vs. time (Fig. 2). At 251C, curve based on the von Bertalanffy equation was fitted (Size 5 3,963.85(1e0.312(Time)), r2 5 0.94, 5 GROWTH RATE AND METABOLISM IN DAPHNIA MAGNA b 16 ab Age at first clutch (day) a 1200 1000 800 600 400 200 2 6000 0.8 Juvenile growth rate (µm day-1) Body size at first clutch (µm) 0 Somatic juvenile growth rate (Gj, day -1) 3000 2000 1000 0 Churchill Nebraska Israel b 4 2000 4000 a 6 700 5000 a 8 4000 2500 b 10 0 3000 a 12 0 3500 a 14 Body size at third clutch (µm) Body size at birth (µm) 1400 600 500 400 300 200 100 0.6 0.4 0.2 0.0 Churchill Nebraska Israel Fig. 1. Growth characteristics (7SD) at 151C (undashed) and 251C (dashed) in seven clones from Churchill (dark gray), nine clones from Nebraska (light gray), and five clones from Israel (white). Populations with same letters do not show significant differences. Standard errors express variability among clones (five individuals per clone). 5000 15˚C 25˚C (Fig. 2). Juvenile growth rate was twice higher at than at 151C 251C (475730 mm day1) (215742 mm day1). At 251C, after the first clutch (around 4.5 days), growth rate decreased and became lower than at 151C (Fig. 2). As a consequence, for approximately 20 days, D. magna individuals were larger at 251C than at 151C and inversely after that threshold (Fig. 2). Size (µm) 4000 3000 2000 1000 Oxygen consumption 0 0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 Time (days) Fig. 2. Growth curves for D. magna at 151C (Size 5 981.33 (Time)0.462 ) and at 251C (Size 5 3,963.85(1e0.312(Time))). Po0.0001). In contrast, the curve was better fitted at 151C when based on a power equation (Size 5 981.33(Time)0.462, r2 5 0.94, Po0.0001) Oxygen consumption rates ranged from 0.055 (70.026) mg O2 hr1 ind1 for juveniles (o10 mg) to 0.390 mg O2 hr1 ind1. There were no interactions of feeding status with mass (F1; 1083 5 1.2, P 5 0.266). Fed Daphnia had oxygen consumption rates that were on an average twice higher than food-deprived Daphnia (F1; 1,092 5 601.1, Po0.001) (Table 1). There were significant interaction effects J. Exp. Zool. 6 J. CHOPELET ET AL. among temperature population mass when individuals were fed (F2; 542 5 5.848, P 5 0.003). Oxygen consumption of D. magna from the three populations was affected by temperature and feeding in different ways (F2; 1,092 5 34.7, Po0.001) (Fig. 3, Table 1). When fed, Churchill clones had significantly higher oxygen consumption rates at 151C than at 251C (F1; 180 5 24.2, Po0.001). By contrast, clones from Nebraska had higher oxygen consumption rates at 251C than at TABLE 1. ANCOVA analysis of oxygen consumption in Daphnia magna from Churchill, Nebraska, and Israel at two temperatures (Temp) for fed and unfed Daphnia (Food) and with mass as covariate Source of variation df SS F-ratio P Temp Pop Food Mass Pop Temp Food Temp Food Pop Food Pop Temp Pop Temp Mass Error 1 2 1 1 2 1 2 2 2 1,092 0.9 0.8 97.1 188.9 13.9 0.9 4.0 5.9 11.2 176.4 5.8 2.4 601.0 1169.2 43.0 5.6 12.4 18.2 34.7 0.016 0.089 o0.001 o0.001 o0.001 0.018 o0.001 o0.001 o0.001 All data were Ln-transformed before analysis. Interactions with the covariate were removed when not significant. Pairwise comparison results are given in the text. ANCOVA, analysis of covariance. Churchill 151C (F1; 253 5 25.1, Po0.001). Oxygen consumption rates of Israel clones were high and did not vary significantly with temperature (Table 1). When unfed, oxygen consumption rates were significantly lower at 251C than at 151C in both Nebraska (F1; 253 5 77.8, Po0.001) and Churchill clones (F1; 181 5 29.0, Po0.001). At 151C, the oxygen consumption of Churchill clones was higher than the oxygen consumption of clones from Nebraska and Israel (when fed C4I4N and when unfed C4N 5 I). At 251C, Churchill clones had a higher oxygen consumption than the other populations only when unfed (C4N 5 I). When fed, Nebraska clones had a higher oxygen consumption than other clones at 251C (N4I 5 C). SDA increased with mass (Fig. 4). At 151C, clones from Nebraska had the lowest SDA values (F2; 261 5 14.730, Po0.001; NoI 5 C). By contrast, at 251C, Churchill clones had lower SDA values than Israel and Nebraska clones (F2; 263 5 7.126, P 5 0.001; CoI 5 N). Israel clones had high aerobic scopes at both temperatures. There were significant interactions among temperaturepopulation mass for SDA (F2; 541 5 26.839, Po0.001). There was no relationship between mass and apparent factorial scope in Nebraska and Churchill clones and a very small albeit significant relationship in Israel clones. Factorial scope did Nebraska Israel 0.5 15ºC 15ºC 15ºC 25ºC 25ºC 25ºC 0.4 Oxygen consumption (µg O2 h-1 ind-1) 0.3 0.2 0.1 0.0 0.5 0.4 0.3 0.2 0.1 0.0 0 20 40 60 80 100 0 20 40 60 80 100 0 20 40 60 80 100 Dry mass (µg) Fig. 3. Oxygen consumption at 15 and 251C for fed (filled) and unfed (empty) D. magna from Churchill, Nebraska, and Israel. J. Exp. Zool. 7 GROWTH RATE AND METABOLISM IN DAPHNIA MAGNA Nebraska Churchill Israel 0.30 15˚C 15˚C 15˚C 25˚C 25˚C 25˚C 0.25 0.20 0.15 0.10 SDA (µg O h ind ) 0.05 0.00 0.30 0.25 0.20 0.15 0.10 0.05 0.00 0 20 40 60 80 100 0 20 40 60 80 100 0 20 40 60 80 100 Dry mass (µg) Fig. 4. SDA for D. magna from Churchill, Nebraska, and Israel at 15 and 251C. SDA, specific dynamic action. not vary with temperature in Israel clones (2.472.1 at 151C and 2.671.5 at 251C), whereas it increased from 1.871.3 at 151C to 2.871.8 at 251C for clones from Nebraska and inversely decreased from 2.171.3 at 151C to 1.772.1 at 251C for Churchill clones. DISCUSSION Metabolic adaptations to temperature This study provides evidence for metabolic adaptations to temperature in D. magna clones from different thermal environments. Metabolic responses to temperature variation were significantly different between subarctic and temperate populations. Adaptation to colder environment in subarctic clones was illustrated by a higher aerobic metabolism at lower temperatures (Fig. 3, Table 1). This result is consistent with the metabolic cold adaptation hypothesis, one of the three paradigms in thermal physiology, namely elevated metabolism in populations inhabiting cold environments (Ege and Krogh, ’14, in Pörtner et al., 2006). By contrast, the temperate clones from Nebraska had higher oxygen consumption rates at 251C than subarctic clones. Churchill clones encounter daily average air temperatures between 6 and 121C, whereas clones from Nebraska cope with daily average temperatures between 15 and 231C during spring and summer. Oxygen consumption rates did not vary with temperature in the Israel population, suggesting that they are equally well adapted at both temperatures and, therefore, that for this species, metabolic adaptation to high temperature is not necessarily associated with the loss of ability at lower temperature regimes. Comparisons of Israel clones with those of Churchill is more difficult as these clones undergo important daily and seasonal temperature fluctuations. More data on the presence of Daphnia in the water column and water temperatures in Israel are needed before we can conclude on the apparent eurythermy of these clones. Interestingly, the SDA scaled positively with mass only at a low temperature for the Churchill clones, at a high temperature for clones from Nebraska, and at both thermal regimes for the clones from Israel. This might suggest that the adjustment of SDA with mass is a required physiological trait in optimal environmental conditions and that collapses of this trait reflect stressful environments. Plasticity of growth Subarctic clones had similar growth rates as temperate clones at either 15 or 251C. This result is consistent with a previous study on temperature reaction norms of somatic juvenile growth rate of D. magna. No significant differences in growth rates (Gj) were found among populations ranging J. Exp. Zool. 8 J. CHOPELET ET AL. from southern Spain to Finland (Mitchell and Lampert, 2000). Our results revealed significant differences in growth rates (IBL) among clones within each population as well as significant clone by temperature interactions, suggesting that a substantial variation for growth under different temperatures is present in D. magna (see also Mitchell and Lampert, 2000). The existence of clones with different growth capacity may enable populations to cope with seasonal alterations of temperature through replacement by alternative thermal specialist clones (Carvalho, ’87; Carvalho and Crisp, ’87). Mitchell and Lampert (2004) did not find differences in juvenile growth rates among clones of D. magna collected at different seasons, suggesting that clones were generalists and able to optimize their phenotypes in a given environment. Growth rates were measured under optimal food conditions in the laboratory. Although laboratory conditions were essential to grow clones under similar environmental conditions, we might have obtained different results in the field with more stringent conditions and scarcer resources. Future studies should measure growth rates and temperature in situ in the field. It is interesting to note that clones from Israel had, on an average, higher somatic juvenile growth rates than both temperate and subarctic clones at both 15 and 251C. The shorter time to reach first reproduction may be an adaptation to Israel environment, characterized by unpredictable environmental conditions. High predation pressures from fish may also select for a rapid growth in these populations. More studies are needed to identify factors responsible for these genetic differences in growth rates. Direct effects of temperature on growth Temperature has direct and opposed effect on growth rate and asymptotic size (Atkinson, ’94; Atkinson and Sibly, ’97). Our results are in accordance with the temperature–size rule and the model of Berrigan and Charnov (’94), which states that growth rate and asymptotic size are negatively correlated. The negative correlation between size and temperature has already been shown in D. magna with a smaller maturation threshold size at 221C than at 121C (McKee and Ebert, ’96). However, our results showed that this negative correlation occurred only after the third clutch. During the first 20 days, D. magna had a larger body size at 251C than at 151C resulting J. Exp. Zool. from a higher growth rate before the first reproduction at 251C. This therefore excludes any temperature modulation of adult size by egg or juvenile size (for example, see Stelzer, 2002) and limits the explanation to a prolonged growth period induced by delayed maturation at a low temperature (Figs. 1 and 2). Growth and metabolism decoupling Growth is an energy-consuming trait and is expected to depend on aerobic metabolism (Jobling, ’85). Therefore, at 151C, subarctic D. magna might be expected to grow faster than temperate D. magna according to higher maximum aerobic capacity, which is not what we observed. The unfed metabolism was also higher in the subarctic population than in the temperate one leaving a lower aerobic scope for growth. At 251C, the mediterranean population had the highest fed metabolism, whereas its unfed metabolism was lower than the subarctic one and equivalent to the temperate one, suggesting higher access to SDA for growth. Again this did not translate into higher somatic juvenile growth rates. This decoupling between growth and SDA at different thermal regimes suggests that growth rates in D. magna are not dictated by aerobic capacity or SDA. In the thermal range covered by this study, the overall metabolic capacity can cope with energetic requirements imposed by growth rate in optimal conditions, or in other words growth processes are not limited by metabolic capacity of an organism. This is in agreement with observations on fast-growing fish larvae, which suggest an excess in overall metabolic capacity to support the growth requirements and limitation at the level of the digestive capacity (see Blier et al., ’97). Under natural conditions, energy allocation and metabolism have to cope with different physiological demands such as maintenance, locomotion, reproduction, or growth. An apparent excess of metabolic capacity would ensure minimum ability to perform different physiological tasks without restricting growth processes when resources are available. The higher aerobic capacity and SDA at a lower temperature in the subarctic population and at a higher temperature in the temperate population with no apparent correlation with growth rate could partly support this interpretation. What appears counterintuitive and difficult to interpret in terms of local adaptation is the increase of SMRA at a low temperature for the subarctic population and at GROWTH RATE AND METABOLISM IN DAPHNIA MAGNA a higher temperature for the temperate population. Standard metabolism or the cost of maintenance has been perceived as a relatively passive process and its optimization being obtained by minimization, allowing higher allocation to active process such as activity or growth rate. Much of the standard metabolism is associated with protein turn-over and mitochondrial uncoupling. Maintenance of a high protein turn-over rate could be associated with the maintenance of highly functional physiological machinery when organisms are highly active. The increase of mitochondrial uncoupling has been associated with modulation of reactive oxygen species production by active mitochondria. It is therefore reasonable to suggest that optimization of standard metabolism cannot be restricted to only energy cost but rather to optimization of the processes that generate these costs. In this context, an increase of protein turn-over rate and mitochondrial uncoupling to meet physiological requirements at an optimal temperature (high or low) could easily be an adaptive response. CONCLUSION Our data clearly revealed that temperature adaptations maximize SDA at temperatures experienced by clones from different localities. In spite of clear metabolic compensations, growth rates did not show the same level of divergences among populations when measured at the same temperature, questioning the function of these metabolic adjustments. D. magna appears to be an excellent model system to investigate physiological basis of thermal sensitivity of metabolism. Crosses between individuals from Churchill and Nebraska would be of interest to enable a finer identification of physiological mechanisms involved in metabolic adaptations. ACKNOWLEDGMENTS This study was supported by a Natural Sciences and Engineering Research Council of Canada (NSERC) and Fonds Québécois de la Recherche sur la Nature et les Technologies (FQRNT) grants to France Dufresne. We thank Adam Petrusek for providing us with samples from Israel, Marlin French for his hospitality in the Crescent Lake National Wildlife Refuge, and Marie-Eve Houde for the sampling in Churchill. Northern scientific training program provided funding for the sampling in Churchill. We thank the staff from the 9 Churchill Northern Study Centre for their help during our stay. LITERATURE CITED Addo-Bediako AS, Chown L, Gaston KJ. 2002. Metabolic cold adaptation in insects: a large-scale perspective. Funct Ecol 16:332–338. Anguilletta, MJ. Steury TD, Sears MW 2004. Temperature, growth rate, and body size in ectotherms: fitting pieces of a life-history puzzle. Integr Comp Biol 44:498–509. Atkinson D. 1994. Temperature and organism size—a biological law for ectotherms. Advances in ecological research, Vol. 25. London: Academic Press. p 1–58. Atkinson D, Sibly RM. 1997. Why are organisms usually bigger in colder environments? Making sense of a life history puzzle. Trends Ecol Evol 12:235–239. Berrigan D, Charnov EL. 1994. Reaction norms for age and size at maturity in response to temperature: a puzzle for life historians. Oikos 70:474–478. Blier PU, Pelletier D, Dutil JD. 1997. Does aerobic capacity set a limit on fish growth rate? Rev Fish Sci 5:323–340 Broenkow WW, Cline JD. 1969. Colorimetric determination of dissolved oxygen at low concentrations. Limnol Oceanogr 14:450–454. Carvalho GR. 1987. The clonal ecology of Daphnia magna (Crustacea: Cladocera) II. Thermal differentiation among seasonal clones. J Anim Ecol 56:469–478. Carvalho GR, Crisp DJ. 1987. The clonal ecology of Daphnia magna (Crustacea: Cladocera) I. J Anim Ecol 56:453–468. Clarke A. 1983. Life in cold water: the physiological ecology of polar marine ectotherms. Oceanogr Mar Biol: Annu Rev 21:341–453. Conover DO. 1990. The relation between capacity for growth and length of growing season: evidence for and implications of countergradient variation. Trans Amer Fish Soc 119: 416–430. Conover DO, Schultz ET. 1995. Phenotypic similarity and the evolutionary significance of countergradient variation. Trends Ecol Evol 10:248–252. Conover DO, Brown JJ, Ehtisham A. 1997. Countergradient variation in growth of young striped bass (Morone saxatilis) from different latitudes. Can J Fish Aquat Sci 54: 2401–2409. Fry FEJ. 1947. Effects of environment on animal activity. Publ Ont Fish Res Lab 55:1–62. Guderley H, Blier PU. 1988. Thermal acclimation in fish: conservative and labile properties of swimming muscle. Can J Zool 66:1105–1115. Hairston Jr NG, Holtmeier CL, Lampert W, Weider LJ, Post DM, Fischer JM, Cáceres CE, Fox JA, Gaedke U. 2001. Natural selection for grazer resistance to toxic cyanobacteria: evolution of phenotypic plasticity? Evolution 55: 2203–2214. Hebert PDN, Beaton MJ. 1993. Methodologies for allozymes analysis using cellulose acetate electrophoresis. Guelph, Ontario: Helena laboratories. Hodkinson ID. 2003. Metabolic cold adaptation in arthropods: a smaller-scale perspective. Funct Ecol 17:562–572. Holeton GF. 1974. Metabolic cold adaptation of polar fish: fact or artefact? Physiol Zool 47:137–152. Jobling M. 1985. Growth. In: Tytler P, Calow P, editors. Fish energetics: new perspectives. London: Croom Helm. p 213–230. J. Exp. Zool. 10 J. CHOPELET ET AL. Lamkemeyer T, Zeis B, Paul RJ. 2003. Temperature acclimation influences temperature-related behaviour as well as oxygen-transport physiology and biochemistry in the water flea Daphnia magna. Can J Zool 81:237–249. Lampert W, Trubetskova I. 1996. Juvenile growth rate as a measure of fitness in Daphnia. Funct Ecol 10:631–635. Lemos D, Jorge RLV, Phan VN. 2003. Simultaneous measurements of oxygen consumption and ammonia-N excretion in embryos and larvae of marine invertebrates. Comp Biochem Physiol A 136:321–328. Levins R. 1969. Thermal acclimation and heat resistance in Drosophila species. Am Nat 103:483–499. Londsale DJ, Levington JS. 1985. Latitudinal differentiation in copepod growth: an adaptation to temperature. Ecology 66:1397–1407. Lynch M, Ennis R 1983. Resource availability, maternal effects and longevity. Exp Gerontol 18:147–165. McKee D, Ebert D. 1996. The effect of temperature on maturation threshold body-length in Daphnia magna. Oecologia 108:627–630. Mitchell SE, Lampert W. 2000. Temperature adaptation in a geographically widespread zooplankter, Daphnia magna. J Evol Biol 13:371–382. Mitchell SE, Lampert W. 2004. Coexistence of similar genotypes of Daphnia magna in intermittent populations: response to thermal stress. Oikos 106:469–478. Mousseau TA, Fox CW. 1998. Maternal effects as adaptations. Oxford: Oxford University Press. Paul RJ, Colmorgen M, Hüller S, Tyroller F, Zinkler D. 1997. Circulation and respiratory control in millimetre-sized J. Exp. Zool. animals (Daphnia magna, Folsmia candida) studied by optical methods. J Comp Physiol B 167:399–408. Peck LS, Morris DJ, Clarke A, Holmes LJ. 1986. Oxygen consumption and nitrogen excretion in the antarctic brachiopod Liothyrella uva (Jackson, 1912) under simulated winter conditions. J Exp Mar Biol Ecol 104:203–213. Pörtner HO, Bennett AE, Bozinovic F, Clare A, Lardies MA, Lucassen M, Pelster B, Schiemer F, Stillman JH. 2006. Trade-offs in thermal adaptation: the need for a molecular to ecological integration. Physiol Biochem Zool 79:295–313. Roland F, Caraco NF, Cole JJ. 1999. Rapid and precise determination of dissolved oxygen by spectrophotometry: evaluation of interference from color and turbidity. Limnol Oceanogr 44:1148–1154. Schmocker C, Hernandez-Leon S. 2003. The effect of food on the respiration rates of Daphnia magna using a flowthrough system. Sci Mar 67:361–365. Sommer AM, Pörtner H-O. 2002. Metabolic cold adaptation in the lugworm Arenicola marina: comparison of a North sea and a White sea population. Mar Ecol Prog Ser 240: 171–182. SPSS Inc. 1999. SYSTAT 9.0, Chicago, IL 60606–6307. Stelzer C-P. 2002. Phenotypic plasticity of body size at different temperatures in a planktonic rotifer: mechanisms and adaptive significance. Funct Ecol 16: 835–841. Wiggins PR, Frappell PB. 2000. The influence of haemoglobin on behavioural thermoregulation and oxygen consumption in Daphnia carinata. Physiol Biochem Zool 73:153–160. Wohlschlag DE. 1960. Metabolism of an antarctic fish and the phenomenon of cold adaptation. Ecology 41:287–292.
© Copyright 2026 Paperzz