Literature DB >> 28533560

Saving the World's Terrestrial Megafauna.

William J Ripple1, Guillaume Chapron1, José Vicente López-Bao1, Sarah M Durant1, David W Macdonald1, Peter A Lindsey1, Elizabeth L Bennett1, Robert L Beschta1, Jeremy T Bruskotter1, Ahimsa Campos-Arceiz1, Richard T Corlett1, Chris T Darimont1, Amy J Dickman1, Rodolfo Dirzo1, Holly T Dublin1, James A Estes1, Kristoffer T Everatt1, Mauro Galetti1, Varun R Goswami1, Matt W Hayward1, Simon Hedges1, Michael Hoffmann1, Luke T B Hunter1, Graham I H Kerley1, Mike Letnic1, Taal Levi1, Fiona Maisels1, John C Morrison1, Michael Paul Nelson1, Thomas M Newsome1, Luke Painter1, Robert M Pringle1, Christopher J Sandom1, John Terborgh1, Adrian Treves1, Blaire Van Valkenburgh1, John A Vucetich1, Aaron J Wirsing1, Arian D Wallach1, Christopher Wolf1, Rosie Woodroffe1, Hillary Young1, Li Zhang1.   

Abstract

Entities:  

Year:  2016        PMID: 28533560      PMCID: PMC5421308          DOI: 10.1093/biosci/biw092

Source DB:  PubMed          Journal:  Bioscience        ISSN: 0006-3568            Impact factor:   8.589


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From the late Pleistocene to the Holocene and now the so-called Anthropocene, humans have been driving an ongoing series of species declines and extinctions (Dirzo et al. 2014). Large-bodied mammals are typically at a higher risk of extinction than smaller ones (Cardillo et al. 2005). However, in some circumstances, terrestrial megafauna populations have been able to recover some of their lost numbers because of strong conservation and political commitment, as well as human cultural changes (Chapron et al. 2014). Indeed, many would be in considerably worse predicaments in the absence of conservation action (Hoffmann et al. 2015). Nevertheless, most mammalian megafauna face dramatic range contractions and population declines. In fact, 59% of the world's largest carnivores (more than or equal to 15 kilograms, n = 27) and 60% of the world's largest herbivores (more than or equal to 100 kilograms, n = 74) are classified as threatened with extinction on the International Union for the Conservation of Nature (IUCN) Red List (supplemental tables S1 and S2). This situation is particularly dire in sub-Saharan Africa and Southeast Asia, home to the greatest diversity of extant megafauna (figure 1). Species at risk of extinction include some of the world's most iconic animals—such as gorillas, rhinos, and big cats (figure 2 top row)—and, unfortunately, they are vanishing just as science is discovering their essential ecological roles (Estes et al. 2011). Here, our objectives are to raise awareness of how these megafauna are imperiled (species in tables S1 and S2) and to stimulate broad interest in developing specific recommendations and concerted action to conserve them.
Figure 1.

A richness map of (a) the number of megafaunal species, (b) the number of declining megafauna species, and (c) the number of threatened megafaunal species in their native ranges. Megafauna are defined as terrestrial large carnivores (more than 15 kilograms) and large herbivores (more than 100 kilograms). Threatened includes all species categorized as Vulnerable, Endangered, or Critically Endangered on the IUCN Red List (see supplemental tables).

Figure 2.

Photographic examples of threatened megafauna. Top row left to right: photos of well-known species, including the Western gorilla (Gorilla gorilla) (CR), black rhino (Diceros bicornis) (CR), and Bengal tiger, (Panthera tigris tigris) (EN). Bottom row left to right: photos of lesser-known species, including the African wild ass (Equus africanus) (CR), Visayan warty pig (Sus cebifrons) (CR), and banteng (Bos javanicus) (EN). Photo credits: Julio Yeste, Four Oaks, Dave M. Hunt, Mikhail Blajenov, KMW Photography, and Kajornyot.

A richness map of (a) the number of megafaunal species, (b) the number of declining megafauna species, and (c) the number of threatened megafaunal species in their native ranges. Megafauna are defined as terrestrial large carnivores (more than 15 kilograms) and large herbivores (more than 100 kilograms). Threatened includes all species categorized as Vulnerable, Endangered, or Critically Endangered on the IUCN Red List (see supplemental tables). Photographic examples of threatened megafauna. Top row left to right: photos of well-known species, including the Western gorilla (Gorilla gorilla) (CR), black rhino (Diceros bicornis) (CR), and Bengal tiger, (Panthera tigris tigris) (EN). Bottom row left to right: photos of lesser-known species, including the African wild ass (Equus africanus) (CR), Visayan warty pig (Sus cebifrons) (CR), and banteng (Bos javanicus) (EN). Photo credits: Julio Yeste, Four Oaks, Dave M. Hunt, Mikhail Blajenov, KMW Photography, and Kajornyot. Megafauna provide a range of distinct ecosystem services through top-down biotic and knock-on abiotic processes (Estes et al. 2011). Many megafauna function as keystone species and ecological engineers, generating strong cascading effects in the ecosystems in which they occur. These species also provide important economic and social services. For example, ecotourism is the fastest growing subsector of tourism in developing countries (UNEP 2013), and megafauna are a major draw for these tourists. Besides contributing considerable revenue to conservation, wildlife-based tourism can contribute significantly to education, economies, job creation, and human livelihoods. Many of the surviving mammalian megafauna remain beset by long-standing and generally escalating threats of habitat loss, persecution, and exploitation (Ripple et al. 2014, 2015). Large mammals are extremely vulnerable to these threats because of their large area requirements, low densities (particularly for carnivores), and relatively “slow” life-history traits (Wallach et al. 2015). Various anthropogenic forces such as deforestation, agricultural expansion, increasing livestock numbers, and other forms of human encroachment have severely degraded critical habitat for megafauna by increased fragmentation or reduced resource availability. Although some species show resilience by adapting to new scenarios under certain conditions (Chapron et al. 2014), livestock production, human population growth, and cumulative land-use impacts can trigger new conflicts or exacerbate existing ones, leading to additional declines. According to the Food and Agriculture Organization, as of 2014, there were an estimated 3.9 billion ruminant livestock on Earth compared with approximately 8.5 million individuals of 51 of the 74 species of wild megaherbivores for which population estimates are available within their native ranges (table S2), a magnitude difference of approximately 400 times. The current depletion of megafauna is also due to overhunting and persecution: shooting, snaring, and poisoning by humans ranging from individuals to governments, as well as by organized criminals and terrorists (Darimont et al. 2015). Megafauna are killed for meat and body parts for traditional medicine and ornaments or because of actual or perceived threats to humans, their crops, or livestock. Meat and body parts are sold locally, sold to urban markets, or traded regionally and internationally. Striking instances include the slaughter of thousands of megafauna, such as African elephants (Loxodonta africana) for their ivory, rhinoceroses for their horns, and tigers (Panthera tigris) for their body parts. In addition, many lesser-known megafauna species (figure 2, bottom row) are now imperiled (tables S1 and S2). Most of the world's megaherbivores remain poorly studied, and this knowledge gap makes conserving them even more difficult (Ripple et al. 2015). Under a business-as-usual scenario, conservation scientists will soon be busy writing obituaries for species and subspecies of megafauna as they vanish from the planet. In fact, this process is already underway: eulogies have been written for Africa's western black rhinoceros (Diceros bicornis longipes) and the Vietnamese subspecies of the Javan rhinoceros (Rhinoceros sondaicus annamiticus, IUCN 2015). Epitaphs will probably soon be needed for the kouprey (Bos sauveli), last seen in 1988; and the northern white rhinoceros (Ceratotherium simum cottoni), which now numbers three individuals (IUCN 2015). The Sumatran rhino (Dicerorhinus sumatrensis) is already extinct in the wild in Malaysia and is very close to extinction in Indonesia, with the population collapsing during the last 30 years from over 800 to fewer than 100 (table S2). The Javan rhino (Rhinoceros sondaicus) is down to a single population of approximately 58 in a single reserve (table S2). The Critically Endangered Bactrian camel (Camelus ferus) and African wild ass (Equus africanus) are not far behind. Even in protected areas, megafauna are increasingly under assault. For example, in West and Central Africa, several large carnivores (including lions, Panthera leo; African wild dogs, Lycaon pictus; and cheetahs, Acinonyx jubatus) have experienced recent severe range contractions and have declined markedly in many protected areas (IUCN 2015). Although many of the general causes and mechanisms of declines are well identified and recognized, this understanding has not translated into adequate conservation action. Some of the existing mammal-prioritization schemes could be incorporated into a comprehensive global strategy for conserving the largest mammals (Rondinini et al. 2011). Increasing prioritization and political will to conserve megafauna—and actions to restore or reintroduce them in areas where they have declined or been extirpated (such as plans to reintroduce scimitar-horned oryx into Chad and to rehabilitate the entire Gorongosa ecosystem in Mozambique)—are urgently needed. We suggest that the problem has two parts: (1) a need to further and more effectively implement, expand, and refine current interventions at relevant scales and (2) a need for large-scale policy shifts and global increases in funding for conservation to alter the framework and ways in which people interact with wildlife. In order to save declining species, there is a need to increase global conservation funding by at least an order of magnitude (McCarthy et al. 2012). Without such a transformation, there is a risk that many of the world's most iconic species may not survive to the twenty-second century. We must not go quietly into this impoverished future. Rather, we believe it is our collective responsibility as scientists who study megafauna to act to prevent their decline. We therefore present a call to the broader international community to join together in conserving the remaining terrestrial megafauna (see declaration in box 1).

A declaration to save the world's terrestrial megafauna.

We conservation scientists Acknowledge that most of the terrestrial megafauna species are threatened with extinction and have declining populations. Some megafauna species that are not globally threatened nonetheless face local extinctions or have Critically Endangered subspecies. Appreciate that “business as usual” will result in the loss of many of the Earth's most iconic species. Understand that megafauna have ecological roles that directly and indirectly affect ecosystem processes and other species throughout the food web; failure to reverse megafaunal declines will disrupt species interactions, with negative consequences for ecosystem function; biological diversity; and the ecological, economic, and social services that these species provide. Realize that megafauna are epitomized as a symbol of the wilderness, exemplifying the public's engagement in nature, and that this is a driving force behind efforts to maintain the ecosystem services they can provide. Recognize the importance of integrating and better aligning human development and biodiversity conservation needs through the engagement and support of local communities in developing countries. Propose that funding agencies and scientists increase conservation research efforts in developing countries, where most threatened megafauna occur. Specifically, there is a need to increase the amount of research directed at finding solutions for the conservation of megafauna, especially for lesser-known species. Request the help of individuals, governments, corporations, and nongovernmental organizations to stop practices that are harmful to these species and to actively engage in helping to reverse declines in megafauna. Strive for increased awareness among the global public of the current megafauna crisis using traditional media as well as social media and other networking approaches. Seek a new and comprehensive global commitment and framework for conserving megafauna. The international community should take necessary action to prevent mass extinction of the world's megafauna and other species. Urge the development of new funding mechanisms to transfer the current benefits accrued through the existence values of megafauna into tangible payments to support research, conservation actions, and local people who bear the cost of living with wildlife in the places where highly valued megafauna must be preserved. Advocate for interdisciplinary scientific interchange between nations to improve the social and ecological understanding of the drivers of the decline of megafauna and to increase the capacity for megafauna science and conservation. Recommend the reintroduction and rehabilitation, following accepted IUCN guidelines, of degraded megafauna populations whenever possible, the ecological and economic importance of which is evidenced by a growing number of success stories, from Yellowstone's wolves (Canis lupus) and the Père David's deer (Elaphurus davidianus) in China to the various megafauna species of Gorongosa National Park in Mozambique. Affirm an abiding moral obligation to protect the Earth's megafauna.

From declaration to action

Social and political commitment to provide sufficient protection across the vast landscapes needed for the conservation of the world's megafauna is increasingly required. International frameworks and conventions such as the Convention on Biological Diversity (CBD), the Convention on the Conservation of Migratory Species of Wild Animals (CMS), and the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) have had some success in safeguarding species. However, the decisions of these conventions are not always binding, and they will require substantially increased political will and financial support if they are to be effective in the critical task of securing the survival of the world's megafauna. Some regional instruments such as the CMS Gorilla Agreement and the Global Tiger Initiative incorporate environmental or biodiversity commitments and are playing a growing role in protecting biodiversity. International agreements are often well placed for enforcing regional frameworks for megafauna; examples include the African Elephant Action Plan and the regional conservation strategy for cheetahs and African wild dogs. However, the implementation of such initiatives requires financial resources and capacity that are seldom available at those locations where the highest diversity of megafauna remains (figure 1). Therefore, the onus is on developed countries, which have long ago lost most of their megafauna, to not only embark on conservation and restoration programs on their own lands but also support conservation initiatives in those nations where diverse megafauna still persist. For conservation efforts to be successful, actions should be taken at all levels by authorities who have the public interest in mind and who work to secure the continued existence of these species. Successfully conserving megafauna requires bold social, political, and financial commitments from nations around the world. Through understanding the value and importance of local human needs and by combining international financial support with a coordinated multilateral approach to conservation, it may be possible to rescue megafauna from the brink of extinction. As biologists, ecologists, and conservation scientists, we are mindful that none of our arguments are new and that our prescriptions are far easier to write out than to accomplish. However, our objective in presenting them together here is to demonstrate a consensus of opinion amongst the global community of scientists who study and conserve these animals, thereby emphasizing to the wider world the gravity of the problem. Our hope is that this declaration, with the proposed actions and list of signatories, will attract the public and media attention that this issue requires to galvanize opinion, catalyze action, and establish new funding mechanisms. Comprehensive actions to save these iconic wildlife species will help to curb an extinction process that appears to have begun with our ancestors in the late Pleistocene. In the supplemental material for this article, this entire paper is available in six other languages: Spanish, Chinese, French, Portuguese, Malay (Bahasa Malaysia), and Thai. Click here for additional data file.
  9 in total

1.  Multiple causes of high extinction risk in large mammal species.

Authors:  Marcel Cardillo; Georgina M Mace; Kate E Jones; Jon Bielby; Olaf R P Bininda-Emonds; Wes Sechrest; C David L Orme; Andy Purvis
Journal:  Science       Date:  2005-07-21       Impact factor: 47.728

Review 2.  Status and ecological effects of the world's largest carnivores.

Authors:  William J Ripple; James A Estes; Robert L Beschta; Christopher C Wilmers; Euan G Ritchie; Mark Hebblewhite; Joel Berger; Bodil Elmhagen; Mike Letnic; Michael P Nelson; Oswald J Schmitz; Douglas W Smith; Arian D Wallach; Aaron J Wirsing
Journal:  Science       Date:  2014-01-10       Impact factor: 47.728

Review 3.  Reconciling global mammal prioritization schemes into a strategy.

Authors:  Carlo Rondinini; Luigi Boitani; Ana S L Rodrigues; Thomas M Brooks; Robert L Pressey; Piero Visconti; Jonathan E M Baillie; Daniele Baisero; Mar Cabeza; Kevin R Crooks; Moreno Di Marco; Kent H Redford; Sandy A Andelman; Michael Hoffmann; Luigi Maiorano; Simon N Stuart; Kerrie A Wilson
Journal:  Philos Trans R Soc Lond B Biol Sci       Date:  2011-09-27       Impact factor: 6.237

Review 4.  Trophic downgrading of planet Earth.

Authors:  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
Journal:  Science       Date:  2011-07-15       Impact factor: 47.728

5.  The difference conservation makes to extinction risk of the world's ungulates.

Authors:  Michael Hoffmann; J W Duckworth; Katharine Holmes; David P Mallon; Ana S L Rodrigues; Simon N Stuart
Journal:  Conserv Biol       Date:  2015-04-27       Impact factor: 6.560

6.  Financial costs of meeting global biodiversity conservation targets: current spending and unmet needs.

Authors:  Donal P McCarthy; Paul F Donald; Jörn P W Scharlemann; Graeme M Buchanan; Andrew Balmford; Jonathan M H Green; Leon A Bennun; Neil D Burgess; Lincoln D C Fishpool; Stephen T Garnett; David L Leonard; Richard F Maloney; Paul Morling; H Martin Schaefer; Andy Symes; David A Wiedenfeld; Stuart H M Butchart
Journal:  Science       Date:  2012-10-11       Impact factor: 47.728

7.  HUMAN IMPACTS. The unique ecology of human predators.

Authors:  Chris T Darimont; Caroline H Fox; Heather M Bryan; Thomas E Reimchen
Journal:  Science       Date:  2015-08-21       Impact factor: 47.728

Review 8.  Defaunation in the Anthropocene.

Authors:  Rodolfo Dirzo; Hillary S Young; Mauro Galetti; Gerardo Ceballos; Nick J B Isaac; Ben Collen
Journal:  Science       Date:  2014-07-25       Impact factor: 47.728

9.  Recovery of large carnivores in Europe's modern human-dominated landscapes.

Authors:  Guillaume Chapron; Petra Kaczensky; John D C Linnell; Manuela von Arx; Djuro Huber; Henrik Andrén; José Vicente López-Bao; Michal Adamec; Francisco Álvares; Ole Anders; Linas Balčiauskas; Vaidas Balys; Péter Bedő; Ferdinand Bego; Juan Carlos Blanco; Urs Breitenmoser; Henrik Brøseth; Luděk Bufka; Raimonda Bunikyte; Paolo Ciucci; Alexander Dutsov; Thomas Engleder; Christian Fuxjäger; Claudio Groff; Katja Holmala; Bledi Hoxha; Yorgos Iliopoulos; Ovidiu Ionescu; Jasna Jeremić; Klemen Jerina; Gesa Kluth; Felix Knauer; Ilpo Kojola; Ivan Kos; Miha Krofel; Jakub Kubala; Saša Kunovac; Josip Kusak; Miroslav Kutal; Olof Liberg; Aleksandra Majić; Peep Männil; Ralph Manz; Eric Marboutin; Francesca Marucco; Dime Melovski; Kujtim Mersini; Yorgos Mertzanis; Robert W Mysłajek; Sabina Nowak; John Odden; Janis Ozolins; Guillermo Palomero; Milan Paunović; Jens Persson; Hubert Potočnik; Pierre-Yves Quenette; Georg Rauer; Ilka Reinhardt; Robin Rigg; Andreas Ryser; Valeria Salvatori; Tomaž Skrbinšek; Aleksandar Stojanov; Jon E Swenson; László Szemethy; Aleksandër Trajçe; Elena Tsingarska-Sedefcheva; Martin Váňa; Rauno Veeroja; Petter Wabakken; Manfred Wölfl; Sybille Wölfl; Fridolin Zimmermann; Diana Zlatanova; Luigi Boitani
Journal:  Science       Date:  2014-12-19       Impact factor: 47.728

  9 in total
  20 in total

1.  Extinction risk is most acute for the world's largest and smallest vertebrates.

Authors:  William J Ripple; Christopher Wolf; Thomas M Newsome; Michael Hoffmann; Aaron J Wirsing; Douglas J McCauley
Journal:  Proc Natl Acad Sci U S A       Date:  2017-09-18       Impact factor: 11.205

2.  Rethinking megafauna.

Authors:  Marcos Moleón; José A Sánchez-Zapata; José A Donázar; Eloy Revilla; Berta Martín-López; Cayetano Gutiérrez-Cánovas; Wayne M Getz; Zebensui Morales-Reyes; Ahimsa Campos-Arceiz; Larry B Crowder; Mauro Galetti; Manuela González-Suárez; Fengzhi He; Pedro Jordano; Rebecca Lewison; Robin Naidoo; Norman Owen-Smith; Nuria Selva; Jens-Christian Svenning; José L Tella; Christiane Zarfl; Sonja C Jähnig; Matt W Hayward; Søren Faurby; Nuria García; Anthony D Barnosky; Klement Tockner
Journal:  Proc Biol Sci       Date:  2020-03-04       Impact factor: 5.349

3.  Canopy structure drives orangutan habitat selection in disturbed Bornean forests.

Authors:  Andrew B Davies; Marc Ancrenaz; Felicity Oram; Gregory P Asner
Journal:  Proc Natl Acad Sci U S A       Date:  2017-07-18       Impact factor: 11.205

4.  Population dynamics and threats to an apex predator outside protected areas: implications for carnivore management.

Authors:  Samual T Williams; Kathryn S Williams; Bradley P Lewis; Russell A Hill
Journal:  R Soc Open Sci       Date:  2017-04-19       Impact factor: 2.963

5.  Freshwater Megafauna: Flagships for Freshwater Biodiversity under Threat.

Authors:  Savrina F Carrizo; Sonja C Jähnig; Vanessa Bremerich; Jörg Freyhof; Ian Harrison; Fengzhi He; Simone D Langhans; Klement Tockner; Christiane Zarfl; William Darwall
Journal:  Bioscience       Date:  2017-09-20       Impact factor: 8.589

6.  Conservation implications for dingoes from the maternal and paternal genome: Multiple populations, dog introgression, and demography.

Authors:  Kylie M Cairns; Sarah K Brown; Benjamin N Sacks; J William O Ballard
Journal:  Ecol Evol       Date:  2017-10-19       Impact factor: 2.912

7.  Loss of protozoan and metazoan intestinal symbiont biodiversity in wild primates living in unprotected forests.

Authors:  Barbora Pafčo; Heidi C Hauffe; Claudia Barelli; Mattia Manica; Francesco Rovero; Roberto Rosà; David Modrý
Journal:  Sci Rep       Date:  2020-07-02       Impact factor: 4.379

8.  Toward reliable population estimates of wolves by combining spatial capture-recapture models and non-invasive DNA monitoring.

Authors:  J V López-Bao; R Godinho; C Pacheco; F J Lema; E García; L Llaneza; V Palacios; J Jiménez
Journal:  Sci Rep       Date:  2018-02-01       Impact factor: 4.379

9.  The paradoxical extinction of the most charismatic animals.

Authors:  Franck Courchamp; Ivan Jaric; Céline Albert; Yves Meinard; William J Ripple; Guillaume Chapron
Journal:  PLoS Biol       Date:  2018-04-12       Impact factor: 8.029

10.  Moose at their bioclimatic edge alter their behavior based on weather, landscape, and predators.

Authors:  Mark A Ditmer; Ron A Moen; Steve K Windels; James D Forester; Thomas E Ness; Tara R Harris
Journal:  Curr Zool       Date:  2017-07-28       Impact factor: 2.624

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