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Until recently, large apex consumers were ubiquitous across the globe and had been for millions of years. The loss of these animals may be humankind’s most pervasive influence on nature. Although such losses are widely viewed as an ethical and aesthetic problem, recent research reveals extensive cascading effects of their disappearance in marine, terrestrial, and freshwater ecosystems worldwide. This empirical work supports long-standing theory about the role of top-down forcing in ecosystems but also highlights the unanticipated impacts of trophic cascades on processes as diverse as the dynamics of disease, wildfire, carbon sequestration, invasive species, and biogeochemical cycles. These findings emphasize the urgent need for interdisciplinary research to forecast the effects of trophic downgrading on process, function, and resilience in global ecosystems.
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www.sciencemag.org/cgi/content/full/333/6040/301/DC1
Supporting Online Material for
Trophic Downgrading of Planet Earth
James A. Estes,* John Terborgh, Justin S. Brashares, Mary E. Power, Joel Berger,
William J. Bond, Stephen R. Carpenter, Timothy E. Essington, Robert D. Holt, Jeremy B. C.
Jackson, Robert J. Marquis, Lauri Oksanen, Tarja Oksanen, Robert T. Paine, Ellen K.
Pikitch, William J. Ripple, Stuart A. Sandin, Marten Scheffer, Thomas W. Schoener,
Jonathan B. Shurin, Anthony R. E. Sinclair, Michael E. Soulé, Risto Virtanen, David A.
Wardle
*To whom correspondence should be addressed. E-mail: jestes@ucsc.edu
Published 15 July 2011, Science 333, 301 (2011)
DOI: 10.1126/science.1205106
This PDF file includes:
Table S1
References
1
SOM Table 1. Examples of regime shifts in terrestrial, freshwater, and marine ecosystems resulting from the loss or addition of
large-bodied vertebrates. Those based on linkages across 3 or more species are noted with an asterisk
Ecosystem Perturbation/Location Response Reference
Terrestrial
Arctic tundra Extinction of megaherbivores/Siberia Conversion of steppe to tundra (43)
*Arctic tundra Introduction of arctic fox/Aleutian Islands Conversion of grass-land to tundra (47, 74)
* Boreal forest Self-introduction of moose/Isle Royale Reduction of balsam fir (63)
* Temperate forest Extirpation of wolf/Yellowstone National
Park Overbrowsing of aspen, cottonwood, willow (75, 76)
*Temperate forest Restoration of wolf/ Yellowstone National
Park Recovery of riparian vegetation (25, 77)
2
Table 1 (continued)
*Temperate forest Extirpation of large predators/Europe,
Japan, and eastern United States Eruption of cervid populations, overbrowsing,
altered forest composition (78-80)
*Temperate forest Loss of cougar/Zion National Park Eruption of mule deer, loss of riparian
vegetation and associated biodiversity, altered
channel morphology
(61)
Temperate forest Introduction of red deer/New Zealand Overbrowsing, altered composition of forests (81)
*Tropical forest Loss of jaguar, cougar, Harpy
eagle/Venezuela Explosion of herbivores, suppression of tree
recruitment (82)
*Tropical forest Decimation of large birds and mammals by
hunting/neotropics Altered tree recruitment (83, 84)
*Tropical savanna Decimation of ungulates by Rinderpest
epidemic/Serengeti Increased extent and frequency of fires (30, 85)
Tropical savanna Recovery of white rhino/South Africa Appearance of grazing lawns, reduced
incidence of fire (86)
Subtropical bush Predator control of dingo/Australia Mesopredator release/ proliferation of exotic
mesopredators and herbivores/reduced
biodiversity
(87)
3
Table 1 (continued)
Freshwater
*Tropical river Exclosures and enclosures/Panama Fishing birds protect algae from grazing catfish (88, 89)
* Temperate stream Exclosures and enclosures/Oklahoma Piscivorous bass protect algae from grazing
minnows (69)
*Temperate stream Predator introduction/New Zealand Invasive trout protect algae from grazing
insects (90, 91)
*Boreal stream Predator introduction/Hokkaido Invasive trout protect algae from grazing
insects (92)
* Fresh water lake Remove piscivore trophic level Reduced water clarity, increase in
phytoplankton and primary production,
increased N:P ratio, increased response to
nutrient inputs, net flux of CO2 into the lake
(26, 93)
*Fresh water lake Introduction of non-native top piscivore Reorganization of fish community, species loss (94)
4
Table 1 (continued)
Marine
*Temperate subtidal Sea otter recovery Recovery of kelp forest (95)
*Temperate subtidal Overharvest of cod Urchin outbreak; collapse of kelp forests (96)
*Temperate estuarine Decimation of apex sharks Outbreak of cow-nosed rays, shellfish decline (19)
Tropical coastal Reduced grazing by green turtles Reduced recycling of turtle grass (97)
*Coral reefs
Overfishing Reduction in crustose coralline algae resulting
in reduced reef calcification, (98)
*Coral reefs Overfishing followed by disease Reef overgrowth by algae (99)
Continental shelf Overharvest of cod Shrimp increases (100)
*Open ocean (North Pacific) Pink salmon fluctuation zooplankton decline, chlorophyll increase (101)
*Open ocean (North Atlantic) Overharvest of cod Planktivorous fish, zooplankton, chlorophyll (102)
Table 1 (continued)
*Open ocean (North Atlantic) Overharvest of cod Sprat increase, zooplankton decline (103, 104)
*Open ocean (North Pacific) Overharvest of great whales Killer whale diet shift, pinniped population
declines (105)
*Open ocean (Southern Ocean) Overharvest of great whales Krill increase, adelie penguin diet shift (106)
*Open ocean (Black Sea) Overfishing Planktivorous fish, gelatanous plankton,
zooplankton, phytoplankton (107)
5
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... Similarly to other apex predators, the loss of raptors, i.e. trophic downgrading, affects a plethora of other species such as prey that are released from predation and overall alters ecosystem services (e.g. disease spreading, Estes et al. 2011). Raptors are thus commonly targeted by conservation translocations (Griffith et al. 1989;Fischer & Lindenmayer 2000;Seddon et al. 2005) The hen harrier (Circus cyaneus) ...
... In conservation science, increased awareness of the complexity of delivering effective conservation measures has led to an increased considerations of the human dimensions through means of social research (Bennett et al. 2017a). Nevertheless, after more than a century of conservation translocations and 30 years after the definition of reintroduction biology as a discipline largely based on project management (Seddon et al. 2007 (Estes et al. 2011). Therefore, conservation translocations have often targeted raptors (Griffith et al. 1989;Fischer & Lindenmayer 2000;Seddon et al. 2005) In this review, we explore the research literature on both conservation and nonconservation translocations and also reintroductions reported in the IUCN Global Reintroduction Perspectives (GRPs). ...
... Birds of prey (raptors) form a polyphyletic group of birds that includes species such as eagles, hawks, vultures and owls(McClure et al. 2019). These represent an optimal choice for several reasons.Raptors have fundamental roles in socio-ecological systems(Estes et al. 2011;Donázar et al. 2016). Specifically, these carry cultural values associated, for example, with religious, aesthetic, and recreational experiences as well as essential providers of ecosystem services(Donázar et al. 2016). ...
Thesis
Conservation science is a relatively young crisis discipline facing a rapid and increasing global loss of biodiversity with anthropogenic causes. Despite its constant evolution, conservation science is still riddled with challenges and uncertainties related to understanding and measuring success as well as achieving effective multidisciplinarity. Conservation translocations, the human mediated movements of wildlife species for conservation benefits, embody conservation science paradigms and the challenge of delivering positive outputs. Specifically, a wide range of socio-ecological factors and difficulties shape the outcomes of conservation translocations and reintroduction biology - the recent sub-discipline born to study these measures - is still struggling in engaging effectively with decision-making and considering their socio-ecological dimensions in an integrated way. Here, we investigated conservation translocations in their ecological and social dimensions, seeking to build a comprehensive understanding of how diverse factors can synergically shape translocation outcomes and, hence, success. We focused on conservation translocations targeting birds of prey (hereafter raptors), given their role in socio-ecological systems, their often-endangered status and, therefore, their resulting inclusion in many conservation translocations. In particular, we studied the proposed reintroduction of hen harriers Circus cyaneus to southern England (hereafter the Southern reintroduction), a locally endangered species at the centre of a long-standing conservation conflict in the United Kingdom. We developed a multidimensional framework to study conservation translocations, where social and ecological dimensions are addressed at the individual and population levels. We used a multi-pronged approach based on the literature on raptor translocations as well as qualitative and quantitative data related to socio-political and ecological aspects of the Southern reintroduction. We found that success is yet to be fully conceptualised and investigated in a holistic way in the literature on raptor translocations. Rare definitions and assessments of success are biased towards ecological considerations even though the challenges most frequently reported by practitioners are socio-political. We advised on the need for a new evaluation framework, that considers the multiple dimensions of translocations while also acknowledging the subjective component of success definition and evaluation. Using Discourse Network Analysis, we identified characteristics and dynamics of the stakeholder debate on the conservation and management of hen harriers in the UK in national newspaper media. The debate is characterised by the presence of vocal stakeholders and has become more polarised over time. Stakeholder coalitions diverge, especially over a conservation measure (i.e. the brood management scheme), but also share common discursive ground in the form of emotional reactions associated with hen harriers and the acknowledged need for collaboration. Through means of participant observation and semi-structured interviews, we disclosed generally favourable perspectives of local stakeholders in Salisbury Plain on the Southern reintroduction. We found key aspects of the engagement practice such as types of engagement activities, timing, and team composition shape engagement and social processes. We showed how these aspects are linked to the positive transformative potential of the Southern reintroduction for the conservation conflict in the UK. We explored the movement behaviour of hen harriers from the reintroduction source population in France. Using Hidden Markov Models (HMMs) and Integrated Step Selection Analysis (ISSA) to analyse, we determined land cover preferences. These showed an overall preference for arable land with differences based on behavioural states (resident and dispersal) and sex. Arable land is also associated with hen harriers transitioning to a resident state. Finally, we developed a population viability modelling approach aimed at simulating socio-ecological realism. By using this novel individual-based model, we showed the potential viability and spatial distribution of the reintroduced population of hen harriers under increasingly informed and complex scenarios where female demographic traits and farming operations significantly affect population establishment. Our findings provide decision-makers, practitioners, and stakeholders involved in the Southern reintroduction with essential information that can be used to inform current and future stages of this conservation programme. Most importantly, we provided conservation practitioners and researchers with a novel multidimensional framework that can be used in conservation programmes, including but not limited to translocations, to investigate their socio-ecological dimensions at different scales. Overall, this work contributes to a better understanding of the roles of both ecological and social drivers in conservation translocations, concluding with the recommendation that redefining reintroduction biology to translocation science would result in a more representative acknowledgement of the broad range of factors influencing translocation success.
... Además, son señalados como especies indicadoras de la calidad de su hábitat (Crooks, 2002;Benchimol, 2016;Botero-Cañola et al., 2018); su ausencia puede provocar un crecimiento descontrolado de las poblaciones de herbívoros, aumentando la presión de herbivoría sobre la vegetación. Esta sobreexplotación de vegetación altera el hábitat y reduce la disponibilidad de recursos para otras especies, lo que desencadena una serie de impactos a nivel del paisaje, incluyendo cambios en la estructura y uso del hábitat, y la disminución de la biodiversidad (Di Bitetti, 2008;Beschta & Ripple, 2009;Estes et al., 2011;Ripple & Beschta, 2012;Ripple et al., 2014;Wallach et al., 2015). ...
... Por otro lado, las presas directas de los depredadores tope tienden a incrementar sus poblaciones debido a la reducción en la presión de depredación (Pérez-Irineo & Santos-Moreno, 2015;Amaya, 2020;Burgos et al., 2023), ambos procesos afectan de manera significativa el equilibrio de los ecosistemas. Este fenómeno se ha observado en regiones de África, Australia, Europa Occidental, y Norte América, tras la desaparición de los leones (Panthera leo), leopardos (Panthera pardus), dingos (Canis dingo), lince euroasiático (Lynx lynx), lobo gris (Canis lupus), oso grizzly (Ursus arctos) y puma (Puma concolor) (Estes et al., 2011;Ripple et al., 2014). ...
... La falta de registros de jaguar y puma en nuestra área de estudio, a pesar de que han sido reportados en los últimos 6 años al norte de la carretera Las Varas-Puerto Vallarta (Illescas, 2019;Cortés, 2022), podría explicar los elevados valores de la abundancia relativa de sus presas principales (pecarí de collar, coatí y mapache), lo cual es consistente con estudios previos que sugieren que la falta de depredadores tope puede generar un aumento en las poblaciones de presas (Estes et al., 2011;Ripple et al., 2014). ...
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... For instance, agriculture transforms complex, mature forests into pastures or grain fields that, eventually, may return to secondary forests which are structurally simpler than mature forests (Colorado Zuluaga & Rodewald, 2015). In aquatic or terrestrial habitats, top-predator extirpation may have cascading effects resulting in a loss of the large autotrophic organisms that structure space (Estes et al., 2011). In oceans, eutrophication, acidification, bottom trawling and dredging all tend to destroy the complex structure provided by benthic habitats such as coral reefs (National Research Council, 2002;Rogers et al., 2014). ...
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... Previous camera trapping data in Bluegums indicate that feral cats and potoroos overlap spatially and temporally, and images have recorded potoroo predation by cats (Miritis et al. 2020). Top-down population regulation is well documented in other species and ecosystems (Estes et al. 2011;Ritchie and Johnson 2009) and, given that cats fill the apex predator role on French Island (Miritis et al. 2020), it is possible that our observations follow a similar pattern. ...
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... Apex predators play an important role in maintaining biodiversity and ecosystem function (Ripple et al. 2014), and the depletion of their populations can have wide-ranging ecosystem consequences (Estes et al. 2011;Ripple et al. 2016;Van Cleave et al. 2018). Due to the high metabolic demands driven by endothermy and body size, large carnivores require access to abundant prey and expansive habitats (Cardillo et al. 2004;Ripple et al. 2016). ...
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