Introduction
Squid play an important role in marine ecosystems, with total standing biomass in the world ocean estimated to attain 375 million tonnes (Boyle & Rodhouse, Reference Boyle and Rodhouse2005). Squid occupy intermediate levels in the marine trophic pyramid, being an abundant food resource for top predators such as large predatory fish, seabirds, seals and whales (Clarke, Reference Clarke1996; Smale, Reference Smale1996). They are voracious predators themselves, with feeding rates between 1–12% body mass per day (Wells & Clarke, Reference Wells and Clarke1996; Boyle & Rodhouse, Reference Boyle and Rodhouse2005). They are characterized by a high metabolic turnover (Wells & Clarke, Reference Wells and Clarke1996; Yatsu et al., Reference Yatsu, Midorikawa, Shimada and Uozumi1997), with ingested prey biomass rapidly converted into body growth (Collins & Pierce, Reference Collins and Pierce1996). High consumption rates can have an important influence on prey species. For example, the winter-spawning cohort of Illex argentinus can consume up to 8.5 million tonnes of their mainly crustacean prey during the feeding period of their annual life cycle on the Patagonian Shelf (Arkhipkin, Reference Arkhipkin2013).
The size of squid prey increases throughout ontogeny, resulting in a diet consisting of a variety of prey species at different trophic levels (Witek & Krajewska-Soltys, Reference Witek and Krajewska-Soltys1989). Such ontogenetic diet changes have previously been described in various squid species, such as I. argentinus (Rosas-Luis et al., Reference Rosas-Luis, Navarro, Martínez-Baena and Sánchez2017) and Loligo forbesii (Collins & Pierce, Reference Collins and Pierce1996; Pierce & Santos, Reference Pierce, Santos, Greenstreet and Tasker1996). The diet of juveniles usually consists of zooplankton, subsequently changing in adults to fish and Cephalopoda (e.g. at 18–23 cm dorsal mantle length in I. argentinus; Ivanovic & Brunetti, Reference Ivanovic and Brunetti1994), with cannibalism also being widespread (Ibáñez & Keyl, Reference Ibáñez and Keyl2010).
Squid of the family Loliginidae are common inhabitants of the coastal and shelf regions of the world oceans. Loliginid squid feed on the outer shelf and transport nutrients to their shallow spawning grounds (Boyle & Rodhouse, Reference Boyle and Rodhouse2005; Arkhipkin, Reference Arkhipkin2013). The Patagonian longfin squid Doryteuthis gahi (d'Orbigny, 1835), is the most southern loliginid, inhabiting shelves of the South-west Atlantic and South-east Pacific. This medium-sized squid typically attains a dorsal mantle length (DML) of 13–17 cm, with a maximum of 44 cm DML (Jereb & Roper, Reference Jereb and Roper2010). It is most abundant in the south-eastern part of the Patagonian Shelf, aggregating in the vicinity of oceanic fronts located around the Falkland Islands and characterized by high productivity (Arkhipkin et al., Reference Arkhipkin, Hatfield, Rodhouse, Rosa, O'Dor and Pierce2013). The population structure of D. gahi consists of two main annual cohorts characterized by different seasons of spawning – the autumn-spawning cohort (ASC) and the spring-spawning cohort (SSC). Hence, the same ontogenetic phases of squid from each cohort live in different seasons and sometimes even in different habitats, experiencing different environmental conditions (Arkhipkin et al., Reference Arkhipkin, Campana, FitzGerald and Thorrold2004a, Reference Arkhipkin, Grzebielec, Sirota, Remeslo, Polishchuk and Middleton2004b; Jones et al., Reference Jones, Arkhipkin, Marriott and Pierce2018).
Stomach content analysis is one of the main tools used to study the diet of a species and its position in the marine food web (Hyslop, Reference Hyslop1980; Buckland et al., Reference Buckland, Baker, Loneragan and Sheaves2017). Additionally, analysis of time series of stomach samples from key species such as predatory fish or squid can enable us to detect temporal shifts in their diet and reveal possible ecosystem changes (Belleggia et al., Reference Belleggia, Giberto and Bremec2017).
Previous studies of D. gahi diet on the Patagonian shelf revealed a predominance of Euphausiacea, pelagic amphipods (mainly Themisto gaudichaudii) and Chaetognatha (Guerra et al., Reference Guerra, Castro and Nixon1991; Brickle et al., Reference Brickle, Olson, Littlewood, Bishop and Arkhipkin2002). A comparative analysis of stomach contents of three squid, D. gahi, I. argentinus and Onykia ingens, found similar prey items, suggesting overlap in the feeding spectra of these species on the Patagonian Shelf. Additionally, stable isotope analysis revealed pelagic neritic feeding habits in D. gahi (Rosas-Luis et al., Reference Rosas-Luis, Sánchez, Portela and Del Rio2014). The diet of D. gahi changes during ontogeny, with maturing individuals feeding primarily on small pelagic crustaceans (such as T. gaudichaudii and Euphausia sp.), and mature individuals feeding on larger crustaceans (Munida gregaria), fish and squid (Rosas-Luis et al., Reference Rosas-Luis, Navarro, Sánchez and Del Río2016, Reference Rosas-Luis, Navarro, Martínez-Baena and Sánchez2017). However, the relatively small sample size in these studies prevented analysis of seasonal and inter-cohort variability in the diet of this squid.
The present study aims to expand our knowledge on the diet of D. gahi on the Patagonian Shelf by revealing possible differences in feeding spectra of the two main cohorts throughout their ontogenies. Additionally, interannual differences in diet have been analysed to identify the impact of environmental and ecosystem shifts on the Patagonian Shelf on the D. gahi diet.
Materials and methods
Data collection
Two sets of samples were examined to compare differences in the diet of D. gahi on the Patagonian shelf. Samples of the first set (2001) were collected from August 2000 to June 2001 within the designated fishing area, the ‘Loligo Box’ (~50–53°S 56–60°W), within the Falkland Island Conservation Zone (FICZ) (Figure 1). A total of 4043 Doryteuthis gahi was collected as random samples from 35 different trawls, frozen and brought to the Fisheries Department (FIFD) laboratory for analysis.
Fig. 1. Sampling sites (triangles) of D. gahi from 2001 (left) and from 2020 (right); FICZ & FOCZ = Falkland Inner & Outer Conservation Zone. The designated fishing area, the ‘Loligo Box’ is represented by the cross-hatched area.
Samples of the second set (2020) were collected between October 2019 and November 2020 within the FICZ and also in international waters to the north of the zone (Figure 1). A total of 4023 specimens was collected as random samples from 50 different trawls, frozen and brought to the FIFD laboratory for further analysis.
For both sets of samples, squid were caught by commercial trawlers deploying bottom trawling gear, ~90% of which were conducted during daylight hours with trawling times ranging from 1.5 to ~9 h. In addition, in 2020 squid were also collected from four research cruises carried out within Falkland Islands waters. The complete datasets from both periods were used for analysis. However, due to some differences in the geographic distribution of sampling in 2020 compared with 2001, which could result in temporal changes and geographic differences in diet being confounded, most analyses were then repeated using only data from the part of the sampling area that was sampled during both periods.
Squid sampled in 2001 and 2020 were analysed in the laboratory in a similar way, with dorsal mantle length (DML ± 0.5 cm) and total weight (TW ± 0.1 g) measured. A qualitative visual stomach fullness index (SFI; Breiby & Jobling, Reference Breiby and Jobling1985) was assigned: 1 = empty; 2 = ¼ filled; 3 = ½ filled; 4 = ¾ filled; 5 = completely full. Non-empty stomachs were retained and stored frozen. In 2001 a subsample of 1495 stomachs containing food was collected; in 2020 a subsample of 570 stomachs containing food was collected.
Data on sample numbers (separately by sex) and squid sizes are presented in Table 1. Similar numbers of males and females were collected, and the former were on average larger.
Table 1. Total number (N), range, median and mean with standard deviation (±) of total weight (TW), dorsal mantle length (DML) of D. gahi individuals sampled in 2001 and 2020, respectively
To make inter-annual and inter-seasonal comparisons, data were split into individuals belonging to the ASC and SSC and into three size-classes: small (<13 cm DML), medium (13–19 cm DML) and large (>19 cm DML). Individuals were assigned to each spawning cohort using their DML, maturity, month of collection and depth in which they were caught, based on findings by Arkhipkin et al. (Reference Arkhipkin, Campana, FitzGerald and Thorrold2004a, Reference Arkhipkin, Hatfield, Rodhouse, Rosa, O'Dor and Pierce2013). Especially in May–July mixing of cohorts occurs, as adult squid from the ASC were still alive and present in the fishing areas, whereas juvenile squid from the SSC had already hatched (see Figure S1 in supplementary material).
Stomach content analysis
Stomach content examination
Stomach content of each individual squid was transferred into a Petri dish and examined under a dissecting microscope. The stomach weight (SW ± 0.01 g) and the content weight (CW ± 0.01 g) were recorded. An overall digestion state was assigned to each stomach (1 = fresh, 2 = start of digestion, 3 = mostly digested). Food items were identified using a reference collection from the Falkland Islands Fisheries Department (FIFD) and identification keys (Boltovskoy, Reference Boltovskoy1999a, Reference Boltovskoy1999b). All prey categories were noted as present or absent (PA) and, for each category present, the percentage share of the total stomach contents was determined employing a grid made from graph paper and using a binocular microscope resulting in scores (P) from 1–100 after the Point Method (Wear & Haddon, Reference Wear and Haddon1987). This was done because masticated food debris did not allow the use of classical gravimetric or volumetric approaches to obtain the weight and volume of single prey items (Breiby & Jobling, Reference Breiby and Jobling1985).
The number of otoliths, statoliths, eye lenses (both fish and crustacean) and Euphausiacea mandibles were counted per stomach from samples collected in 2020. Total Euphausiacea mandible length (TML ± 0.05 mm) was measured randomly for up to 12 mandibles in each stomach.
Comparability of datasets
In 2001, several prey items were identified to species level, whereas in 2020 prey items were mostly identified to genus or group level. In order to obtain comparable prey categories for the two datasets, for the various analyses and methods, the prey groups for both datasets were pooled in two different ways. To perform Generalized Additive Models (GAMs), prey groups were pooled into class level or comparable (e.g. unidentified fish). For the standardized niche analysis, they were pooled into genus/family level or comparable (e.g. unidentified Myctophidae). Statistics analysing trends regarding different years were repeated with a subsample of the 2020 dataset including only datapoints with a similar geographic distribution as in 2001.
Calculation of frequency of occurrence and per cent by weight
The scores (Pi) of each prey category i were divided by the sum of scores to calculate a percentage of prey category i after Wear & Haddon (Reference Wear and Haddon1987).
Percentage of prey category i was then multiplied by the stomach content weight to obtain the item weight IW.
Frequency of occurrence (FO%) was calculated (the percentage of D. gahi that fed on a certain prey) as
where ni is the occurrence of a specific prey in stomachs and n is total number of stomachs.
Mandible measurements
Nickels et al. (Reference Nickels, Sala and Ohman2018) found a correlation between the length of a Euphausiacea mandible and the size of the Euphausiacea. To reconstruct the individual total length (TL) of Euphausiacea ingested by D. gahi, 16 Thysanoessa macrura and 40 Euphausia lucens were caught with a Bongo net (350 μm) in January and February 2020 in Falkland Islands waters. Individuals were preserved in ethanol (95%), TL (± 0.01 mm) and TML (± 0.005 mm) of the left and right mandibles were measured and averaged. The relationship between TL and TML was best described by the linear function:
(R 2 = 0.7273).
Trophic niche
To compare sampling periods, size classes and cohorts, niche width was used to quantify the degree of foraging specialization (Krebs, Reference Krebs1999). In this study, ‘resource states’ were based on prey taxa found in the stomachs. To measure uniformity in the utilization of prey items among all prey categories, Levins' Measure of Niche Width and the Shannon Index of Evenness were calculated (Krebs, Reference Krebs1999). Both measures were standardized to a scale from 0 (minimum niche width) to 1 (maximum niche width) according to Krebs (Reference Krebs1999).
For Levins' niche width:
where B is niche width and pj is the fraction of items in the diet that are of food category j .
To standardize B:
where n is the number of prey items found in the stomachs of the investigated species or group.
The Shannon Equitability Index (EH) was calculated from the Shannon Diversity Index (H), thus:
Both Levins' standardized B and Shannons' EH give an index ranging between 0 and 1, where 1 means dietary generalization or even utilization of resource states and 0 means dietary specialization.
Statistical analysis
All statistical analyses were conducted using R v.4.0.3 (R Core Team, 2020), considering a significance level of P < 0.05. All statistical tests were performed on both datasets, except the tests on Euphausiacea size, which could only be done using mandible lengths measured in 2020.
Influential species were detected with a similarity percentages breakdown (SIMPER) procedure (Clarke, Reference Clarke1993). FO% values for each month of the year were investigated and to detect trends a 2nd degree polynomial locally weighted scatter-plot smoother (LOESS) with a span of 0.75 was used.
Generalized Additive Models (GAMs) were used in this study as these generalizations of linear models permit the inclusion of non-linear relationships (Hastie & Tibshirani, Reference Hastie and Tibshirani1986). Following the approach advocated by some ecologists (e.g. Whittingham et al., Reference Whittingham, Stephens, Bradbury and Freckleton2006; Mundry & Nunn, Reference Mundry and Nunn2009) and which is also usual in social sciences, we chose to avoid a stepwise model selection process, preferring to fit full models and determine the significance of each term. However, in GAM, an interaction between a continuous explanatory variable (the effect of which is fitted as a smoother) and a categorical explanatory variable, is represented as multiple smoothers (one per unique value of the categorical variable). As such, the significance of the interaction term is determined by comparing goodness of fit of models with and without the interaction (effectively a stepwise model selection process).
GAMs (with a Gaussian distribution of log transformed IW values) were performed on influential prey groups (groups identified with SIMPER) to investigate the relationship of IW with month (continuous variable), squid size class (3 level factor) and their interaction (equation (9)). Cyclic cubic splines, penalized cubic regression splines whose ends meet up, were fitted to month to avoid discontinuity between December and January. Knots to separate each predictor and specify the dimension of the basis function were used to represent the smoothing term. Number of knots (k) in the smoothers was set to 4. Two models were compared based on their Akaike Information Criterion (AIC) to determine a possible effect of a month~size interaction.
As Euphausiacea mandible lengths were measured, a Gaussian GAM was performed to model the influence of size and seasonality on the size of Euphausiacea eaten by the squid for the sampling period 2019–2020 (equation (10)). The DML was log-transformed to reduce the influence of high values. The AIC values of models with interaction (equation (10A)) and without the interaction (equation (10B)) of size-class with month were compared. Number of k was set to 4.
To test for inter-annual and inter-seasonal differences between size-classes, a Permutational Multivariate Analysis of Variance Using Distance Matrices (ADONIS) was performed. ‘Bray–Curtis Dissimilarity Distances’ and 10,000 permutations on all size-classes of D. gahi, based on item weights IW were used. Influential species were detected with a SIMPER procedure.
GAMs were performed on those influential prey groups to model the influence, on the relative abundance of prey, of DML (continuous variable), sampling period (2 level factor) and spawning cohort (2 level factor). In order to test the three-way interaction, we defined a combined categorical variable cohort.year (with 4 levels: ASC-2001, SSC-2001, ASC-2020 and SSC-2020) (equation (11)). Since there are multiple interactions in this model, some between continuous and categorical variables, fitted as multiple smoothers using s(X1, by as.factor (X2)), in order to determine the significance of some terms it was necessary to compare (based on AIC) different models as follows:
A Gaussian distribution was assumed and IW values were log transformed. The DML was also log transformed to reduce the influence of a small number of high values. Residuals were checked for normality.
All GAMs were performed with the R package ‘mgcv’ (Wood, Reference Wood2017). The statistical tests SIMPER and ADONIS were performed with the R package ‘vegan’ (Oksanen et al., Reference Oksanen, Blanchet, Friendly, Kindt, Legendre, Mcglinn, Minchin, O'Hara, Simpson, Solymos, Stevens, Szoecs and Wagner2020).
Results
Feeding spectrum
In 2001, 62% of all sampled stomachs contained food. The mean content weight (CW) was 0.6 g (1.26% of TW) and the median CW was 0.3 g (0.8% of TW), although the distribution of CW was heavily skewed towards higher values. The maximum CW was 32.5 g, measured from a large male individual of 28 cm DML (14.4% of TW). From all the stomachs collected in 2001, a total of 20 prey categories were found (Table 2). In 2020, 63% of all sampled stomachs contained food. Mean CW (0.61 g, 1.28% of TW) and median CW (0.38 g, 0.95% of TW) of 2020 were comparable with 2001. Maximum CW in 2020 was 6.6 g (7.45% of TW). In 2020, a total of 16 prey categories were identified.
Table 2. Frequency of Occurrence (FO%) of prey items within stomachs of D. gahi during 2001 and 2020; summarized separately for the ASC (autumn-spawning cohort) and SSC (spring-spawning cohort)
The main items within the stomachs were Euphausiacea, Chaetognatha, Amphipoda and squid, identified as D. gahi (considered as cannibalism). Crustacean parts were frequently found within the stomachs but were highly macerated. Unidentifiable parts of Crustacea were pooled and assigned to the prey group Crustacea. Of the 24 prey categories, 10 were found in less than 1% of the stomachs.
The amphipods Themisto gaudichaudii, Primno sp. and Phronima sp. were identified. Euphausiacea found in the stomachs were often highly masticated. Intact parts or whole individuals were identified as the species Euphasia lucens or Thysanoessa macrura. Chaetognatha were identified by the size and shape of hooks found in the stomachs, indicating the presence of species of the genus Sagitta. Gastropoda were identified as Limacina helicana antarctica, L. retroversa and L. spp. Fish species identified from otoliths included Patagonotothen ramsayi, other species from the genus Patagonotothen, Eleginops maclovinus and Sprattus fuegensis and the myctophid Gymnoscopelus spp. The only ctenophore was found in 2001, which was Mnemiopsis leidyi.
FO% of all dietary items were calculated for each year, cohort and size class (Table 2). To account for any effects of regionality, FO% were also calculated using data from only the Loligo Box (see Table S1 in supplementary material). Comparing FO% between all areas and only from the Loligo Box, FO% of D. gahi and Chaetognatha are higher, FO% of Euphausiacea and M. gregaria are lower with fish completely absent looking at data only from the Loligo Box compared with all areas.
Gender-specific differences in the food spectrum were investigated primarily on a graphical basis and did not reveal any differences. The inclusion of ‘sex’ as a categorical variable to the models did not significantly improve the AIC. For those reasons, an analysis on gender-specific diet variation was not included in this study.
Size-related variation in squid diet
Trends were observed for the diet of D. gahi in relation to body size. The most abundant prey group Euphausiacea was consumed by small D. gahi (75 FO%), but frequency decreased with increasing DML (Figure 2). Based on FO%, cannibalism and consumption of Cephalopoda and fish increased with increasing DML. Chaetognatha were mainly consumed by squid between 8–15 cm DML and were more frequently consumed than Amphipoda. An increasing trend with DML was observed for the lobster krill M. gregaria, remains of which were found in 38 stomachs of squid between 7–18 cm DML.
Fig. 2. FO (%) vs DML (cm) of D. gahi for each prey category. In the background: Histogram of the percentage of total stomachs investigated per 3 cm size range. Unident. = Unidentified.
Table 3 shows the percentage (dietary) similarity values for the different size classes of squid, calculated separately for each of the main prey types. Dietary differences were based on the lowest cumulative sum (cumsum, summed proportions that each prey type contributes to the similarities between different size groups). Differences between large and medium sized squid and between large and small squid were based on differences in IW of cannibalism, followed by Euphausiacea and fish. Differences between medium sized squid and small squid were mainly based differences in IW of Euphausiacea, followed by cannibalism and Chaetognatha (SIMPER, Table 3).
Table 3. Similarity percentages (CUMSUM) from SIMPER analysis of prey-type IW in stomachs of D. gahi for comparisons between size classes
Results from GAM models 11, 12, 13 and 14 indicated that model 11 (which includes the three-way interactions between the effects of DML, year and cohort) was the best model (lowest AIC for all five main prey categories; Table 4).
The GAM (equation (11)) results revealed a significant effect of DML on the importance of prey categories (expressed as IW) in different years and cohorts (Table 5A). Euphausiacea IW peaked in squid between 10–15 cm DML in the SSC 2001 and the ASC 2020 at ~0.5 g (Figure 3). In the SSC 2020, IW of Euphausiacea increased with DML, up to 2 g in squid of ~30 cm DML. The importance of cannibalism increased significantly with DML in all years and cohorts, with highest values (~10 g) for the SSC in 2001. The importance of fish increased with DML in all years and cohorts. The consumption weights of Chaetognatha in the stomachs of D. gahi increased significantly with increasing size in ASC 2001.
Fig. 3. GAM smoother DML ~ IW for (A) Amphipoda; (B) Chaetognatha; (C) D. gahi; (D) Euphausiacea and (E) Fish. Model for both cohorts ASC and SSC and years 2001 and 2020 with 95% confidence intervals (grey shaded area).
Table 5. Summary of GAM results for models of item weights (IW) of the main prey categories vs explanatory variables DML, year, cohort and the interactions between them. The three-way interactions are captured by combining year and cohort into a new categorical variable with four possible values and fitting the smoother for DML separately for each value of the variable. (A) Details of smoothers describing the effect of DML for each value of the combined year-cohort variable: expected degrees of freedom (edf) and P-values (significance indicated by *); (B) Effects of categorical explanatory variables: Parameter estimate and P-value (significance indicated by *). For the variable Year, the coefficients given are for year 2020 (vs 2001 as the baseline); thus a positive value indicated greater consumption in 2020. For the variable Cohort, the coefficients given are for the SSC (vs ASC as the base); thus a positive value indicates high consumption by the SSC
Using only data from the Loligo Box, most trends remained the same (Table S2A in supplementary material), although uncertainty increased (represented by grey shaded areas as confidence intervals, Figure S2 in supplementary material). IW of Euphausiacea in the SSC 2020 peaked at ~15 cm DML instead of increasing steadily.
Seasonal diet variation
Mean FO% were plotted for each month and trends in FO% were investigated using LOESS smoothers (Figure 4). The average FO% of Chaetognatha increased during winter (except July) and decreased during summer for D. gahi individuals smaller than 13 cm DML. LOESS showed for the FO% of cannibalism an increasing trend in winter months for all size classes. For the FO% of Euphausiacea a decreasing trend in winter months was detected for the size class 13–19 cm. Euphausiacea trends for <13 cm and >19 cm were not distinct.
Fig. 4. Mean FO% per month plotted as bars for each size class of squid (<13 cm, 13–19 cm and >19 cm) for Chaetognatha, D. gahi (cannibalism) and Euphausiacea. Black line = ‘loess’ smoother with span = 1.
To investigate the seasonality in diet, whilst accounting for ontogenetic change, GAMs were performed on the item weight (IW) values for each prey group with the model formula (equation (9A)), which includes the effects of size, month, and their interaction. To test whether this interaction was important, AIC values were compared between equations (9A) and (9B) (Table 6). The model with equation (9A) showed lower AIC values and was therefore chosen.
Table 6. AIC for the models equations (9A) and (9B) applied for each of the major prey groups with k = 4
The item weights of Euphausiacea had a significant negative trend towards the austral winter months for small squid (Table 7, Figure 5). Amphipoda item weights were higher during winter in squid between 13–19 cm. Chaetognatha IW were significantly higher in summer months for squid larger than 19 cm, even though trends for smaller squid seem to be the contrary (Table 8). Cannibalism was more prevalent during the austral winter months in small and medium sized individuals. Small and medium sized squid consumed more fish during winter months. Trends were not significant for Amphipoda in small and large squid, nor for Euphausiacea in medium sized squid or for fish in large sized squid.
Fig. 5. GAM smoothing curves: Seasonal variation and 95% confidence interval (grey shaded area) in the abundance of (A) Amphipoda, (B) Chaetognatha, (C) D. gahi, (D) Euphausiacea and (E) Fish in the stomachs of D. gahi over the months.
Table 7. GAM results (equation (9A)): Intercept and size classes of each prey category found in the stomachs of D. gahi (estimate, standard error, t-value and P-value)
Significant results indicated by *.
Table 8. Model output for the smoother of month by size class. All factors of size class with 2 reference degrees of freedom
Mandible measurements
Euphausiid mandibles found in the stomachs of D. gahi sampled in 2020 ranged from 0.5–2.25 mm.
Using the relationship between TL and TML to recalculate the size of Euphausiacea, it was estimated that Euphausiacea that were preyed upon by D. gahi ranged from 10–30 mm TL. Therefore, the predator–prey ratio ranged from 0.28–3.2% (TML/DML). AIC of the model with the interaction equation (10A) was significantly lower (−395 compared with 11) and was therefore chosen to investigate the influence of seasonality with an interaction of DML for samples collected in 2020.
The resulting 3-dimensional gam smoother showed that TML changed significantly in different seasons (P < 0.01, R 2 = 0.529), with smaller mandibles found in the austral winter months (April–October) and larger mandibles found in the austral summer months (November–March, Figure 6). The interaction of month and DML was significant (edf = 14.14, P < 0.01) and showed especially in December, that larger Euphausiacea mandibles were found in smaller squid. A 2-dimensional excerpt from this 3-dimensional model for the mean squid length of 11 cm can be found in the supplementary material (Figure S3).
Fig. 6. Three-dimensional GAM: Euphausiacea TML vs month × log(DML) (solid surface) and 95% confidence interval (semi-translucent surface). Month and DML on x- and y-axes, TML on z-axis.
Inter-annual and -cohort diet variation
The ADONIS revealed significant differences in IW between the two sampling periods, the two spawning cohorts and the three size-classes (Table 9). Although the differences were significant, the R2 values were small, as the ‘noise’ of the model with many single stomach records was high. ADONIS model based on data only from the Loligo Box can be found in the supplementary material (Table S3).
Table 9. Results of the ADONIS (Permutational Multivariate Analysis of Variance Using Distance Matrices); Df (Degrees of freedom) based on the IW (item weights) of D. gahi prey items for different years, cohorts and size-classes
Sum Of Sqs (Sum of Squares), R 2, F statistic and P-value of the F-statistic.
The SIMPER analysis revealed differences in prey group IW between years and cohorts. Inter-annual differences in the ASC were mainly based on D. gahi and secondly on Euphausiacea (Table 10), inter-annual differences in the SSC were also based on those two prey groups but in reversed order of importance. Similarly, inter-seasonal differences in 2001 were mainly due to Euphausiacea followed by D. gahi. In contrast to 2001, differences between cohorts in 2020 were mainly caused by D. gahi IW, secondly by Euphausiacea. Differences in IWs of Chaetognatha and Fish also contributed to the dissimilarity between cohorts in 2020. Taking only data from the Loligo Box into account, basic trends remained similar (Table S4 in supplementary material). Differences between years in the ASC were caused by D. gahi and fish. Differences between cohorts in 2020 were caused by D. gahi, Euphausiacea and Amphipoda rather than Chaetognatha.
Table 10. CUMSUM from SIMPER analysis of prey-type IW in stomachs of D. gahi for inter-annual and inter-seasonal comparisons
The GAM (equation (11)) showed that importance of Amphipoda as prey was significantly different between years and cohorts, with higher item weights in 2001 compared with 2020 and in the ASC compared with the SSC (Table 5B). Chaetognatha IW had a significant interaction between year and cohort and higher values in the SSC compared with the ASC (Figure 3). Less cannibalism occurred in 2020 compared with 2001 and in the SSC compared with the ASC. Differences in IW between years or cohorts were non-significant at the 5% level for Euphausiacea, but there was a trend of lower IW in the SSC compared with the ASC. Fish was significantly more consumed in 2020 compared with 2001.
However, these observations could be a result of underlying irregularities due to the different geographic distribution of the samples collected in 2001 compared with 2020. For this reason, the same model was run with data sampled only within the Loligo Box from both years. Associated tables and plots can be found in the supplementary material. Number of knots k was set to 4.
A comparison of the two models, one containing all data and one containing only data from the Loligo Box, revealed similar trends with some important differences (Table IIB supplementary material). In contrast to the first model, IW of Chaetognatha and Euphausiacea in the Loligo Box model were higher in 2020 compared with 2001. Excluding data from the areas resulted in the exclusion of data of fish as a prey item for the ASC 2020. Smoother terms of all species for all years and cohorts remained significant except for Amphipoda and Fish in the SSC 2020.
Niche width
Levins' niche width and the Shannon Equitability Index showed similar trends (Table 11). Overall, the niche width increased with size for both years and cohorts. Niche width was wider in 2020 than in 2001. In 2020, the ASC had a wider niche than the SSC, given the same amount of utilized prey categories. The use of these prey categories also seems to have been evenly distributed, represented by a higher Shannon Equitability Index, but increased with DML. Smaller squid fed on a higher variety of prey categories but used them in a less balanced manner, focusing mainly on Euphausiacea. Therefore, the Shannon Equitability Index was smaller for smaller squid. It was also smaller in 2001 compared with 2020, when a higher variety of prey categories was identified, most of them occurring rarely.
Table 11. Levins' niche width, Shannon Equitability Index and number of prey categories found per year, cohort and size class of D. gahi; Small: <13 cm, medium: 13–19 cm, large: >19 cm
Similar to the series of GAMs, Levins' niche width and the Shannon Equitability Index were also calculated for data obtained only from the Loligo Box (see (Table 5 in supplementary material). Trends did not change due to exclusion of data. Overall, the niche width and the even use of resources indicated by the Shannon Index increased for 2020 except for small squid. Naturally they did not change for 2001 as the same data were used.
Discussion
This study used extensive datasets on stomach contents of D. gahi collected throughout the year and during two sampling periods almost 20 years apart. Despite each cohort experiencing different environmental factors at the same ontogenetic phase, their feeding spectra appear to be broadly similar although with variations in the detailed dietary composition. Observed interannual changes in the D. gahi diet may reflect decadal changes in plankton composition within the Patagonian Shelf ecosystem.
The most frequent prey items of D. gahi found in the present study were Euphausiacea and Chaetognatha. Cannibalism was also reported frequently. These results confirm findings from previous studies in this area (Guerra et al., Reference Guerra, Castro and Nixon1991; Rosas-Luis et al., Reference Rosas-Luis, Sánchez, Portela and Del Rio2014). Cannibalism is also reported in other loliginid squid (Pierce et al., Reference Pierce, Boyle, Hastie and Santos1994; Collins & Pierce, Reference Collins and Pierce1996). Cannibalistic net feeding may have occurred but was never reported on research cruises or by fisheries observers. Excluding data and focusing on the Loligo Box showed higher FO% of D. gahi, probably due to the higher concentration of animals in this area and in lower FO% of Euphausiacea, M. gregaria and fish.
The diet composition of D. gahi changed with increasing DML. Smaller squids fed mainly on Euphausiacea, whereas larger squid fed mainly on fish and squid, including cannibalism. Similar ontogenetic changes in diet were described previously in other loliginid squid, such as Loligo forbesii (Collins & Pierce, Reference Collins and Pierce1996) and Doryteuthis pealeii (Macy, Reference Macy1982; Vovk, Reference Vovk1985). This variation reflects the development of morphological features related to feeding, e.g. growth of the beak and tentacles, thus enabling the squid to feed on larger prey (Boucher-Rodoni et al., Reference Boucher-Rodoni, Boucaud-Camou, Mangold and Boyle1987). In the present study, diet did not seem to be dependent on sex.
The diet of D. gahi was found to vary throughout the year, with higher item weights of Euphausiacea being ingested during austral summer months (November–March) and higher item weights of cannibalism in small and medium sized squid during austral winter months (April–October), although large sized squid had a less cannibalistic diet in winter. The importance of seasonality for the diet composition of squid was described in L. forbesii by Wangvoralak et al. (Reference Wangvoralak, Hastie and Pierce2011), with peak copepod consumption coinciding with peak copepod biomass off the eastern coast of Scotland. Likewise, predation of D. gahi on Euphausiacea seem to be dependent on the Euphausiacea biomass peak of the Southern Ocean, where higher abundances of zooplankton can be found between January and March (Sabatini & Colombo, Reference Sabatini and Colombo2001; Sabatini et al., Reference Sabatini, Reta and Matano2004). The increased amount of ingested fish and the prevalence of cannibalism in D. gahi during the austral winter months could be due to the decreased availability of plankton such as Euphausiacea and Chaetognatha.
The present study showed that the diet of D. gahi is dependent on squid growth and seasonal availability of prey. Very few studies have investigated dietary differences between squid spawning cohorts. These differences may be related to seasonal differences in environmental conditions and prey availability experienced by the two cohorts. The two spawning cohorts of D. gahi had similar feeding spectra but different diet compositions, mainly due to the variable role of Euphausiacea in their diet, probably due to seasonality. Doryteuthis gahi individuals undergo complex horizontal and vertical migrations during their ontogeny and are affected by different environmental conditions (Arkhipkin et al., Reference Arkhipkin, Campana, FitzGerald and Thorrold2004a, Reference Arkhipkin, Grzebielec, Sirota, Remeslo, Polishchuk and Middleton2004b). Individuals of the ASC have their feeding period during the austral summer, remaining in warm shallow waters of the Transient Zone of the Patagonian shelf (100–200 m). SSC individuals have their feeding period during winter, residing in the warmest available water layer almost exclusively between 150–250 m depths (Arkhipkin et al., Reference Arkhipkin, Hatfield, Rodhouse, Rosa, O'Dor and Pierce2013). This coincides with the main depth range of Euphausia lucens (Gibbons et al., Reference Gibbons, Barange and Pillar1991). Furthermore, D. gahi and Euphausiacea show the same diel vertical migration pattern (Nocera et al., Reference Nocera, Gimenez, Diez, Retana and Winkler2021). The SSC of D. gahi in 2020 fed on smaller amounts of Euphausiacea, due to lower abundances of Euphausiacea during winter (Sabatini & Colombo, Reference Sabatini and Colombo2001). TML of Euphausiacea was smaller in winter months compared with summer months, suggesting smaller Euphausiacea prey size in winter. SSC individuals seem to feed more on fish when taking all sampled areas into account. This coincides with the higher amounts of fish being ingested during winter. However, in the GAM models, both of which used all areas and only data from the Loligo Box, slightly less cannibalism was observed in the SSC. This seems to contradict the results from the seasonal model which showed more cannibalism in winter. But less cannibalism in the SSC revealed from the inter-annual and inter-cohort model could be due to seasonal overlap, as individuals of each cohort are known to live up to ~300 days, or due to a mixing of cohorts. Especially in the autumn and winter months March–April squid cohorts often cannot be distinguished without age determination, for example by statolith readings (Jones et al., Reference Jones, Arkhipkin, Marriott and Pierce2018).
Studies on decadal diet shifts are scarce, especially in squid. The ecosystem of the Patagonian shelf underwent some significant changes within the last two decades. For example, stocks of the planktivorous southern blue whiting, Micromesistius australis, collapsed at the end of the 2000s, leading to a temporary explosion of another planktivorous fish, rock cod (Patagonotothen ramsayi). These two species are considered as important planktivorous species, occupying intermediate trophic levels and therefore competing for the same resources as D. gahi (Laptikhovsky et al., Reference Laptikhovsky, Arkhipkin and Brickle2013). Changes in the prevalence of planktivorous fish stocks may have restructured the ecosystem of the Patagonian shelf, especially as cold-water ecosystems are particularly vulnerable to trophic cascades (Frank et al., Reference Frank, Petrie, Choi and Leggett2005, Reference Frank, Petrie and Shackell2007). Inter-annual effects in the present study revealed fewer Amphipoda, more fish, less cannibalism and the appearance of Munida gregaria in the diet of D. gahi in 2020 compared with 2001 considering all sampled areas. Focusing only on the Loligo Box, also slightly less cannibalism occurred in 2020 compared with 2001. It is important to mention that Brickle et al. (Reference Brickle, Olson, Littlewood, Bishop and Arkhipkin2002) also found M. gregaria in the stomachs of D. gahi, but its prominence within the last decade seems to have increased (Rosas-Luis et al., Reference Rosas-Luis, Navarro, Sánchez and Del Río2016). Munida gregaria became one of the most important bycatch species in Patagonian fisheries in Argentine waters (Varisco et al., Reference Varisco, Vinuesa and Góngora2015) and in the last decade an increased abundance of M. gregaria was observed on the Patagonian shelf (Diez et al., Reference Diez, Cabreira, Madirolas and Lovrich2016). A study by Diez et al. (Reference Diez, Cabreira, Madirolas and Lovrich2016) indicated a population expansion of M. gregaria over the whole Patagonian shelf due to the shelf's increased productivity. As squid are opportunistic, the increased abundance of M. gregaria would explain their higher frequency in stomachs of D. gahi.
The diet of squid can differ regionally, such as in Onykia ingens (Phillips et al., Reference Phillips, Nichols and Jackson2003). Although geographic variation in diet composition seems to be important for D. gahi, it was not statistically evaluated in this study due to the focus on seasonal and decadal diet shifts. However, major trends remained the same when investigating only the Loligo Box, the area of highest density of D. gahi within catches and investigating the entire FICZ and international waters. In this case, excluding data would maintain comparability and rule out the effects of regionality but would weaken the resolution of the study. For the application of future ecosystem models, diet observations over the whole habitat would be necessary.
Wangvoralak et al. (Reference Wangvoralak, Hastie and Pierce2011) found a change in the diet composition of L. forbesii over a period of ~15 years. Due to fishing pressure, abundance of small, non-commercially targeted fish increased in Scottish waters alongside their proportion in the diet of L. forbesii. Nothing like this was observed in D. gahi, although the species assemblage around the Falkland Islands may have changed due to fishing activities within the last 20 years. As fish in the diet of D. gahi was only important for the minority of squid over ~20 cm DML, these effects may be difficult to identify.
Overall, the niche width of D. gahi indicated a moderate specialization in foraging behaviour. Niche width increased with growth, similar to D. pealeii (Hanlon et al., Reference Hanlon, Buresch, Moustahfid, Staudinger, Rosa, O'Dor and Pierce2013). The niche of the ASC in 2020 was wider than the SSC. As the ASC stay in shallower waters compared with the SSC squid, prey may be more diverse, resulting in a wider niche width. The presence of M. gregaria might explain the wider niche in 2020 compared with 2001. Overall, the niche width was similar to other squid species like Ommastrephes bartramii (0.22–0.56), whereas Sthenoteuthis oualaniensis showed a higher degree of specialization (0.086–0.097; Parry, Reference Parry2006).
Conclusions
The Patagonian long-finned squid Doryteuthis gahi appears to have the typical ontogenetic diet change found in many other squid species. Seasonal differences in Euphausiacea consumption were found, which coincide with Euphausiacea biomass peaks on the Patagonian shelf. A decadal shift to higher frequencies of the planktonic stage of lobster krill Munida gregaria within the diet is probably due to increased abundances of M. gregaria within the ecosystem itself. Differences in diet composition between spawning cohorts seem to be related to the opportunistic behaviour of D. gahi, comparable with many other cephalopod species. Effects of regionality on the diet of this study species seem to be likely and should be addressed in future studies. Niche width and evenness of prey category utilization appear to be similar between spawning cohorts and consistent over decades, but both increase with size.
This study provided the basis for future studies on ecosystem dynamics of the Patagonian shelf focusing on the commercially important squid species D. gahi and its seasonal spawning cohorts. With these findings and in combination with powerful tools such as stable isotope analysis, more detailed information on the trophic position of D. gahi could be revealed, helping the management of this important resource as well as the overall management of the ecosystem.
Supplementary material
The supplementary material for this article can be found at https://doi.org/10.1017/S0025315422000194.
Acknowledgements
The authors would like to thank the observer team of the Falkland Islands Fisheries Department for the collection of D. gahi. Furthermore, thanks goes to the editor of this journal and the anonymous reviewers for helping to improve this paper. The authors would also like to thank the crews from the fishing vessels ‘Castelo’, ‘Argos Cies’ and the ‘Beagle’. More thanks are extended to Zhanna Shcherbich and Rebecca Piontek for help with the identification of prey items and the collection of planktonic reference species. The director of the FIG Department of Natural Resources, Dr Andrea Clausen, is thanked for supporting this project with the necessary infrastructure. Finally, we thank all colleagues from the Fisheries Department for the advice they gave during this project.
Financial support
The ‘Beauchene Fishing’ company is thanked for the sponsorship of the PhD post. The University of Vigo supported this research by covering any publication expenses.
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