Variations in isotope incorporation rates and trophic discrimination factors of carbon and nitrogen stable isotopes in scales from three European sea bass (Dicentrarchus labrax) populations
Introduction
Analysis of carbon (δ13C) and nitrogen (δ15N) stable isotopes has proven to be a powerful tool in marine ecology, to study trophic relationships and migrations of various species through time and space (Hansson et al., 1997; Perga and Gerdeaux, 2003; Dempson et al., 2010; Sweeting, 2010). The δ13C and δ15N values of organisms reflect those of assimilated dietary sources as it is generally accepted that consumers are enriched by 1.0 and 3.5‰ in 13C and 15N, respectively, relative to their diets (Fry and Arnold, 1982; Minagawa and Wada, 1984). However, these assumptions are not universal and reconstruction of diet history as well as quantification of trophic relationships of organisms in their environment require better estimations of both carbon and nitrogen isotope incorporation rates and trophic discrimination factors (TDF) under controlled conditions (Wolf et al., 2009; Martínez del Rio and Carleton, 2012).
Isotope incorporation rate is defined as the time required by an organism to acquire the isotopic composition of its new diet (Martínez del Rio and Carleton, 2012). This variable is essential to determine the temporal window in which stable isotope data can be used to elucidate the diet of an animal (Perga and Gerdeaux, 2005; Wolf et al., 2009). Stable isotope values of an organism in a situation of disequilibrium, after a change in diet, do not represent either the past or the present diet (Sweeting, 2010). It is well established that isotope incorporation rates are higher in metabolically active species, organisms or tissues, depending on both growth rate (i.e., anabolic rate or adjunction of new tissues) and catabolic rate (i.e., replacement of tissues; Hesslein et al., 1993; MacNeil et al., 2006). Generally, isotope incorporation rates are higher in liver and plasma than in muscle and red blood cells of fishes (Carleton and Martínez del Rio, 2010). Moreover, isotope incorporation rates vary with environmental conditions such as temperature, food quantity and quality as well as the physiological state of the animal, such as ontogenetic stage or level of stress (Witting et al., 2004; Carleton and Martínez del Rio, 2010; Bloomfield et al., 2011; Carter et al., 2019).
Trophic discrimination factor, the difference between stable isotope values of a consumer and its diet when at isotopic equilibrium, also fluctuates considerably. For fishes, carbon and nitrogen TDF vary from 0.2 to 4.0‰ and from −0.4 to 5.5‰, respectively (Sweeting et al., 2007a, Sweeting et al., 2007b). Accurate values are required to interpret relationships across trophic levels. A robust estimation of TDF is also a fundamental requirement for mixing models that predict the proportional composition of consumers' diets from stable isotope data (Phillips et al., 2014). Physiological mechanisms underlying TDF are not thoroughly understood but result from the balance between processes of assimilation and excretion of light versus heavy elements acquired in the food (Minagawa and Wada, 1984; Ponsard and Averbuch, 1999; Olive et al., 2003). Thus, TDF is influenced by both dietary and non-dietary factors (Trueman et al., 2005; Barnes et al., 2007; Matley et al., 2016; Nuche-Pascual et al., 2018).
In isotope-based studies, variation among individuals has been evaluated as the variance of δ13C and δ15N values. For fishes, δ13C and δ15N values of tissues have been shown to vary within and among populations (Barnes et al., 2008), and especially with sex (Kim et al., 2012; Marcus et al., 2019). To date, however, studies of variation in isotope incorporation rates and TDF within and among populations are scarce. When distinct isotope values appear among individuals, the assumption commonly made is that they must have been feeding on distinct food sources (e.g. Grey, 2001). However, several studies revealed an inherent variability between individuals fed with a same diet (Matthews and Mazumder, 2004; Araújo et al., 2007; Barnes et al., 2008). These studies underscored the need to take this variability into account in field-studies before concluding that individuals have distinct feeding habits. Differences in individual physiology are suggested to be the cause of this inherent individual variability (Bearhop et al., 2004). Isotope incorporation rates are estimated by changing from one isotopically distinct experimental diet to another, and then sampling tissues over time. In fishes, most isotope incorporation rate studies have used dorsal white muscle, so individuals must be sacrificed at each sampling point to monitor stable isotope values (Hesslein et al., 1993; German and Miles, 2010; Madigan et al., 2012). This precludes the study of individual variation in the kinetics of isotopic incorporation. Using non-lethal methods, such as sampling of red blood cells, plasma, fins and scales, would permit multiple sequential samplings on the same individuals, to study variation in isotope incorporation rates. Moreover, the development of non-lethal methods is desirable from a perspective of animal welfare (European Union, 2010; Australian Government, 2013; US Government, 2015). To our knowledge, the few studies that have sampled the same individuals over time after diet change have shown marked variation in carbon and nitrogen isotope incorporation rates (Hilderbrand et al., 1996; Voigt et al., 2003; Evans Ogden et al., 2004; Kim et al., 2012). Similarly, individual variation in TDF was revealed within different species (Lecomte et al., 2011; Kurle et al., 2014; Galván et al., 2016).
In the present study, we estimated isotope incorporation rates and TDF of carbon and nitrogen stable isotopes in the scales of 48 European sea bass (Dicentrarchus labrax) from three distinct populations (Atlantic AT, West Mediterranean WM and East Mediterranean EM; Guinand et al., 2017) reared under controlled conditions. European sea bass is highly prized by both commercial and sports fishermen, but a severe decline in stocks has recently raised concern about the conservation status of the species (de Pontual et al., 2019). The use of carbon and nitrogen stable isotope analyses is a good tool to improve the management of this species because it can reveal its feeding habitats and migrations (Cambiè et al., 2016). We assessed whether there were differences in isotope incorporation rates and TDF among (1) the three populations, (2) sexes and (3) individuals. Finally, empirical stable isotope mixing models were run with different carbon and nitrogen TDF to assess their influence on dietary predictions in field-based studies. Scales are a superposition of an organic layer mainly composed of proteins (mostly collagen) and an inorganic layer which is a carbonate salt (Hutchinson and Trueman, 2006). However, scales are not an inalterable record: several studies support the existence of a catabolic activity in scales with the destruction and the renewal of collagen by cells within the scale structure, respectively named osteoclasts and osteoblasts (Sire et al., 1990; Suzuki et al., 2000). Thus, it can be hypothesized that isotope incorporation rate in scale might not be only driven by growth.
Section snippets
Ethics statement
This study was carried out in accordance with the recommendations of Directive 2010-63-EU on the protection of animals used for scientific purposes. Protocols were approved by C2EA − 36 (“Comité d'éthique en expérimentation animale Languedoc-Roussillon”) under the authorization APAFiS n° 2,018,081,714,549,886 (version 2).
Animals and rearing conditions
A controlled feeding experiment was conducted on the three populations of European sea bass: AT, WM and EM. Fish were produced at the Ifremer Experimental Aquaculture Research
Fish growth rates and survival
Fish survival was 100% throughout the experiment and no significant difference appeared when comparing growth rates between sampled and non-sampled fish. Among the sampled fish, the numbers of males and females were respectively 6 and 10 for AT, 5 and 11 for WM and 6 and 10 for EM.
During the experiment, fish grew exponentially from 22.5 ± 5.5 g to 167.2 ± 45.3 g for AT, 22.3 ± 7.4 g to 183.6 ± 64.6 g for WM and 23.2 ± 7.2 g to 188.2 ± 80.7 g for EM (Fig. 1). Growth rates (Kg) were similar among
Discussion
In the present study, non-lethal sampling of scales permitted estimation of how carbon and nitrogen isotope incorporation rates, and TDF, differed among populations, sexes and individuals of European sea bass. This revealed variation between sexes in both carbon and nitrogen isotope incorporation rates, among populations in carbon TDF, and was particularly marked among individuals. Empirical mixing models showed that (1) the specific TDF of scales is needed to obtain accurate predictions,
Author contributions
CR, HdV and SN designed the experiment; CR, HdV and FC performed the experiment on the fish; CR and CM analysed the scale samples; CR, HdV, SL, CM, and SN analysed the data; CR, HdV and SN wrote the paper with the support of MV, FA, DJMK and JAHB. All authors read and approved the final manuscript.
Declaration of Competing Interest
None.
Acknowledgements
This publication was made possible through support provided by CIRAD and the CGIAR Research Program on Fish Agrifood Systems (FISH) and the International Fund for Agricultural Development (IFAD). The authors are grateful to the the Ifremer Experimental Aquaculture Research Station staff and facilities and to H2020 AQUAEXCEL2020 (No. 652831). SL was supported through the ISIT-U project by the French government through the Programme Investissement d'Avenir (I-SITE ULNE / ANR-16-IDEX-0004 ULNE)
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