The behavioral strategies developed by predators to capture and kill their prey are fascinating, notably for predators that forage for prey at, or beyond, the boundaries of their ecosystem. We report here the occurrence of a beaching behavior used by an alien and large-bodied freshwater predatory fish (Silurus glanis) to capture birds on land (i.e. pigeons, Columbia livia). Among a total of 45 beaching behaviors observed and filmed, 28% were successful in bird capture. Stable isotope analyses (δ13C and δ15N) of predators and their putative prey revealed a highly variable dietary contribution of land birds among individuals. Since this extreme behavior has not been reported in the native range of the species, our results suggest that some individuals in introduced predator populations may adapt their behavior to forage on novel prey in new environments, leading to behavioral and trophic specialization to actively cross the water-land interface.
Citation: Cucherousset J, Boulêtreau S, Azémar F, Compin A, Guillaume M, Santoul F (2012) “Freshwater Killer Whales”: Beaching Behavior of an Alien Fish to Hunt Land Birds. PLoS ONE 7(12): e50840. https://doi.org/10.1371/journal.pone.0050840
Editor: Dirk Steinke, Biodiversity Insitute of Ontario - University of Guelph, Canada
Received: August 6, 2012; Accepted: October 24, 2012; Published: December 5, 2012
Copyright: © 2012 Cucherousset et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: JC was supported by an “ERG Marie Curie” grant (PERG08-GA-2010- 276969) in the lab EDB, part of the “Laboratoire d”Excellence (LABEX) entitled TULIP (ANR -10-LABX-41). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
To capture, handle, kill and/or swallow their prey, predators have developed numerous strategies, including pack hunting, venin, cooperation, trapping webs and the use of tools. For instance, savannah chimpanzees have been reported to construct wooden spear-like tools to hunt their preys  while New Caledonian crows can use stick tools to capture highly energetic wood-boring beetle larvae . However, perhaps the most astonishing strategies are when the preys targeted by the predator are located outside of the predator’s ecosystem boundaries. These strategies can be grouped into three broad categories. First, the predators can passively lie in ambush until the preys cross the water-land interface (voluntarily or accidently) and capture them. This is notably the case of crocodiles that capture migrating wildebeest crossing rivers and of terrestrial predators such as birds, spiders and bats that capture emerging aquatic insects , . Second, some predators may develop strategies that force the prey to enter their ecosystem. For instance, archerfish (Toxotes jaculatrix Pallas) have developed complex optical and morphological adaptations to ‘shoot down’ insects located on trees by expelling droplets on the insects that will subsequently fall in the water . Third, and most spectacularly, predators can actively cross the water-land interface to capture the prey. Some marine predators such as killer whales (Orcinus orca L.) and bottlenose dolphins (Tursiops sp.) display intentional ‘beaching’ behavior to catch prey on beaches , . In many predators, these extreme hunting behaviors represent a form of ecological specialization ,  that is displayed only by a subset of individuals in the populations . Here, we report the occurrence of a hunting behavior, analogous to the intentional beaching of marine mammals, in an alien freshwater fish species (European catfish Silurus glanis L., the world’s third largest and Europe’s largest freshwater fish) ,  to capture land birds. Additionally, we demonstrate the existence of trophic niche variability within the population with only some individuals foraging on land birds.
Materials and Methods
(a) Behavioral Monitoring
European catfish originates from Europe (east of Rhine River) and has been introduced in many ecosystems of Western Europe, including Spain, Italy and Southwestern France . We conducted the present study in the Tarn River (Southwestern France) within the historical city center of Albi, a UNESCO World Heritage Centre. European catfish were introduced in the Tarn River in 1983 and have since established self-sustained populations . Behavioral monitoring was performed from a bridge above a gravel island where pigeons (Columbia livia Gmelin) regroup for drinking and cleaning (43° 55′ 51.77″ N, 2° 08′ 41.83″ E). At the studied stretch, the Tarn River is approximately 100 m wide with a mean depth of 3 m (maximum depth 5.4 m) and belongs to a protected area where angling is prohibited. In total, 24 surveys (approx. 3-hour long on average, total observation and filming time of approx. 72 h) were performed from June 30th to October 19th 2011 in the morning or in the afternoon. The number and success rate of beaching behavior were determined by filming the predatory fish nearby the gravel island. Throughout the survey, river discharge was low and the water was clear, allowing full observation of all displayed behavior (Figure 1 and Movie S1).
Several individuals were observed swimming nearby the gravel beach in shallow waters where pigeons regroup for drinking and cleaning (large picture). One individual is seen approaching land birds and beaching to successfully capture one (small pictures).
δ13C and δ15N values (‰) of each individual (n = 14) and the putative aquatic (fish, n = 9 and crayfish, n = 3) and terrestrial (pigeon, n = 6) prey are displayed. The large symbols for each prey represent the mean value (± SD).
(b) Stable Isotope Analyses
Tissue samples of European catfish and their potential prey were collected in the observation site from 18th September to 14th October 2011 to quantify the contribution of land birds to the catfish diet using stable isotope analyses. Sampling was allowed by the permit “Arrêté Préfectoral no. 2011–018”. Stable isotope analyses (principally δ13C and δ15N) are now commonly used by ecologists to provide reliable estimates of long-term dietary patterns of predators , , including trophic specialization ,  and the ecological impacts of non-native fish species , . A total of 14 European catfish located within the study area (estimated body size ranging from 900 to 2000 mm) were sampled. Fin clips were collected by angling from 5 individuals while muscle samples were collected on the flank of 9 additional individuals by scuba divers using a spear gun equipped with a 40-mm length and 27-mm diameter stainless steel biopsy tip. Fin and muscle samples were pooled in the analyses since their stable isotope values do not differ significantly in this species . No lipid correction was performed since samples have low and homogeneous C:N ratios (3.2±0.2 SD) . Muscle samples of the putative aquatic and terrestrial prey present in the study area were also collected. These included crayfish (Orconectes limosus Rafinesque n = 3) and Cyprinids prey fish (Blicca bjoerkna L. n = 3, Cyprinus carpio L. n = 3, and Rutilus rutilus L. n = 3, pooled for analyses) which represent the most abundant aquatic prey. Additionally, muscle samples of pigeons were collected on in 2010 (n = 3) and 2011 (n = 3) from local hunting society within 2 km of the study site where pigeons forage. No other potential terrestrial prey sources were observed in the study area. Samples for SIA were oven dried (60°C for 48 h) and analyzed at the Cornell Isotope Laboratory (COIL, Ithaca, NY).
(c) Mixing Models
A Bayesian mixing model (Stable Isotope Analysis in R, SIAR)  was used to estimate the contribution of each prey (fish, crayfish and pigeon) to the diet of each individual European catfish (function siarsolomcmcv4, 500000 iterations) since it accounts for potential variability in the stable isotope values of consumers, prey and trophic fractionation . Since no specific trophic fractionation values exist for European catfish, we followed a conservative approach  that consisted in using commonly reported fractionation factors with error estimates (1 ‰ (±1 SD) and 3.4 ‰ (±1 SD) for δ13C and δ15N, respectively) , . For each individual, the lower and upper 50, 75 and 95% Bayesian credibility intervals of the contribution of each prey were predicted by the mixing models. Potential effects of individual body size, sampling date and sampled tissue on the mean predicted contribution of pigeon to the diet of each individual were tested using Spearman correlations and Kruskal-Wallis test, respectively. All statistical analyses were performed using R .
(a) Behavioral Observations
During the 24 surveys conducted in an urbanized stretch of the Tarn River (France), between 1 and 9 European catfish (mean 3.9±2.1 SD, estimated body size range: 900–1500 mm) were observed swimming nearby a small island where pigeons regrouped for drinking and cleaning (Figure 1). Fifty-four beaching behaviors with partial and mostly complete stranding were observed and filmed (Movie S1), among which 28% (n = 15) were successful, i.e. the land birds were captured on land, returned to the river and swallowed (Figure 1 and Movie S1). On one occasion, complete stranding was observed but the attack was unsuccessful in capturing the pigeon. In approximately 40% of all observations, European catfish had more than half of their body outside of the water. The beaching behavior was quick, lasting from less than one second to no more than 4 seconds. The attacks were systematically triggered by active pigeons. Indeed, motionless pigeons, even very closed to the European catfish, were never attacked. Before the attack, European catfish were observed to exhibit erected upper jaw barbels on the upper jaw when they approach pigeons, suggesting that water vibrations, rather than visual cues, were used to detect and attack the prey.
(b) Stable Isotope Analyses
Stable isotope analyses of European catfish revealed a high level of trophic niche variability among individuals, notably for δ13C that ranged from −26.6 ‰ to −22.8 ‰ while the variability in δ15N was somewhat lower (12.1 ‰ to 14.7 ‰, Figure 2). As fish and crayfish were 13C-depleted compared to pigeons (Figure 2 and Table S1), this indicated varying importance of aquatic (i.e. fish and crayfish) and terrestrial (i.e. pigeons) prey in the diet of the sampled individuals. Specifically, mixing models predicted a highly variable dietary contribution of pigeons among individuals, with 95% Bayesian credibility intervals ranging from 0–51% to 12–78% (Figure 3). While the dietary contribution of crayfish was relatively similar among individuals, the dietary contribution of pigeons increased as the dietary contribution of fish decreased (Figure 3). No significant effects of sampling date and sampled tissue on the mean predicted dietary contribution of pigeons were observed (Spearman correlation, P = 0.203 and Kruskal-Wallis test, P = 0.317, n = 14, respectively). However, the estimated body size range of European catfish observed hunting for pigeons (range: 900–1500 mm) tended to somewhat smaller that the estimated body size range of the individuals sampled in the study area (range: 900–2000 mm), suggesting a potential effect of individual body size on the display of this novel beaching behavior. This was partially confirmed by the existence of a negative but marginally significant relationship between individual body size and the mean predicted dietary contribution of pigeons (Spearman correlation, r = −0.60, P = 0.065, n = 14).
Although the consumption of terrestrial prey by aquatic predators is a ubiquitous phenomenon , , we document here a novel behavior displayed by an alien freshwater predator that was not, to the best of our knowledge, reported in its native range. This behavior allowed the capture of birds on land through intentional crossing of the water-land interface (beaching). Introduced species can display ecological and evolutionary adaptations in their new environment, and the occurrence of new behaviors can increase invasive species success . Here, this new hunting strategy leads to a high level of trophic variability among individuals. Theories predict that behavioral and trophic specialization can have strong ecological and evolutionary consequences on intraspecific competition and individual fitness , which might subsequently affect the invasive success of the population. However, since European catfish were not monitored at the individual level in the present study, the potential correlation between success rate of attacks, dietary contribution of pigeons and individuals fitness were not tested. Therefore, it would be of great interest to determine the individual ecological consequences of this hunting behavior in an introduced population.
Understanding the ecological causes triggering the occurrence and maintenance of this unusual predation behavior is important, but it remains unknown at this stage. The emergence of trophic specialization in wild populations can be triggered by an increased intraspecific competition caused by an increased population density and/or a decreased in prey availability , . European catfish have recently widely expanded its non-native distributional range through multiple introductions and colonization , , and although temporal patterns of the fish community in the study area are unknown, a potential increased density of European catfish and/or a potential decreased in prey fish might have caused this behavior to occur. This hypothesis might be explained by the existence of a negative and marginally significant relationship between individual body size and the dietary contribution of pigeons, assuming that smaller individuals are less competitive than larger individuals to prey upon prey fish. Alternatively, the risk of being stranded on the riverbank and the energy cost of attacking a pigeon on land might be lower for smaller individuals than for large-bodied specimen (i.e. >1500 mm). In this case, the costs associated with displaying this new beaching behavior (e.g. learning, risk of being stranded) might be counterbalanced by high energy returns provided by the consumption of the new prey, as observed elsewhere . Therefore, land birds certainly represent a new ecological opportunity  that increases the diversity of trophic resources available to the introduced predator and that could drive individual specialization, as observed in other populations of predators foraging on allochtonous prey (e.g. ).
In conclusion, these findings suggest that this new predation behavior might represent an extreme example of the ability of introduced species to adapt to a new environment that could have unexpected implications for consumer-resources dynamics and ecosystem functioning ,  that deserve further investigations.
Stable isotope values of the three potential prey sources (fish, crayfish and pigeon) used in the mixing models. Reported values are the number of sampled individuals (n) and mean (± SD) δ13C and δ15N (in ‰).
We thank J.D. Olden, J.R. Britton, S. Blanchet, E. Danchin, J. Syväranta and anonymous reviewers for comments on the manuscript, P. Marty, S. Planes, B. Lenclos and C. Musseau for field assistance and the ONEMA and FDAAPPMA 81. Sampling was conducted under the permit “Arrêté Préfectoral 2011–018” and we are grateful to local angling and hunting societies for providing some samples.
Conceived and designed the experiments: JC AC FA FS. Performed the experiments: FA AC MG FS. Analyzed the data: JC SB FS. Contributed reagents/materials/analysis tools: FS. Wrote the paper: JC SB FS.
- 1. Pruetz JD, Bertolani P (2007) Savanna Chimpanzees, Pan troglodytes verus, Hunt with Tools. Curr Biol 17: 412–417 (doi:10.1016/j.cub.2006.12.042)..
- 2. Rutz CR, Bluff LA, Reed N, Troscianko J, Newton J, et al. (2010) The Ecological Significance of Tool Use in New Caledonian Crows. Science 329: 1523–1525 (doi:10.1126/science.1192053)..
- 3. Nakano S, Murakami M (2001) Reciprocal subsidies: Dynamic interdependence between terrestrial and aquatic food webs. Proc Natl Acad Sci USA 98: 166–170 (doi:10.2307/3054647)..
- 4. Baxter CV, Fausch KD, Carl Saunders W (2005) Tangled webs: reciprocal flows of invertebrate prey link streams and riparian zones. Freshwater Biol 50: 201–220 (doi:10.1111/j.1365-2427.2004.01328.x)..
- 5. Schuster S, Rossel S, Schmidtmann A, Jäger I, Poralla J (2004) Archer fish learn to compensate for complex optical distortions to determine the absolute size of their aerial prey. Curr Biol 14: 1565–1568 (doi:10.1111/j.1365-2427.2004.01328.x)..
- 6. Guinet C, Bouvier J (1995) Development of intentional stranding hunting techniques in killer whale (Orcinus orca) calves at Crozet Archipelago. Can J Zool 73: 27–33 (doi:10.1139/z95-004)..
- 7. Sargeant BL, Mann J, Berggren P, Krützen M (2005) Specialization and development of beach hunting, a rare foraging behavior, by wild bottlenose dolphins (Tursiops sp.).. Can J Zool 83: 1400–1410 (doi:10.1139/Z05-136)..
- 8. Bolnick DI, Svanbäck R, Fordyce JA, Yang LH, Davis JM, et al. (2003) The ecology of individuals: incidence and implications of individual specialization. Am Nat 161: 1–28 (doi:10.1086/343878)..
- 9. Araújo MS, Bolnick DI, Layman CA (2011) The ecological causes of individual specialisation. Ecol Lett 14: 948–958 (doi:10.1111/j.1461-0248.2011.01662.x.)..
- 10. Stone R (2007) The Last of the Leviathans. Science 316: 1684–1688 (doi:10.1126/science.316.5832.1684)..
- 11. Copp GH, Britton JR, Cucherousset J, Garcia-Berthou E, Kirk R, et al. (2009) Voracious invader or benign feline? A review of the environmental biology of European catfish Silurus glanis in its native and introduced ranges. Fish Fisheries 10: 252–282 (doi:10.1111/j.1467-2979.2008.00321.x)..
- 12. Syväranta J, Cucherousset J, Kopp D, Crivelli A, Céréghino R, et al. (2010) Dietary breadth and trophic position of introduced European catfish Silurus glanis in the River Tarn (Garonne River basin), southwest France. Aquat Biol 8: 137–144 (doi:10.3354/ab00220)..
- 13. Fry B (2006) Stable isotope ecology. New York, USA: Springer.
- 14. Vander Zanden MJ, Casselman JM, Rasmussen JB (1999) Stable isotope evidence for the food web consequences of species invasions in lakes. Nature 401: 464–467 (doi:10.1038/46762)..
- 15. Araújo MS, Bolnick DI, Machado G, Giaretta AA, Reis SF (2007) Using δ13C stable isotopes to quantify individual-level diet variation. Oecologia 152: 643–654 (doi:10.1007/s00442-007-0687-1)..
- 16. Cucherousset J, Acou A, Blanchet S, Britton JR, Beaumont WR, et al. (2011) Fitness consequences of individual specialisation in resource use (and trophic morphology in European eels. Oecologia 167: 75–84 (doi:10.1007/s00442-011-1974-4)..
- 17. Cucherousset J, Boulêtreau S, Martino A, Roussel J-M, Santoul F (2012) Using stable isotope analyses to determine the ecological effects of non-native fishes. Fisheries Manage Ecol 19: 111–119 (doi:10.1111/j.1365-2400.2011.00824.x)..
- 18. Post DM, Arrington DA, Layman CA, Takimoto G, Quattrochi J, et al. (2007) Getting to the fat of the matter: models, methods and assumptions for dealing with lipids in stable isotope analyses. Oecologia 152: 179–189 (doi:10.1007/s00442-006-0630-x)..
- 19. Parnell AC, Inger R, Bearhop S, Jackson AL (2010) Source Partitioning Using Stable Isotopes: Coping with Too Much Variation. PLoS ONE 5: e9672 (doi:10.1371/journal.pone.0009672)..
- 20. Post DM (2002) Using stable isotopes to estimate trophic position: models, methods, and assumptions. Ecology 83: 703–718 (doi:10.2307/3071875)..
- 21. R Development Core Team (2012) R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. ISBN 3-900051-07-0, URL http://www.R-project.org/.
- 22. Bartels P, Cucherousset J, Steger K, Eklöv P, Tranvik LJ, et al. (2011) Reciprocal subsidies between freshwater and terrestrial ecosystems structure consumer-resource dynamics. Ecology 93: 1173–1182 (doi:10.1890/11-1210.1)..
- 23. Holway DA, Suarez AV (1999) Animal behavior: an essential component of invasion biology. Trends Ecol Evol 14: 328–330.
- 24. 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 (doi:10.1073/pnas.0709263105)..
- 25. Poulet N, Beaulaton L, Dembski S (2011) Time trends in fish populations in metropolitan France: insights from national monitoring data. J Fish Biol 79: 1436–1452 (doi:10.1111/j.1095-8649.2011.03084.x)..
- 26. Darimont CT, Paquet PC, Reimchen TE (2009) Landscape heterogeneity and marine subsidy generate extensive intrapopulation niche diversity in a large terrestrial vertebrate. Journal of Animal Ecology 78: 126–133 (doi: 10.1111/j.1365-2656.2008.01473.x)..
- 27. Cucherousset J, Olden JD (2011) Ecological impacts of nonnative freshwater fishes. Fisheries 36: 215–230 (doi:10.1080/03632415.2011.574578)..
- 28. Boulêtreau S, Cucherousset J, Villéger S, Masson R, Santoul F (2011) Colossal aggregations of giant alien freshwater fish as a potential biogeochemical hotspot. PLoS ONE 6: e25732 (doi:10.1371/journal.pone.0025732)..