Latitudinal patterns in the diet of Andean condor (Vultur gryphus) in Chile: Contrasting environments influencing feeding behavior

https://doi.org/10.1016/j.scitotenv.2020.140220Get rights and content

Highlights

  • Anthropized environments alter availability of resources for Andean condors.

  • Little evidence as to how condor's diet vary along their large latitudinal range

  • Introduced domestic and exotic species are common Andean condor prey across Chile.

  • Condors in anthropized areas use C4-based food from landfills/corn-fed livestock.

  • Anthropic subsidies may help stabilize populations, also enhance mortality risks.

Abstract

Human-dominated environments alter the availability and quality of resources for many species, especially for scavengers that have large home ranges and plastic foraging behaviors that enable them to exploit novel resources. Along the western slope of the Andes, the modification of natural landscapes have resulted in significant declines in native prey, the introduction of non-native species, and an increase in the availability of anthropogenic resources. These factors have likely influenced the resources available to Andean condors (Vultur gryphus), however, data are lacking as to how condor's diet vary along their large latitudinal range. We evaluated differences in Andean condor diet along a ~2500 km latitudinal gradient in Chile from the heavily modified Central zone (32–34°S) to the more pristine Austral zone (44–56°S). We assessed diet composition through the identification of prey remains in condor pellets, and carbon and nitrogen isotope analysis of condor feathers and their primary prey identified from pellet analysis. Our results identified medium- and large-bodied domesticated mammals (ungulates) and introduced exotic species (lagomorphs) as common prey across the study area. Condors from the Central zone had the largest isotopic niche width, probably related to consumption of anthropogenic resources with distinctly high carbon isotope values indicative of C4-based foods likely acquired from landfills or corn-fed livestock. Isotopic niches for condors from the Southern and Austral zones almost completely overlapped. Andean condor diet is strongly influenced by local conditions determining differential access to prey sources. The high dependence of Andean condors on livestock across a large geographical area, and landfills in more (sub)urban areas, may help stabilize their populations via anthropogenic resources subsidies. Long-term dependence on such resources, however, may have health costs including contaminant exposure and greater mortality risk. These data will help identify potential threats related to resource availability and use, and better inform management and conservation decisions.

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;

References (76)

  • F. Ballejo et al.

    Trophic niche overlap among scavengers in Patagonia supports the condor-vulture competition hypothesis

    Bird Conserv. Int.

    (2017)
  • F. Barbar et al.

    Emerging ecosystems change the spatial distribution of top carnivores even in poorly populated areas

    PLoS One

    (2015)
  • F. Barbar et al.

    Medium-sized exotic prey create novel food webs: the case of predators and scavengers consuming lagomorphs

    PeerJ

    (2016)
  • E. Bonnet et al.

    A software tool for simple and partial mantel tests

    J. Stat. Softw.

    (2002)
  • G. Ceballos

    Mammal population losses and the extinction crisis

    Science

    (2002)
  • C. Chehébar et al.

    Guía para el reconocimiento microscópico de los pelos de mamíferos de la patogonia

    Doana Acta Vertebrata

    (1989)
  • R.K. Colwell et al.

    Models and estimators linking individual-based and sample-based rarefaction, extrapolation and comparison of assemblages

    J. Plant Ecol.

    (2012)
  • A. Cortés-Avizanda et al.

    Supplementary feeding and endangered avian scavengers: benefits, caveats, and controversies

    Front. Ecol. Environment

    (2016)
  • M.G. Day

    Identification of hair and feather remains in the gut and faeces of stoats and weasels

    J. Zool.

    (1966)
  • J. Del Hoyo et al.

    New world vultures to guineafowl

  • C. Deygout et al.

    Impact of food predictability on social facilitation by foraging scavengers

    Behav. Ecol.

    (2010)
  • J.A. Donázar et al.

    Too sanitary for vultures

    Science

    (2009)
  • J.A. Donázar et al.

    Effects of sex-associated competitive asymmetries on foraging group structure and despotic distribution in Andean condors

    Behav. Ecol. Sociobiol.

    (1999)
  • O. Duriez et al.

    Intra-specific competition in foraging Griffon Vultures gyps fulvus: 2. The influence of supplementary feeding management

    Bird Study

    (2012)
  • E.C. Ellis et al.

    Anthropogenic transformation of the biomes, 1700 to 2000: anthropogenic transformation of the biomes

    Glob. Ecol. Biogeogr.

    (2010)
  • F. Falabella et al.

    El maíz (Zea mays) en el mundo prehispánico de Chile central

    Latin Am. Antiq.

    (2008)
  • R. García-Jiménez et al.

    Drivers of daily movement patterns affecting an endangered vulture flight activity

    BMC Ecol.

    (2018)
  • B.A. González et al.

    Unveiling current guanaco distribution in Chile based upon niche structure of phylogeographic lineages: Andean puna to subpolar forests

    PLoS One

    (2013)
  • M.O. Hill

    Correspondence analysis: a neglected multivariate method

    Appl. Stat.

    (1974)
  • INE

    Síntesis Agropecuaria: Encuestas intercensales agropecuarias 2017–2018

    (2018)
  • IUCN

    The IUCN red list of threatened species. Version 2019-3

  • A.L. Jackson et al.

    Comparing isotopic niche widths among and within communities: SIBER - Stable Isotope Bayesian Ellipses in R: Bayesian isotopic niche metrics

    J. Anim. Ecol.

    (2011)
  • A.H. Jahren et al.

    Carbon and nitrogen stable isotopes in fast food: signatures of corn and confinement

    Proc. Nat. Acad. Sci.

    (2008)
  • F.M. Jaksic et al.

    The conservation status of raptors in the Metropolitan Region, Chile

    J. Raptor Res.

    (2001)
  • F.M. Jaksic et al.

    Invaders without frontiers: cross-border invasions of exotic mammals

    Biol. Invasions

    (2002)
  • C.J. Kendall et al.

    African vultures don’t follow migratory herds: scavenger habitat use is not mediated by prey abundance

    PLoS One

    (2014)
  • C.M. Kurle et al.

    Discrimination factors for stable isotopes of carbon and nitrogen in blood and feathers from chicks and juveniles of the California condor

    Condor

    (2013)
  • S.A. Lambertucci

    Biología y conservación del cóndor andino (Vultur gryphus) en Argentina

    Hornero

    (2007)
  • Cited by (20)

    • High incidence of plastic debris in Andean condors from remote areas: Evidence for marine-terrestrial trophic transfer

      2023, Environmental Pollution
      Citation 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).

    • Foraging in the Anthropocene: Feeding plasticity of an opportunistic predator revealed by long term monitoring

      2021, Ecological Indicators
      Citation 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).

    View all citing articles on Scopus
    View full text