Consistent habitat segregation between sexes in the spider crabs Maja brachydactyla and Maja squinado (Brachyura), as revealed by stable isotopes

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Summary

Differences in the resource use patterns of males and females of the spider crab species Maja brachydactyla Balss, 1922 and M. squinado (Herbst, 1788) from several geographic areas (three in the Atlantic and two in the Mediterranean) were studied through the analysis of stable isotopes of carbon and nitrogen in the exoskeleton of post-pubertal (adult) specimens. Results confirmed that males and females from the same population usually did not differ in ä15N values and hence foraged at the same trophic level. In contrast, females were usually enriched in 13C as compared with males from the same population, thus suggesting that females use shallower habitats than males before the terminal moult. The results reported here also indicate that stable isotopes can be useful for the traceability of commercial Maja species, but only if species and sex are incorporated in the analysis.

 

Keywords: Maja brachydactyla; Maja squinado; stable isotopes; trophic level; sexual segregation; traceability.

 

Introduction

The spider crabs of the genus Maja Lamarck, 1801 (Majoidea: Majidae), with around 20 described species worldwide, are represented on European coasts by four species: M. brachydactyla (Balss, 1922), M. crispata (Risso, 1827), M. goltziana (D’Oliveira, 1888) and M. squinado (Herbst, 1788) (Neumann 1998, Ng et al. 2008, Sotelo et al. 2008, 2009). M. brachydactyla and M. squinado are the largest European species of the genus and are found from subtidal areas to about 90 m depth (De Kergariou 1984, Števcic 1973). M. brachydactyla inhabits the eastern Atlantic from the British Isles to Senegal and has a high commercial value, while M. squinado inhabits the Mediterranean and is considered an endangered species (UNEP 1996, Freire et al. 2002, Martín et al. 2012, Sotelo et al. 2008, Guerao and Rotllant 2010, Guerao et al. 2011, Abelló et al. 2014), although it was abundant until the first half of the 20th century (Pons Muñoz 1994). Until recently, M. brachydactyla was considered a synonym of M. squinado (Zariquiey-Álvarez 1968, Neumann 1996, 1998, Ng et al. 2008), but molecular studies indicated that M. squinado is more closely related to M. crispate than to M. brachydactyla (Sotelo et al. 2009). Molecular analysis also revealed that the divergence between M. brachydactyla and M. squinado-M. crispata clade occurred in the Miocene (9.5 mya) and the divergence between M. squinado and M. crispata, occurred in the Pliocene (3.9 mya). Accordingly, the large morphological resemblance between M. brachydactyla and M. squinado could be also due to convergent evolution (see Neumann 1996, 1998, Sotelo et al. 2008, 2009 for taxonomic status). A diagnostic tool was developed to identify the four species of Maja in Europe with morphological and molecular methods (Guerao et al., 2011). Adults of M. brachydactyla and M. squinado are commercially exploited species and a simple relationship between carapace length (CL) and antorbital spine length could be used to differentiate the two species.

 

Marine brachyuran crabs are usually opportunistic consumers (Števèiæ 1967, Choy 1986, Abelló and Cartes 1987, Abelló 1989) and this is also true for M. brachydactyla according to studies based on stomach contents (De Kergariou 1974, Bernárdez et al. 2000): M. brachydactyla feed on a large variety of preys, consuming 50% of algae and a mixture of animals (mollusks, crustaceans, echinoderms, etc.). De Kergariou (1974) and Bernárdez et al. (2000) found differences in the diet between males and females and between juveniles and adults which they attributed to an uneven bathymetric distribution, a pattern typical of many large brachyuran crabs (e.g. Bennett and Brown 1983, Hines et al. 1987, Spivak et al. 1994). However, recent research using stable isotopes has failed to find any differences between sexes in diet or habitat use patterns either in adults (Bodin et al. 2007) or juveniles (Bodin et al. 2007, Freire et al. 2009).

 

Stable isotope ratios of carbon and nitrogen are widely used in ecology for the study of trophic rela­tionships and habitat use patterns, because the stable isotope ratios in a consumer’s tissues reflect those in the diet, which in turn depends on the relative availabil­ity of the light and heavy isotopes of each element for primary producers (Hobson 1999, Koch 2008, Graham et al. 2010). Marine macrophytes are typically enriched in 13C compared with phytoplankton, but macrophytes occur only in shallow waters and hence the stable isotope ratio of carbon consumers typically decreases with depth in coastal areas (e.g. Cardona et al. 2007, Drago et al. 2009, Freire et al. 2009, Pinela et al. 2010). Accordingly, the stable isotope ratio of carbon can be used to explore intraspecific differences in bathymetric distribution by sex or age, although tissue selection is critical because stable isotope turnover rates are tissue-dependent (Martínez del Río et al. 2009).

 

Previous studies on M. brachydactyla using stable isotope ratios concluded that no sexual difference ex­isted in diet or habitat use (Freire et al. 2009, Bodin et al. 2007), in contrast with earlier studies based on stomach contents (De Kergariou 1974, Bernárdez et al. 2000). This incongruence may be due to the fact that they analysed tissues with a relatively high turnover rate sampled from specimens collected from the same habitat. This experimental design was useful to assess the existence of dietary differences between groups in the same habitat, but likely failed to detect any previ­ous habitat segregation.

 

Tissues that remain inert after synthesis (e.g. feathers, hair, nails and arthropod exoskeleton) are a good choice for the study of habitat use patterns, as they record the unmodified stable isotope ratios of the habitat where they were formed (Hirons et al. 2001, Cherel and Hobson 2005). The organic matter in the exoskeleton, a mixture of chitin and proteins, offers a good alternative, as the stable isotope ratios of arthropod exoskeleton remain stable after synthesis (Hobson et al. 1999) and spider crabs have a terminal moult, i.e. they do not moult after the moult of maturity. The last intermoult period is the longest representing several months (González-Gurriarán et al. 1995, Corgos et al. 2007). During the moulting process, energy reserves are used to form the exoskeleton of these crabs (Vernet and Charmantier 1994), so the imprint of feeding during the last intermoult will be recorded in the carapace of the crabs. Thus, stable isotope ratios in the carapace are expected to represent a long-term signal of habitat use, compared to muscle and hepatopancreas tissues.

 

The aim of this study was to test the hypothesis that, within every population of M. brachydactyla and M. squinado, males and females forage at the same trophic level but differ in bathymetric distribution, and that this pattern is consistent across populations and species.

 

Materials and methods

Sampled individuals

In 2007-2009, 98 adult specimens of M. brachy­dactila and M. squinado (CL=141±20 mm) were col­lected by commercial fishery vessels in the Atlantic and Mediterranean Sea (Table 1, Fig. 1). Males and females were collected during the same sampling trials from all localities, except from Morocco, where only males were available.

 

Table 1. Sampling locations for isotope studies of Maja brachydactyla and Maja quinado.

 

Stable isotope analysis

Exoskeleton samples were collected from the propodus and dactylus segments without debris areas of the pereiopods of individuals from each population and sex. Exoskeletons were chosen to have at least a oneyear signature integrating fed intake in a broad area of distribution where specimens lived and fed.

 

Samples were stored frozen at –20°C, thawed, and dried at 60°C for 48-72 h. Then, each sample was sub divided in two sub-samples. Lipids were removed from one of them by rinsing the powdered samples several times with a 2:1 chloroform:methanol solution (Bligh and Dyer 1959). The same sub-samples were then treated for decarbonation with a 0.5 M hydrochloric acid (HCl) solution (e.g. Drago et al. 2009, Eder et al. 2012). 

 

Fig. 1. Map of sampling locations for isotope studies of Maja brachydactyla and Maja quinado.


As lipid extraction and decarbonation with HCl may affect the δ15N values (Bunn et al. 1995, Yokoy­ama et al. 2005), the untreated exoskeleton samples were used to measure δ15N. One milligram of sample was used for δ15N determination and 0.5-0.7 mg of sample was used for δ13C determination. The samples were weighed in tin cups (3.3-5 mm) and combusted in a continuous-flow isotope-ratio mass spectrometer (Flash 1112 IRMS Delta C Series EA, Thermo Finni­gan, Bremen, Germany). The samples were processed at the Serveis Científics i Tecnològics of the University of Barcelona.

 

Isotopic composition was expressed in the standard δ notation in parts per thousand (‰) relative to pre­defined international standards, V-PDB (Vienna Pee Dee Belemnite) calcium carbonate for δ13C and atmos­pheric N2 (air) for δ15N, according to:

 

where X is 13C or 15N, Rsample is the heavy-light isotope ratio of the sample (13C/12C or 15N/14N) and Rstandard is the heavy-light isotope ratio in the reference standards. The conventional use of these internationally accepted standards with relatively low and high levels of 13C and 15N, respectively, results in negative carbon and positive nitrogen isotope values. The international stable isotope secondary standards of known 13C/12C ratios, as given by the International Atomic Energy Agency (IAEA, Vienna, Austria), namely polyethylene (IAEA CH7, ä13C=–31.8‰), L-glutamic acid (IAEA USGS40, ä13C=–26.3‰) and sucrose (IAEA CH6, ä13C=–10.4‰), were used for calibration at a precision of 0.2‰. For nitrogen, international stable isotope secondary standards of known 15N/14N ratios, namely (NH4)2SO4 (IAEA N1, ä15N=+0.4‰ and IAEA N2, ä15N=+20.3‰), L-glutamic acid (ä15N=–4.5‰), and caffeine (IAEA 600 ä15N=+.0‰), were used to a precision of 0.3‰.

 

Data analysis

Two-way analysis of variance (ANOVA) (sex x population) was used to test whether males and fe­males differed in δ13C and δ15N values consistently across populations and species. As only males were available from Morocco, one-way ANOVA was used to analyse the effect of population on the stable isotope ratios of males.

 

We estimated the isotopic niche width using the con­vex hull area in the isotopic space defined by δ13C and δ15N (Layman et al. 2007). However, the use of Euclid­ean methods, such as convex hulls to define the isotopic niche space of a species in a community (Layman et al. 2007), is subject to sampling biases and sensitive to sample size (Jackson et al. 2011). The standard ellipse areas estimated by Bayesian inference can incorporate uncertainties such as sampling biases and small sample sizes into niche metrics (Jackson et al. 2011). Then we estimated the width of the isotopic niche at the popula­tion level using the Bayesian standard ellipse area by the function SIBER (Stable Isotope Bayesian Ellipses in R; Jackson et al. 2011) of the library SIAR (Stable Isotope Analysis in R; Parnell et al. 2010) in the free software R (R Core Team 2013). Furthermore, we calculated the magnitude of the isotopic overlap between sexes in each population based on 100000 posterior draws of the standard ellipse areas corrected for small sample size pa­rameters (Jackson et al. 2011). This approach, based on Markov-chain Monte Carlo simulation, assigns meas­ures of uncertainty to construct parameters of ellipses in a similar way to a bootstrap.

 

Discriminant Analysis was applied to δ13C and δ15N to test their reliability when used for individual assig­nation to the population of origin.

 

Results 

Figure 2 shows the δ13C and δ15N values of males and females of M. brachydactyla and M. squinado from the five considered populations. Males were consistently depleted in 13C when compared with females from the same population (ANOVA, model: F7.64<0.001, sex: F1.64<0.023, population, F3.64<0.001). Furthermore, differences among populations were unrelated to species identity, as a Tukey post-hoc test revealed differences between the δ13C of M. brachydactyla from Ceuta and Galicia, but no differences between the δ13C of M. brachydactyla from Ceuta and that of M. squinado from Ancona or between the δ13C of M. squinado from Catalonia and the δ13C of M. brachydactyla from Galicia (Table 2). That geographic pattern did not change when the males from Morocco were incorporated into the analysis and all the females were removed (ANOVA, model: F4.42<0.001), as a Tukey post-hoc test revealed differences between the δ13C of M. brachydactyla from Ceuta and those from Galicia and Morocco but no differences between the δ13C of M. squinado from Catalonia and the δ13C of M. brachydactyla from Galicia and those from Morocco.

 

Fig. 2. Distribution of δ13C and δ15N values (mean±SD) among population and sex of Maja brachydactyla (triangles) and M. sqi­nado (squares). Sex is denoted by colour (males, black; females, white) and population by letter: a, Ancona; b, Catalonia; c, Ceuta; d, Galicia; e, Morocco.

 

Table 2.  Results of the Tukey post-hoc tests. Values are the re­gional averages. 

 

Fig. 3. Bayesian standard ellipse areas (solid lines) and their re­spective convex hulls (dashed lines) for Maja brachydactyla (top panel) and Maja squinado (bottom panel), calculated by SIBER using the bivariate isotopic values (individual symbols) of each spe­cies, population and sex.

 

Statistically significant differences were observed among populations for δ15N values, but differences between sexes were not consistent across populations, although results were on the verge of similarity (ANOVA, model: F7.64<0.001, sex: F1.64<0.083, population, F3.64<0.001). Differences among populations were also unrelated to species identity, as a Tukey post-hoc test revealed differences between the δ15N of M. brachydactyla from Ceuta and Galicia but no differences between the δ15N of M. squinado from Catalonia and the δ15N of M. brachydactyla from Galicia (Table 2). The same was true when the females were removed from the analysis and the males from Morocco were incorporated, as only the males of M. squinado from Ancona were statistically different from the males of M. squinado from Catalonia and those of M. brachydactyla from Ceuta, Morocco and Galicia (ANOVA, model: F4.42<0.001: Table 2).

 

The Bayesian ellipses of females were larger than those of males in the population of M. brachydactyla from Galicia and in the two populations of M. squinado from Catalonia and Ancona, whereas the opposite was true for the population of M. brachydactyla from Ceuta (Fig. 3). Everywhere, the overlap of the Bayesian el­lipses of both sexes was highly asymmetrical. In the population of M. brachydactyla from Galicia and in the two populations of M. squinado from Catalonia and Ancona, the overlap area represented a larger fraction of the surface of the male ellipses than that of the fe­male ellipses (42.1% vs. 11.3%, 74.3% vs. 52. 9% and 32.6% vs. 19.7% respectively), whereas the opposite was true for the population of M. brachydactyla from Ceuta (males, 13.8%; females, 53.5%).

 

Discriminant analysis ignoring species and sex classified correctly only 53.7% of the samples (Fig. 4), which is significantly higher than expected by chance but too low for traceability. Individual assignation improved when discriminant analysis was run independently for each species, as 81.6% of the samples of M. squinado and 66. 7% of those of M. brachydactyla were classified correctly. The highest accuracy was achieved when the discriminant analysis was run independently for the males and females of each species (Fig. 4). Figure 4 shows the accuracy of individual assignments for each species, sex and locality. The lowest accuracy was achieved for males of M. brachydactyla from Galicia (70%) and the highest for the females of the same species from Ceuta (100%) and males of M. squinado from Ancona (100%).  

Fig. 4. Performance of discriminant analysis based on δ13C and δ15N without any prior information, incorporating species identity, and incorporating species and sex.


Discussion

Maja brachydactyla is an opportunistic species that consumes any range of food items that is avail­able (Števcic 1967, De Kergariou 1974, Bernárdez et al. 2000). Although there are no studies on the feeding habits of M. squinado, it seems quite possible that this species is also an opportunistic feeder. Both species have a complex biological cycle, with varying habitat requirements and changes in behaviour depending on the growth phase and the specific time period in the life history (Števcic 1973, González-Gurriarán and Freire 1994, Hines et al. 1995, González-Gurriarán et al. 2002). The juvenile stage lasts approximately two years until a terminal moult, at which time sexual maturity is achieved (González-Gurriarán et al. 1995, Hines et al. 1995, Sampedro et al. 1999). After the terminal moult, the adult individuals migrate to deeper waters (González-Gurriarán et al. 2002), where mat­ing probably occurs. Only the adult females return to the shallower waters to spawn. In terms of carbon and nitrogen stable isotopic composition, tissues with high turnover rates (muscle and hepatopancreas) reflect the diet in the short term, and could be indicative of differ­ences in diet during the days or weeks previous to their capture and analysis (Freire et al. 2009). However, the carapace provides an integrated signal of the animal assimilated diet on a long-term time scale (Hobson et al. 1999). In the present study, all animals were post-pubertal specimens and their exoskeleton was formed before the terminal moult (Sampedro et al. 1999). Therefore, isotope signatures may provide insight into the trophic preferences during the last intermoult pe­riod before the animals reached sexual maturity (<3 months; Corgos et al. 2007).

 

As expected, the stable isotope ratios of carbon and nitrogen in M. brachydactyla and M. squinado differed dramatically among populations, independently of species identity, hindering the capacity of stable isotopes for traceability unless species and sex are included in the analysis as priors. The relative abundance of 15N in marine primary producers and their consumers depends on the balance of fixed and recycled nitrogen and is usually very low in oligotrophic regions (Graham et al. 2010, Somes et al. 2010), so it is lower in the Mediterranean than in the adjoining Atlantic (e.g. Borrell et al. 2006, Gómez-Díaz and González-Solís 2007, Giménez et al. 2013). Actually, the lowest δ15N values were observed in the specimens of M. squinado from Ancona, likely to be captured in the northern Ionian Sea, a region characterized by very low δ15N values in particulate organic matter (Pantoja et al. 2002). Moreover, the relative abundance of 13C in marine primary producers and their consumers depends on the availability of inorganic carbon within their boundary layer, which in turn depends on primary productivity, water turbulence, and plant architecture (Post 2002). Interestingly, the highest values were observed in specimens from Morocco, Galicia and Catalonia, which are the most productive of the five regions considered (Longhurst 1998, Bosc et al. 2004). This result suggests that the highest interpopulation variability in the δ13C values of the two species of crabs considered here depends on the intensity of the regional primary productivity, although other factors such as differences in the arrival of terrestrial allochthonous organic matter may also play a role.

 

The ä13C values within an area are also influenced by depth, because macrophytes are typically enriched in 13C when compared with phytoplankton in both the Atlantic (Freire et al. 2009) and the Mediterranean (Cardona et al. 2007), but macrophytes occur only in shallow waters. As a consequence, the ä13C values typically decrease in deeper, off-shore habitats as compared with shallow, on-shore habitats where the relevance of macrophytes as a source of organic carbon is higher (e.g. Cardona et al. 2007). In this scenario, the consistent enrichment in 13C of females across populations and species suggests that female spider crabs use shallower habitats than males before the post-pubertal moult. Furthermore, Bayesian ellipses show that sexes differ dramatically in the breadth of their isotopic niches in all the populations studied and that females usually have a broader isotopic niche than males, ex­cept for M. brachydactyla in Ceuta.

 

These results are in agreement with the strong evi­dence that spatial and seasonal segregation exists by sex between adults and reproductive stage in this group of species (De Kergariou 1971, 1984, Števcic 1973, Rodhouse 1984, González-Gurriarán and Freire 1994, González-Gurriarán et al. 2002, Corgos et al. 2007, Fahy and Carroll 2009). M. brachydactyla adults migrate to deep water in association with gonad maturation and the development of seminal receptacles in the females. They return to shallow inshore water to incubate eggs and release larvae. However, males migrate longer distances than females (Fahy and Carroll 2009). Our results suggested that males and females may be spa­tially segregated before the terminal (pubertal) moult, as indicated by δ13C values in their exoskeletons, indi­cating that pre-pubertal males migrate to deeper waters than females, though females may remain in shallow waters and migrate to deep water mainly for coupling. However, δ13C short-term isotopic signature values in the muscle of migrating males and females were simi­lar in M. brachydactyla from western Brittany (Bodin et al. 2007), indicating that both sexes co-habited and preyed on similar food items during migratory periods.

 

The δ15N values of individuals from the same spe­cies inhabiting the same area may also vary, depending on their trophic level (Post 2002). In the present study, the absence of statistically significant differences be­tween sexes for δ15N suggests that males and females did not differ consistently in their trophic level, al­though differences may exist in some populations. Ex­periments in captivity suggest that the exoskeleton of crustaceans has a negative 15N fractionation, in contrast with the positive fractionation of muscle (Yokoyama et al. 2005). These differences explain why the δ15N val­ues reported here are much lower than those reported for the muscle of M. brachydactyla (Bodin et al. 2007, Freire et al. 2009). Considering an average diet-to-exoskeleton fractionation of –2.4‰ reported by Yoko­hama et al. (2005), the δ15N values reported here for M. brachydactyla from Galicia suggest a diet with a δ15N value of approximately 7.4‰, consistent with an om­nivorous diet with a strong plant component according to the regional isospace (Freire et al. 2009). Likewise, the δ15N values reported here for M. squinado from the Mediterranean (2.5‰) suggest a diet with a δ15N value of approximately 4.9‰, also consistent with an om­nivorous diet with a strong plant component according to the regional isospace (Cardona et al. 2007).

 

Stomach content studies have shown that macroal­gae were food items of importance in the diet of these species (Števcic 1967, Bernárdez et al. 2000). Isotopic signals from the current study suggested that macroal­gae seemed to be better digested and assimilated than other preys ingested (e.g. crustaceans, mollusks and echinoderms). This hypothesis is supported by the high level of α-amylase activities found in adult specimens held in captivity, which were one order of magnitude higher than total proteases (Rotllant et al. 2013). In the present study, differences between sexes for δ15N values were significant for populations of M. brachty­latyla from Galicia and M. squinado from Ancona. The low δ15N values observed in males indicate a higher capacity to digest organic material from vegetal origin, which is supported by their higher digestive enzyme capacities, in particular in α-amylase activity, observed in males compared to females caught in Galicia (Rotl­lant et al. 2013). In our study, higher δ15N values were observed in Atlantic populations than in Mediterranean ones, as previously reported for other species (e.g. Bor­rell et al. 2006, Gómez-Díaz and González-Solís 2007, Giménez et al. 2013).

 

The results reported here are useful for product traceability. In the Spanish market, during the whole year, but particularly during the spider crab closed season (May to November approximately, annual variations depending on total fishing quotas), the fisheries market is supplied by M. brachydactyla specimens caught in Ireland, France, the United Kingdom and/or Morocco (Mercasa 2007), although crabs from Galicia fetch higher prices. In this study, stable isotope signatures for commercial Maja species allow their geographical origin of capture to be identified. Thus, this methodology could be used for fisheries management to identify the origin of the product, prevent fraud and guarantee its traceability along the commercial chain.

 

Acknowledgements

Financial support was provided by the Ministry of Science and Research to GG (post-doctoral fellow­ship; INIA). Bench fees were provided by JACUMAR (REPES project) to GR.

 

 

This article was originally published in Scientia Marina 80(1): 103-110. doi: http://dx.doi.org/10.3989/scimar.04236.23B. This is an Open Access article distributed under the Creative Commons Attribution-Non Commercial License (by-nc) Spain 3.0.

 

 

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