Introduction
Ovivory is common in the animal kingdom, with many species well adapted to identifying visual or olfactory cues generated by animal nests. For example, scent and soil disturbance allow foxes (
Nesting by freshwater fishes may function as a resource pulse event for many opportunist predators, where either high-quality eggs or guarding parental fish become temporarily vulnerable to predation. Resource pulses in freshwater environments, from the decomposition of salmon carcasses following migratory runs (Wipfli et al. 1998) and the seasonal emergence of invertebrates providing energy and nutrients for both aquatic and terrestrial consumers (Baxter et al. 2005), can shape recruitment outcomes and stabilize competitive interactions (Bailey and Moore 2020; Ritchie and Colby 1988). The ability of predators to flexibly exploit ephemeral and abundant lower trophic level resources, from invertebrates to fish eggs, is an example of dynamic omnivory, which can also play a role in food web stability (Gutgesell et al. 2022; McCann et al. 1998). The predictability of spawning and nesting events may be a widespread mechanism that sets up foraging opportunities for predators. Because nest guarding can be energetically costly for parental individuals (Steinhart et al. 2005), it is also informative to consider the effectiveness of guarding for preventing nest predation, and whether guarding individuals themselves are susceptible to predation. Thus, the nesting period presents a promising opportunity for studying species interactions that have a wide range of potential consequences from parent and offspring survival to consumer–resource interactions and the broader community (Yang et al. 2008).
The present study examines predation attempts on pumpkinseed sunfish nests, hereafter pumpkinseed, during nest guarding. The colonial nature and synchrony of nesting pumpkinseed may give rise to potential opportunities for predators, seeking to exploit either nest contents or nest-guarding individuals. We observed predation by opportunist predators across 3 days in an Ontario wetland and highlight the importance of documenting ecological interactions during fish nesting.
Methods
Site and Subjects
Big Creek National Wildlife Area (NWA) (Port Rowan, ON, Canada) is a 770-ha wetland located on the perimeter of Lake Erie, supporting a diverse wildlife assemblage. The wetland is home to an array of predators, including birds, snakes, fishes, and turtles. Over 30 species of freshwater fish have been identified here, including pumpkinseed. The Hahn marsh habitat accommodates a natural population of pumpkinseed, which offer an excellent model for studying nest guarding as they form nesting colonies and perform complex courtship and guarding behaviors (Rios-Cardenas and Webster 2005).
Data Collection
Between May 20, 2024 and May 23, 2024, pumpkinseeds were actively spawning, and males were nest guarding along the shore of the Big Creek Unit. Five 100 m transects were established along the Big Creek Trail loop. Estimates of pumpkinseed nest density were made by visual survey along each transect and extended two meters offshore. Nesting sites are characterized by a circular depression in the substrate with a male present, easily identified along the shoreline. We spent a total of 6 hours in search of and observing nest interactions over 3 days. When observed, snapping turtles were followed closely before, during, and after nest inspection and predation, noting the time spent on each nest. Nest inspection behavior was defined as a downward head posture with beaks near the nest substrate. To document the impact of nest interactions on potential nest abandonment, we returned to three nests within 48 h of each event. Any instances of predation on nesting males by snapping turtles or other predators were recorded.
Results
Nesting
Across the study area, we observed a total of 118 pumpkinseed nests with a transect density ranging from 0.065 to 0.155 nests/m2. Most nests were highly concentrated, with colonies separated by emergent vegetation near the shoreline. Five nests were identified to be solitary based on isolation from surrounding colonies. Several instances of active spawning were observed during surveys, but the majority of nests were occupied by a single guarding male on the nest.
Predation by Snapping Turtles
During shoreline surveys, we observed seven adult snapping turtles and one juvenile, five of which actively inspected pumpkinseed nests. Three turtles, not involved in predation attempts, were observed within approximately 3 m of pumpkinseed nesting colonies.
Nest inspection by adult snapping turtles ranged from 10 to 694 s (n = 9), with an average time of 259 s. Once at the nest, turtles positioned their head close to the substrate, appearing to search (Figure 1). During the two longest nest encounters (663 and 694 s), turtles actively consumed nest contents, as indicated by a guttural gulping motion. Following inspection and apparent egg predation, turtles exited the nesting area and moved to deeper water. In one case, an individual turtle interacted with a total of six nests, seemingly predating only one of the nests before moving into deeper water. On two occasions, snapping turtles approached and inspected nests with an actively mating pair of pumpkinseed, resulting in the dissolution of mating. Unfortunately, due to logistical constraints, of the nine recorded instances of nest inspection, we were only able to revisit three of the nests and each was abandoned by the male pumpkinseed.
[IMAGE OMITTED. SEE PDF]
Nest Guarding
During nest interactions between snapping turtles and pumpkinseed, pumpkinseed males generally stayed on or near the nest (Video 1). In many cases, this was the extent of the behavior exhibited by defending pumpkinseed males. However, some pumpkinseed demonstrated repeated diversion behavior occurring either during nest inspection or as the turtle was approaching. Only one instance of physical aggression was observed across all nine nest inspection observations. Here, the male repeatedly lunged at the head of the turtle until the turtle vacated the nest (Video 2).
[IMAGE OMITTED. SEE PDF]
[IMAGE OMITTED. SEE PDF]
Many instances of nest inspection by turtles were observed in close proximity to other nests with a guarding male pumpkinseed, but an altruistic behavioral response, such as mobbing was not elicited, despite being observed in other closely related species, such as bluegill (
Other Interactions
During surveys, we observed several other opportunist predators among pumpkinseed nesting colonies. Leuciscids were observed within the perimeter of nests but were swiftly chased away by guarding males. Bowfin (
[IMAGE OMITTED. SEE PDF]
Discussion
This study details a rarely documented predator–prey interaction between pumpkinseed and opportunistic snapping turtles during spring nesting. Although examples of nest predation by snapping turtles in the literature are uncommon, over 70% of observed adult turtles were found interacting with and, in some cases, foraging on pumpkinseed nests. Pumpkinseed exhibit an array of defensive behavioral strategies in response to nest predation by snapping turtles; however, they appear largely unsuccessful. Hence, the high concentration of nests and energy-rich eggs give rise to foraging opportunities for snapping turtles even when guarded. Furthermore, guarding adults may be susceptible to predation by other fishes, as demonstrated by bowfin. Interestingly, no observations of predation by conspecifics were made despite the vast majority of males concentrated in nesting colonies. Colonial nesting may provide additional defensive opportunities and function to reduce predation pressure on any one individual, similar to fish schooling behavior (Magurran 1990). Although some debate exists regarding whether pumpkinseed are true colonial nesters (Gross 1982; Gross and MacMillan 1981), numerous cases of highly aggregated nesting support our observations of colonial nesting in the present study (Jordan et al. 2009; McPhail 2007; Scott and Crossman 1973; Ingram and Odum 1941; Krecker 1916). Future research could explore how local conditions or other factors influence the degree of colonial nesting in pumpkinseed sunfish.
Snapping turtles appear to exhibit egg predation more broadly prior to nesting in the early spring. For example, Moldowan et al. (2015) observed a female snapping turtle feeding on spotted salamander (
In addition to the influence of egg predation on offspring mortality in fishes, energy and nutrients from egg predation may provide important resources for pre-spawning snapping turtles. In Ontario, snapping turtles spawn in late spring, following a period of low availability of aquatic vegetation (Obbard and Brooks 1981). Other freshwater turtle species exhibit shifts toward carnivory during periods of low vegetative abundance before spawning (Petrov et al. 2024). Consumption of aggregated egg masses from nesting fishes may thus act as an ephemeral but high-quality resource pulse rich in fat and protein (Kowalska-Góralska et al. 2020). Our results identify a novel energy channel and highlight the potentially diverse dietary contributions to reproductive output in omnivorous turtle species, warranting further consideration.
Predator–prey interactions play a significant role in governing food web structure and dynamics (McCann et al. 1998). Though ephemeral and temporally dynamic interactions can be challenging to observe in the wild, such interactions can have drastic consequences for predator growth and behavior (Armstrong and Bond 2013). The extent to which nesting behavior and colonial spawning may function as important mediators of temporally structured predator–prey interactions remains largely unknown. As such, future work should consider the potential role of nesting in subsidizing the diet of opportunistic predators.
Despite this opportunity for predators, behavioral tactics employed by nest guarders are likely central to nesting and reproductive success (Gravel and Cooke 2009). Pumpkinseed are known to exhibit aggressive behaviors during nesting, ranging from opercular spreading, lunging, and nipping, making physical contact with an intruder (Stacey and Chiszar 1978). Although fine-scale behaviors such as opercular spreading could not be observed, the majority of interactions did not involve physical aggression on the part of the guarding male. Appreciating the variation in nest guarding behaviors may be important for understanding the impact of novel or invasive predators on reproductive success and coping strategies of nesting freshwater fishes.
The present study outlines a unique interaction between nest guarding pumpkinseed and opportunistic predation by snapping turtles, providing newfound insights into the underappreciated role of nesting in generating predator–prey interactions in aquatic environments. The generality of egg predation in snapping turtles in other locations is currently unclear. However, nesting among freshwater fish species gives rise to several avenues for further study of the behaviors elicited by nest predation, their contribution to reproductive success against an array of predators, and the outcomes of nest predation for predator growth and food web dynamics. Future research should examine the costs of nest foraging opportunities for predators and seek to understand the extent to which nest predation may subsidize their diet, with careful consideration of its contribution to seasonal and reproductive energetics.
Author Contributions
Brett M. Studden: conceptualization (lead), investigation (lead), methodology (lead), writing – original draft (lead), writing – review and editing (equal). Timothy Fernandes: conceptualization (supporting), writing – original draft (supporting), writing – review and editing (equal). Bailey McMeans: conceptualization (supporting), funding acquisition (lead), writing – original draft (supporting), writing – review and editing (equal).
Acknowledgments
The authors would like to acknowledge Katherine Court for their contribution to field operations.
Conflicts of Interest
The authors declare no conflicts of interest.
Data Availability Statement
Data available through Dryad data repository, doi: . Further inquiries may be directed to the corresponding author.
Armstrong, J. B., and M. H. Bond. 2013. “Phenotype Flexibility in Wild Fish: Dolly Varden Regulate Assimilative Capacity to Capitalize on Annual Pulsed Subsidies.” Journal of Animal Ecology 82: 966–975.
Bailey, C. J., and J. W. Moore. 2020. “Resource Pulses Increase the Diversity of Successful Competitors in a Multi‐Species Stream Fish Assemblage.” Ecosphere 11: e03211.
Baxter, C. V., K. D. Fausch, and W. C. Saunders. 2005. “Tangled Webs: Reciprocal Flows of Invertebrate Prey Link Streams and Riparian Zones.” Freshwater Biology 50: 201–220.
Baylis, J. R. 1981. “The Evolution of Parental Care in Fishes, With Reference to Darwin's Rule of Male Sexual Selection.” Environmental Biology of Fishes 6: 223–251.
Buse, A. J., M. A. Douglas, T. N. Giguère, and B. W. Robinson. 2017. “Adult Snapping Turtle (Chelydra serpentina) Feeding on Goldeneye Embryos of Pumpkinseed (Lepomis gibbosus) in Defended Nests.” Canadian Field‐Naturalist 131: 254–257.
Dominey, W. J. 1983. “Mobbing in Colonially Nesting Fishes, Especially the Bluegill, Lepomis macrochirus.” Copeia 1983: 1086–1088.
Fernandes, T. J., R. O'Connor, K. S. McCann, B. J. Shuter, and B. C. McMeans. 2024. “Ephemeral Piscivory in a Mesopredator Sunfish: Implications for Pond Food Webs.” Ecology 105: e4431.
Geller, G. A., and S. L. Parker. 2022. “What Are the Primary Cues Used by Mammalian Predators to Locate Freshwater Turtle Nests? A Critical Review of the Evidence.” Frontiers in Ecology and Evolution 9: 784786.
Gravel, M.‐A., and S. J. Cooke. 2009. “Influence of Inter‐Lake Variation in Natural Nest Predation Pressure on the Parental Care Behaviour of Smallmouth Bass (Micropterus dolomieu).” Ethology 115: 608–616.
Gross, M. R. 1982. “Sneakers, Satellites and Parentals: Polymorphic Mating Strategies in North American Sunfishes.” Zeitschrift für Tierpsychologie 60: 1–26.
Gross, M. R., and A. M. MacMillan. 1981. “Predation and the Evolution of Colonial Nesting in Bluegill Sunfish (Lepomis macrochirus).” Behavioral Ecology and Sociobiology 8: 163–174.
Gutgesell, M. K., K. S. McCann, G. Gellner, et al. 2022. “On the Dynamic Nature of Omnivory in a Changing World.” Bioscience 72: 416–430.
Ingram, W. M., and E. P. Odum. 1941. “Nests and Behavior of Lepomis gibbosus (Linnaeus) in Lincoln Pond, Rensselaerville, New York.” American Midland Naturalist 26: 182–193.
Jones, H. M., and C. A. Paszkowski. 1997. “Effects of Northern Pike on Patterns of Nest Use and Reproductive Behavior of Male Fathead Minnows in a Boreal Lake.” Behavioural Ecology 8: 655–662.
Jordan, C., N. Backe, M. C. Wright, and C. P. Tovey. 2009. “Biological Synopsis of Pumpkinseed (Lepomis gibbosus).” Canadian Manuscript Report of Fisheries and Aquatic Sciences 2886: 16.
Kowalska‐Góralska, M., K. Formicki, Z. Dobrzański, et al. 2020. “Nutritional Composition of Salmonidae and Acipenseridae Fish Eggs.” Annals of Animal Science 20: 629–645.
Krecker, F. H. 1916. “Sunfish Nests of Beimiller's Cove.” Ohio Journal of Science 16: 125–134.
Magurran, A. E. 1990. “The Adaptive Significance of Schooling as an Anti‐Predator Defence in Fish.” Annales Zoologici Fennici 27: 51–66.
Mason, K., and D. O. Evans. 2011. “Predation of Lake Trout and Lake Whitefish Embryos by Crayfish: Implications of Shifts in Crayfish Dominance in Lake Simcoe.” Journal of Great Lakes Research 37: 113–123.
McCann, K., A. Hastings, and G. Huxel. 1998. “Weak Trophic Interactions and the Balance of Nature.” Nature 395: 794–798.
McPhail, J. D. 2007. The Freshwater Fishes of British Columbia, 501. University of Alberta Press.
Moldowan, P. D., M. G. Keevil, P. B. Mills, R. J. Brooks, and J. D. Litzgus. 2015. “Diet and Feeding Behaviour of Snapping Turtles (Chelydra serpentina) and Midland Painted Turtles (Chrysemys Picta marginata) in Algonquin Provincial Park, Ontario.” Canadian Field‐Naturalist 129: 403–408.
Nester, R. T., and T. P. Poe. 1984. “Predation on Lake Whitefish Eggs by Longnose Suckers.” Journal of Great Lakes Research 10: 327–328.
Obbard, M. E., and R. J. Brooks. 1981. “A Radio‐Telemetry and Mark‐Recapture Study of Activity in the Common Snapping Turtle, Chelydra serpentina.” Copeia 1981: 630–637.
Petrov, K., J. U. Van Dyke, A. Georges, C. Keitel, and R.‐J. Spencer. 2024. “Maternal Diet Influences Fecundity in a Freshwater Turtle Undergoing Population Decline.” Conservation Physiology 12: coae033.
Rios‐Cardenas, O., and M. S. Webster. 2005. “Paternity and Paternal Effort in the Pumpkinseed Sunfish.” Behavioral Ecology 16: 914–921.
Ritchie, B. J., and P. J. Colby. 1988. “Even‐Odd Year Differences in Walleye Year‐Class Strength Related to Mayfly Production.” North American Journal of Fisheries Management 8: 210–215.
Scott, W. B., and E. J. Crossman. 1973. Freshwater Fishes of Canada, 713–718. Fisheries Research Board of Canada.
Spencer, R. 2002. “Experimentally Testing Nest Site Selection: Fitness Trade‐Offs and Predation Risk in Turtles.” Ecology 83: 2136–2144.
Stacey, P. B., and D. Chiszar. 1978. “Body Color Pattern and the Aggressive Behavior of Male Pumpkinseed Sunfish (Lepomis gibbosus) During the Reproductive Season.” Behaviour Research and Therapy 64: 271–296.
Steinhart, G. B., M. E. Sandrene, S. Weaver, R. A. Stein, and E. A. Marschall. 2005. “Increased Parental Care Cost for Nest‐Guarding Fish in a Lake With Hyperabundant Nest Predators.” Behavioral Ecology 16: 427–434.
Wipfli, M. S., J. Hudson, and J. Caouette. 1998. “Influence of Salmon Carcasses on Stream Productivity: Response of Biofilm and Benthic Macroinvertebrates in Southeastern Alaska, U.S.A.” Canadian Journal of Fisheries and Aquatic Sciences 55: 1503–1511.
Yang, L. H., J. L. Bastow, K. O. Spence, and A. N. Wright. 2008. “What Can We Learn From Resource Pulses.” Ecology 89: 621–634.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
© 2025. This work is published under http://creativecommons.org/licenses/by/4.0/ (the "License"). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.
Abstract
ABSTRACT
The construction and defense of nests leading up to and following spawning is widespread across freshwater fishes. Despite the known role of nesting in sexual selection and the establishment of social hierarchy, how nesting and nest guarding behavior may shape predation risk for both offspring and nest guarding individuals remains relatively underexplored for many species. Here, we documented a novel interaction between a nest guarding fish species, the pumpkinseed sunfish (
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
Details


1 Department of Biology, University of Toronto Mississauga, Mississauga, Ontario, Canada, Department of Ecology and Evolutionary Biology, University of Toronto, Toronto, Ontario, Canada
2 Department of Biology, University of Toronto Mississauga, Mississauga, Ontario, Canada