FIGURE 1. Map of the Galapagos Islands, Ecuador, with zoom in to Wolf Volcano, Isabela Island. Red star represents the location where first record of a Galapagos Hawk Buteo galapagoensis preying upon a feral cat Felis catus was taken by a camera trap.

For conservation purposes and monitoring Galapagos Pink Iguanas, a camera trap project was started in January 2022 with the primary objective of evaluating the actual demographics of the iguanas, identifying possible nesting areas, and determining the existence of active reproduction and recruitment within the population. This project was funded by the non-governmental organization Galápagos Conservancy and carried out in collaboration with the Galapagos National Park Directorate. During the monitoring phase, 53 Reconyx camera traps, model HyperFire 2, were set up in strategic places, covering the iguana’s distribution area, on slopes, crests, and inside the volcano crater. Cameras were checked and pictures extracted every 20 days, one of which caught the predation event.

FIGURE 2 FIGURE 2 First record of a Galapagos Hawk Buteo galapagoensis preying upon a feral cat Felis catus on Wolf Volcano, Isabela Island, Galapagos, taken by a camera trap as bycatch data. FIGURE 2 First record of a Galapagos Hawk Buteo galapagoensis preying upon a feral cat Felis catus on Wolf Volcano, Isabela Island, Galapagos, taken by a camera trap as bycatch data.

FIGURE 2. First record of a Galapagos Hawk Buteo galapagoensis preying upon a feral cat Felis catus on Wolf Volcano, Isabela Island, Galapagos, taken by a camera trap as bycatch data.

On the 18th of January, 2022, a Galapagos Hawk Buteo galapagoensis was pictured with a feral cat Felis catus in its right claw (Fig. 2). The event occurred at the northern slopes of Wolf Volcano (0°02’18.2”N 91°21’04.3”W), at an altitude of 1,234 m above sea level, on inclined ground. The prey item was identified as a cat based on its size, fur coloration, and the absence of any other similarly sized mammal species on the island. Distinct features such as legs, paws, and thick fur further supported this identification. The cat appears to be a juvenile based on size and is missing its head. The hawk has apparent blood marks on its beak and right claws, suggesting hunting included attacking the head (which is missing from the images). Overall, 10 pictures of the event were taken, where the hawk stands grabbing the cat tightly in its claws. It was the only event of this nature registered.

This record presents the first documented case of Buteo galapagoensis preying on a feral cat Felis catus, further highlighting the hawk’s opportunistic and generalist feeding behavior and adding a previously unrecorded prey item to its extensive dietary repertoire that includes more than six mammalian prey. The availability of introduced prey species can provide important insights into ecosystem dynamics on the Galapagos Islands. Predation on an introduced predator such as a feral cat may have broader implications, potentially indicating a shift in the hawk’s diet towards non-native species. However, given the hawk’s highly opportunistic and idiosyncratic prey selection [1], this single event does not necessarily indicate a population-wide trend. Regardless, it does contribute to discussions on the ecological impacts of introduced species and their integration into native food webs. On some islands, such as Santiago, black rats have become the primary food source for the hawk following goat eradication [8]. With the addition of feral cats, the number of known introduced prey species in the hawk’s diet now increases to five: small goats and goat carrion Capra capra, black rats Rattus rattus, mice Mus musculus, domestic poultry Gallus spp. [1,4], and now feral cats Felis catus. This opens discussions about the role of introduced species in supporting native predator diets and may present initial insights into the hawk’s potential role in the ecological control of invasive cats or others, since the event shows a positive interaction towards the ecosystem, where cats threaten endangered species such as the critically endangered pink iguanas. This event highlights the potential but probably limited role of native predators in mitigating the impacts of invasive species, something that could complement ongoing conservation efforts. However, further research is needed to understand ecosystem resilience and inform cautious, scientificbased conservation strategies, as well as the importance of considering native predator responses in conservation efforts.

The observation raises several important ecological questions: Is the hawk’s consumption of introduced species indicative of a dietary shift, or is it driven by the decline of native prey? Does the increasing abundance of invasive species such as feral cats simply raise the chances of such predation events? Is it also possible that such interactions have gone unrecorded due to the lack of monitoring in places where both species coincide? On Santa Cruz, San Cristóbal, and Floreana, hawks were extirpated primarily due to hunting and the depletion of food resources [1,2,5]. Introduced species played a significant role in this decline, as they contributed to the depletion of native food sources [6]. Considering this, while introduced species may now provide an alternative food source for the hawk, suggesting that they benefit them must be approached with caution, given their historical role in ecosystem disruption. While all of these questions remain unresolved, the observation does contribute with valuable insights not only into the ecology of B. galapagoensis, but also into the broader dynamics of food webs in the Galapagos ecosystem. We highlight the need for further monitoring both cat and hawk populations on the islands. Further research is needed to determine whether events such as this one are isolated or part of a broader, emerging pattern that could influence invasive species management and predator-prey dynamics across the Galapagos.

We would like to thank Mgs. Danny Rueda Cordova and Dr. Luis Ortiz Catedral for their contributions to the Pink Iguana Conservation Program. We also thank Galápagos Conservancy for awarding the grant that made this project possible. Additionally, we are grateful to the Red Ecuatoriana de Herpetología (REH) for organizing the I Congreso Ecuatoriano de Herpetología, a place for collaboration and strengthening science in Ecuador, where the authors met and were able to share information and develop this manuscript.

Conceptualization: Elias Viteri-Basso (EVB); Data curation: Johannes Ramirez Kastdalen (JRK) and EVB; Formal analysis: EVB and JRK; Funding acquisition: Jorge Carrión-Tacuri (JCT) and JRK; Investigation: EVB; Methodology: JRK and EVB; Resources: JRK and JCT; Visualization: EVB; Writing-original draft: EVB; Writing-review and editing: EVB, JRK, and JCT.

For this work, the author(s) did not use generative or AI-assisted tools in the preparation of the manuscript; therefore, no such use is declared.

No data were used in this study.

The authors declare no conflict of interest.