List of recently extinct mammals
{{Short description|None}}
{{See also|List of prehistoric mammals}}
{{Use dmy dates|date=July 2020}}
File:Extinctions Africa Austrailia NAmerica Madagascar.gif
{{Mammals by population sidebar}}
{{IUCN mammal chart}}
Recently extinct mammals are defined by the International Union for Conservation of Nature (IUCN) as any mammals that have become extinct since the year 1500 CE. Since then, roughly 80 mammal species have become extinct.{{cite book|last1=Ceballos|first1=G.|last2=Ehrlich|first2=A. H.|last3=Ehrlich|first3=P. R.|year=2015|title=The Annihilation of Nature: Human Extinction of Birds and Mammals|location=Baltimore, Maryland|publisher=Johns Hopkins University Press|isbn=978-1421417189}} "69"
Extinction of taxa is difficult to confirm, as a long gap without a sighting is not definitive, but before 1995 a threshold of 50 years without a sighting was used to declare extinction.
One study found that extinction from habitat loss is the hardest to detect, as this might only fragment populations to the point of concealment from humans. Some mammals declared as extinct may very well reappear.{{cite journal|first1=Diana O.|last1=Fisher|first2=Simon P.|last2=Blomberg|year=2011|title=Correlates of rediscovery and the detectability of extinction in mammals|journal=Proceedings of the Royal Society B: Biological Sciences|volume=278|issue=1708|pages=1090–1097|doi=10.1098/rspb.2010.1579|pmc=3049027|pmid=20880890}} For example, a study found that 36% of purported mammalian extinction had been resolved, while the rest either had validity issues (insufficient evidence) or had been rediscovered.{{cite book|chapter-url=https://www.researchgate.net/publication/305712631|title=Extinctions in Near Time|chapter=Requiem Æternam: the last five hundred years of mammalian species extinctions|first1=Ross D. E.|last1=Macphee|first2=Clare|last2=Flemming|year=1999|isbn=978-1-4419-3315-7|series=Advances in Vertebrate Paleobiology|volume=2|editor-first=Ross D. E.|editor-last=MacPhee| editor2-first=Hans-Dieter|editor2-last=Sues}}
As of June 2023, the IUCN listed 233 mammalian species as critically endangered, while 27% of all mammalian species were threatened with extinction.{{cite web|title=IUCN Red List version 2022.2|url=http://www.iucnredlist.org/|website=The IUCN Red List of Threatened Species|publisher=International Union for Conservation of Nature and Natural Resources (IUCN) |access-date=21 June 2023 }}
Conventions
All species listed here as extinct (no known individuals remaining) are designated by the International Union for Conservation of Nature (IUCN). Species which are extinct in the wild only reside in captivity. Species listed as possibly extinct are classified as being critically endangered, as it is unknown whether or not these species are extinct.{{cite web|url=http://cmsdocs.s3.amazonaws.com/summarystats/2016-1_Summary_Stats_Page_Documents/2016_1_RL_Stats_Table_9.pdf|title=Possibly Extinct and Possibly Extinct in the Wild Species|publisher=IUCN Redlist of Threatened Species|year=2016|access-date=29 August 2016}} Extinct subspecies such as the Javan tiger (Panthera tigris sondaica){{cite iucn |author=Jackson, P. |author2=Nowell, K. |date=2008 |title=Panthera tigris ssp. sondaica |volume=2008 |page=e.T41681A10509194 |doi=10.2305/IUCN.UK.2008.RLTS.T41681A10509194.en |access-date=12 November 2021}} are not listed here as the species, in this case Panthera tigris, is still extant. The IUCN Redlist classification for each species serves as a citation, and the superscripted "IUCN" by the date is a link to that species' page. A range map is provided where available, and a description of their former or current range is given if a range map is not available.
Causes of extinction
Anthropogenic (human caused) habitat degradation is the main cause of species extinctions now. The main cause of habitat degradation worldwide is agriculture, with urban sprawl, logging, mining and some fishing practices close behind. The physical destruction of a habitat, both directly (deforestation for land development or lumber) and indirectly (burning fossil fuels), is an example of this.{{cite book|title=Essentials of Conservation Biology|last=Primack|first=R. B.|publisher=Sinauer Associates|year=2006|isbn=978-0-87893-720-2|edition=4th|location=Sunderland, MA.|pages=177–188|chapter=Habitat destruction}}{{cite journal|url= |title=Combustion of available fossil fuel resources sufficient to eliminate the Antarctic Ice Sheet |last1=Winkelmann |first1=Ricarda |author1-link=Ricarda Winkelmann |last2=Levermann |first2=Anders |year=2015|doi=10.1126/sciadv.1500589 |pmid=26601273|pmc=4643791 |last3=Ridgwell |first3=Andy |last4=Caldeira |first4=Ken |journal=Science Advances |volume=1 |issue=8 |pages=e1500589 |bibcode=2015SciA....1E0589W}}
Also, increasing toxicity, through media such as pesticides, can kill off a species very rapidly, by killing all living members through contamination or sterilizing them. Persistent organic pollutants (POPs), for example, can bioaccumulate to hazardous levels, getting increasingly dangerous further up the food chain.{{cite journal|last1=Kelly|first1=B. C.|last2=Ikonomou|first2=M. G.|last3=Blair|first3=J. D.|last4=Morin|first4=A. E.|last5=Gobas|first5=F. A. P. C.|year=2007|title=Food Web-Specific Biomagnification of Persistent Organic Pollutants|journal=Science|volume=317|issue=5835|pages=236–239|doi=10.1126/science.1138275|pmid=17626882|bibcode=2007Sci...317..236K|s2cid=52835862}}
Disease can also be a factor: white nose syndrome in bats, for example, is causing a substantial decline in their populations and may even lead to the extinction of some species.{{cite journal|last=Langwig|first=K.E.|year=2012|title=Sociality, density-dependence and microclimates determine the persistence of populations suffering from a novel fungal disease, white-nose syndrome|journal=Ecology Letters|volume=15|issue=1|pages=1050–1057|doi=10.1111/j.1461-0248.2012.01829.x|pmid=22747672|author2=W.F. Frick|author3=J.T. Bried|author4=A.C. Hicks|author5=T.H. Kunz|author6=A.M. Kilpatrick|bibcode=2012EcolL..15.1050L }}
Overhunting also has an impact. Terrestrial mammals, such as the tiger and deer, are mainly hunted for their pelts and in some cases meat, and marine mammals can be hunted for their oil and leather. Specific targeting of one species can be problematic to the ecosystem because the sudden demise of one species can inadvertently lead to the demise of another (coextinction) especially if the targeted species is a keystone species. Sea otters, for example, were hunted in the maritime fur trade, and their drop in population led to the rise in sea urchins—their main food source—which decreased the population of kelp—the sea urchin's and Steller's sea cow's main food source—leading to the extinction of the Steller's sea cow.{{cite journal|last1=Estes|first1=James A.|last2=Burdin|first2=Alexander|last3=Doak|first3=Daniel F.|year=2016|title=Sea otters, kelp forests, and the extinction of Steller's sea cow|journal=Proceedings of the National Academy of Sciences of the United States of America|volume=113|issue=4|pages=880–885|doi=10.1073/pnas.1502552112|pmc=4743786|pmid=26504217|bibcode=2016PNAS..113..880E|doi-access=free}} The hunting of an already limited species can easily lead to its extinction, as with the bluebuck whose range was confined to {{convert|1700|sqmi|sqkm}} and which was hunted into extinction soon after discovery by European settlers.{{cite journal|last1=Husson|first1=A. M.|last2=Holthuis|first2=L. B.|year=1969|title=On the type of Antilope leucophaea preserved in the collection of the Rijksmuseum van Natuurlijke Historie Leiden|journal=Zoologische Mededelingen|volume=44|pages=147–157}}
Australia
Island creatures are usually endemic to only that island, and that limited range and small population can leave them vulnerable to sudden changes.{{cite book|url={{Google books|plainurl=yes|id=JmSsNuwMAxgC|page=225}}|title=Evolution of Island Mammals: Adaptation and Extinction of Placental Mammals on Islands|last1=van der Geer|first1=Alexandra|last2=Lyras|first2=George|last3=de Vos|first3=John|last4=Dermitzakis|first4=Michael|publisher=Wiley-Blackwell|year=2010|isbn=978-1-4051-9009-1|location=Oxford|pages=225–227}} While Australia is a continent and not an island, due to its geographical isolation, its unique fauna has suffered an extreme decline in mammal species, 10% of its 273 terrestrial mammals, since European settlement (a loss of one to two species per decade); in contrast, only one species in North America has become extinct since European settlement.{{Citation needed|date=September 2022}} Furthermore, 21% of Australia's mammals are threatened, and unlike in most other continents, the main cause is predation by feral species, such as cats.{{cite journal|last1=Woinarskia|first1=John C. Z.|last2=Burbidge|first2=Andrew A.|last3=Harrison|first3=Peter L.|year=2015|title=Ongoing unraveling of a continental fauna: Decline and extinction of Australian mammals since European settlement|url=http://www.pnas.org/content/112/15/4531.full.pdf|journal=Proceedings of the National Academy of Sciences of the United States of America|volume=112|pages=4531–4540|doi=10.1073/pnas.1417301112|number=5|pmid=25675493|pmc=4403217|bibcode=2015PNAS..112.4531W|doi-access=free}}
Extinct species
{{See also|Extinction}}
A species is declared extinct after exhaustive surveys of all potential habitats eliminate all reasonable doubt that the last individual of a species, whether in the wild or in captivity, has died. Recently extinct species are defined by the IUCN as becoming extinct after 1500 CE.
class="wikitable sortable"
!Common name!!Binomial name!!Order!!data-sort-type=isoDate|Date of extinction!!width=120pt|Former range!!Picture |
Broad-faced potoroo
|Potorous platyops |1875 {{IUCNlink|18103|1}} |
Eastern hare wallaby
|Lagorchestes leporides |1889 {{IUCNlink|11163|1}} |180px |
Lake Mackay hare-wallaby
|Lagorchestes asomatus |1932 {{IUCNlink|11160|1}} |Australia | |
Desert rat-kangaroo
|Caloprymnus campestris |1935 {{IUCNlink|3626|1}} |180px |
Thylacine or Tasmanian wolf/tiger |Thylacinus cynocephalus |1936 {{IUCNlink|21866|1}} |130px |
Toolache wallaby
|Macropus greyi |1939 {{IUCNlink|12625|1}} |Australia |
Desert bandicoot
|Perameles eremiana |1943 {{IUCNlink|16570|1}} |Australia |
New South Wales barred bandicoot{{Cite journal|last1=TRAVOUILLON|first1=KENNY J.|last2=PHILLIPS|first2=MATTHEW J.|date=2018-02-07|title=Total evidence analysis of the phylogenetic relationships of bandicoots and bilbies (Marsupialia: Peramelemorphia): reassessment of two species and description of a new species|url=https://doi.org/10.11646/zootaxa.4378.2.3|journal=Zootaxa|volume=4378|issue=2|pages=224–256|doi=10.11646/zootaxa.4378.2.3|pmid=29690027 |issn=1175-5334}}
|Perameles fasciata |data-sort-value="1850"|mid-19th century |Australia |File:Gerard Krefft - Western barred Bandicoot, Perameles bougainville - Google Art Project.jpg |
Southwestern barred bandicoot
|Perameles myosuros |data-sort-value="1850"|mid-19th century |Australia |
Southern barred bandicoot
|Perameles notina |data-sort-value="1850"|mid-19th century |Australia | |
Nullarbor barred bandicoot
|Perameles papillon |data-sort-value="1915" | early 20th century |Australia | |
Lesser bilby or yallara |Macrotis leucura |data-sort-value="1965"|1960s {{IUCNlink|12651|1}} |180px |
Southern pig-footed bandicoot
|Chaeropus ecaudatus |data-sort-value="1955"|1950s {{IUCNlink|4322|1}} |180px |
Northern pig-footed bandicoot
|Chaeropus yirratji |data-sort-value="1955"|1950s |
Crescent nail-tail wallaby
|Onychogalea lunata |1956 {{IUCNlink|15331|1}} |Australia (western and central) |
Red-bellied gracile opossum or red-bellied gracile mouse opossum |Cryptonanus ignitus |1962 {{IUCNlink|41320|1}} | |
Nullarbor dwarf bettong
|Bettongia pusilla |{{sort|1500 |
|Australia (Nullarbor Plain)
|
|-
|Hydrodamalis gigas
{{small|von Zimmermann, 1780}}
|1768 {{IUCNlink|10303|1}}
|Commander Islands (Russia, United States)
|-
|Melomys rubicola
{{small|Thomas, 1924}}
|2016 {{IUCNlink|13132|1}}
|Australia (Bramble Cay)
|-
|Boromys offella
{{small|Miller, 1916}}
|{{sort|1500|}} early 1500s {{IUCNlink|2885|1}}
|Cuba
|-
|Boromys torrei
{{small|Allen, 1917}}
|{{sort|1500|}} early 1500s {{IUCNlink|2886|1}}
|Cuba
|-
|Hexolobodon phenax
{{small|Miller, 1929}}
|{{sort|1500|}} early 1500s {{IUCNlink|10034|1}}
|Hispaniola (currently Haiti and the Dominican Republic)
|
|-
|Isolobodon montanus
{{small|Miller, 1922}}
|{{sort|1500|}} early 1500s {{IUCNlink|10859|1}}
|Hispaniola
|
|-
|Lagostomus crassus
{{small|Thomas, 1910}}
|{{sort|1900|}} early 1900s {{IUCNlink|136452|1}}
|Peru
|
|-
|Megaoryzomys curioi
{{small|Niethammer, 1964}}
|{{sort|1500|}} 1500s {{IUCNlink|136657|1}}
|Santa Cruz Island (Galápagos)
|-
|Geocapromys columbianus
{{small|Chapman, 1892}}
|{{sort|1500|}} early 1500s {{IUCNlink|16645|1}}
|Cuba
|
|-
|Brotomys voratus
{{small|Miller, 1916}}
|data-sort-value="1540"|1536–1546 {{IUCNlink|3121|1}}
|Hispaniola
|
|-
|Isolobodon portoricensis
{{small|Allen, 1916}}
|{{sort|1900|}} early 1900s {{IUCNlink|10860|1}}
|Hispaniola; introduced to Puerto Rico, Saint Thomas Island, Saint Croix, U.S. Virgin Islands and Mona Island
|
|-
|Notomys macrotis
{{small|Thomas, 1921}}
|1843 {{IUCNlink|14865|1}}
|Australia (central Western Australia)
|
|-
|Notomys mordax
{{small|Thomas, 1921}}
|1846 {{IUCNlink|14866|1}}
|Australia (Darling Downs, Queensland)
|
|-
|Conilurus albipes
{{small|Lichtenstein, 1829}}
|{{sort|1860|}} early 1860s {{IUCNlink|5223|1}}
|Australia (eastern coast)
|-
|Conilurus capricornensis
{{small|Cramb and Hocknull, 2010}}
|{{sort|1500|}} early 1500s {{IUCNlink|75927841|1}}
|Australia (Queensland)
|
|-
|Notomys amplus
{{small|Brazenor, 1936}}
|1896 {{IUCNlink|14861|1}}
|Australia (Great Sandy Desert)
|
|-
|Notomys longicaudatus
{{small|Gould, 1844}}
|1901 {{IUCNlink|14864|1}}
|Australia
|-
|Notomys robustus
{{small|Mahoney, Smith and Medlin, 2008}}
|{{sort|1800|}} mid-1800s {{IUCNlink|45958541|1}}
|Australia (Flinders Ranges and Davenport Ranges)
|
|-
|Desmarest's pilorie
or Martinique giant rice rat
|Megalomys desmarestii
{{small|Fischer, 1829}}
|1902 {{IUCNlink|12980|1}}
|-
|Saint Lucia pilorie
or Saint Lucia giant rice rat
|Megalomys luciae
{{small|Major, 1901}}
|1881 {{IUCNlink|12981|1}}
|-
|Rattus nativitatis
{{small|Thomas, 1888}}
|1903 {{IUCNlink|19351|1}}
|-
|Rattus macleari
{{small|Thomas, 1887}}
|1903 {{IUCNlink|19344|1}}
|Christmas Island
|-
|Nesoryzomys darwini
{{small|Osgood, 1929}}
|1930 {{IUCNlink|14706|1}}
|
|-
|Pseudomys gouldii
{{small|Waterhouse, 1839}}
|1930 {{IUCNlink|18551|1}}
|Australia (southern half)
|-
|Plains rat
or palyoora
|Pseudomys auritus
{{small|Thomas, 1910}}
|{{sort|1800|}} early 1800s {{IUCNlink|75927882|1}}
|Australia (Kangaroo Island and the Younghusband Peninsula)
|
|-
|Peromyscus pembertoni
{{small|Burt, 1932}}
|1931 {{IUCNlink|16645|1}}
|San Pedro Nolasco Island, Mexico
|-
|Plagiodontia ipnaeum
{{small|Johnson, 1948}}
|{{sort|1500|}} early 1500s {{efn|A 1985 study suggested they may have survived into the 1900s based on local legends of the "comadreja"}} {{IUCNlink|17462|1}}
|Hispaniola
|
|-
|Antillothrix bernensis
{{small| MacPhee, Horovitz, Arredondo, & Jimenez Vasquez, 1995}}
|data-sort-value="1515"| early 16th century
|Hispaniola (currently Dominican Republic)
|
|-
|Lesser stick-nest rat
or white-tipped stick-nest rat
|Leporillus apicalis
{{small|John Gould, 1854}}
|1933 {{IUCNlink|11633|1}}
|Australia (west-central)
|-
|Indefatigable Galápagos mouse
|Nesoryzomys indefessus
{{small|Thomas, 1899}}
|1934 {{IUCNlink|14708|1}}
|Galápagos Islands
|
|-
|Geocapromys thoracatus
{{small|True, 1888}}
|1955 {{IUCNlink|9003|1}}
|-
|Pseudomys glaucus
{{small|Thomas, 1910}}
|1956 {{IUCNlink|18564|1}}
|Australia (Queensland, New South Wales)
|
|-
|Buhler's coryphomys
or Buhler's rat
|Coryphomys buehleri
{{small|Schaub, 1937}}
|{{sort|1500|}} early 1500s {{IUCNlink|5414|1}}
|
|-
|Heteropsomys insulans
{{small|Anthony, 1916}}
|{{sort|1500|}} early 1500s {{IUCNlink|10025|1}}
|Vieques Island, Puerto Rico
|
|-
|Juscelinomys candango
{{small|Moojen, 1965}}
|1960 {{IUCNlink|10946|1}}
|Central Brazil
|-
|Neotoma anthonyi
{{small|Allen, 1898}}
|1926 {{IUCNlink|14576|1}}
|Isla Todos Santos, Mexico
|
|-
|Neotoma bunkeri
{{small|Burt, 1932}}
|1931 {{IUCNlink|14577|1}}
|Coronado Islands, Mexico
|
|-
|Noronhomys vespuccii
{{small|Carleton and Olson, 1999}}
|1500 {{IUCNlink|136692|1}}
|Fernando de Noronha, Brazil
|
|-
|St. Vincent colilargo
or St. Vincent pygmy rice rat
|Oligoryzomys victus
{{small|Thomas, 1898}}
|1892 {{IUCNlink|15255|1}}
|
|-
|Oryzomys antillarum
{{small|Thomas, 1898}}
|1877 {{IUCNlink|136540|1}}
|Jamaica
|-
|Oryzomys nelsoni
{{small|Merriam, 1889}}
|1897 {{IUCNlink|15583|1}}
|Islas Marías, Mexico
|-
|Nevis rice rat,
St. Eustatius rice rat, or St. Kitts rice rat
|Pennatomys nivalis
{{small|Turvey, Weksler, Morris & Nokkert, 2010}}
|{{sort|1500|}} early 1500s {{efn|There were reports of unusual rats on Nevis being eaten by islanders in the 1930s.{{cite journal|first1=Samuel T.|last1=Turvey|first2=Marcelo|last2= Weksler|first3=Elaine L.|last3=Morris|first4=Mark|last4=Nokkert|year=2010|title=Taxonomy, phylogeny, and diversity of the extinct Lesser Antillean rice rats (Sigmodontinae: Oryzomyini), with description of a new genus and species|journal=Zoological Journal of the Linnean Society|volume=160|issue=4|pages=748–772|doi=10.1111/j.1096-3642.2009.00628.x|doi-access=free}}}} {{IUCNlink|199838|1}}
| Sint Eustatius and Saint Kitts and Nevis
|-
|Pipistrellus murrayi
{{small|Andrews, 1900}}
|2009 {{IUCNlink|136769|1}}
|Christmas Island
|
|-
|Prolagus sardus
{{small|Wagner, 1832}}
|1774 {{IUCNlink|18338|1}}
|-
|Solenodon marcanoi
{{small|Patterson, 1962}}
|{{sort|1500|}} 1500s {{IUCNlink|20322|1}}
|Dominican Republic
|
|-
|Nesophontes edithae
{{small|Anthony, 1916}}
|{{sort|1500|}} early 1500s {{IUCNlink|41313|1}}
|Puerto Rico, Vieques Island, Saint John, U.S. Virgin Islands and Saint Thomas, U.S. Virgin Islands
|-
|Nesophontes hypomicrus
{{small|Miller, 1929}}
|{{sort|1500|}} early 1500s {{IUCNlink|14672|1}}
|Hispaniola
|
|-
|Nesophontes major
{{small|Arredondo, 1970}}
|{{sort|1500|}} early 1500s {{IUCNlink|136381|1}}
|Cuba
|
|-
|Nesophontes micrus
{{small|Allen, 1917}}
|{{sort|1500|}} early 1500s {{IUCNlink|14673|1}}
|Cuba (including Isla de la Juventud)
|
|-
|Nesophontes paramicrus
{{small|Miller, 1929}}
|{{sort|1500|}} early 1500s {{IUCNlink|14674|1}}
|Hispaniola
|
|-
|Nesophontes zamicrus
{{small|Miller, 1929}}
|{{sort|1500|}} early 1500s {{IUCNlink|14676|1}}
|Haiti
|
|-
|Lesser Mascarene flying fox
or dark flying fox
|Pteropus subniger
{{small|kerr, 1792}}
|1864 {{IUCNlink|18761|1}}
|-
|Guam flying fox
or Guam fruit bat
|Pteropus tokudae
{{small|Tate, 1934}}
|1968 {{IUCNlink|18763|1}}
|Guam
|
|-
|Dusky flying fox
or Percy Island flying fox
|Pteropus brunneus
{{small|Dobson, 1878}}
|1870 {{IUCNlink|18718|1}}
|Percy Islands (Australia)
|
|-
|Pteropus pilosus
{{small|Andersen, 1908}}
|1874 {{IUCNlink|18749|1}}
|
|-
|Palaeopropithecus ingens
{{small|Grandidier, 1899}}
|1620 {{IUCNlink|136532|1}}
|130px
In green
|-
|Bos primigenius
{{small|Bojanus, 1827}}
|1627 {{IUCNlink|136721|1}}
|-
|Hippotragus leucophaeus
{{small|Pallas, 1766}}
|1800 {{IUCNlink|10168|1}}
|-
|Eudorcas rufina
{{small|Thomas, 1894}}
|{{sort|1800|}} late 1800s {{IUCNlink|8974|1}}
|Algeria
|-
|Rucervus schomburgki
{{small|Blyth, 1863}}
|1932 {{IUCNlink|4288|1}}
|Thailand
|-
|Queen of Sheba's gazelle
or Yemen gazelle
|Gazella bilkis
{{small|Grover and Lay, 1985}}
|1951 {{IUCNlink|8987|1}}
|Yemen
|
|-
|Madagascan dwarf hippopotamus
|Hippopotamus lemerlei
{{small|Milne-Edwards, 1868}}
|{{sort|1500|}} early 1500s {{efn|Although, 14C dating points their extinction at 1000 C. E., a 1991 study found they coexisted with humans and survived into the 1500s.{{cite journal|first1=R. D. E.|last1=MacPhee|first2=David A.|last2=Burney|year=1991|title=Dating of modified femora of extinct dwarf Hippopotamus from Southern Madagascar: Implications for constraining human colonization and vertebrate extinction events|journal=Journal of Archaeological Science|volume=18|issue=6|pages=695–706|doi=10.1016/0305-4403(91)90030-S|doi-access=free|bibcode=1991JArSc..18..695M }}}} {{IUCNlink|40782|1}}
|Madagascar
|-
|Falkland Islands wolf or warrah
|Dusicyon australis
{{small|Kerr, 1792}}
|1876 {{IUCNlink|6923|1}}
|-
|Dusicyon avus
{{small|Burmeister, 1866}}
|{{sort|1500|}} early 1500s {{IUCNlink|82337482|1}}
|Argentina, Chile, Brazil, Uruguay, Paraguay
|
|-
|Neogale macrodon
{{small|Prentiss, 1903}}
|1894 {{IUCNlink|40784|1}}
|United States (Maine, Massachusetts) and Canada (New Brunswick, Newfoundland)
|
|-
|Zalophus japonicus
{{small|Peters, 1866}}
|data-sort-value="1975"|1970s {{IUCNlink|41667|1}}
|-
|Neomonachus tropicalis
{{small|Gray, 1850}}
|1952 {{IUCNlink|13655|1}}
|-
|Cryptoprocta spelea
{{small|Grandidier, 1902}}
|{{sort|1658|}} before 1658 {{IUCNlink|136456|1}}
|-
|Nyctophilus howensis
{{small|McKean, 1975}}
|data-sort-value="1972"| prior to 1972 {{IUCNlink|15006|1}}
|Lord Howe Island, Australia
|-
|Lutra nippon
Imaizumi & Yoshiyuki, 1989
|}
Extinct subspecies
class="wikitable sortable"
!Common name!!Binomial name!!Species!!Order!!Date of extinction!!width=120pt|Former range!!Picture | |
Mississippi Valley wolf
|Canis rufus gregoryi |Red wolf (Canis rufus) |1980 | | |
Caucasian wisent
| Bison bonasus caucasicus | European bison (Bison bonasus)
|1927 |
Carpathian wisent
|Bison bonasus hungarorum |European bison (Bison bonasus) |1852 | | |
Quagga
|Equus quagga quagga |Plains zebra (Equus quagga) |1883 | |
Japanese wolf
|Canis lupus hodophilax |Grey wolf (Canis lupus) |1905 |Asia | |
Hokkaido wolf
|Canis lupus hattai |Grey wolf (Canis lupus) |1889 |Asia | |
Atlas bear
|Ursus arctos crowtheri |Brown bear (Ursus arctos) |1890 |Africa | |
Bali tiger
|Panthera tigris sondaica |Tiger (Panthera tigris) |1950s |Asia | |
Caspian tiger
|Panthera tigris tigris |Tiger (Panthera tigris) |1970s |Asia | |
Javan tiger
|Panthera tigris sondaica |Tiger (Panthera tigris) |1980s |Asia | |
Bubal hartebeest
|Alcelaphus buselaphus buselaphus |Hartebeest (Alcephalus buselaphus) |1925 | |
Portuguese ibex
|Capra pyrenaica lusitanica |Iberian ibex (Capra pyrenaica) |1892 | |
Pyrenean ibex
|Capra pyrenaica pyreneica |Iberian ibex (Capra pyrenaica) |2000 | |
Western black rhinoceros
|Diceros bicornis longipes |Black rhinoceros (Diceros bicornis) |2011 | |
Cape lion
|Panthera leo melanochaita |Lion (Panthera leo) |mid 19th century | |
Barbary lion
|Panthera leo leo |Lion (Panthera leo) |1960s | |
Southern Rocky Mountain wolf
|Canis lupus nubilus |Grey wolf (Canis lupus) |1935 | |
Kenai Peninsula wolf
|Canis lupus occidentalis |Grey wolf (Canis lupus) |1925 | |
Banks Island wolf
|Canis lupus arctos |Grey wolf (Canis lupus) |1952 | |
Newfoundland wolf
|Canis lupus nubilus |Grey wolf (Canis lupus) |1911 | |
Florida black wolf
|Canis rufus floridanus |Red wolf (Canis rufus) |1934 | |
Cascade Mountains wolf
|Canis lupus nubilus |Grey wolf (Canis lupus) |1944 |North America | |
Mogollon mountain wolf
|Canis lupus nubilus |Grey wolf (Canis lupus) |1970s | |
Texas wolf
|Canis lupus nubilus |Grey wolf (Canis lupus) |19th century | |
Sicilian wolf
|Canis lupus cristaldii |Grey wolf (Canis lupus) |1924 | |
Mexican grizzly bear
|Ursus arctos nelsoni |Brown bear (Ursus arctos) |1965 | |
California grizzly bear
|Ursus arctos californicus |Brown bear (Ursus arctos) |1924 | |
Tarpan
|Equus ferus ferus |Wild horse (Equus ferus) |1909 |
Extinct in the [[Wildlife|wild]]
{{See also|Extinct in the wild}}
A species that is extinct in the wild is one which has been categorized by the International Union for Conservation of Nature (IUCN) as only known by living members kept in captivity or as a naturalized population outside its historic range due to massive habitat loss. A species is declared extinct in the wild after thorough surveys have inspected its historic range and failed to find evidence of a surviving individual.{{cite book|url=http://www.iucnredlist.org/documents/redlist_cats_crit_en.pdf|title=IUCN Redlist Categories and Criteria|year=2012|publisher= IUCN Species Survival Commission|edition=2nd|isbn=978-2-8317-1435-6|location=Gland, Switzerland}}
class="wikitable sortable"
!Common name!!Binomial name!!Order!!Date of extinction!!Former range!!Picture |
Père David's deer
|Elaphurus davidianus |1939 {{IUCNlink|7121|1}} |China |
Possibly extinct
{{See also|Possibly extinct}}
Extinction of taxa is difficult to detect, as a long gap without a sighting is not definitive. Some mammals declared as extinct may very well reappear. For example, a study found that 36% of purported mammalian extinction had been resolved, while the rest either had validity issues (insufficient evidence) or had been rediscovered. As of December 2015, the IUCN listed 30 mammalian species as "critically endangered (possibly extinct)".
class="wikitable sortable"
!Common name!!Binomial name!!Order!!Last confirmed sighting!!Range!!Picture |
Kouprey or forest ox |Bos sauveli |1988 {{IUCNlink|2890|1}} | |
Garrido's hutia
|Capromys garridoi |1989 {{IUCNlink|14254|1}}{{dead link|date=July 2018}} | |
Christmas Island shrew
|Crocidura trichura |1985 {{IUCNlink|136379|1}} | |
Wimmer's shrew
|Crocidura wimmeri |1976 {{IUCNlink|5587|1}} | |
Baiji or Yangtze river dolphin |Lipotes vexillifer |2002 {{efn|The species may be functionally extinct.{{cite journal|first1=Samuel T.|last1=Turvey|first2=Robert L.|last2=Pitman|first3= Barbara L.|last3=Taylor |first4=Jay|last4=Barlow|first5=Tomonari|last5=Akamatsu|first6=Leigh A.|last6=Barrett|first7=Xiujiang|last7=Zhao|first8=Randall R.|last8=Reeves|first9=Brent S.|last9=Stewart|last10=Kexiong|first10= Wang|last11=Zhuo|first11=Wei |first12=Xianfeng|last12=Zhang|first13=L. T.|last13=Pusser|first14=Michael|last14=Richlen|first15=John R.|last15=Brandon|first16=Ding|last16=Wang|year=2007|title=First human-caused extinction of a cetacean species?|journal=Biology Letters|volume=3|issue=5|doi=10.1098/rsbl.2007.0292|pages=537–540|pmid=17686754|pmc=2391192}}}} {{IUCNlink|12119|1}} |
Zuniga's dark rice rat
|Melanomys zunigae |1949 {{IUCNlink|13048|1}} |Peru | |
Dwarf hutia
|Mesocapromys nanus |1937 {{IUCNlink|13217|1}} |Ciénaga de Zapata, | |
San Felipe hutia or little earth hutia |Mesocapromys sanfelipensis |1978 {{IUCNlink|13218|1}} |Cuba | |
One-striped opossum
|Monodelphis unistriata |1899 {{IUCNlink|13703|1}} | |
Gloomy tube-nosed bat
|Murina tenebrosa |1962 {{IUCNlink|13948|1}} |Tsushima Island and possibly Yaku Island, | |
New Zealand greater short-tailed bat
|Mystacina robusta |1967 {{IUCNlink|14260|1}} |
Ethiopian amphibious rat or Ethiopian water mouse |Nilopegamys plumbeus |1920s {{IUCNlink|40766|1}} |Mouth of the Lesser Abay River, | |
Angel Island mouse
|Peromyscus guardia |1991 {{IUCNlink|16664|1}} |Isla Ángel de la Guarda, | |
Puebla deer mouse
|Peromyscus mekisturus |1950s {{IUCNlink|16675|1}} |Ciudad Serdan and Tehuacán, | |
Telefomin cuscus
|Phalanger matanim |1997 {{IUCNlink|16851|1}} | |
Montane monkey-faced bat
|Pteralopex pulchra |1990s {{IUCNlink|18658|1}} | |
Aru flying fox
|Pteropus aruensis |1877 {{IUCNlink|136504|1}} | |
Emma's giant rat
|Uromys emmae |1990s {{IUCNlink|136470|1}} |Papua Province, | |
Emperor rat
|Uromys imperator |1888 {{IUCNlink|22803|1}} |Guadalcanal, | |
Guadalcanal rat
|Uromys porculus |1888 {{IUCNlink|22805|1}} |Guadalcanal, | |
Malabar large-spotted civet or Malabar civet |Viverra civettina |late 1900s {{efn|The last confirmed sighting is unknown and their range in the wild is unconfirmed. Camera traps in Karnataka, their presumed habitat, found no individuals after 1,084 nights in 2006.{{cite journal|last1= Rao|first1=S.|last2=Ashraf|first2=N. V. K.|last3=Nixon|first3=A. M. A.|year=2007|title=Search for the Malabar Civet Viverra civettina in Karnataka and Kerala, India, 2006–2007|journal=Small Carnivore Conservation|volume=37| pages=6–10}}}} {{IUCNlink|23036|1}} | |
See also
Notes
{{notelist|50em}}
References
{{Reflist}}
{{Mammals}}
{{Mammal lists}}
{{DEFAULTSORT:List of Extinct Mammals}}