Abstract
The diet of an individual is a result of the availability of dietary items and the individual's foraging skills and preferences. Behavioural differences may thus influence diet variation, but the evolvability of diet choice through behavioural evolution has not been studied. We used experimental evolution combined with a field enclosure experiment to test whether behavioural selection leads to dietary divergence. We analysed the individual dietary niche via stable isotope ratios of nitrogen (δ15N) and carbon (δ13C) in the hair of an omnivorous mammal, the bank vole, from four lines selected for predatory behaviour and four unselected control lines. Predatory voles had higher hair δ15N values than control voles, supporting our hypothesis that predatory voles would consume a higher trophic level diet (more animal versus plant foods). This difference was significant in the early but not the late summer season. The δ13C values also indicated a seasonal change in the consumed plant matter and a difference in food sources among selection lines in the early summer. These results imply that environmental factors interact with evolved behavioural tendencies to determine dietary niche heterogeneity. Behavioural selection thus has potential to contribute to the evolution of diet choice and ultimately the species' ecological niche breadth.
Keywords: bank vole, diet choice, predatory behaviour, specialization, stable isotopes, trophic niche
1. Introduction
The diet an individual consumes is a result of the availability of different food items, the species-specific dietary range, and individual specialization [1,2]. The realized dietary niche is thus a combination of the species’ fundamental niche (e.g. the hypothetical ideal diet), and the constraints on access to the ideal diet [3,4]. Differences among individuals in dietary niche are generated by environmental and genetic variation as well as phenotypic plasticity [1,2], but the relative effects of these factors have rarely been tested [2,5–7]. Inherited effects might manifest through various morphological, physiological, or behavioural traits that shape preferences for certain foods and specialized behaviours connected to seeking or processing food items [5]. For example, stable individual differences have been observed in hunting behaviours (antlions Myrmeleon hyalinus [8], guillemots Uria lomvia [9]). Genetically determined behavioural differences could thus contribute to dietary specialization at the individual level, with significant consequences for resource competition and even community functioning [2,10,11]. Yet, the role of evolved behavioural traits in shaping diet choice remains poorly understood [5] and research has focused primarily on predatory behaviour of carnivores, which may specialize more than other trophic groups [2]. Deciphering the relative effects of genetic and environmental influences on realized diets of individuals is challenging but essential for understanding the evolvability and plasticity of the dietary niche [7]. In this study, we address this problem by combining artificial selection for a predatory behaviour in an omnivorous mammal with a field experiment.
Omnivores, animals that consume diets from more than one trophic level [12], are an understudied but exceptionally interesting group for diet choice studies because of the broad range of different types of dietary items they can potentially consume. This potential could facilitate trophic niche heterogeneity among individuals under intraspecific competition [13]. The wide potential dietary breadth of omnivores involves morphological and physiological adaptations such as changes in dentition, gut length and structure, digestive enzymes and stomach acidity compared to related herbivorous or carnivorous species [12,14–16]. Individual-level variation in trophic niche has not been previously linked with behaviours, although such divergence could be widespread and under selection in omnivores [17]. Behavioural adaptations such as capturing and processing prey would be required to transition from strict herbivory to omnivory. Yet, the significance and evolvability of behavioural traits associated with the diet breadth of omnivores remains unknown.
In this study, we assessed the significance of a behavioural adaptation on diet choice in an omnivorous rodent, the bank vole (Myodes [Clethrionomys] glareolus). We assessed the relative importance of a genetically determined behavioural type and environmental variation on the realized diet of individuals. We compared the dietary niche of bank voles from lines artificially selected for an increased predatory tendency [18] with unselected lines by measuring stable isotope ratios of carbon and nitrogen in the hair of field-reared individuals of both types. Stable isotope methods are suited to studying individual dietary niches as they permit an evaluation of the consumed diet based on the isotopic signatures in the animal's tissues, integrating dietary information over longer time periods [4,19]. A higher isotope ratio of nitrogen (15N/14N), relative to other organisms in the same system, indicates consumption of food items from a higher trophic level because 15N is enriched along the food chain [20]. Isotope ratios of carbon (13C/12C) in turn are more conserved through the food webs but variable among primary producers [20] and allow differentiation among consumers' diet sources. Using these isotope ratios as indicators of long-term diet choice, we evaluated the potential for behavioural selection to shape the dietary niche. We specifically hypothesized that the artificially selected tendency for predatory behaviour would lead to the consumption of a diet from a higher trophic level (higher proportion of animal sources, such as invertebrate prey) in field conditions, indicated by a higher δ15N ratio in the hair of predatory relative to control line voles.
2. Material and methods
(a) . Study system
The bank vole is a common, widespread rodent, whose dietary profile is uniquely placed among European rodent species, occupying an intermediate niche between herbivorous arvicoline species and granivorous–insectivorous murine species [21,22]. The majority of their diet consists of different plant sources (seeds, leaves, flowers, roots, bark) [21,23–25], but the proportion of animal matter (primarily invertebrates) in stomach contents can range from 0 to 23% [25–28] and the proportion of fungi from 0 to 10% [22,25–29] among populations and seasons. The majority of the animal food consists of insect larvae especially in the early season, but adult insects, worms or molluscs and vertebrate remains are infrequently consumed [22,25,29]. Possible heterogeneity in diet among individual bank voles remains poorly known because the relative proportions of different dietary items consumed by individuals over time has been difficult to assess with gut content analyses (but see [24]). The degree of dietary niche divergence among individuals is therefore unknown.
To test the importance of artificial selection (overall genotypic differences) in the realized diet, we used bank voles from a unique long-term selection experiment (for details see [18,30,31]). Briefly, several selection lines were established from a source population of 320 voles captured in Poland in the years 2000–2001. To generate voles with a ‘predatory’ phenotype, voles are allowed to interact with a live cricket and the state of the cricket is checked at standardized time intervals. The voles that captured a cricket in the shortest time period in each generation were selected to breed. The selection has influenced both the time lag and overall propensity to predate a cricket relative to control lines. Four parallel predatory (P) and four unselected control (C) lines are maintained. The continued selection has resulted in significant divergence in predatory efficiency, with predatory voles catching the cricket more than five times more often than control voles by the 24th generation [31]. In the present study, we used descendants (offspring and grand-offspring) of the 25th selected generation. The voles used in this experiment were never exposed to live prey prior to the experiment. The parental generation (founders) were born and reared in laboratory conditions at the University of Jyväskylä, Finland with ad libitum water and standard rodent chow (Avelsfoder för råtta och mus R36; Lactamin, Stockholm, Sweden; 301 kcal per 100 g; macronutrient content: 18.5% protein; 4.0% fat; 55.7% carbohydrate) until release to field enclosures.
(b) . Field experiment
To test whether the voles selected for a predatory tendency consumed a diet from a higher trophic level than control voles, we performed a field experiment. Founder voles were released into eleven 0.2 ha field enclosures near Konnevesi research station in Central Finland over two replicate experimental rounds in early (June–July) and late (August–September) summer (hereafter: early versus late season) in 2018 (total 22 enclosure replicates). The field enclosures had early succession vegetation consisting primarily of grasses, forbs and shrubs. This study was performed in connection with a larger field experiment designed to test density- and frequency-dependent selection on behavioural tactics (Z. Boratyński, A.M. Hämäläinen, M. Kiljunen, E. Koskela, P. Koteja, T. Mappes, P.C. Watts 2022, unpublished data in preparation), for which the initial density (8 or 16 adults per enclosure) and ratio of the P- and C-line adults (1 : 3 or 3 : 1) varied among the enclosures. The initial adult sex ratio was 1 : 1 in all enclosures.
The founders were mated (maintaining selection line separation) in spring-summer 2018 in the animal facilities in Jyväskylä. Females were monitored daily to determine the exact date of delivery. Within a day of the birth of a litter, the pups were individually marked by distal phalanx removal, sexed, weighed and their head widths measured. After parturition, the females with their newborn litters were transported into the enclosures in their home cage [32]. The cages were placed open and on their side on the ground with partial shelter and a small quantity of food (approx. 2 days minimum energy requirement) so that the females could transport the pups out at leisure. Litter size ranged 2–7 (C mean = 4.13, P mean = 4.47), with the total initial number of pups released per enclosure ranging 15–38.
The dams were left to rear the young to independence on a natural diet. After ca 25 days, when the juveniles move around independently, all animals were captured from the enclosures using live traps baited with sunflower seeds and potato (details on enclosures and live trapping e.g. [33]). In total, 133 weaned young (65 P-line, 68 C-line) were captured from the enclosures in the two rounds (first: n = 50, second: n = 83). The number of weaned offspring per enclosure per round ranged from 0 to 28 individuals. One enclosure had no surviving offspring in either round and another two enclosures had none in the first round. Captured young voles were identified, sexed, weighed, head width measured and a small patch of hair was clipped from the back with scissors (aiming to collect entire hair shafts) for isotope analyses. All hair samples for isotope analyses were thus derived from individuals that had spent their entire lifetime, from age 1–3 days (i.e. before growing any fur) until sampling, in the field enclosures. The dams relied on natural food items after the first few days of lactation. The pups begin to feed on solid food by the age of ca two weeks (A.M. Hämäläinen, E. Koskela, P. Koteja, T. Mappes 2022, personal observations from laboratory conditions) and are weaned by age 20 days [18,34]. Thus, the isotope composition in the hair of the weaned juveniles consists of the combined (and indistinguishable) effects of the diet consumed by the individual and by its mother. The hair samples were stored in Eppendorf tubes in room temperature until analyses in summer 2019.
(c) . Collection of possible dietary items
To relate the isotope ratios in the voles' hair to the available food items, we collected samples of plants, invertebrates and fungi from the field enclosures and analysed their isotope signatures. The detailed methods are provided in the electronic supplementary material.
(d) . Isotopes of captive voles
To account for the possibility that any differences between the selection lines are owing to intrinsic differences in physiology (e.g. differential fractionation into hair owing to differences in metabolism), we collected hair samples from individuals that had lived their entire lives in the laboratory on the standard rodent diet supplied to the adults in this experiment before their release into the field enclosures. We shaved hair from the backs of two females from each of the four parallel predatory selection lines and the four control lines, producing eight samples per selection direction (total n = 16). The samples were analysed in the same manner as the samples derived from the field conditions.
(e) . Isotope analyses
Lipids were removed from the hair samples with a chloroform–methanol extraction [35], samples were dried and then 0.5–0.7 mg of each sample was weighed into tin capsules (see also the electronic supplementary material). All samples representing vole diet (invertebrates, plant material, fungi) were freeze-dried to a constant weight, ground to a fine powder using a ball mill or mortar and pestle, and then also weighed into tin capsules. Stable isotope analyses for carbon and nitrogen were conducted using a Thermo Finnigan DELTAplus Advantage continuous-flow stable isotope-ratio mass spectrometer (CF-SIRMS) coupled with a FlashEA 1112 elemental analyser. Results are expressed using the standard δ notation as parts per thousand (‰) differences from the international standard. The reference materials used were internal standards of known relation to the international standards of Vienna PeeDee Belemnite (for carbon) and atmospheric N2 (for nitrogen). Precision was always better than 0.13‰ for carbon and 0.38‰ for nitrogen, based on the standard deviation of replicates of the internal standards.
(f) . Trophic enrichment factors
To relate the stable isotopes in vole hair to the isotope ratios of possible food items, we determined the average trophic enrichment factor (TEF, Δ), i.e. difference in isotope ratios between the consumed food items and the measured isotope ratios in hair. We used the 16 samples collected from captive voles maintained on a standard diet of rodent pellets to determine the TEFs (i.e. the degree of fractionation). We computed the average isotope values for the rodent pellets fed to the captive voles as δ15N = 1.778 ± 0.268 (mean ± s.d.), and δ13C = −26.613 ± 2.491. We related these to the isotope values measured from the hair of the captive voles (δ15N = 7.11 ± 0.55, δ13C = −24.47 ± 0.24) and determined the TEFs as Δ15N = 5.335 ± 0.553, and Δ13C = 2.145 ± 0.239. These values were used to correct the isotope ratios of the food source samples from the field experiment to associate the food items with the vole isotopes.
(g) . Statistics
Inspection of the isotope data indicated an outlier in δ15N (δ15N = 8.73, 4 s.d. divergence from mean δ15N; Grubbs's outlier test: G = 5.12996, U = 0.79912, p < 0.001) that skewed the δ15N data disproportionately. As the reason for the exceptionally high reading was unknown but might indicate e.g. a sample handling error, we chose to conduct all further analyses without this observation, with a final sample size of n = 132 for all analyses. Including the outlier in the models did not qualitatively change the analysis outcomes but reduced the significance of some results (electronic supplementary material, table S2). The isotope data with both seasons combined were not normally distributed (Shapiro–Wilk test of δ13C and δ15N both p < 0.001), so we used Wilcoxon tests for bivariate analyses of the raw data. Differences in dietary variation (i.e. individual niche differentiation) between seasons and selection lines were explored with Levene's test for homogeneity of variance (median-centred approach; car-package [36]).
We constructed linear mixed effects models (LME) to examine the effects of selection and environment on isotope values while accounting for maternal and enclosure effects. We performed Box-Cox power transformation of the isotope values (δ15N: λ = −1, δ13C: λ = 2) and used a Gaussian error distribution with an identity link function for both models (see the electronic supplementary material for details). We present the model-derived estimates for the Box-Cox- transformed data and back-transformed estimates for the variables of interest.
For each response variable (δ15N and δ13C values in hair), we created a full LME-model including as predictor variables the selection regime (C = control, P = predatory), season (1 = early, 2 = late summer), density treatment (high, low), sex (male, female) and body condition (residual body mass relative to head width). We also included an interaction term of selection regime and season to test for the possibility that the seasonal food availability would influence the realized diets of the selection regimes differently. As intraspecific competition is thought to increase selection for niche divergence [2,37–39] we also evaluated the possibility that niche divergence between the lines is higher in high-density conditions by including an interaction term of density treatment and selection regime. When an interaction term was statistically non-significant (p > 0.05), it was dropped from the model to facilitate easier interpretation of the main effects. For δ15N, we included the random effects of the enclosure (1–10; possible differences in microhabitat and in the social environment) and mother's identity (n = 52). For δ13C, including enclosure caused non-convergence owing to a singularity, thus only mother's identity was included as a random effect. The relative strength of the effects (standardized estimates) of all variables included in the final models are shown in figure 1.
Figure 1.
Effects of predictor variables on isotope ratios of δ15N and δ13C. Forest plots for (a) δ15N and (c) δ13C show standardized (divided by 2 s.d.) estimates for fixed effects derived from linear mixed-effects models (electronic supplementary material, table S1) with Box-Cox-transformed isotope ratios as the response variables. The dots and associated numbers denote the relative effect, horizontal lines indicate 95% confidence intervals (CIs) and asterisk notation refers to the effect significance (p-value). The predicted values and 95% CI for the marginal interactive effects of season x selection regime from these models are shown in panel (b) for δ15N and (d) for δ13C. For raw data and details on the random effects, see the electronic supplementary material. (Online version in colour.)
All analyses were completed using R program v.4.0.3 [40]. We fitted LMEs with restricted maximum likelihood estimation using the R-package lme4 [41]. p-values were computed using Satterthwaite's method with the package lmerTest [42]. Pseudo-R2-values were computed using the MuMIn package [43]. The results were visualized using packages ggplot2 [44], ggsignif [45], sjPlot [46].
3. Results
(a) . Isotope ratios of captive voles
In the laboratory, no significant difference was found between the predatory and control voles in δ13C (W = 43, p = 0.279) or δ15N (W = 50, p = 0.065; electronic supplementary material, figure S1). Thus, any differences between the lines observed in the field conditions are probably not owing to intrinsic differences in physiology (e.g. differential assimilation of macronutrients).
(b) . Models of isotope ratios in the field
The δ15N values were strongly affected by an interaction between the effects of selection regime and the experiment round (figure 1; electronic supplementary material, figure S2 and table S1). In line with our hypothesis, the δ15N values of the predatory selection direction were higher than those of the control-line voles, indicating that voles selected for predatory behaviour consumed a diet from a higher average trophic level than non-selected voles. The back-transformed estimates indicate a ca 12% difference in δ15N between C and P regimes in the early season (predicted δ15N for C: 5.88 [95% CI: 5.88, 6.25]; for P: 6.67 [6.25, 6.67]). However, in the late season, no difference between the selection regimes was found (predicted δ15N for C: 5.88 [5.56, 6.25]; for P: 5.88 [5.56, 5.88]). δ15N values were on average slightly higher in the low-density treatment, suggesting that higher intraspecific competition may lead to an overall lower-level dietary niche. This effect of density was not dependent on selection regime (interaction of density and selection p > 0.1).
Similarly, the δ13C-values were higher in the predatory lines in the early but not in the late summer (figure 1; electronic supplementary material, figure S2 and table S1). The back-transformed estimates indicate a ca 3% difference in δ13C between C and P regimes in the early season (C: −25.77 [95% CI: −26.24, −25.39]; for P: −24.99 [−25.23, −24.77]) and a 0.2% difference in the late season (C: −24.32 [−24.48, −24.16]; for P: −24.39 [−24.56, −24.22]). The δ13C -values were also significantly higher in the second replicate overall, suggesting that the voles' diet probably consisted of different plant sources in early and late season (figure 1; electronic supplementary material, figure S2; table S1). Density treatment did not influence δ13C (interaction with selection regime and main effect of density both p > 0.1).
Mother's identity (random effect, n= 52) had a significant influence on both δ13C (χ251 = 111.02, p < 0.001; electronic supplementary material, figure S4A) and δ15N (χ251 = 108.89, p < 0.001, electronic supplementary material, figure S4B) and δ15N varied among enclosures (χ2 9= 33.894, p < 0.001; electronic supplementary material, figure S4C). The differences in marginal and conditional pseudo-R2 (electronic supplementary material, table S1) suggest that mother's identity explained ca 25% of the variation in δ13C. In δ15N, the random effects of enclosure and mother's identity together explained ca 48% of the variation (in a model excluding enclosure, mother's identity explained ca 45% of variation). The average number of juveniles per mother did not significantly differ between selection regimes (on average 2.6 juveniles with the same mother in C, 2.5 in P).
(c) . Variances of isotope ratios
The variances of isotope ratios were significantly higher in the early than in the late season for both δ15N (F1,130 = 22.479, p < 0.001; electronic supplementary material, figure S2A) and δ13C (F1,130 = 15.548, p < 0.001; electronic supplementary material, figure S2B), suggesting an overall higher degree of niche differentiation among individuals in the early relative to late summer (see also the electronic supplementary material, figure S3). When split by selection regime, the seasonal differences remained significant for both selection regimes for δ15N (control: F1,66 = 12.196, p < 0.001; predatory: F1,62 = 4.461, p = 0.039) but not for δ13C (control: F = 0.879, p = 0.352; predatory: F = 3.245, p = 0.076). There were no significant differences in variance between selection regimes in δ13C (p > 0.1 overall and when split by season). For δ15N, variance was significantly higher overall for predatory relative to control line voles (F1,130 = 6.137, p = 0.015), but this difference did not hold within seasons. Variances of δ13C or δ15N did not significantly differ among density treatments in either P or C voles.
(d) . Vole isotopes relative to isotopes of food sources
Vole isotope values were mainly within the isotope bi-plot area bounded by the TEF-corrected dietary source values (figure 2; for raw data, see the electronic supplementary material, figure S5). As the isotope ratios of the voles are derived from the combination of the different food items they consumed, these results imply that the voles consumed a primarily herbivorous diet (δ15N values low relative to animal sources), with the higher δ13C values especially in the late season suggesting a high consumption of grass inflorescences and seeds and possibly fungi. Although the vole hair samples fall within the range of isotope values of the sampled food items, the slight bias towards the lower right corner suggests a possibility that some food sources were missed from the analyses (e.g. lichens [22,25,27] with high δ13C and low δ15N [47] were not encountered during sampling). This hampered the use of stable isotope mixing models (e.g. MixSIAR) to formally estimate dietary proportions (analyses not shown).
Figure 2.
Isotope values of food sources and voles. Shown are mean values and standard deviations for vegetative parts (leaves, stems, roots) and reproductive parts (inflorescences, seeds) of forbs and grasses, mosses, fungi, herbivorous and predatory invertebrates, and mammal tissue (vole brain and muscle, shrew muscle). The isotope values of the food sources have been corrected for TEF (Δ15N: 5.335, Δ13C: 2.145). Vole hair values represent raw data (early and late season, selection regimes C: control, P: predatory; note that the symbols for C and P overlap in late season). See the electronic supplementary material, figure S3 for the raw data for the vole hair samples only and figure S5 for the raw data for food sources. (Online version in colour.)
4. Discussion
(a) . Interaction of evolved behavioural type and environment create dietary niche variation
Individual dietary preferences are frequently observed, but the significance of a genetic component in foraging behaviours and thus the heritability of the dietary niche remains unresolved [1,2]. Individual heterogeneity in dietary niche of omnivores and especially diet partitioning among different trophic levels is largely unknown (but see [17]) despite the potentially significant implications for community functioning. This study provides, to our knowledge, the first evidence of an inherited foraging behaviour affecting the niche divergence of an omnivorous rodent in a field setting. As predicted, an artificially selected predatory tendency was associated with a higher trophic level diet (higher δ15N isotope ratio suggesting consumption of more animal food relative to plants) relative to control line animals inhabiting the same field enclosures. This difference was limited to the early summer season, however, and disappeared later in the season, suggesting plasticity in dietary niche despite an underlying genetic tendency for dietary divergence. The diets of the predatory and control line animals also diverged in terms of carbon isotopes in the early summer, confirming that the realized diets of the selection lines differed. Thus, the predatory and control line voles occupied slightly different positions in the food web in the early season, probably owing to a low availability of preferred high-energy seeds in the early season. We conclude that differences in an inherited behaviour were associated with a small but significant effect in dietary niche differentiation in interaction with the seasonal environment.
(b) . The evolution of foraging behaviour contributes to dietary niche differentiation
The genetic basis of individual niche variation remains poorly understood [2] but variation in realized diet may depend on e.g. preference, capacity to capture or process certain items, competitive ability and behavioural types, which all have a genetic component (reviewed in [1,2,5]). Many foraging behaviours such as prey recognition or preference [6,48,49] as well as morphological traits relevant to prey selection are partly heritable [50], including the predatory tendency selected for in the vole selection lines used in this study [18,31]. This study shows that artificial selection for a behaviour contributes to dietary niche divergence under natural food conditions (the diet consumed in the field being subject to a range of foraging behaviours). Interestingly, a complement of this association was found in sea otters [39], in which dietary specialization (owing to food limitation) had consequences for behavioural phenotype divergence. Together, these studies indicate a possibly bidirectional association between diet and behaviour. This first evidence of behavioural selection generating variation in diet suggests an intriguing prospect for a broader role of behavioural evolution contributing to dietary niche differentiation, as suggested previously for adaptive radiation of species into different trophic niches [51]. Future studies should evaluate the possibility that selective pressures acting on behavioural syndromes [52] or traits such as risk taking, exploration and aggression could simultaneously impact on the niche breadth or specialization of individuals, contributing to associations between ecological roles and behavioural types.
Diet could be further shaped by other traits coevolving with the selected behavioural traits. Consistent behavioural traits frequently correlate with physiological or life-history traits that facilitate adaptation to specific environments [53–55]. For example, individuals with active personalities are expected to have a high metabolism and a high energy requirement, which in turn should be met by higher energy consumption, and possibly a broader dietary niche [5]. Thus, associations between dietary preferences and behavioural traits may be reinforced, e.g. by the differing energetic needs and digestive efficiency associated with behavioural types [56–58]. Several other traits have been indirectly selected alongside the directional selection for an increased predatory tendency and prey catching speed in our study system [18,31]. Predatory lines tend to have a proactive behavioural style [30], possible stress sensitivity [31], and tendencies for aggression and an elevated sensitivity to hunger (according to transcriptome analysis [59]). The predatory phenotype is thus characterized by various mechanisms that can drive predatory foraging behaviours.
In addition to directly selected behaviours, niche divergence could also be facilitated by behavioural plasticity in diet choice and foraging [13,37]. Dietary flexibility itself can improve fitness [60] and if selection operates on genes that increase plasticity per se [61], behavioural plasticity in foraging and diet choice could be under selection. Predatory voles in this study might have higher dietary plasticity, manifesting as either (i) predatory individuals' diets consisting of a broader range of food items, or (ii) different individuals specializing in different subsets of available items. In support of the latter possibility, predatory voles tended to have overall higher trophic niche heterogeneity over the summer (higher overall variance in δ15N among predatory line individuals relative to control animals). Trophic niche position was determined only once per individual, preventing assessment of within-individual diversity or consistency of diet choice. Thus, we can only speculate whether the observed plasticity results from specialization or stochasticity involved in the selection of rare food items, such as animal foods. Specialization to certain dietary items can have fitness benefits through the improved ability to effectively exploit those specific resources [62–64] but entails possible trade-offs because of the limited flexibility in dietary range or foraging behaviours [5,65] (see also [60]). Specializing could also allow individuals to escape direct competition (e.g. switching to hunting instead of competing for plant protein), but we found no evidence of higher competition (density) influencing the dietary niche of predatory voles more than control voles.
The genetic component of the dietary niche development may be reinforced by cross-generational transmission of preferences in species with parental care (see also cross-generational host fidelity in insects [66]). This possibility is suggested by the observed maternal effects in the isotope profiles of the juveniles (random effect of mother's identity), which might result from maternal genetic and epigenetic effects, possible differences owing to e.g. litter size or the timing of weaning, a direct influence of the maternal diet choice through milk, or preferences or skills the young voles learned from their mothers. Juvenile nutrition during nursing is derived from maternal diet choices (guided by their genetic background) in the form of milk. The resulting isotope profile may be fine tuned by the fractionation in isotopes between mother's diet, isotope ratios in milk, and consolidation in offspring tissues. The foraging behaviours of the juvenile voles themselves may develop in part through observation and exposure to specific foods in early life (described for sea otters [67]). It is not possible here to differentiate the contribution of the mother's versus the juvenile's diet on the resulting isotope ratios in the hair of juveniles because no information is currently available on the fractionation from mother to offspring in voles or the time lag in their effects (e.g. for how long are the elements/isotope ratios derived from milk retained in offspring hair). Importantly, however, we have no reason to assume that this constraint influences the effect of selection on trophic niche. Our sample also captures the dietary niche variation of surviving young voles only and we do not have information on the diets of those voles that died early in the experiment, but body condition of the surviving voles was unassociated with their isotope profiles. Dietary niche variation can have fitness effects (e.g. in pigeon guillemots [62], isopods [63], toads [60] and insect herbivores [68], see also [7]), thus the observed niche variation could result from the selective survival of those individuals that were able to best adapt their diet to the environment and intraspecific competition.
(c) . Niche divergence is tempered by the environment
Features of the physical and social environment define what food resources are available to individuals. We observed overall seasonal differences in the isotope ratios in the hair of voles, probably owing to the phenology of plants, animals and fungi altering the availability of specific dietary items over the summer. Energy-dense seeds are a preferred food [69] and seed abundance is lowest in the early summer, which might limit total energy availability and enforce diet shifting to alternative sources. For example, in German farmland, animals and green plants made up the majority of bank vole diet in early summer, whereas cereals, seeds and fruits were consumed in later summer [24]. Stomach content analyses suggest that animal matter consumption typically peaks in the summer months [25–28].
Individuals are thought to benefit from specializing to avoid competition when food is limited [1,64], especially in generalist species [70]. The early-season difference among the selection regimes could be explained by stronger competition leading to higher specialization in the absence of seeds, with the control and predatory voles preferring different alternative food items, the predatory lines foraging more e.g. insect larvae. In the late season, both C and P voles more likely fed on abundant seeds, eliminating this difference. Intraspecific competition for resources can lead to dietary niche expansion [13] or specialization [71], depending on the environmental conditions [2] and genetic variation of the population [37]. The specific outcome of the environment and intrinsic mechanisms of niche divergence can have significant effects on the stability of ecological networks [1,5]. In this study, high-density treatment did not seem to increase specialization (variances did not differ between density treatments), but high density was associated with a lower overall trophic niche, possibly implying higher competition for food items from a higher trophic level in both P and C lines.
5. Conclusion
Given the possible genetic basis and potential fitness benefits of dietary niche flexibility or specialization under resource competition [37,60], traits associated with diet choice may be important targets for selection. We demonstrated that artificial selection for a predatory behaviour shapes the diet of an omnivorous rodent in field conditions by increasing the predatory individuals' trophic level. The dietary niche of individuals measured in the long term via stable isotopes in hair indicated a small but consistent difference in dietary niche in interaction with the environment. Behavioural selection could, therefore, play a role in defining the trophic niche of individuals. Individual differences in diet choice and diet breadth can, in turn, have significant ecological consequences [1,5]. Our results point to the necessity of considering the significance of consistent behavioural variation in foraging when assessing the overall role of omnivores in the ecological community.
Acknowledgements
We thank Tanja Hirvonen, Tommi Vuori and Konnevesi Research Station staff for help with field and laboratory work.
Ethics
The research was conducted in accordance with the relevant laws and all procedures performed on the animals had an ethical committee approval (ESAVI/3981/2018).
Data accessibility
The data used in this paper are available from the Dryad Digital Repository: https://doi.org/10.5061/dryad.3tx95x6hq [72].
Authors' contributions
A.H.: conceptualization, data curation, formal analysis, funding acquisition, investigation, methodology, supervision, visualization, writing—original draft; M.K.: data curation, formal analysis, methodology, supervision, visualization, writing—review and editing; E.K.: conceptualization, data curation, investigation, supervision, writing—review and editing; P.K.: conceptualization, data curation, funding acquisition, resources, writing—review and editing; T.M.: conceptualization, data curation, funding acquisition, investigation, methodology, resources, supervision, writing—review and editing; M.R.: data curation, investigation, writing—review and editing; K.T.: data curation, investigation, writing—review and editing.
All authors gave final approval for publication and agreed to be held accountable for the work performed therein. The author order is alphabetical.
Competing interests
We declare we have no competing interests.
Funding
Funding was obtained from the Academy of Finland (projects 324605, 326533 to T.M.) and National Science Centre (NCN, Poland) (2018/29/B/NZ8/01924 to A.H.). The base colony of the voles (the selection experiment) was funded by NCN (2016/23/B/NZ8/00888 to P.K.) and Jagiellonian University (project DS/WBINOZ/INOS/757).
References
- 1.Bolnick DI, Svanbäck R, Fordyce JA, Yang LH, Davis JM, Hulsey CD, Forister ML. 2003. The ecology of individuals: incidence and implications of individual specialization. Am. Nat. 161, 1-28. ( 10.1086/343878) [DOI] [PubMed] [Google Scholar]
- 2.Araújo MS, Bolnick DI, Layman CA. 2011. The ecological causes of individual specialisation. Ecol. Lett. 14, 948-958. ( 10.1111/j.1461-0248.2011.01662.x) [DOI] [PubMed] [Google Scholar]
- 3.Hutchinson GE. 1957. Concluding remarks. Cold Spring Harb. Symp. Quant. Biol. 22, 415-427. [Google Scholar]
- 4.Matich P, Bizzarro JJ, Shipley ON. 2021. Are stable isotope ratios suitable for describing niche partitioning and individual specialization? Ecol. Appl. 31, 1-8. ( 10.1002/eap.2392) [DOI] [PubMed] [Google Scholar]
- 5.Toscano BJ, Gownaris NJ, Heerhartz SM, Monaco CJ. 2016. Personality, foraging behavior and specialization: integrating behavioral and food web ecology at the individual level. Oecologia 182, 55-69. ( 10.1007/s00442-016-3648-8) [DOI] [PubMed] [Google Scholar]
- 6.Sabelis MW, Lesna I. 2010. Does artificial selection for fixed prey preference affect learning in a predatory mite? Experiments to unravel mechanisms underlying polyphagy in Hypoaspis aculeifer. Acarologia 50, 257-268. ( 10.1051/acarologia/20101971) [DOI] [Google Scholar]
- 7.Moosmann M, Cuenca-Cambronero M, De Lisle S, Greenway R, Hudson CM, Lürig M, Matthews B. 2021. On the evolution of trophic position. Ecol. Lett. 24, 2549-2562. ( 10.1111/ele.13888) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Alcalay Y, Scharf I, Ovadia O. 2015. Foraging syndromes and trait variation in antlions along a climatic gradient. Oecologia 178, 1093-1103. ( 10.1007/s00442-015-3284-8) [DOI] [PubMed] [Google Scholar]
- 9.Woo KJ, Elliott KH, Davidson M, Gaston AJ, Davoren GK. 2008. Individual specialization in diet by a generalist marine predator reflects specialization in foraging behaviour. J. Anim. Ecol. 77, 1082-1091. ( 10.1111/j.1365-2656.2008.01429.x) [DOI] [PubMed] [Google Scholar]
- 10.Des Roches S, Post DM, Turley NE, Bailey JK, Hendry AP, Kinnison MT, Schweitzer JA, Palkovacs EP. 2018. The ecological importance of intraspecific variation. Nat. Ecol. Evol. 2, 57-64. ( 10.1038/s41559-017-0402-5) [DOI] [PubMed] [Google Scholar]
- 11.Barabás G, D'Andrea R. 2016. The effect of intraspecific variation and heritability on community pattern and robustness. Ecol. Lett. 19, 977-986. ( 10.1111/ele.12636) [DOI] [PubMed] [Google Scholar]
- 12.Coll M, Guershon M. 2002. Omnivory in terrestrial arthropods: mixing plant and prey diets. Annu. Rev. Entomol. 47, 267-297. ( 10.1146/annurev.ento.47.091201.145209) [DOI] [PubMed] [Google Scholar]
- 13.Svanbäck R, Bolnick DI. 2007. Intraspecific competition drives increased resource use diversity within a natural population. Proc. R. Soc. B 274, 839-844. ( 10.1098/rspb.2006.0198) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Milton K. 1999. A hypothesis to explain the role of meat-eating in human evolution. Evol. Anthropol. 8, 11-21. () [DOI] [Google Scholar]
- 15.Clauss M, Frey R, Kiefer B, Lechner-Doll M, Loehlein W, Polster C, Rössner GE, Streich WJ. 2003. The maximum attainable body size of herbivorous mammals: morphophysiological constraints on foregut, and adaptations of hindgut fermenters. Oecologia 136, 14-27. ( 10.1007/s00442-003-1254-z) [DOI] [PubMed] [Google Scholar]
- 16.Beasley DE, Koltz AM, Lambert JE, Fierer N, Dunn RR. 2015. The evolution of stomach acidity and its relevance to the human microbiome. PLoS ONE 10, e0134116. ( 10.1371/journal.pone.0134116) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Dumont F, Lucas E, Réale D. 2017. Coexistence of zoophytophagous and phytozoophagous strategies linked to genotypic diet specialization in plant bug. PLoS ONE 12, 1-13. ( 10.1371/journal.pone.0176369) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Sadowska ET, Baliga-Klimczyk K, Chrząścik KM, Koteja P. 2008. Laboratory model of adaptive radiation: a selection experiment in the bank vole. Physiol. Biochem. Zool. 81, 627-640. ( 10.1086/590164) [DOI] [PubMed] [Google Scholar]
- 19.Bearhop S, Adams CE, Waldron S, Fuller RA, Macleod H. 2004. Determining trophic niche width: a novel approach using stable isotope analysis. J. Anim. Ecol. 73, 1007-1012. ( 10.1111/j.0021-8790.2004.00861.x) [DOI] [Google Scholar]
- 20.Ben-David M, Flaherty EA. 2012. Stable isotopes in mammalian research: a beginner's guide. J. Mammal. 93, 312-328. ( 10.1644/11-MAMM-S-166.1) [DOI] [Google Scholar]
- 21.Butet A, Delettre YR. 2011. Diet differentiation between European arvicoline and murine rodents. Acta Theriol. (Warsz) 56, 297-304. ( 10.1007/s13364-011-0049-6) [DOI] [Google Scholar]
- 22.Hansson L. 1979. Condition and diet in relation to habitat in bank voles Clethrionomys glareolus: population or community approach? Oikos 33, 55-63. [Google Scholar]
- 23.Selva N, Hobson KA, Cortés-Avizanda A, Zalewski A, Donázar JA. 2012. Mast pulses shape trophic interactions between fluctuating rodent populations in a primeval forest. PLoS ONE 7, e51267. ( 10.1371/journal.pone.0051267) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Abt KF, Bock WF. 1998. Seasonal variations of diet composition in farmland field mice Apodemus spp. and bank voles Clethrionomys glareolus. Acta Theriol. (Warsz) 43, 379-389. ( 10.4098/AT.arch.98-49) [DOI] [Google Scholar]
- 25.Hansson L. 1985. The food of bank voles, wood mice and yellow-necked mice. Symp. Zool. Soc. Lond. 55, 141-168. [Google Scholar]
- 26.Canova L. 1993. Resource partitioning between the bank vole Clethrionomys glareolus and the wood mouse Apodemus sylvaticus in woodland habitats. Bolletino di Zool. 60, 193-198. ( 10.1080/11250009309355809) [DOI] [Google Scholar]
- 27.Viro P, Sulkava S. 1985. Food of the bank vole in northern Finnish spruce forests. Acta Theriol. (Warsz) 30, 259-266. ( 10.4098/at.arch.85-17) [DOI] [Google Scholar]
- 28.Gębczyńska Z. 1976. Food habits of the bank vole and phenological phases of plants in an oak hornbeam forest. Acta Theriol. (Warsz) 21, 223-236. ( 10.4098/at.arch.76-21) [DOI] [Google Scholar]
- 29.Holišová V. 1971. The food of Clethrionomys glareolus at different population densities. Acta Sc. Nat. Brno 5, 1-43. [Google Scholar]
- 30.Maiti U, Sadowska ET, ChrzĄścik KM, Koteja P. 2018. Experimental evolution of personality traits: open-field exploration in bank voles from a multidirectional selection experiment. Curr. Zool. 65, 375-384. ( 10.1093/cz/zoy068) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Lipowska MM, Sadowska ET, Bauchinger U, Goymann W, Bober-Sowa B, Koteja P. 2020. Does selection for behavioral and physiological performance traits alter glucocorticoid responsiveness in bank voles? J. Exp. Biol. 223, jeb219865. ( 10.1242/jeb.219865) [DOI] [PubMed] [Google Scholar]
- 32.Mappes T, Koskela E, Ylonen H. 1995. Reproductive costs and litter size in the bank vole. Proc. R. Soc. B 261, 19-24. ( 10.1098/rspb.1995.0111) [DOI] [PubMed] [Google Scholar]
- 33.Koskela E, Mappes T, Ylönen H. 1997. Territorial behaviour and reproductive success of bank vole Clethrionomys glareolus females. J. Anim. Ecol. 66, 341-349. [Google Scholar]
- 34.Ylönen H, Horne TJ, Luukkonen M. 2004. Effect of birth and weaning mass on growth, survival and reproduction in the bank vole. Evol. Ecol. Res. 6, 433-442. [Google Scholar]
- 35.Arostegui MC, Schindler DE, Holtgrieve GW. 2019. Does lipid-correction introduce biases into isotopic mixing models? Implications for diet reconstruction studies. Oecologia 191, 745-755. ( 10.1007/s00442-019-04525-7) [DOI] [PubMed] [Google Scholar]
- 36.Fox J, Weisberg S. 2019. An R companion to applied regression, 3rd edn. Thousand Oaks, CA: Sage. See https://socialsciences.mcmaster.ca/jfox/Books/Companion/. [Google Scholar]
- 37.Agashe D, Bolnick DI. 2010. Intraspecific genetic variation and competition interact to influence niche expansion. Proc. R. Soc. B 277, 2915-2924. ( 10.1098/rspb.2010.0232) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38.Costa-Pereira R, Araújo MS, Souza FL, Ingram T. 2019. Competition and resource breadth shape niche variation and overlap in multiple trophic dimensions. Proc. R. Soc. B 286, 20190369. ( 10.1098/rspb.2019.0369) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Tinker MT, Bentall G, Estes JA. 2008. Food limitation leads to behavioral diversification and dietary specialization in sea otters. Proc. Natl Acad. Sci. USA 105, 560-565. ( 10.1073/pnas.0709263105) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.R Core Team. 2020. R: a language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing. See https://www.R-project.org/.
- 41.Bates D, Maechler M, Bolker B, Walker S. 2015. Fitting linear mixed-effects models using lme4. J. Stat. Softw. 67, 1-48. ( 10.18637/jss.v067.i01) [DOI] [Google Scholar]
- 42.Kuznetsova A, Brockhoff PB, Bojesen Christensen RH. 2017. lmerTest package: tests in linear mixed effects models. J. Stat. Soft. 82, 1-26. ( 10.18637/jss.v082.i13) [DOI] [Google Scholar]
- 43.Barton K. 2015. MuMIn: Multi-Model Inference. R package version 1.15.1. See https://CRAN.Rproject.org/package=MuMln.
- 44.Wickham H. 2016. Ggplot2: elegant graphics for data analysis. New York, NY: Springer. [Google Scholar]
- 45.Ahlmann-Eltze C, Patil I. 2021. ggsignif: R Package for displaying significance brackets for ‘ggplot2’. PsyArXiv ( 10.31234/osf.io/7awm6) [DOI]
- 46.Lüdecke D. 2021. sjPlot: data visualization for statistics in social science. R package version 2.8.9. See https://CRAN.Rproject.org/package=sjPlot.
- 47.Lee Y II, Lim HS, Yoon H II. 2009. Carbon and nitrogen isotope composition of vegetation on King George Island, maritime Antarctic. Polar Biol. 32, 1607-1615. ( 10.1007/s00300-009-0659-5) [DOI] [Google Scholar]
- 48.Gibbons ME, Ferguson AM, Lee DR. 2005. Both learning and heritability affect foraging behaviour of red-backed salamanders, Plethodon cinereus. Anim. Behav. 69, 721-732. ( 10.1016/j.anbehav.2004.06.021) [DOI] [Google Scholar]
- 49.Latshaw JS, Smith BH. 2005. Heritable variation in learning performance affects foraging preferences in the honey bee (Apis mellifera). Behav. Ecol. Sociobiol. 58, 200-207. ( 10.1007/s00265-004-0904-4) [DOI] [Google Scholar]
- 50.Grant PR, Price TD. 1981. Population variation in continuously varying traits as an ecological genetics problem. Integr. Comp. Biol. 21, 795-811. ( 10.1093/icb/21.4.795) [DOI] [Google Scholar]
- 51.Richards EJ, McGirr JA, Wang JR, St. John ME, Poelstra JW, Solano MJ, O'Connell DC, Turner BJ, Martin CH. 2021. A vertebrate adaptive radiation is assembled from an ancient and disjunct spatiotemporal landscape. Proc. Natl Acad. Sci. USA 118, e2011811118 ( 10.1073/pnas.2011811118) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 52.Sih A, Bell A, Johnson JC. 2004. Behavioral syndromes: an ecological and evolutionary overview. Trends Ecol. Evol. 19, 372-378. ( 10.1016/j.tree.2004.04.009) [DOI] [PubMed] [Google Scholar]
- 53.Réale D, Garant D, Humphries MM, Bergeron P, Careau V, Montiglio PO. 2010. Personality and the emergence of the pace-of-life syndrome concept at the population level. Phil. Trans. R. Soc. B 365, 4051-4063. ( 10.1098/rstb.2010.0208) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54.Royauté R, Berdal MA, Garrison CR, Dochtermann NA. 2018. Paceless life? A meta-analysis of the pace-of-life syndrome hypothesis. Behav. Ecol. Sociobiol. 72, 64. ( 10.1007/s00265-018-2472-z) [DOI] [Google Scholar]
- 55.Hämäläinen AM, Guenther A, Patrick SC, Schuett W. 2021. Environmental effects on the covariation among pace-of-life traits. Ethology 127, 32-44. ( 10.1111/eth.13098) [DOI] [Google Scholar]
- 56.Britt EJ, Hicks JW, Bennett AF. 2006. The energetic consequences of dietary specialization in populations of the garter snake, Thamnophis elegans. J. Exp. Biol. 209, 3164-3169. ( 10.1242/jeb.02366) [DOI] [PubMed] [Google Scholar]
- 57.Careau V, Thomas D, Humphries MM, Réale D. 2008. Energy metabolism and animal personality. Oikos 117, 641-653. ( 10.1111/j.2008.0030-1299.16513.x) [DOI] [Google Scholar]
- 58.McGhee KE, Pintor LM, Bell AM. 2013. Reciprocal behavioral plasticity and behavioral types during predator-prey interactions. Am. Nat. 182, 704-717. ( 10.1086/673526) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 59.Konczal M, Koteja P, Orlowska-Feuer P, Radwan J, Sadowska ET, Babik W. 2016. Genomic response to selection for predatory behavior in a mammalian model of adaptive radiation. Mol. Biol. Evol. 33, 2429-2440. ( 10.1093/molbev/msw121) [DOI] [PubMed] [Google Scholar]
- 60.Costa-Pereira R, Toscano B, Souza FL, Ingram T, Araújo MS. 2019. Individual niche trajectories drive fitness variation. Funct. Ecol. 33, 1734-1745. ( 10.1111/1365-2435.13389) [DOI] [Google Scholar]
- 61.Snell-Rood EC, Ehlman SM. 2021. Ecology and evolution of plasticity. In Phenotypic plasticity & evolution (eds Goldstein I, Ehrenreich IM), pp. 139-160. Boca Raton, FL: CRC Press. [Google Scholar]
- 62.Golet GH, Kuletz KJ, Roby DD, Irons DB. 2000. Adult prey choice affects chick growth and reproductive success in pigeon guillemots. Auk 117, 82-91. ( 10.1642/0004-8038(2000)117[0082:APCACG]2.0.CO;2) [DOI] [Google Scholar]
- 63.Basset A, Rossi L. 1987. Relationships between trophic niche breadth and reproductive capabilities in a population of Proasellus coxalis Dollfus (Crustacea: Isopoda). Funct. Ecol. 1, 13. ( 10.2307/2389352) [DOI] [Google Scholar]
- 64.Roughgarden J. 1974. Evolution of niche width. Am. Nat. 108, 142-143. ( 10.1086/282892) [DOI] [Google Scholar]
- 65.Paull JS, Martin RA, Pfennig DW. 2012. Increased competition as a cost of specialization during the evolution of resource polymorphism. Biol. J. Linn. Soc. 107, 845-853. ( 10.1111/j.1095-8312.2012.01982.x) [DOI] [Google Scholar]
- 66.Henry LM, Roitberg BD, Gillespie DR. 2008. Host-range evolution in Aphidius parasitoids fidelity, virulence and fitness trade-offs on an ancestral host. Evolution 62, 689-699. [DOI] [PubMed] [Google Scholar]
- 67.Estes JA, Riedman ML, Staedler MM, Tinker MT, Lyon BE. 2003. Individual variation in prey selection by sea otters: patterns, causes and implications. J. Anim. Ecol. 72, 144-155. ( 10.1046/j.1365-2656.2003.00690.x) [DOI] [Google Scholar]
- 68.Mody K, Unsicker SB, Linsenmair KE. 2007. Fitness related diet-mixing by intraspecific host-plant-switching of specialist insect herbivores. Ecology 88, 1012-1020. ( 10.1890/06-1338) [DOI] [PubMed] [Google Scholar]
- 69.Hansson L. 1971. Small rodent food, feeding and population dynamics: a comparison between granivorous and herbivorous species in Scandinavia. Oikos 22, 183-198. [Google Scholar]
- 70.Robinson ML, Strauss SY. 2020. Generalists are more specialized in low-resource habitats, increasing stability of ecological network structure. Proc. Natl Acad. Sci. USA 117, 2043-2048. ( 10.1073/pnas.1820143117) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 71.Gerardo Herrera ML, Korine C, Fleming TH, Arad Z. 2008. Dietary implications of intrapopulation variation in nitrogen isotope composition of an old world fruit bat. J. Mammal. 89, 1184-1190. ( 10.1644/07-MAMM-A-263.1) [DOI] [Google Scholar]
- 72.Hämäläinen A, Kiljunen M, Koskela E, Koteja P, Mappes T, Rajala M, Tiainen K. 2022. Data from: Artificial selection for predatory behaviour results in dietary niche differentiation in an omnivorous mammal. Dryad Digital Repository. ( 10.5161/dryad.3tx95x6hq) [DOI] [PMC free article] [PubMed]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
The data used in this paper are available from the Dryad Digital Repository: https://doi.org/10.5061/dryad.3tx95x6hq [72].


