Latitudinal patterns in the diet of Andean condor (Vultur gryphus) in Chile: Contrasting environments influencing feeding behavior
Graphical abstract
Introduction
Land-use activities have transformed >50% of the Earth's surface to provide humans access to critical natural resources and ecosystem services. The clearing of natural forest and grassland ecosystems for forestry, agricultural, and livestock production, and more recently for (sub)urban and industrial expansion (Ellis et al., 2010), has influenced the availability and quality of resources on which many species rely (Barbar et al., 2015). In particular, predators (Newsome et al., 2015) and scavengers (Cortés-Avizanda et al., 2016) have been disproportionately impacted by both direct (e.g., overhunting) and indirect (e.g., habitat loss) anthropogenic influences. Vulture populations in particular have been severely affected as a result of negative interactions with humans (Ogada et al., 2012) and currently 52% of vulture species are threatened with extinction worldwide (IUCN, 2020).
Large-bodied soaring scavengers such as vultures have extensive home ranges and can efficiently search large areas to locate patchily distributed prey (Barbar et al., 2015). In natural environments, seasonal variation in mortality and movement of potential prey strongly influences the territory and movement of scavengers (Kendall et al., 2014; Newsome et al., 2015; Lambertucci et al., 2018; García-Jiménez et al., 2018). In anthropized environments, domestic herbivores as well as introduced wild herbivores change the species composition and abundance of prey for scavengers (Jaksic et al., 2002; Vázquez, 2002), which results in close and in some cases obligatory ecological relationships between introduced herbivores and scavengers (Barbar et al., 2016). Population declines of natural prey, the presence of veterinary drugs in carcasses, sanitary regulations, and livestock management strategies can alter prey availability, and may have contributed to large-scale declines in Old World vultures (Donázar et al., 2009; Margalida et al., 2014, Margalida et al., 2017; Buechley and Şekercioğlu, 2016; Arrondo et al., 2018). While livestock may benefit scavengers by providing resource subsidies (Jaksic et al., 2002; Vázquez, 2002), these sources of prey have also been identified as high-risk resources that may impact scavenger health and by extension lead to increased mortality risk (Blanco et al., 2017). Although livestock carcass dumps, landfills, and even fisheries bycatch have become a novel and relatively predictable food source for scavengers (Cortés-Avizanda et al., 2016; Tauler-Ametller et al., 2017), the use of these resources may be associated with either beneficial and detrimental health effects (Plaza and Lambertucci, 2017).
The Andean condor (Vultur gryphus) is the largest avian scavenger in South America and occurs along the Andes mountain range from ~5°N to 55°S latitude (Del Hoyo et al., 1994). In most areas in this distribution, condor populations have declined due to poisoning, hunting, and decreases in resource availability. Only in the southernmost margin of its range does condor population size appear to be more dense (Lambertucci, 2010; Pavez, 2012) and stable (Jaksic et al., 2001). Like other scavengers, the Andean condor has had to adapt to a changing environment and to modify its foraging behavior and diet (Lambertucci et al., 2009, Lambertucci et al., 2018). Historically, Andean condors consumed a combination of marine resources sourced from the productive Humboldt Current (Lambertucci et al., 2018) and native terrestrial resources such as guanacos (Lama guanicoe) and lesser rheas (Rhea pennata) (Lambertucci et al., 2009). In addition to dramatic declines in native fauna (Ceballos, 2002), a suite of terrestrial mammals (e.g., red and fallow deer, wild boar) were introduced to Chile and Argentina more than a century ago (Jaksic et al., 2002) and are considered to be an ecological plague that have negative impacts on agriculture, livestock, and native vegetation and fauna (Vázquez, 2002). Some introduced species such as the lagomorphs like European hares (Lepus europaeus) and rabbits (Oryctolagus cuniculus) may also provide an indirect ecological benefit by serving as an alternate source of prey to large native predators and by extension decreasing predation pressure on native herbivores (Jaksic et al., 2002). These two lagomorph species, along with the introduced red deer (Cervus elaphus) and wild boar (Sus scrofa) are important dietary components of Andean condors inhabiting some regions of Chile and Argentina (Lambertucci et al., 2009; Perrig et al., 2016; Ballejo et al., 2017; Pavez et al., 2019). At present, Andean condors feed primarily on introduced terrestrial mammals (e.g., ungulates and lagomorphs) that are the most abundant sources of carrion in rural environments (Lambertucci et al., 2009; Ballejo et al., 2017; Pavez et al., 2019). Nevertheless, livestock production over the past 50 years in Chile has declined up to 40%, and along with the intensification and technological advances of livestock production strategies has led to a decrease in the availability of carrion to Andean condor populations, especially in the central area of the country (INE, 2018). While Andean condors have historically avoided habitats extensively modified by human activities (Wallace and Temple, 1988), the recent decline in ranching activities and the scarcity of native prey in central Chile (Pavez, 2012) have changed their feeding behavior to include more reliable sources of anthropogenic foods in landfills and (sub)urban areas (Pavez et al., 2019).
Although the diet of Andean condors has been studied previously (Wallace and Temple, 1987; Lambertucci et al., 2009; Perrig et al., 2016; Pavez et al., 2019), all of these efforts focused on a single population in a relatively small area of the species large latitudinal range. The objective of our study was to characterize Andean condor diet across a wide latitudinal range of >2500 km (from ~32 to 56°S) along the western slope of the Andes to assess spatial variation in prey composition that may relate to varying levels of anthropogenic influence. We use faunal analysis of condor pellets collected from 20 roosting sites coupled with carbon (δ13C) and nitrogen (δ15N) isotope analysis of condor feathers and potential prey sources. This work provides a better understanding of the role that different sources of prey are playing in maintaining condor populations across Chile, which currently hosts ~70% of the global populations of this iconic species. These data may also help identify potential threats related to local resource availability and used to guide management decisions for Andean condor conservation strategies.
Section snippets
Study area
Our study was conducted in continental Chile from 32°10′ S to 56°30′ S covering a latitudinal range of ~2500 km and altitudes between ~50 and ~2100 m above sea level, conditions that determine a wide variety of climates and landscapes and contrasting situations in relation to anthropogenic activities (Sánchez and Morales, 2002), availability and diversity of food resources for the Andean condor. We defined a priori three zones within the study area considering two main criteria. First, each
Pellet analysis
We identified 39 different items in 343 pellets collected from nine selected communal roosts (three roosts per zone). Twenty-nine items were animal remains (mammals, birds, and insects), seven anthropogenic waste items, two plant types (digested and undigested) and one rock fragment (Table 1). Pellets collected from the Central and Southern zones had lower prey species richness (15 species) than those from the Austral zone (26 species). Likewise, the highest Shannon's diversity values for
Discussion
Our results identified medium and large-sized domesticated mammals (cows and sheep) and introduced exotic species (lagomorphs) as common prey for condors across Chile (Fig. 3). We also found differences in diet among the three latitudinal zones considered in our study. Condors in the Central zone consumed a higher proportion of C4-based anthropogenic resources in comparison to those from the Southern or Austral zones, while extensive use of marine resources was limited to a few individuals in
Conclusions
Our results show that condor's diet varies across along a latitudinal gradient along the western slope of Andes and are strongly influenced by the availability of native versus anthropogenic resources. We also observed a high degree of dietary plasticity among individuals within a single region that appears to be related to age-based hierarchies and access to relatively predictable anthropogenic resources found in lowland agricultural areas (livestock) and/or landfills (refuse), especially in
Credit authorship contribution statement
Melanie Duclos: Conceptualization, Methodology, Formal analysis, Investigation, Writing - original draft, Writing - review & editing, Visualization, Supervision, Project administration. Pablo Sabat: Methodology, Formal analysis, Investigation, Writing - original draft, Writing - review & editing, Visualization, Supervision. Seth D. Newsome: Methodology, Formal analysis, Investigation, Writing - original draft, Writing - review & editing, Visualization, Supervision. Eduardo F. Pavez:
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
We thank specially to José Díaz Tavié, Cristián Saucedo and Catalina Silva for providing valuable logistical support. To all volunteers for their assistance during field and laboratory work (Cristián Álvarez, Rody Álvarez, Alejandro Galilea, Cristián Concha, Mauricio Montt, Patricio Herrera, Fernanda Salvo and Daniela Fuentes). To Antonella Bernucci for graphical abstract design and Pamela Pérez for maps design. To National Museum of Natural History, Santiago; Quilpué Zoo - Valparaíso Region;
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2023, Environmental PollutionCitation Excerpt :The Andean condor (Vultur gryphus), an emblematic and vulnerable vulture species of South America, is experiencing population decline because of diverse human disturbances (Plaza and Lambertucci, 2020). In recent years, some populations of this species have been exposed to plastic debris in Chile, especially when foraging in rubbish dumps (Duclos et al., 2020). In contrast, when Andean condors forage in natural and semi natural areas in Argentina, within or close to protected areas, the occurrence of plastic is less common (Ballejo et al., 2021).
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2021, Ecological IndicatorsCitation Excerpt :For instance, wildlife exploitation of anthropogenic food subsidies (i.e., food generated by human activities that becomes available for wildlife) is one of the main factors driving the current ecology and population dynamics of a wide range of opportunistic species worldwide (Rose and Polis, 1998; Kuijper et al., 2016; Table 1). A common trait among opportunistic species is trophic plasticity (i.e., the ability of organisms to modify their diet in response to fluctuating environmental resources; Zhang et al., 2019; Duclos et al., 2020), which facilitates the exploitation of anthropogenic food subsidies shortly after they become available in the environment. Opportunistic species efficiently exploit these resources because most of them are predictable over space and time, (e.g., landfill waste, fishing discards, meat industry waste, crop residues, bird feeders, etc.; Table 1).