Abstract
We assessed the prevalence of alien species as a driver of recent extinctions in five major taxa (plants, amphibians, reptiles, birds and mammals), using data from the IUCN Red List. Our results show that alien species are the second most common threat associated with species that have gone completely extinct from these taxa since AD 1500. Aliens are the most common threat associated with extinctions in three of the five taxa analysed, and for vertebrate extinctions overall.
Keywords: non-native species, amphibian, bird, mammal, plant, reptile
1. Introduction
Biological diversity naturally varies substantially over space and time, but this variation is ultimately the product of just four key processes: speciation, immigration, emigration and extinction [1]. These processes are increasingly being perturbed, and subsequently shaped, by the actions of humans [2]. Human exploitation of species and appropriation of land and water have greatly increased extinction rates in recent centuries relative to the background levels in the fossil record [3,4]. Human activities have also greatly increased the rates of immigration [5,6], by deliberately or accidentally transporting and introducing large numbers of species to areas beyond normal biogeographic barriers to their spread, where they may establish viable populations (here termed alien) [7]. Alien species have had a range of impacts documented in their new environments [8], and there are well-documented examples of native species that have been driven extinct by aliens [9,10]. Indeed, alien species are often cited as the second most common cause of recent and ongoing extinctions (since AD 1500) after habitat destruction (i.e. for the USA, see [11]).
Human activities are clearly elevating extinction rates, but it is contentious how much of that elevation is due to direct effects of exploitation and appropriation, and how much arises indirectly as a consequence of our elevation of species' immigration. As a consequence, the role of aliens as important drivers of past extinctions and/or current extinction risk has been disputed [12–14], the evidence underpinning the ‘second commonest cause’ claim has been questioned [15], and indeed, speciation by aliens has even been argued to lead to a net increase in diversity in some taxa in some regions [16]. These arguments form part of a narrative that the detrimental effects of alien species have been overemphasized [14–18].
Some of the arguments about the impacts of alien species [12,19] have been based on data on extinction, and extinction risk, from the IUCN (International Union for Conservation of Nature) Red List. This is a dynamic resource, for which regular updates add ever greater and more accurate information on the conservation status of increasing numbers of species. Here, we revisit this resource to assess the current state of knowledge on associated causes of extinction in five of the best-studied taxa worldwide. Specifically, we assess the frequency with which alien species are cited under the causes of loss of plant, amphibian, reptile, bird and mammal species considered to be extinct (category EX) and extinct in the wild (category EW).
2. Methods
The Red-Listing process identifies and classifies 12 major threats to the persistence of species (IUCN threat classification scheme v. 3.0) [20]. We compiled data on the total numbers of described, extinct and possibly extinct (category EX), and extinct in the wild (category EW) plant, amphibian, reptile, bird and mammal species from the 2015 IUCN Red List with threat information (n = 247) [21]. We maintained the same classification scheme as IUCN except for threat category number 8 (‘Invasive and other problematic species, genes & diseases’), which we subdivided into alien species (i.e. invasive non-native (alien) species and diseases) and other problematic species (i.e. native species or species of unknown origin).
We ascribed threats to each EX and EW species according to the information in the IUCN Red list. For instance, if a species is recorded as threatened by biological resource use according to IUCN, it was given a ‘1’ in the data matrix; otherwise, it received a value of ‘0’. We repeated this process for the 12 external threats listed. This allows that species may have been affected by multiple threats. For each taxonomic group, we calculated the number of EX + EW species for which alien species are cited as a threat among species with known threats. This allowed us to calculate the proportion of all threats that relate to alien species. We classified EX and EW species either as an island endemic or mainland species using the IUCN Red List database (www.iucnredlist.org; accessed June 2015). Geographical range distributions were also used to assign each EX and EW species to one of 12 biogeographic regions (figure 1).
All analyses were conducted in R v. R 3.2.0 [22].
3. Results
A total of 215 species from the five taxa considered here are recorded as extinct in the IUCN Red List, and a further 32 are extinct in the wild (table 1). Alien species are listed as a cause for 58% of all EX, and 31% of all EW species for which a cause is given (see electronic supplementary material, table S1, for the species list). These percentages vary across taxa (table 1). Aliens are less important as an extinction (EX + EW) driver for plants (27%, 15/55 species) than for vertebrates (62%, 119/192), and indeed, they are listed as a driver for more than half of the extinctions in each of the vertebrate taxa analysed (table 1). Extinct species commonly have more than one threat identified (mean = 1.90), but aliens compose from 14% (plants) to 45% (mammals) of all listed threats for a given taxon, and 28.51% of all threats listed (table 1). For those species with just a single extinction (EX + EW) driver listed, this driver is alien species for 17% of plants, no amphibians, 25% of reptiles, 27% of birds and 47% of mammals.
Table 1.
taxon | status | species | Salien | %Salien | threats | %T |
---|---|---|---|---|---|---|
plants | EX | 32 | 9 | 28 | 2 (±1) | 14 |
EW | 23 | 6 | 26 | 2 (±1) | 15 | |
amphibians | EX | 15 | 10 | 67 | 4 (±2) | 19 |
EW | 2 | 1 | 50 | 4 (±1) | 13 | |
reptiles | EX | 6 | 4 | 67 | 2 (±1) | 29 |
EW | 1 | 0 | 0 | 1 | 0 | |
birds | EX | 119 | 71 | 60 | 2 (±1) | 35 |
EW | 4 | 3 | 75 | 3 (±2) | 27 | |
mammals | EX | 43 | 30 | 70 | 2 (±1) | 45 |
EW | 2 | 0 | 0 | 3 (±1) | 0 | |
total | 247 | 134 | 54 | 2 (±1) | 29 |
For all four vertebrate taxa, the top three threats ranked by the percentage of extinct (EX) species impacted are agriculture and aquaculture, alien species and biological resource use (overexploitation; table 2). Alien species is the top-ranked threat for extinct amphibians, reptiles and mammals. For plants, residential and commercial development is one of the top three threats, displacing alien species down to fourth (table 2). In total, 58% of EX species (125/215) in the five taxa analysed were listed as impacted by biological resource use, which is the highest ranked overall. Alien species comes in a close second, with 58% of extinct species (124/215) impacted, whereas agriculture and aquaculture ranks a distant third (61/215; 28%).
Table 2.
taxon | status | rank 1 | rank 2 | rank 3 | rank 4 |
---|---|---|---|---|---|
plants | threat | AG | BR | UR | AS |
% (number) | 59 (19) | 44 (14) | 34 (11) | 28 (9) | |
amphibians | threat | AS | AG | BR | PO |
% (number) | 67 (10) | 60 (9) | 53 (8) | 47 (7) | |
reptiles | threat | AS | BR | AG | |
% (number) | 67 (4) | 50 (3) | 33 (2) | ||
birds | threat | BR | AS | AG | SM |
% (number) | 70 (83) | 60 (71) | 17 (20) | 8 (10) | |
mammals | threat | AS | BR | AG | SM |
% (number) | 70 (30) | 40 (17) | 26 (11) | 7 (3) |
Most recorded extinctions (EX + EW) in the taxa analysed for which alien species are a listed driver have concerned island endemic species (86%, 115/134 species; electronic supplementary material, figure S1). All EX + EW plants and reptiles were island endemic species, whereas 27% of amphibians, 93% of birds and 80% of mammals were island endemics. Nevertheless, there are eight amphibian, five bird and six mammal species with continental mainland populations for which alien species are listed as an extinction driver (electronic supplementary material, figure S1). Most of the species that aliens have helped to drive extinct have been lost from Australia, New Zealand and other locations in the Pacific (figure 1). However, most amphibian losses have been from the Americas (figure 1).
4. Discussion
Our results confirm that, for the five major taxa analysed here, alien species are the second most common threat associated with species that have gone completely extinct since AD 1500. They are relegated into second place by biological resource use, by the smallest possible margin (125 versus 124 species affected). In fact, alien species are the most common threat associated with extinctions in three of the five taxa analysed, and for vertebrate extinctions overall. Alien species are listed as having contributed to the extinction of more than half of all the species in our analyses (EX + EW), and to almost two-thirds of the vertebrates. Around 30 alien taxa are implicated, including ‘bees’, rainbow trout Oncorhynchus mykiss, ‘tortoises’, great horned owls Bubo virginianus and guinea pigs Cavia porcellus, but especially rats Rattus spp. and cats Felis catus for extinct birds and mammals, diseases (especially chytridiomycosis and avian malaria) for extinct amphibians and birds, and herbivores (especially goats Capra hircus, sheep Ovis aries and European rabbits Oryctolagus cuniculus) and alien plants for extinct plant species [21]. Extinctions since AD 1500 are only a small proportion of the vertebrate species lost in the period following human expansion out of Africa [23,24]. However, well-typified fossil assemblages reveal a number of extinctions that are most likely to have been caused by alien species [25]. Thus, alien-driven extinctions are unlikely to be just a modern phenomenon.
The IUCN Red List represents probably the best available data on the factors associated with recent extinctions, and on current extinction risk, and we have taken the causes of extinction it records at face value. It remains possible that the Red List may systematically overestimate the impact of alien species, if these are not the causal agents of extinction, but symptoms of the real causes (e.g. habitat destruction) [13]. We doubt that any such overestimation is substantial. Alien species may often act in synergy with other extinction drivers—and indeed, most extinctions are associated with more than one—but the impacts of alien species have been well documented in multiple contexts [9,26]. Further, habitat loss, harvesting and human disturbance co-occur randomly with impact from aliens as threats to vertebrates on the IUCN Red List [27]. One could argue equally convincingly that the impacts of alien species may in many cases be underestimated, as many interactions (especially between alien parasites and native hosts) [28] are very hard to detect. Nevertheless, in many cases, the true contribution of alien species versus other extinction drivers will never be known, given that the impacted species concerned are now extinct.
Alien species are not just a problem for island species. While most of the recent extinctions associated with alien species relate to island endemics (figure 1), 14% of alien-related extinctions have concerned species with mainland populations. Alien species are a significant concern for mainland species currently threatened with extinction. In particular, the highest absolute number of species threatened by alien species are located in South American countries [29]. In summary, our results do not support arguments that the detrimental effects of alien species have been overemphasized [14–18].
Supplementary Material
Acknowledgements
We thank Barry Brook and John Alroy for inviting us to write this paper, and three anonymous referees for helpful comments.
Data accessibility
The data on which this paper is based are freely available on the IUCN Red List website (www.redlist.org). A list of extinct species is given in the electronic supplementary material.
Authors' contributions
C.B., P.C. and T.M.B. conceived the study; C.B. compiled and analysed the data; C.B., P.C. and T.M.B. wrote the paper. The authors agree to be accountable for all aspects of the work reported.
Competing interests
The authors have no competing interests.
Funding
C.B. was supported by an AXA Fellowship. P.C. was supported by an ARC Future Fellowship (FT0914420) and by an ARC Discovery grant (DP140102319). T.M.B. had no funding for this work.
References
- 1.Cracraft J. 1994. Species diversity, biogeography, and the evolution of biotas. Am. Zool. 34, 33–47. ( 10.1093/icb/34.1.33) [DOI] [Google Scholar]
- 2.Vitousek PM, D'Antonio CM, Loope LL, Rejmánek M, Westbrooks R. 1997. Introduced species: a significant component of human-caused global change. N. Z. J. Ecol. 21, 1–16. [Google Scholar]
- 3.Lawton JH, May RM. 1995. Extinction rates. Oxford, UK: Oxford University Press. [Google Scholar]
- 4.Ceballos G, Ehrlich PR, Barnosky AD, García A, Pringle RM, Palmer TM. 2015. Accelerated modern human-induced species losses: entering the sixth mass extinction. Sci. Adv. 1, e1400253.abstract ( 10.1126/sciadv.1400253) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Gaston KJ, Jones AG, Hanel C, Chown SL. 2003. Rates of species introduction to a remote oceanic island. Proc. R. Soc. Lond. B 270, 1091–1098. ( 10.1098/rspb.2003.2332) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Hulme PE. 2009. Trade, transport and trouble: managing invasive species pathways in an era of globalization. J. Appl. Ecol. 46, 10–18. ( 10.1111/j.1365-2664.2008.01600.x) [DOI] [Google Scholar]
- 7.Blackburn TM, Pyšek P, Bacher S, Carlton JT, Duncan RP, Jarošík V, Wilson JRU, Richardson DM. 2011. A proposed unified framework for biological invasions. Trends Ecol. Evol. 26, 333–339. ( 10.1016/j.tree.2011.03.023) [DOI] [PubMed] [Google Scholar]
- 8.Vilà M, et al. 2011. Ecological impacts of invasive alien plants: a meta-analysis of their effects on species, communities and ecosystems. Ecol. Lett. 14, 702–708. ( 10.1111/j.1461-0248.2011.01628.x) [DOI] [PubMed] [Google Scholar]
- 9.Courchamp F, Chapuis J-L, Pascal M. 2003. Mammal invaders on islands: impact, control and control impact. Biol. Rev. 78, 347–383. ( 10.1017/S1464793102006061) [DOI] [PubMed] [Google Scholar]
- 10.Clavero M, Brotons L, Pons P, Sol D. 2009. Prominent role of invasive species in avian biodiversity loss. Biol. Conserv. 142, 2043–2049. ( 10.1016/j.biocon.2009.03.034) [DOI] [Google Scholar]
- 11.Wilcove DS, Rothstein D, Dubow J, Phillips A, Losos E. 1998. Quantifying threats to imperiled species in the United States. BioScience 48, 607–615. ( 10.2307/1313420) [DOI] [Google Scholar]
- 12.Gurevitch J, Padilla DK. 2004. Are invasive species a major cause of extinctions? Trends Ecol. Evol. 19, 470–474. ( 10.1016/j.tree.2004.07.005) [DOI] [PubMed] [Google Scholar]
- 13.Didham RK, Tylianakis JM, Hutchison MA, Ewers RM, Gemmell NJ. 2005. Are invasive species the drivers of ecological change? Trends Ecol. Evol. 20, 470–474. ( 10.1016/j.tree.2005.07.006) [DOI] [PubMed] [Google Scholar]
- 14.Thomas CD, Palmer G. 2015. Non-native plants add to the British flora without negative consequences for native diversity. Proc. Natl Acad. Sci. USA 112, 4387–4392. ( 10.1073/pnas.1423995112) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Thompson K. 2014. Where do camels belong? The story and science of invasive species. London, UK: Profile Books. [Google Scholar]
- 16.Thomas CD. 2013. The Anthropocene could raise biological diversity. Nature 502, 7 ( 10.1038/502007a) [DOI] [PubMed] [Google Scholar]
- 17.Davis MA, et al. 2011. Don't judge species on their origins. Nature 474, 153–154. ( 10.1038/474153a) [DOI] [PubMed] [Google Scholar]
- 18.Brown JH, Sax D. 2004. An essay on some topics concerning invasive species. Austral. Ecol. 29, 530–536. ( 10.1111/j.1442-9993.2004.01340.x) [DOI] [Google Scholar]
- 19.Clavero M, Garciá-Berthou E. 2005. Invasive species are a leading cause of animal extinctions. Trends Ecol. Evol. 20, 110 ( 10.1016/j.tree.2005.01.003) [DOI] [PubMed] [Google Scholar]
- 20.Salafsky N, et al. 2008. A standard lexicon for biodiversity conservation: unified classifications of threats and actions. Conserv. Biol 22, 897–911. ( 10.1111/j.1523-1739.2008.00937.x) [DOI] [PubMed] [Google Scholar]
- 21.IUCN. 2015. The IUCN red list categories and criteria: version 3.1. Gland, Switzerland: International Union for Conservation of Nature. [Google Scholar]
- 22.R Core Team. 2014. R: a language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing; See http://www.R-project.org/. [Google Scholar]
- 23.Martin PS, Klein R. 1984. Quaternary extinctions: a prehistoric revolution. Tucson, AZ: University of Arizona Press. [Google Scholar]
- 24.Turvey ST (ed.).. 2009. Holocene extinctions. Oxford, UK: Oxford University Press. [Google Scholar]
- 25.Holdaway RN. 1999. Introduced predators and avifaunal extinction in New Zealand. In Extinctions in near time: causes, contexts, and consequences (ed. MacPhee RDE. ), pp. 189–238. New York, NY: Kluwer Academic/Plenum. [Google Scholar]
- 26.Pyšek P, Blackburn TM, Garcia-Berthou E, Perglová I, Rabitsch W. 2016. Displacement and local extinction of native and endemic species. In Impact of biological invasions on ecosystem services (eds Vila M, Hulme PE, Ruiz G). Berlin, Germany: Springer. [Google Scholar]
- 27.Berglund H, Järemo J, Bengtsson G. 2013. Associations of invasive alien species and other threats to IUCN Red List species (Chordata: vertebrates). Biol. Inv. 15, 1169–1180. ( 10.1007/s10530-012-0359-x) [DOI] [Google Scholar]
- 28.Blackburn TM, Ewen J. 2016. Parasites as drivers and passengers of human-mediated biological invasions. EcoHealth. ( 10.1007/s10393-015-1092-6) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Bellard C, Genovesi P, Jeschke JM. 2016 Global patterns in threats to vertebrates by biological invasions. Proc. R. Soc. B 283, 20152454 ( 10.1098/rspb.2015.2454) [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
The data on which this paper is based are freely available on the IUCN Red List website (www.redlist.org). A list of extinct species is given in the electronic supplementary material.