ArticlePDF Available

Abstract

The oft-repeated claim that Earth's biota is entering a sixth " mass extinction " depends on clearly demonstrating that current extinction rates are far above the " background " rates prevailing in the five previous mass extinctions. Earlier estimates of extinction rates have been criticized for using assumptions that might overestimate the severity of the extinction crisis. We assess, using extremely conservative assumptions, whether human activities are causing a mass extinction. First, we use a recent estimate of a background rate of 2 mammal extinctions per 10,000 species per 100 years (that is, 2 E/MSY), which is twice as high as widely used previous estimates. We then compare this rate with the current rate of mammal and vertebrate extinctions. The latter is conservatively low because listing a species as extinct requires meeting stringent criteria. Even under our assumptions, which would tend to minimize evidence of an incipient mass extinction, the average rate of vertebrate species loss over the last century is up to 114 times higher than the background rate. Under the 2 E/MSY background rate, the number of species that have gone extinct in the last century would have taken, depending on the vertebrate taxon, between 800 and 10,000 years to disappear. These estimates reveal an exceptionally rapid loss of biodiversity over the last few centuries, indicating that a sixth mass extinction is already under way. Averting a dramatic decay of biodiversity and the subsequent loss of ecosystem services is still possible through intensified conservation efforts, but that window of opportunity is rapidly closing.
ENVIRONMENTAL SCIENCES
Accelerated modern humaninduced species
losses: Entering the sixth mass extinction
Gerardo Ceballos,
1
* Paul R. Ehrlich,
2
Anthony D. Barnosky,
3
Andrés García,
4
Robert M. Pringle,
5
Todd M. Palmer
6
The oft-repeated claim that Earths biota is entering a sixth mass extinctiondepends on clearly demonstrating that
current extinction rates are far above the backgroundrates prevailing in the five previous mass extinctions. Earlier
estimates of extinction rates have been criticized for using assumptions that might overestimate the severity of the
extinction crisis. We assess, using extremely conservative assumptions, whether human activities are causing a mass
extinction. First, we use a recent estimate of a background rate of 2 mammal extinctions per 10,000 species per
100 years (that is, 2 E/MSY), which is twice as high as widely used previous estimates. We then compare this rate
with the current rate of mammal and vertebrate extinctions. The latter is conservatively low because listing a
species as extinct requires meeting stringent criteria. Even under our assumptions, which would tend to minimize
evidence of an incipient mass extinction, the average rate of vertebrate species loss over the last century is up to
114 times higher than the background rate. Under the 2 E/MSY background rate, the number of species that have
gone extinct in the last century would have taken, depending on the vertebrate taxon, between 800 and 10,000
years to disappear. These estimates reveal an exceptionally rapid loss of biodiversity over the last few centuries,
indicating that a sixth mass extinction is already under way. Averting a dramatic decay of biodiversity and the
subsequent loss of ecosystem services is still possible through intensified conservation efforts, but that window
of opportunity is rapidly closing.
INTRODUCTION
The loss of biodiversity is one of the most critical current environmental
problems, threatening valuable ecosystem services and human well-
being (17). A growing body of evidence indicates that current species
extinction rates are higher than the pre-human background rate (815),
with hundreds of anthropogenic vertebrate extinctions documented in
prehistoric and historic times (1623). For example, in the islands of
tropical Oceania, up to 1800 bird species (most described in the last
few decades from subfossil remains) are estimated to have gone extinct
in the ~2000 years since human colonization (24). Written records of
extinctions of large mammals, birds, and reptiles date back to the 1600s
and include species such as the dodo (Raphus cucullatus, extinguished
in the 17th century), Stellersseacow(Hydrodamalis gigas, extinguished
in the 18th century), and the Rodrigues giant tortoise (Cylindraspis
peltastes, extinguished in the 19th century). More species extinction
records date from the 19th century and include numerous species of
mammals and birds. Records of extinction for reptiles, amphibians,
freshwater fishes, and other organisms have mainly been documented
since the beginning of the 20th century (14,17). Moreover, even in
species that are not currently threatened, the extirpation of popula-
tionsisfrequentandwidespread,with losses that far outstrip species-
level extinctions (18,25). Population-level extinction directly threatens
ecosystem services and is the prelude to species-level extinction (18).
Here,weanalyzethemodernratesofvertebrate species extinction
and compare them with a recently computed background rate for mam-
mals (7). We specifically addressed the following questions: (i) Are
modern rates of mammal and vertebrate extinctions higher than the
highest empirically derived background rates? (ii) How have modern
extinction rates in mammals and vertebrates changed through time?
(iii) How many years would it have taken for species that went extinct
in modern times to have been lost if the background rate had prevailed?
These are important issues because the uncertainties about estimates of
species loss have led skeptics to question the magnitude of anthropo-
genic extinctions (26) and because understanding the magnitude of
the extinction crisis is relevant for conservation, maintenance of eco-
system services, and public policy.
Until recently, most studies of modern extinction rates have been
based on indirect estimates derived, for example, on the rates of de-
forestation and on species-area relationships (11,14). Problems related
to estimating extinction since 1500 AD (that is, modern extinctions)
have been widely discussed, and the literature reflects broad agreement
among environmental scientists that biases lead to underestimating the
number of species that have gone extinct in the past few centuries
the period during which Homo sapiens truly became a major force on
the biosphere (14,68,14,15). However, direct evaluation is complicated
by uncertainties in estimating the incidence of extinction in historical
time and by methodological difficulties in comparing contemporary ex-
tinctions with past ones.
Less discussed are assumptions underlying the estimation of
background extinction rates. The lower these estimates, the more dra-
matic current extinction rates will appear by comparison. In nearly all
comparisons of modern versus background extinction rates, the
background rate has been assumed to be somewhere between 0.1 and
1 species extinction per 10,000 species per 100 years (equal to 0.1 to
1 species extinction per million species per year, a widely used metric
known as E/MSY). Those estimates reflect the state of knowledge avail-
able from the fossil record in the 1990s (7,913). In a recent analysis,
which charted the stratigraphic ranges of thousands of mammal species,
1
Instituto de Ecología, Universidad Nacional Autónoma de México, México D.F. 04510,
México.
2
Department of Biology, Stanford University, Stanford, CA94304, USA.
3
Department
of Integrative Biology and Museums of Paleontology and Vertebrate Zoology, University of
California, Berkeley, Berkeley, CA 947203140, USA.
4
Estación de Biología Chamela, Instituto
de Biología, Universidad Nacional Autónoma de México, Jalisco 48980, México.
5
Department of Ecology and Evolutionary Biology, Princeton University, Princeton, NJ
08544, USA.
6
Department of Biology, University of Florida, Gainesville, FL 326118525, USA.
*Corresponding author. E-mail: gceballo@ecologia.unam.mx
2015 © The Authors, some rights reserved;
exclusive licensee American Association for
the Advancement of Science. Distributed
under a Creative Commons Attribution
NonCommercial License 4.0 (CC BY-NC).
10.1126/sciadv.1400253
RESEARCH ARTICLE
Ceballos et al. Sci. Adv. 2015;1:e1400253 19 June 2015 1of5
extinction rates were measured over intervals ranging from single years
to millions of years, and the mean extinction rate and variance were
computed for each span of time (7). In this way, the background extinc-
tion rate estimated for mammals was estimated at 1.8 E/MSY, here
rounded upward conservatively to 2 E/MSY (that is, 2 extinctions per
100 years per 10,000 species). This is double the highest previous rough
estimate.
Those previously estimated background rates were primarily derived
from marine invertebrate fossils, which are likely to have greater species
longevity than vertebrates (10,15). Data deficiencies make it impossible
to conduct empirical analyses (as was done for mammals) for non-
mammal terrestrial vertebrates; therefore, we assume the background
rates of other vertebrates to be similar to those of mammals. This sup-
position leads to a more conservative assessment of differences between
current and past extinction rates for the vertebrates as a whole, com-
pared with using the very low background extinction rate derived from
marine invertebrates.
The analysis we present here avoids using assumptions such as loss
of species predicted from species-area relationships, which can suggest
very high extinction rates, and which have raised the possibility that
scientists are alarmistsseeking to exaggerate the impact of humans
on the biosphere (26). Here, we ascertain whether even the lowest esti-
mates of the difference between background and contemporary extinc-
tion rates still justify the conclusion that people are precipitating a global
spasm of biodiversity loss.
RESULTS
Modern and background rates of vertebrate extinctions
Modern rates of vertebrate extinction were much higher than a
background extinction rate of 2 E/MSY. Among the vertebrate taxa
evaluated by the International Union of Conservation of Nature
(IUCN), 338 extinctions have been documented since 1500 [extinct
(EX), Table 1]. An additional 279 species have become either extinct in
the wild(EW) or listed as possibly extinct(PE), totaling 617 verte-
brate species summed over the three categories. Most extinctions have
occurred in the last 114 years (that is, since 1900; Table 1). Our esti-
mated highly conservative(that is, using data for EX species only)
and conservative(that is, by including EX, EW, and PE) modern ex-
tinction rates for vertebrates varied from 8 to 100 times higher than the
background rate (Table 2). This means, for example, that under the 2
E/MSY background rate, 9 vertebrate extinctions would have been
expected since 1900; however, under the conservative rate, 468 more
vertebrates have gone extinct than would have if the background rate
had persisted across all vertebrates under that period. Specifically, these
468 species include 69 mammal species, 80 bird species, 24 reptiles, 146
amphibians, and 158 fish.
Table 1. Numbers of species used in the Table 2 calculations of highly conservativeand conservativemodern extinction rates based on
the IUCN Red List (17). For the highly conservative rates, only species verified as extinct(EX) were included; for the conservative extinction rates,
species in the categories extinct in the wild(EW) and possibly extinct(PE) were also included.
Vertebrate taxon
No. of species, IUCN 2014.3
Highly conservative
rates (EX)
Conservative rates
(EX + EW + PE) No. of species
evaluated by IUCN
Since 1500 Since 1900 Since 1500 Since 1900
Vertebrates 338 198 617 477 59% (39,223)
Mammals 77 35 111 69 100% (5,513)
Birds 140 57 163 80 100% (10,425)
Reptiles 21 8 37 24 44% (4,414)
Amphibians 34 32 148 146 88% (6,414)
Fishes 66 66 158 158 38% (12,457)
Table 2. Elevation of highly conservativeand conservativemod-
ern vertebrate extinction rates above background rate of 2 E/MSY (see
table S2 for calculations). For each assessment category, two periods are
shown: extinction rates computed from 1500 to the present, and from
1900 to the present.
Animal group
Elevation of modern rates with
respect to expected rates
Highly conservative Conservative
Since 1500 Since 1900 Since 1500 Since 1900
Vertebrates 8 22 15 53
Mammals 14 28 20 55
Birds 13 24 15 34
Reptiles 5 8 8 24
Amphibians 5 22 22 100
Fishes 5 23 12 56
RESEARCH ARTICLE
Ceballos et al. Sci. Adv. 2015;1:e1400253 19 June 2015 2of5
Variation in modern extinction rates through time
Modern extinction rates have increased sharply over the past 200 years
(corresponding to the rise of industrial society) and are considerably
higher than background rates (Fig. 1). Rates of modern extinctions vary
among vertebrate groups (Fig. 1). For example, amphibians, comprising
of ~7300 species, show an accelerating rate of extinction: only 34 extinc-
tions have been documented with a high level of certainty since 1500,
yet >100 species have likely disappeared since 1980 (17,23). This may
not only reflect real trends but also a shortage of data for groups for
which most species are not yet evaluated, such as reptiles and fish
(21,22).
Modern extinctions if background rate had prevailed
Our results indicate that modern vertebrate extinctions that occurred
since 1500 and 1900 AD would have taken several millennia to occur
if the background rate had prevailed. The total number of vertebrate
species that went extinct in the last century would have taken about
800 to 10,000 years to disappear under the background rate of 2 E/MSY
(Fig. 2). The particularly high losses in the last several decades accentu-
ate the increasing severity of the modern extinction crisis.
DISCUSSION
Arguably the most serious aspect of the environmental crisis is the loss
of biodiversitythe other living things with which we share Earth. This
affects human well-being by interfering with crucial ecosystem services
such as crop pollination and water purification and by destroying
humanitys beautiful, fascinating, and culturally important living
companions (4,5,15,2730).
Our analysis shows that current extinction rates vastly exceed
natural average background rates, even when (i) the background rate is
considered to be double previous estimates and when (ii) data on mod-
ern vertebrate extinctions are treated in the most conservative plausible
way. We emphasize that our calculations very likely underestimate the
severity of the extinction crisis because our aim was to place a realistic
lower boundon humanitys impact on biodiversity. Therefore, al-
though biologists cannot say preciselyhow many species there are, or
exactly how many have gone extinct in any time interval, we can con-
fidently conclude that modern extinction rates are exceptionally high,
that they are increasing, and that they suggest a mass extinction under
waythe sixth of its kind in Earths 4.5 billion years of history.
Cumulative extinctions as % of IUCN-evaluated species
1.60
1.40
1.20
1.00
0.80
0.60
0.40
0.20
0
1500-1600 1600-1700 1700-1800 1800-1900 1900-2014
Time interval
Mammals
Birds
Vertebrates
Other vertebrates
Background
A
Cumulative extinctions as % of IUCN-evaluated species
2.50
2.00
1.50
1.00
0.50
0.00
1500-1600 1600-1700 1700-1800 1800-1900 1900-2010
Time interval
Mammals
Vertebrates
Birds
Other vertebrates
Background
B
Fig. 1. Cumulative vertebrate species recorded as extinct or extinct in the wild by the IUCN (2012). Graphs show the percentage of the number of
species evaluated among mammals (5513; 100% of those described), birds (10,425; 100%), reptiles (4414; 44%), amphibians (6414; 88%), fishes (12,457;
38%), and all vertebrates combined (39,223; 59%). Dashed black curve represents the number of extinctions expected under a constant standard
background rate of 2 E/MSY. (A) Highly conservative estimate. (B) Conservative estimate.
Fishes Amphibians Reptiles Birds Mammals Vertebrates
10000
8000
6000
4000
2000
0
Times (years)
Very conservative
Conservative
Fig. 2. Number of years that would have been required for the ob-
served vertebrate species extinctions in the last 114 years to occur un-
der a background rate of 2 E/MSY. Red markers, highly conservative
scenario; blue markers, conservative scenario. Note that for all vertebrates,
the observed extinctions would have taken between 800 to 10,000 years to
disappear, assuming 2 E/MSY. Different classes of vertebrates all show qual-
itatively similar trends.
RESEARCH ARTICLE
Ceballos et al. Sci. Adv. 2015;1:e1400253 19 June 2015 3of5
A final important point is that we focus exclusively on species, ignor-
ing the extirpation of populationsthe units relevant to ecological
functioning and the delivery of ecosystem services (4,5,29). Population
extinction cannot be reliably assessed from the fossil record, precluding
any analysis along the lines of that presented here. Also, although it is
clear that there are high rates of population extinction (18), existing data
aremuchlessreliableandfarhardertoobtainthanthoseforspecies,
which will remain true for the foreseeable future. Likewise, we have not
considered animals other than vertebrates because of data deficiencies.
The evidence is incontrovertible that recent extinction rates are un-
precedented in human history and highly unusual in Earthshistory.
Ouranalysisemphasizesthatourglobal society has started to destroy
species of other organisms at an accelerating rate, initiating a mass ex-
tinction episode unparalleled for 65 million years. If the currently
elevated extinction pace is allowed to continue, humans will soon (in
as little as three human lifetimes) be deprived of many biodiversity
benefits. On human time scales, this loss would be effectively permanent
because in the aftermath of past mass extinctions, the living world took
hundreds of thousands to millions of years to rediversify. Avoiding a
true sixth mass extinction will require rapid, greatly intensified efforts
to conserve already threatened species and to alleviate pressures on their
populationsnotably habitat loss, overexploitation for economic gain,
and climate change (3133). All of these are related to human popula-
tion size and growth, which increases consumption (especially among
the rich), and economic inequity (6). However, the window of oppor-
tunity is rapidly closing.
MATERIALS AND METHODS
To estimate modern extinction rates, we compiled data on the total
number of described species and the number of extinct and possibly
extinct vertebrate species from the 2014 IUCN Red List (17). In the
IUCNs list, extinct species can be viewed as the minimum number
of actual extinctions during recent human history (that is, since 1500)
because it lists species known to be extinct (EX), extinct in the wild
(EW), and possibly extinct (PE, a subcategory within critically
endangeredreserved for species thought to be extinct, but not con-
firmed) (17) (table S1). We used the IUCN data to calculate modern
extinction rates in two ways: (i) we estimate a highly conservative mod-
ern extinction rateby using the data exclusively on species listed as EX,
and (ii) we calculate a conservative extinction rateby including also
both EW and PE species (table S2). Including these latter two categories
recognizes that there is only a slim chance that most of the species in
those categories can reestablish viable populations in their native habi-
tats. In terms of biological impact and the provision of ecosystem
services, we consider EW and PE species to be functionally equivalent
to EX species: even if some individuals still exist, their abundances are
not sufficient to have a substantial influence on ecological function and
processes.
The IUCNs list is considered the authoritative, albeit likely conserv-
ative, assessment of the conservation status of plant and animal species.
About 1.8 million species have been described since 1758 (when the cur-
rent nomenclature system was developed), of which 1.3 million are
animals (3,17). Of these animal species, about 39,223 (of the currently
counted 66,178) vertebrate species have been formally assessed and re-
ported in the 2014 IUCN Red List (17). In the IUCN sample, mammals,
birds, and amphibians have had between 88 and 100% of their known
species evaluated, whereas only 44% of reptiles and 38% of fish species
have been assessed (Table 1). We focus our comparisons on vertebrates
becausetheyarethegroupforwhichthemostreliabledataexist,both
fossil and modern.
To produce conservative comparisons with modern extinctions, we
assumed a background extinction rate of 2 E/MSY as the highest likely
baseline average background extinction rate (7); that is, we should ex-
pect 2 extinctions per 10,000 vertebrate species per 100 years. That
background extinction rate was empirically determined using the ex-
ceptionally good fossil records of mammals, combining extinction counts
from paleontological databases and published literature on the fossil, sub-
fossil, and historical records (7).Usingtheresultinghighbackgroundex-
tinction rate provides a stringent test for assessing whether current modern
extinction rates indicate that a mass extinction event is under way. Previous
estimates of background extinction rates for other taxa are invariably
lower than the mammal-derived estimate of 2 E/MSY used here.
SUPPLEMENTARY MATERIALS
Supplementary material for this article is available at http://advances.sciencemag.org/cgi/content/
full/1/5/e1400253/DC1
Table S1. Definitions of IUCN categories (17) used to assess modern extinction rates.
Table S2. Estimation of modern extinction rates since 1500 and 1900.
REFERENCES AND NOTES
1. G. Ceballos, A. Garcia, P. R. Ehrlich, The sixth extinction crisis: Loss of animal populations
and species. J. Cosmology 8, 18211831 (2010).
2. R. Dirzo, P. H. Raven, Global state of biodiversity and loss. Annu. Rev. Environ. Resour. 28,
137167 (2003).
3. G. Mace, K. Norris, A. Fitter, Biodiversity and ecosystem services: A multilayered relation-
ship. Trends Ecol. Evol. 27,1926 (2012).
4. G. Mace, C. Revenga, E. Ken, Biodiversity, in Ecosystems and Human Well-Being: Cur rent
State and Trends, G. Ceballos, G. Orians, S. L. Pacala, Eds. (Island Press, Washington, DC,
2005), chap. 4, pp. 77121.
5. G. C. Daily, P. A. Matson, Ecosystem services: From theory to implementation. Proc. Natl.
Acad. Sci. U.S.A. 105, 94559456 (2008).
6. P. R. Ehrlich, A. Ehrlich, Can a collapse of global civilization be avoided? Proc. Biol. Sci. 280,
20122845 (2013).
7. A.D.Barnosky,N.Matzke,S.Tomiya,G.O.Wogan,B.Swartz,T.B.Quental,C.Marshall,
J. L. McGuire, E. L. Lindsey, K. C. Maguire, B. Mersey, E. A. Ferrer, Has the Earthssixthmass
extinction alre ady arriv ed? Nature 471,5157 (2011).
8. R. Dirzo, H. S. Young, M. Galletti, G. Ceballos, J. B. Nick, B. Collen, Defaunation in the
Anthropocene. Science 345, 401406 (2014).
9. R. Leakey, R. Lewis, The Sixth Extinction: Patterns of Life and the Future of Humankind (Doubleday,
New York, 1995).
10. D. M. Raup, A kill curve for Phanerozoic marine species. Paleobiology 17,3748 (1991).
11. R. M. May, J. H. Lawton, E .Stork, Assessing extinction rates, in Extinction Rates, J. H. Lawton,
R. M. May, Eds. (Oxford University Press, Oxford, 1995), chap. 1. pp. 124.
12. S. L. Pimm, G. J. Russell, J. L. Gittleman, T. M. Brooks, The future of biodiversity. Science 269,
347350 (1995).
13. J. Alroy, Constant extinction, constrained diversification, and uncoordinated stasis in North
American mammals. Palaeogeogr. Palaeoclimatol. Palaeoecol. 127, 285311 (1996).
14. J. E. M. Baillie, Z. Cokeliss, Extinctions in recent time, in 2004 IUCN Red List of Threatened
Species: A Global Species Assessment, J. E. M. Baillie, C. Hilton-Taylor, S. N. Stuart, Eds. (IUCN,
Gland, Switzerland and Cambridge, UK, 2004); pp. 3350.
15. R. M. May, Ecological science and tomorrows world. Philos. Trans. R. Soc. Lond. B Biol. Sci.
365,4147 (2010).
16. H. M. Pereira, P. W. Leadley, V. Proença, R. Alkemade, J. P. Scharlemann, J. F. Fernandez-Manjarrés,
M. B. Araújo, P. Balvanera, R. Biggs, W. W. Cheung, L. Chini, H. D. Cooper, E. L. Gilman, S. Guénette,
G. C. Hurtt, H. P. Huntington, G. M. Mace, T. Oberdorff, C. Revenga, P. Rodrigues, R. J. Scholes,
U. R. Sumaila, M. Walpole, Scenarios for global biodiversity in the 21st century. Science,330,
14961501 (2010).
17. IUCN, The IUCN Red List of Threatened Species, Version 2014.3 (IUCN, 2014); http://www.
iucnredlist.org (downloaded on 11 March 2015).
RESEARCH ARTICLE
Ceballos et al. Sci. Adv. 2015;1:e1400253 19 June 2015 4of5
18. G. Ceballos, P. R. Ehrlich, Mammal population losses and the extinction crises. Proc. Natl.
Acad. Sci. U.S.A. 106, 38413846 (2009).
19. J. Schipper, J. S. Chanson, F. Chiozza, N. A. Cox, M. Hoffmann, V. Katariya, J. Lamoreux,
A. S. Rodrigues, S. N. Stuart, H. J. Temple, J. Baillie, L. Boitani, T. E. Lacher Jr., R. A. Mittermeier,
A. T. Smith, D. Absol on, J. M. Aguiar, G. Amori, N. Bakkour, R. Baldi, R. J. Berridge, J. Bielby,
P.A.Black,J.J.Blanc,T.M.Brooks,J.A.Burton,T.M.Butynski,G.Catullo,R.Chapman,
Z. Cokeliss, B. Collen, J. Conroy, J. G. Cooke, G. A. da Fonseca, A. E. Derocher, H. T. Dublin,
J.W.Duckworth,L.Emmons,R.H.Emslie,M.Festa-Bianchet,M.Foster,S.Foster,D.L.Garshelis,
C. Gates, M. Gimenez-Dixon, S. Gonz alez, J. F. Gonzalez-Maya, T. C. Good, G. Hammerson ,
P. S. Hammond, D. Ha ppold, M. Happold, J. Hare, R. B. Ha rris, C. E. Hawkins, M. Haywood,
L. R. Heaney, S. Hedges, K. M. Helgen, C. Hilton-Taylor, S. A. Hussain, N. Ishii, T. A. Jefferson,
R. K. Jenkins, C. H. Johnston, M. Keith, J. Kingdon, D. H. Knox, K. M. Kovacs, P. Langhammer,
K. Leus, R. Lewison, G. Lichtenstein, L. F. Lowry, Z. Macavoy, G. M. Mace, D. P. Mallon, M. Masi,
M. W. McKnight, R. A. Medellín, P. Medici, G. Mills, P. D. Moehlman, S. Molur, A. Mora, K. Nowell,
J.F.Oates,W.Olech,W.R.Oliver,M.Oprea,B.D.Patterson,W.F.Perrin,B.A.Polidoro,
C. Pollock, A. Powel, Y. Protas, P. Racey, J. Ragle, P. Ramani, G. Rathbun, R. R. Reeves, S. B. Reilly,
J. E. Reynolds III, C. Rondinini, R. G. Rosell-Ambal, M. Rulli, A. B. Rylands, S. Savini, C. J. Schank,
W. Sechrest, C. Self-Sullivan, A. Shoemaker, C. Sillero-Zubiri, N. De Silva, D. E. Smith, C. Srinivasulu,
P. J. Stephenson, N. van Strien, B. K. Talukdar, B. L. Taylor, R. Timmins, D. G. Tirira, M. F. Tognelli,
K. Tsytsulina, L. M. Veiga, J. C. Vié, E. A. Williamson, S. A. Wyatt, Y. Xie, B. E. Young, The status of
the worlds land and marine mammals: Diversity, threat, and knowledge. Science 322, 225230
(2008).
20. S. L. Pimm, P. Raven, A. Peterson, C. H. Şekercioğlu, P. R. Ehrlich, Human impacts on the rates
of recent, present, and future bird extinctions. Proc. Natl. Acad. Sci. U.S.A. 103, 1094110946
(2006).
21. N. M. Burkhead, Extinction rates in North American freshwater fishes, 19002010. BioScience
62,798808 (2012).
22. M. Böhm, B. Collen, J. E. M. Baillie, P. Bowles, J. Chanson, N. Cox, G. Hammerson, M. Hoffmann,
S. R. Livingstone, M. Ram, A. G. J. Rhodin, S. N. Stuart, P. P. van Dijk, B. E. Young, L. E. Afuang,
A. Aghasyan, A. García, C. Aguilar, R. Ajtic, F. Akarsu, L. R. V. Alencar, A. Allison, N. Ananjeva,
S. Anderson, C. Andrén, D. Ariano-Sánchez, J. C. Arredondo, M. Auliya, C. C. Austin, A. Avci,
P. J. Baker, A. F. Barreto-Lima, C. L. Barrio-Amorós, D. Basu, M. F. Bates, A. Batistella,
A. Bauer, D. Bennett, W. Böhme, D. Broadley, R. Brown, J. Bu rgess, A. Captain, S. Carreira,
M. del Rosario Castañeda, F. Castro, A. Catenazzi, J. R. Cedeño-Vázquez, D. G. Chapple,
M. Cheylan, D. F. Cisneros-Heredia, D. Cogalniceanu, H. Cogger, C. Corti, G. C. Costa, P. J. Couper,
T. Courtney, J. Crnobrnja-Isailovic, P.-A. Crochet, B. Crother, F. Cruz, J. C. Daltry, R. J. Ranjit Daniels,
I. Das, A. de Silva, A. C. Diesmos, L. Dirksen, T. M. Doan, C. K. Dodd Jr., J. S. Doody, M. E. Dorcas,
J. D. de Barros Filho, V. T. Egan, E. H. El Mouden, D. Embert, R. E. Espinoza, A. Fallabrino,
X. Feng, Z.-J. Feng, L. Fitzgerald, O. Flores-Villela, F. G. R. França, D. Frost, H. Gadsden, T. Gamble,
S.R.Ganesh,M.A.Garcia,J.E.García-Pérez,J.Gatus,M.Gaulke,P.Geniez,A.Georges,J.Gerlach,
S.Goldberg,J.-C.T.Gonzalez,D.J.Gower,T.Grant,E.Greenbaum,C.Grieco,P.Guo,
A. M. Hamilton, K. Hare, S. B. Hedges, N. Heideman, C. Hilton-Taylor, R. Hitchmough,
B. Hollingsworth, M. Hutchinson, I. Ineich, J. Iverson, F. M. Jaksic, R. Jenkins, U. Joger, R. Jose,
Y. Kaska, U. Kaya, J. S. Keogh, G. Köhler, G. Kuchling, Y. Kumlutaş, A. Kwet, E. La Marca, W. Lamar,
A.Lane,B.Lardner,C.Latta,G.Latta,M.Lau,P.Lavin,D.Lawson,M.LeBreton,E.Lehr,D.Limpus,
N.Lipczynski,A.S.Lobo,M.A.López-Luna,L.Luiselli,V.Lukoschek,M.Lundberg,P.Lymberakis,
R. Macey, W. E. Magnusson, D. L. Mahler, A. Malhotra, J. Mariaux, B. Maritz, O. A. V. Marques,
R.Márquez,M.Martins,G.Masterson,J.A.Mateo,R.Mathew,N.Mathews,G.Mayer,J.R.McCranie,
G. J. Measey, F. Mendoza-Quijano, M. Menegon, S. Métrailler, D. A. Milton, C. Montgomery,
S. A. A. Morato, T. Mott, A. Muñoz-Alonso, J. Murphy, T. Q. Nguyen, G. Nilson, C. Nogueira,
H. Núñez, N. Orlov, H. Ota, J. Ottenwalder, T. Papenfuss, S. Pasachnik, P. Passos, O. S. G. Pauwels,
N. Pérez-Buitrago, V. Pérez-Mellado, E. R. Pianka, J. Pleguezuelos, C. Pollock, P. Ponce-Campos,
R. Powell, F. Pupin, G. E. Quintero Díaz, R. Radder, J. Ramer, A. R. Rasmussen, C. Raxworthy,
R.Reynolds,N.Richman,E.L.Rico,E.Riservato,G.Rivas,P.L.B.daRocha,M.-O.Rödel,
L. Rodríguez Schettino, W. M. Roosenburg, J. P. Ross, R. Sadek, K. Sanders, G. Santos-Barrera,
H. H. Schleich, B. R. Schmidt, A. Schmitz, M. Sharifi, G. Shea, H.-T. Shi, R. Shine, R. Sindaco,
T. Slimani, R. Somaweera, S. Spawls, P. Stafford, R. Stuebing, S. Sweet, E. Sy, H. J. Temple ,
M. F. Tognelli, K. Tolley, P. J. Tolson, B. Tuniyev, S. Tuniyev, N. Üzüm, G. van Buurt, M. Van Sluys,
A. Velasco, M. Vences, M. Veselý, S. Vinke, T. Vinke, G. Vogel, M. Vogrin, R. C. Vogt, O. R. Wearn,
Y. L. Werner, M. J. Whiting, T. Wiewandt, J. Wilkinson, B. Wilson, S. Wren, T. Zamin, K. Zhou, G. Zug,
The conservation status of the worldsreptiles.Biol. Conserv. 157, 372385 (2013).
23. S. N. Stuart, J. S. Chanson, N. A. Cox, B. E. Young, A. S. Rodrigues, D. L. Fischman, R. W. Waller, Status
and trends of amphibian declines and extinctions worldwide. Science 306, 17831786 (2004).
24. D. W. Steadman, Extinction and Biogeography of Tropical Pacific Birds (Chicago University
Press, Chicago, 2006).
25. J. B. Hughes, G. C. Daily, P. R. Ehrlich, Population diversity: Its extent and extinction. Science
278, 689692 (1997).
26. B. Lomborg, The Skeptical Environmentalist: Measuring the Real State of the World (Cam-
bridge University Press, Cambridge, UK, 2001).
27. S. Dullinger, F. Essl, W. Rabitsch, K. H. Erb, S. Gingrich, H. Haberl, K. Hülber, V. Jarosík, F. Krausmann,
I. Kühn, J. Pergl, P. Pysek, P. E. Hulme, Europes other debt crisis caused by the long legacy of
future extinctions. Proc. Nat. Acad. Sci. U.S.A. 110,73427347 (2013).
28. D. S. Karp, H. V. Moeller, L. O. Frishkoff, Nonrandom extinction patterns can modulate pest
control service decline. Ecol. Appl. 23, 840849 (2013).
29. C. D. Mendenhall, D. S. Karp, C. F. Meyer, E. A. Hadly, G. C. Daily, Predicting biodiversity
change and averting collapse in agricultural landscapes. Nature 509, 213217 (2014).
30. L. O. Frishkoff, D. S. Karp, L. K. MGonigle, C. D. Mendenhall, J. Zook, C. Kremen, E. A. Hadly,
G. C. Daily, Loss of avian phylogenetic diversity in Neotropical agricultural systems. Science
345, 13431346 (2014).
31. M.deL.Brooke,S.H.M.Butchart,S.T.Garnett,G.M.Crowley,N.B.Mantilla-Beniers,A.J.Stattersfield,
Rates of movement of threatened bird species between IUCN Red List categories and toward
extinction. Conserv. Biol. 22,417427 (2008).
32. S. Butchart, A. Stattersfield, N. Collar, How many bird extinctions have we prevented? Oryx
40, 266278 (2006).
33. M. Hoffmann, C. Hilton-Taylor, A. Angulo, M. Böhm, T. M. Brooks, S. H. Butchart, K. E. Carpenter,
J. Chanson, B. Collen, N. A. Cox, W. R. Darwall, N. K. Dulvy, L. R. Harrison, V. Katariya,
C. M. Pollock, S. Quader, N. I. Richman, A. S. Rodrigues, M. F. Tognelli, J. C. Vié, J. M. Aguiar,
D. J. Allen, G. R. Allen, G. Amori, N. B. Ananjeva, F. Andreone, P. Andrew, A. L. Aquino Ortiz,
J. E. Baillie, R. Baldi, B. D. Bell, S. D. Biju, J. P. Bi rd, P. Black-Decima, J. J. Blanc, F. Bolaños,
W. Bolivar-G, I. J. Burfield, J. A. Burton, D. R. Capper, F. Castro, G. Catullo, R. D. Cavanagh,
A. Channing, N. L. Chao, A. M. Chenery, F. Chiozza, V. Clausnitzer, N. J. Collar, L. C. Collett,
B. B. Collette, C. F. Cortez Fernandez, M. T. Craig, M. J. Crosby, N. Cumberlidge, A. Cuttelod,
A.E.Derocher,A.C.Diesmos,J.S.Donaldson,J.W.Duckworth,G.Dutson,S.K.Dutta,
R. H. Emslie, A. Farjon, S. Fowler, J. Freyhof, D. L. Garshelis, J. Gerlach, D. J. Gower, T. D. Grant,
G. A. Hammerson, R. B. Harris, L. R. Heaney, S. B. Hedges, J. M. Hero, B. Hughes, S. A. Hussain,
M. J. Icochea, R. F. Inger, N. Ishii, D. T. Iskandar, R. K. Jenkins, Y. Kaneko, M. Kottelat,
K.M.Kovacs,S.L.Kuzmin,E.LaMarca,J.F.Lamoreux,M.W.Lau,E.O.Lavilla,K.Leus,R.L.Lewison,
G.Lichtenstein,S.R.Livingstone,V.Lukoschek,D.P.Mallon,P.J.McGowan,A.McIvor,
P.D.Moehlman,S.Molur,A.MuñozAlonso,J.A.Musick,K.Nowell,R.A.Nussbaum,
W. Olech, N. L. Orlov, T. J. Papenfuss, G. Parra-Olea, W. F. Perrin, B. A. Polidoro, M. Pourkazemi,
P. A. Racey, J. S. Ragle, M. Ram, G. Rathbun, R. P. Reynolds, A. G. Rhodin, S. J. Richards,
L. O. Rodríguez, S. R. Ron, C. Rondinini, A. B. Rylands, Y. de Mitcheson Sadovy, J. C. Sanciangco,
K. L . S and e rs, G . Santos-Barrera, J. Schipper, C . Self-Sullivan, Y. Shi, A. Shoemaker, F. T. Short,
C. Sillero-Zubiri, D. L. Silvano, K. G. Smith, A. T. Smith, J. Snoeks, A. J. Stattersfield, A. J. Symes,
A. B. Taber, B. K. Taluk dar, H. J. Temple, R. Timmins, J. A. Tobias, K. Tsytsul ina, D. Tweddle,
C. Ubeda, S. V. Valenti, P. P. van Dijk, L. M. Veiga, A. Veloso, D. C. Wege, M. Wilkinson, E. A. Williamson,
F. Xie, B. E. Young, H. R. Akçakaya, L. Bennun, T. M. Blackburn, L. Boitani, H. T. Dublin,
G.A.daFonseca,C.Gascon,T.E.LacherJr.,G.M.Mace,S.A.Mainka,J.A.McNeely,R.A.Mittermeier,
G.M.Reid,J.P.Rodriguez,A.A.Rosenberg,M.J.Samways,J.Smart,B.A.Stein,S.N.Stuart,The
Impact of conservation on the status of the worlds vertebrates. Science 330, 15031509 (2010).
Acknowledgments: We would like to thank B. Young for helping us with the data on possibly
extinct speciespublished by IUCN. J. Soberon, C. Mendenhall, and J. Pacheco gave valuable
suggestions on the manuscript. Funding: This work has been supported by the Programa de
apoyo a proyectos de investigación e innovación tecnológica from UNAM. Competing
interests: The authors declare that they have no competing interests.
Submitted 23 December 2014
Accepted 1 May 2015
Published 19 June 2015
10.1126/sciadv.1400253
Citation: G.Ceballos,P.R.Ehrlich,A.D.Barnosky,A.García,R.M.Pringle,T.M.Palmer,
Accelerated modern humaninduced species losses: Entering the sixth mass extinction. Sci.
Adv. 1, e1400253 (2015).
RESEARCH ARTICLE
Ceballos et al. Sci. Adv. 2015;1:e1400253 19 June 2015 5of5
... The extinction rate control variable is challenging to apply in operational contexts, but data and methods for directly assessing the genetic diversity component of biosphere integrity are emerging [(23) and the Supplementary Materials]. Although the baseline rate of extinctions (and of new species' evolution) is both highly variable and difficult to quantify with confidence through geological time, the current rate of species extinctions is estimated to be at least tens to hundreds of times higher than the average rate over the past 10 million years and is accelerating (24). We conservatively set the current value for the extinction rate at >100 E/MSY (24)(25)(26). ...
... Although the baseline rate of extinctions (and of new species' evolution) is both highly variable and difficult to quantify with confidence through geological time, the current rate of species extinctions is estimated to be at least tens to hundreds of times higher than the average rate over the past 10 million years and is accelerating (24). We conservatively set the current value for the extinction rate at >100 E/MSY (24)(25)(26). Of an estimated 8 million plant and animal species, around 1 million are threatened with extinction (16), and over 10% of genetic diversity of plants and animals may have been lost over the past 150 years (23). ...
Article
This planetary boundaries framework update finds that six of the nine boundaries are transgressed, suggesting that Earth is now well outside of the safe operating space for humanity. Ocean acidification is close to being breached, while aerosol loading regionally exceeds the boundary. Stratospheric ozone levels have slightly recovered. The transgression level has increased for all boundaries earlier identified as overstepped. As primary production drives Earth system biosphere functions, human appropriation of net primary production is proposed as a control variable for functional biosphere integrity. This boundary is also transgressed. Earth system modeling of different levels of the transgression of the climate and land system change boundaries illustrates that these anthropogenic impacts on Earth system must be considered in a systemic context.
... Future research should validate the use of BLAM emitters in a large-scale field setting. Although humans benefit greatly from biomimetic research 17,18 , the natural plant, the product of 3.8 billion years of evolution with biodiversity, is under siege 51,52 . We, therefore, need to develop sustainable strategies in agricultural applications [53][54][55] , such as the proposed BLAM-emitter drip irrigation strategy, to meet a sustainable future. ...
Article
Full-text available
Irrigation is limited by water scarcity. Here, we show how a drip irrigation system inspired by the leaf of the fig tree Ficus religiosa (also known as the bodhi tree) can improve irrigation efficiency. The reverse curvature of the leaf regulates the convergence process of multiple water streams, while its long-tail apex allows for fast water drainage with the droplet separation centroid beyond the leaf apex. We explain why drip frequency increases after the break-up of contact line pinning at the apex tip by using scaling laws for drip volume and analyzing drainage dynamics. We build a drip irrigation emitter inspired by the bodhi leaf apex and compare the germination efficiency of wheat, cotton, and maize under different irrigation modes. These results show that the proposed bodhi-leaf-apex-mimetic (BLAM) drip irrigation can improve water saving while ensuring germination and seedling growth.
... These services encompass provisioning, regulating, supporting, and cultural aspects, contributing to human survival and development [1][2][3]. Nevertheless, the interplay of climate change, continuous population growth, and unsustainable utilization of natural resources has given rise to a cascade of challenges, including heightened occurrences of extreme climatic events [4], land degradation [5], environmental pollution [6], and a notable decline in biodiversity [7]. As a consequence, ecosystem degradation has emerged as a critical global concern [8]. ...
Article
Full-text available
The National Key Ecological Function Zones (NKEFZ) serve as crucial ecological security barriers in China, playing a vital role in enhancing ecosystem services. This study employed the theoretical framework of ecological benefits assessment in major ecological engineering projects. The primary focus was on the ecosystem macrostructure, ecosystem quality, and key ecosystem services, enabling quantitative analysis of the spatiotemporal changes in the ecosystem status of the NKEFZ from 2000 to 2019. To achieve this, remote sensing data, meteorological data, and model simulations were employed to investigate five indicators, including land use types, vegetation coverage, net primary productivity of vegetation, soil conservation services, water conservation services, and windbreak and sand fixation services. The analysis incorporated the Theil–Sen Median method to construct an evaluation system for assessing the restoration status of ecosystems, effectively integrating ecosystem quality and ecosystem services indicators. The research findings indicated that land use changes in NKEFZ were primarily characterized by the expansion of unused land and the in of grassland. The overall ecosystem quality of these zones improved, showing a stable and increasing trend. However, there were disparities in the changes related to ecosystem services. Water conservation services exhibited a decreasing trend, while soil conservation and windbreak and sand fixation services showed a steady improvement. The ecosystem of the NKEFZ, in general, displayed a stable and recovering trend. However, significant spatial heterogeneity existed, particularly in the southern region of the Qinghai–Tibet Plateau and at the border areas between western Sichuan and northern Yunnan, where some areas still experienced deteriorating ecosystem conditions. Compared to other functional zones, the trend in the ecosystem of the NKEFZ might not have been the most favorable. Nonetheless, this could be attributed to the fact that most of these areas were situated in environmentally fragile regions, and conservation measures may not have been as effective as in other functional zones. These findings highlighted the considerable challenges ahead in the construction and preservation of the NKEFZ. In future development, the NKEFZ should leverage their unique natural resources to explore distinctive ecological advantages and promote the development of eco-friendly economic industries, such as ecological industry, ecological agriculture, and eco-tourism, transitioning from being reliant on external support to self-sustainability.
... These are of primary importance to human society: sea level rise removes the terrestrial environment, threatening major world cities; changes in weather such as in precipitation, temperature and drought reduce habitability, change ecosystems, reduce the capacity of land to provide food, and force migrations of people and animals, exposing them to new threats. All these things together cause extinctions of so many species that we are now in a 'mass extinction' event (Ceballos et al. 2015) with the consequent expectation that more than 75% of all known multicellular species will be lost (Barnosky et al. 2011). ...
Preprint
Full-text available
This is modified late draft, published with revisions as: Barker T. and Fisher J. (2019). Ecosystem health as the basis for human health. Chapter 19 in Selendy J.M.H (editor), Water and Sanitation Related Diseases and the Changing Environment: Challenges, Interventions and Preventive Measures. Second edition, Wiley-Blackwell and Horizon International, Hoboken and Chichester.
Article
Full-text available
Beyond climate change, the planet faces several other environmental challenges that are at least as threatening, such as the loss of biodiversity. In each case, the problems are driven by similar factors, such as fossil fuels and intensive livestock farming. This paper presents a legal analysis concerning the binding nature of the Convention on Biological Diversity’s (CBD) overarching objective to halt biodiversity loss, within the framework of international environmental and human rights law. Using the established legal techniques encompassing grammatical, systematic, teleological, and historical interpretations, the article demonstrates that the CBD’s objective to halt biodiversity loss is indeed legally binding and justiciable. This conclusion is directly drawn from interpreting Article 1 CBD. Furthermore, a comparable obligation emerges indirectly from international climate law. The imperative to curtail biodiversity loss also finds grounding in human rights law, albeit necessitating a re-evaluation of certain aspects of freedom, similar to what has been explored in the context of climate protection. Moreover, the article underscores that various other biodiversity-related regulations within international law, including those laid out in the CBD, the Aichi Targets, and the Kunming–Montreal Global Biodiversity Framework, also carry partial legal significance. Nonetheless, it is crucial to note that these regulations, including the Kunming–Montreal Framework, do not modify the obligation mandate to halt biodiversity loss, which was established at the latest when the CBD entered into force in 1993. Because this obligation has been violated since then, states could potentially be subject to legal action before international or domestic courts for their actions or inactions contributing to global biodiversity loss.
Chapter
The history of life on Earth has been shaken in the last half billion years by five mass extinctions that have killed at least three-quarters of biodiversity in a geologically short time. These five extinctions were due to major ecological upheavals, with endogenous or exogenous drivers (volcanic eruptions, impact of asteroids, etc.). Today, many data show that the current extinction rate is comparable to or even worse than that of the Big Five mass extinctions of the past. The difference is that this time the asteroid is one species: Homo sapiens. There are good reasons to include the Sixth Mass Extinction in the definition of the Anthropocene. This drastic reduction in biodiversity will leave an irreversible geological and paleontological mark. It interacts with climate change, with a multiplicative effect. It contributes to the environmental crisis that reduces ecosystem services and threatens human health (i.e., likelihood of spillovers).
Chapter
Geocentric Greek astronomers called seven heavenly bodies visible to the naked eye (sun, moon, Mercury, Venus, Mars, Jupiter, and Saturn) πλανητες—wanderers—because unlike all the other αστρα, their relative positions were constantly changing. While the Romans changed the Greek names of the individual planets to those still in use, they retained the generic name, which now occurs in many European languages. In acentric modern astronomy a planet is a satellite of a star. In addition to the five actual planets known to the Greeks, Earth, Uranus, and Neptune also orbit the sun, a smallish star about half the distance from the centre of the Milky Way to its outer reaches. Earth is the only planet on which life is known for certain to exist. The search is on for concrete evidence of existing or formerly existing life on Mars (Dunbar B. et al. Perseverance Mars rover. NASA. https://www.nasa.gov/perseverance. Retrieved 06/16/2021, 2021). Technology for detecting the chemical signature of life in the atmospheres of some planets of other stars may become available in the near future (Fujii Y. et al. Astrobiology 18 (6): 739–778, 2018)—proving a point made by (Lovelock J. Gaia: A new look at life on earth. Oxford University Press, New York, 1979) that life is a whole-planet phenomenon. That is, the Earth does not just harbour or support life; it has a life of its own. The Earth is a living planet in relationship to which individual organisms are as ephemeral cells (Vernadsky VI. Am Sci 33:1–12, 1945).
Chapter
The biosphere coevolves with the atmosphere, hydrosphere and lithosphere to maintain a habitable space on Earth. Over billions of years – and despite periodic setbacks – it has evolved increasing complexity, from its microbial beginnings to the complex interactions between animals, plants, fungi and unicellular microscopic life that sustain its present state. Recently, the biosphere has been profoundly changed by humans. In part, this includes increased rates of extinction that are reminiscent of past fundamental perturbations to life. But the change is even more profound, resulting from a combination of marked translocations of species beyond their indigenous ranges, overt concentration of biomass in humans and their farm animals, reconfiguration of landscape habitats and over-utilisation of ocean life, excessive appropriation of energy from the biosphere (including its fossilised component), and increasing interconnectivity between technology and life.
Article
Mass extinctions during the past 500 million y rapidly removed branches from the phylogenetic tree of life and required millions of years for evolution to generate functional replacements for the extinct (EX) organisms. Here we show, by examining 5,400 vertebrate genera (excluding fishes) comprising 34,600 species, that 73 genera became EX since 1500 AD. Beyond any doubt, the human-driven sixth mass extinction is more severe than previously assessed and is rapidly accelerating. The current generic extinction rates are 35 times higher than expected background rates prevailing in the last million years under the absence of human impacts. The genera lost in the last five centuries would have taken some 18,000 y to vanish in the absence of human beings. Current generic extinction rates will likely greatly accelerate in the next few decades due to drivers accompanying the growth and consumption of the human enterprise such as habitat destruction, illegal trade, and climate disruption. If all now-endangered genera were to vanish by 2,100, extinction rates would be 354 (average) or 511 (for mammals) times higher than background rates, meaning that genera lost in three centuries would have taken 106,000 and 153,000 y to become EX in the absence of humans. Such mutilation of the tree of life and the resulting loss of ecosystem services provided by biodiversity to humanity is a serious threat to the stability of civilization. Immediate political, economic, and social efforts of an unprecedented scale are essential if we are to prevent these extinctions and their societal impacts.
Article
Full-text available
Effective and targeted conservation action requires detailed information about species, their distribution, systematics and ecology as well as the distribution of threat processes which affect them. Knowledge of reptilian diversity remains surprisingly disparate, and innovative means of gaining rapid insight into the status of reptiles are needed in order to highlight urgent conservation cases and inform environmental policy with appropriate biodiversity information in a timely manner. We present the first ever global analysis of extinction risk in reptiles, based on a random representative sample of 1500 species (16% of all currently known species). To our knowledge, our results provide the first analysis of the global conservation status and distribution patterns of reptiles and the threats affecting them, highlighting conservation priorities and knowledge gaps which need to be addressed urgently to ensure the continued survival of the world’s reptiles. Nearly one in five reptilian species are threatened with extinction, with another one in five species classed as Data Deficient. The proportion of threatened reptile species is highest in freshwater environments, tropical regions and on oceanic islands, while data deficiency was highest in tropical areas, such as Central Africa and Southeast Asia, and among fossorial reptiles. Our results emphasise the need for research attention to be focussed on tropical areas which are experiencing the most dramatic rates of habitat loss, on fossorial reptiles for which there is a chronic lack of data, and on certain taxa such as snakes for which extinction risk may currently be underestimated due to lack of population information. Conservation actions specifically need to mitigate the effects of human-induced habitat loss and harvesting, which are the predominant threats to reptiles.
Article
Full-text available
Habitat conversion is the primary driver of biodiversity loss, yet little is known about how it is restructuring the tree of life by favoring some lineages over others. We combined a complete avian phylogeny with 12 years of Costa Rican bird surveys (118,127 detections across 487 species) sampled in three land uses: forest reserves, diversified agricultural systems, and intensive monocultures. Diversified agricultural systems supported 600 million more years of evolutionary history than intensive monocultures but 300 million fewer years than forests. Compared with species with many extant relatives, evolutionarily distinct species were extirpated at higher rates in both diversified and intensive agricultural systems. Forests are therefore essential for maintaining diversity across the tree of life, but diversified agricultural systems may help buffer against extreme loss of phylogenetic diversity.
Article
Full-text available
Today the number of species is the largest in the history of life; however a considerable proportion of that biodiversity is endangered and many species have suffered anthropogenic extinctions. Species and population extinctions are natural phenomena, and massive biodiversity declines have occurred five times in the remote geological past. However, the current extinction episode, the "sixth extinction wave," may prove to be the most rapid and devastating. To assess the seriousness of this wave, we analyze the present extent of life's diversity, the number of species that have gone extinct in historic times, the current rates of species extinction, and the extent of population losses. Estimates of the likely number of eukaryotic species vary from 5 to 100 million, but we are now in a "new age of discovery." There is an explosion of descriptions of new species even in previously "well-known" groups such as mammals, suggesting that previous estimates of the magnitude of biodiversity may be too low. Based on the 2008 IUCN evaluation of the status of world´s species, we estimate that extinctions caused by human activities are occurring at a rate thousands of times higher than the background rate.
Article
Full-text available
We live amid a global wave of anthropogenically driven biodiversity loss: species and population extirpations and, critically, declines in local species abundance. Particularly, human impacts on animal biodiversity are an under-recognized form of global environmental change. Among terrestrial vertebrates, 322 species have become extinct since 1500, and populations of the remaining species show 25% average decline in abundance. Invertebrate patterns are equally dire: 67% of monitored populations show 45% mean abundance decline. Such animal declines will cascade onto ecosystem functioning and human well-being. Much remains unknown about this “Anthropocene defaunation”; these knowledge gaps hinder our capacity to predict and limit defaunation impacts. Clearly, however, defaunation is both a pervasive component of the planet’s sixth mass extinction and also a major driver of global ecological change.
Article
The relationship between biodiversity and the rapidly expanding research and policy field of ecosystem services is confused and is damaging efforts to create coherent policy. Using the widely accepted Convention on Biological Diversity definition of biodiversity and work for the U.K. National Ecosystem Assessment we show that biodiversity has key roles at all levels of the ecosystem service hierarchy: as a regulator of underpinning ecosystem processes, as a final ecosystem service and as a good that is subject to valuation, whether economic or otherwise. Ecosystem science and practice has not yet absorbed the lessons of this complex relationship, which suggests an urgent need to develop the interdisciplinary science of ecosystem management bringing together ecologists, conservation biologists, resource economists and others.
Article
Effective and targeted conservation action requires detailed information about species, their distribution, systematics and ecology as well as the distribution of threat processes which affect them. Knowledge of reptilian diversity remains surprisingly disparate, and innovative means of gaining rapid insight into the status of reptiles are needed in order to highlight urgent conservation cases and inform environmental policy with appropriate biodiversity information in a timely manner. We present the first ever global analysis of extinction risk in reptiles, based on a random representative sample of 1500 species (16% of all currently known species). To our knowledge, our results provide the first analysis of the global conservation status and distribution patterns of reptiles and the threats affecting them, highlighting conservation priorities and knowledge gaps which need to be addressed urgently to ensure the continued survival of the world’s reptiles. Nearly one in five reptilian species are threatened with extinction, with another one in five species classed as Data Deficient. The proportion of threatened reptile species is highest in freshwater environments, tropical regions and on oceanic islands, while data deficiency was highest in tropical areas, such as Central Africa and Southeast Asia, and among fossorial reptiles. Our results emphasise the need for research attention to be focussed on tropical areas which are experiencing the most dramatic rates of habitat loss, on fossorial reptiles for which there is a chronic lack of data, and on certain taxa such as snakes for which extinction risk may currently be underestimated due to lack of population information. Conservation actions specifically need to mitigate the effects of human-induced habitat loss and harvesting, which are the predominant threats to reptiles.
Article
Abstract? Biodiversity, a central component of Earth's life support systems, is directly relevant to human societies. We examine the dimensions and nature of the Earth's terrestrial biodiversity and review the scientific facts concerning the rate of loss of biodiversity and the drivers of this loss. The estimate for the total number of species of eukaryotic organisms possible lies in the 5?15 million range, with a best guess of ?7 million. Species diversity is unevenly distributed; the highest concentrations are in tropical ecosystems. Endemisms are concentrated in a few hotspots, which are in turn seriously threatened by habitat destruction?the most prominent driver of biodiversity loss. For the past 300 years, recorded extinctions for a few groups of organisms reveal rates of extinction at least several hundred times the rate expected on the basis of the geological record. The loss of biodiversity is the only truly irreversible global environmental change the Earth faces today.