Island gigantism, or insular gigantism, is a biological phenomenon in which the size of an animal species isolated on an island increases dramatically in comparison to its mainland relatives. Island gigantism is one aspect of the more general "island effect" or "Foster's rule", which posits that when mainland animals colonize islands, small species tend to evolve larger bodies, and large species tend to evolve smaller bodies (insular dwarfism). This is itself one aspect of the more general phenomenon of island syndrome which describes the differences in morphology, ecology, physiology and behaviour of insular species compared to their continental counterparts. Following the arrival of humans and associated introduced predators (dogs, cats, rats, pigs), many giant as well as other island endemics have become extinct (e.g. the dodo and Rodrigues solitaire, giant flightless pigeons related to the Nicobar pigeon). A similar size increase, as well as increased woodiness, has been observed in some insular plants such as the Mapou tree (Cyphostemma mappia) in Mauritius which is also known as the "Mauritian baobab" although it is member of the grape family (Vitaceae).
Large mammalian carnivores are often absent on islands because of insufficient range or difficulties in over-water dispersal. In their absence, the ecological niches for large predators may be occupied by birds, reptiles or smaller carnivorans, which can then grow to larger-than-normal size. For example, on prehistoric Gargano Island in the Miocene-Pliocene Mediterranean, on islands in the Caribbean like Cuba, and on Madagascar and New Zealand, some or all apex predators were birds like eagles, falcons and owls, including some of the largest known examples of these groups. However, birds and reptiles generally make less efficient large predators than advanced carnivorans.
Since small size usually makes it easier for herbivores to escape or hide from predators, the decreased predation pressure on islands can allow them to grow larger.[1] Small herbivores may also benefit from the absence of competition from missing types of large herbivores.
Benefits of large size that have been suggested for island tortoises include decreased vulnerability to scarcity of food and/or water, through ability to survive for longer intervals without them, or ability to travel longer distances to obtain them. Periods of such scarcity may be a greater threat on oceanic islands than on the mainland.[2]
Thus, island gigantism is usually an evolutionary trend resulting from the removal of constraints on the size of small animals related to predation and/or competition.[3] Such constraints can operate differently depending on the size of the animal, however; for example, while small herbivores may escape predation by hiding, large herbivores may deter predators by intimidation. As a result, the complementary phenomenon of island dwarfism can also result from the removal of constraints related to predation and/or competition on the size of large herbivores.[4] In contrast, insular dwarfism among predators more commonly results from the imposition of constraints associated with the limited prey resources available on islands.[4] As opposed to island dwarfism, island gigantism is found in most major vertebrate groups and in invertebrates.
Territorialism may favor the evolution of island gigantism. A study on Anaho Island in Nevada determined that reptile species that were territorial tended to be larger on the island compared to the mainland, particularly in the smaller species. In territorial species, larger size makes individuals better able to compete to defend their territory. This gives additional impetus to evolution toward larger size in an insular population.[5]
A further means of establishing island gigantism may be a founder effect operative when larger members of a mainland population are superior in their ability to colonize islands.[6]
Island size plays a role in determining the extent of gigantism. Smaller islands generally accelerate the rate of evolution of changes in organism size, and organisms there evolve greater extremes in size.[7]
Examples of island gigantism include:
Many rodents grow larger on islands, whereas carnivorans, proboscideans and artiodactyls usually become smaller.
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Balearic giant shrew | Nesiotites hidalgo | Majorca and Menorca | Extinct (3000-2000 BC) | Red-toothed shrews | |
Sardinian giant shrew | Asoriculus similis | Sardinia and Corsica | Extinct (Holocene) | ||
Sicilian giant shrew | Asoriculus burgioi | Sicily | Extinct (Early Pleistocene) | ||
Deinogalerix | Deinogalerix spp. | Extinct (Late Miocene) | Moon rats |
Example | Binomial name | Native range | Current status | Continental relative | Insular / mainland length or mass ratio | |
---|---|---|---|---|---|---|
Amblyrhiza inundata | Extinct (Pleistocene) | |||||
Clidomys osborni | Extinct (Late Pleistocene) | |||||
Elasmodontomys obliquus | Extinct (c. 1 AD) | |||||
Quemisia gravis | Extinct | |||||
Arboreal giant hutia[8] | Tainotherium valei | Extinct | ||||
Lesser Jamaica giant hutia | Xaymaca fulvopulvis | Extinct | ||||
Majorcan giant hamsters | Apocricetus darderi Tragomys macpheei | Extinct | Apocricetus alberti[9] Cricetus kormosi[10] | |||
Gargano giant hamster | Hattomys gargantua | Extinct | ||||
Apodemus sylvaticus hirtensis | Least Concern | MR ≈ 2 [11] | ||||
Rhagamys orthodon | Extinct (After 1300 BC) | |||||
Canariomys bravoi | Extinct (Late Pleistocene) | |||||
Canariomys tamarani | Extinct (before AD 1500) | |||||
Formentera black-tailed garden dormouse | Eliomys quercinus ophiusae | Rare (Introduced by humans)[12] | ||||
Balearic giant dormice | Hypnomys spp. | Mallorca & Menorca | Extinct (Holocene) | |||
Sicilian-Maltese giant dormice | Leithia cartei | Sicily and Malta | Extinct | |||
Leithia melitensis | ||||||
Microtus arvalis orcadensis | Vulnerable | |||||
Mikrotia magna M. maiuscula M. parva | Extinct (Early Pliocene) | |||||
Mus musculus muralis | Extinct (c. AD 1930) | |||||
Papagomys armandvillei | ||||||
Paruromys dominator | Least Concern | |||||
Admiralty giant rat | Rattus detentus | Unknown / Likely threatened[13] | ||||
Congreso black rat population[14] | Rattus rattus | Least Concern | ||||
Channel Islands deer mice | Peromyscus anyapahensis P. nesodytes | Extinct (c. 6000 BC) | ||||
Gargano giant dormouse | Stertomys laticrestatus[15] | Extinct | Glirinae dormice |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Nuralagus rex | Extinct (Middle Pliocene) | Alilepus (?) Trischizolagus (?) | ||
Prolagus imperialis | Extinct | Pikas | ||
Prolagus sardus | Extinct (c. AD 1800) |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Antillothrix bernensis | Extinct (before AD 1600) | Cheracebus | ||
Insulacebus toussaintiana | Extinct | |||
Cuban monkeys | Paralouatta marianae[16] P. varonai | Extinct (Pleistocene) | ||
Xenothrix mcgregori | Extinct | |||
Archaeoindris fontoynontii | Extinct (c. 350 BC) | Lorisoids | ||
Archaeolemur spp. Hadropithecus spp. | Extinct (before AD 1280) | |||
Sloth lemurs | Babakotia spp. Palaeopropithecus spp. | Western and Central Madagascar | Extinct (c. AD 1500) | |
Megaladapis edwardsi M. grandidieri M. madagascariensis | Madagascar | Extinct (AD 1280–1420) |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Megalenhydris barbaricina | Extinct (Late Pleistocene) | Otters | ||
Cryptoprocta ferox | Vulnerable | Mongooses | ||
Cryptoprocta spelaea | Extinct (before AD 1400) |
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Balaur | B. bondoc | Extinct (Late Cretaceous) | Jeholornis[17] | ||
Gargantuavis | G. philohinos | Ibero-Armorican Island | Extinct (Late Cretaceous) | Patagopteryx (?) |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Kiwis | Apterygidae | Variable | Proapteryx | |
Greater elephant birds | Aepyornithidae | Extinct (c. AD 1700) | ||
Lesser elephant birds | Mullerornithidae | Extinct (c. AD 1260) | ||
Giant moas | Dinornithidae | Extinct (c. AD 1450) | Tinamous | |
Lesser moas | Emeidae | Extinct (c. AD 1460) | ||
Upland moas | Megalapterygidae | Extinct (c. AD 1300) | ||
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Biziura delautouri | Extinct (after AD 1500) | Australian musk duck | |||
Cnemiornis calcitrans C. gracilis | Extinct | Cape Barren goose | |||
Garganornis | G. ballmanni | Gargano and Scontrone islands | Extinct (Late Miocene) | Geese[18] | |
Chelychelynechen quassus | Extinct (c. AD 1000) | Dabbling ducks | |||
Ptaiochen pau | Extinct (c. AD 1000) | ||||
Thambetochen chauliodous | Extinct (c. AD 1000) | ||||
Thambetochen xanion | Extinct (c. AD 1000) | ||||
Cygnus falconeri | Extinct (Middle Pleistocene) | Mute swan | |||
Malacorhynchus scarletti | Extinct (after AD 1500) | Pink-eared duck |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Megapodius molistructor | Extinct (c. 1500 BC) | Scrubfowl | ||
Megavitiornis | Megavitiornis altirostris | Extinct | Galliformes | |
Sylviornis | Sylviornis neocaledoniae | Extinct | ||
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Aphanapteryx bonasia | Extinct (c. AD 1700) | Rails | |||
Diaphanapteryx hawkinsi | Extinct (c. AD 1900) | ||||
Nesotrochis debooyi | Extinct | ||||
Cuban cave rail | Nesotrochis picapicensis | Extinct | |||
Haitian cave rail | Nesotrochis steganinos | Extinct | |||
Porphyrio hochstetteri | Endangered | ||||
Porphyrio mantelli | Extinct (before AD 1900) | ||||
Adzebills | Aptornis defossor A. otidiformis | Extinct | Madagascar flufftail[19] | ||
Fulica chathamensis | Extinct (after AD 1500) | Red-knobbed coot and other coots | |||
Fulica newtonii | Extinct (c. AD 1700) | ||||
Fulica prisca | Extinct (after AD 1280) | ||||
Porphyrio coerulescens | Extinct (c. AD 1730) | Purple swamphens |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Natunaornis gigoura | Extinct | Crowned pigeons | ||
Caloenas canacorum | Extinct (c. 500 BC) | Nicobar pigeon | ||
Pezophaps solitaria | Extinct (before AD 1778) | |||
Raphus cucullatus | Extinct (c. AD 1662) |
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Liko Cave golden eagle | Aquila chrysaetos simurgh | Extinct (Late Pleistocene) | Golden eagle | ||
Giant crab-hawk[20] | Buteogallus borrasi | Extinct | Great black hawk and other hawks | ||
Giant hawk | Gigantohierax sp. | Extinct | |||
Titanohierax gloveralleni | Extinct | ||||
Caracara tellustris | Extinct | Caracaras | |||
Circus eylesi | Extinct (c. AD 1000) | Swamp harrier | |||
Gargano Island eagles | Garganoaetus freudenthali G. murivorus | Extinct (Late Miocene) | Aquila delphinensis | ||
Hieraaetus moorei | Extinct (c. AD 1400) | Little eagle | |||
Pithecophaga jefferyi | Critically endangered | Bateleur[21] |
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Heracles inexpectatus | Extinct (Miocene) | Other parrots | |||
Strigops habroptilus | Critically Endangered | ||||
Lophopsittacus mauritianus | Extinct (c. AD 1680) | Psittaculine parrots |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Athene cretensis | Extinct (Pleistocene) | Little owl | ||
Cuban giant owls | Ornimegalonyx spp. | Extinct (Pleistocene) | Wood owls | |
Greater Gargano giant owl | Tyto gigantea | Extinct (Late Miocene) | Barn owls | |
Tyto pollens | Extinct (before AD 1600) | |||
Tyto riveroi | Extinct | |||
Lesser Gargano giant owl | Tyto robusta | Extinct (Early Pliocene) | ||
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Aegotheles novazelandiae | Extinct (c. AD 1200) | Australian owlet-nightjar | ||
Aegotheles savesi | Critically endangered |
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Corvus moriorum | Extinct | New Zealand raven | |||
Emberiza alcoveri | Extinct (after AD 1) | Cabanis's bunting | |||
Hemignathus vorpalis | Extinct (after AD 1000) | Finches | |||
Tasmanian superb fairywren | Malurus cyaneus cyaneus | Least Concern | Superb fairywren | ||
Kangaroo Island superb fairywren | Malurus cyaneus ashbyi | Least Concern | |||
Pachyplichas yaldwyni | Extinct | Other passeriforms | |||
Troglodytes troglodytes hirtensis | Unknown | Eurasian wren | |||
Zosterops lateralis chlorocephalus | Unknown | Silvereye |
Example | Binomial name | Native range | Current status | Continental relative | Insular / mainland length or mass ratio |
---|---|---|---|---|---|
Tongan giant iguana[22] | Brachylophus gibbonsi | Extinct (c. 800 BC) | South American iguanas | ||
Fijian giant iguana [23] | Lapitiguana impensa | Extinct (c. 1000 BC) | |||
Sauromalus hispidus | Near Threatened | MR ≈ 5 [24] | |||
Sauromalus varius | Endangered | MR ≈ 5 |
Example | Binomial name | Native range | Current status | Continental relative | Insular / mainland length or mass ratio | |
---|---|---|---|---|---|---|
Gigarcanum delcourti | New Caledonia | Extinct (c. AD 1870) | LR ≈ 6.75 | |||
Rhacodactylus leachianus | Least Concern | LR ≈ 4.4 MR ≈ 60 | ||||
Phelsuma gigas | Extinct (c. AD 1850) |
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Chioninia vaillanti | Endangered | Mainland mabuyine skinks | |||
Macroscincus coctei | Extinct (after AD 1900) | ||||
Leiolopisma mauritiana | Extinct (after AD 1600) | Mainland eugongyline skinks | |||
Phoboscincus bocourti | Endangered | Mainland eugongyline skinks | |||
Plestiodon kishinouyei | Vulnerable | Asian Plestiodon spp. |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Gallotia auaritae | Critically endangered | Mediterranean sandrunner lizards | ||
Gallotia bravoana | Critically endangered | |||
Tenerife giant lizard[25] | Gallotia goliath | Extinct (c. AD 1500) | ||
Gallotia simonyi | Critically endangered | |||
Gallotia stehlini | Least Concern | |||
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Crotalus mitchellii angelensis | Least Concern | Speckled rattlesnake | |||
Tadanae-jima striped snake population[26] | Elaphe quadrivirgata | Unknown | Japanese striped snake | ||
Island tiger snake populations | Notechis scutatus | Islands Mount Chappell (Tasmania); Williams, Hopkins, and the Nuyts Archipelago (all South Australia)[27] | Least Concern[28] | Tiger snake | |
Isla Cerralvo long-nosed snake | Rhinocheilus lecontei etheridgei | Unknown | Long-nosed snake |
Example | Binomial name | Native range | Current status | Continental relative | Insular / mainland length or mass ratio | |
---|---|---|---|---|---|---|
São Tomé giant tree frog | Hyperolius thomensis[35] | Endangered | ||||
Palm forest tree frog | Leptopelis palmatus | Príncipe Island | Vulnerable | LR ≈ 1.2 | ||
Giant Fiji ground frog | Platymantis megabotoniviti[36] | Extinct | ||||
São Tomé giant grass frog | Ptychadena newtoni | São Tomé Island | Endangered |
Example | Binomial name | Native range | Current status | Continental relative |
---|---|---|---|---|
Birgus latro | Indian Ocean islands and Polynesia[37] | Vulnerable | Coenobita hermit crabs | |
Deinacrida spp. | Variable | South African king crickets | ||
Giant pseudoscorpion[38] | Garypus titanius | Critically Endangered | Garypoids | |
Hissing cockroaches | Gromphadorhini spp. | Unknown | Blaberids | |
Labidura herculeana | Extinct (c. AD 1967) | Shore earwig | ||
Megachile pluto | Vulnerable | Callomegachile | ||
Megalara | Megalara garuda | Unknown | Crabronine wasps | |
Microsphaerotherium spp. Sphaeromimus spp. Zoosphaerium spp. | Unknown | Indian giant pill-millipedes (Arthrosphaera) | ||
Orsonwelles | Orsonwelles spp. | Unknown | Money spiders | |
Thaumatogryllus conanti | Unknown | Tree crickets | ||
Giant Fijian long-horned beetle[39] | Xixuthrus heros | Endangered | Australasian Xixuthrus | |
Xixuthrus terribilis | Unknown |
In addition to size increase, island plants may also exhibit "insular woodiness".[40] The most notable examples are the megaherbs of New Zealand's subantarctic islands. Increased leaf and seed size was also reported in some island species regardless of growth form (herbaceous, bush, or tree).[41]
Example | Binomial name | Native range | Current status | Continental relative | |
---|---|---|---|---|---|
Anisotome latifolia | Unknown | Apiaceae | |||
Bulbinella rossii | Naturally Uncommon | New Zealand Maori lily | |||
Chatham Islands korokio[42] | Corokia macrocarpa | Unknown | New Zealand korokio[43] | ||
Damnamenia vernicosa | Naturally Uncommon | Astereae | |||
Cucumber tree[44] | Dendrosicyos socotranus | Vulnerable | Gourds | ||
Coco de mer[45] | Lodoicea maldivica | Endangered | Borassoid palms | ||
Pleurophyllum criniferum | Unknown | Cineraria | |||
Silver-leaf daisy | Pleurophyllum hookeri | Unknown | |||
Pleurophyllum speciosum | Naturally Uncommon | ||||
Stilbocarpa polaris | Vulnerable | Araliaceae |