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Green sea turtle
Green sea turtle
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Green sea turtle
Temporal range: 0.21–0 Ma[1]
Male sea turtle in Moorea, French Polynesia
Female sea turtle
CITES Appendix I (CITES)[3]
Scientific classification Edit this classification
Kingdom: Animalia
Phylum: Chordata
Class: Reptilia
Order: Testudines
Suborder: Cryptodira
Family: Cheloniidae
Subfamily: Cheloniinae
Genus: Chelonia
Brongniart, 1800
Species:
C. mydas
Binomial name
Chelonia mydas
Synonyms[4]
Species synonymy
  • Testudo mydas
    Linnaeus, 1758
  • Testudo macropus
    Walbaum, 1782
    (nomen illegitimum)
  • Testudo viridis
    Schneider, 1783
  • Testudo japonica
    Thunberg, 1787
  • Testudo marina vulgaris
    Lacépède, 1788
  • Testudo viridisquamosa
    Lacépède, 1788
  • Testudo mydas macropus
    Suckow, 1798
  • Chelonia mydas
    Brongniart, 1800
  • Testudo chloronotos
    Bechstein, 1800
  • Testudo cepediana
    Daudin, 1801
  • Testudo rugosa
    Daudin, 1801
  • Chelone mydas
    — Brongniart, 1805
  • Chelonia japonica
    Schweigger, 1812
  • Chelonia virgata
    Schweigger, 1812
  • Caretta cepedii
    Merrem, 1820
  • Caretta esculenta
    Merrem, 1820
  • Caretta thunbergii
    Merrem, 1820
  • Caretta mydas
    Fitzinger, 1826
  • Caretta virgata
    — Fitzinger, 1826
  • Chelonia lachrymata
    Cuvier, 1829
  • Chelonia maculosa
    Cuvier, 1829
  • Chelonia midas [sic]
    Wagler, 1830
    (ex errore)
  • Chelonia mydas var. japonica
    Gray, 1831
  • Chelonia esculenta
    Wiegmann & Ruthe, 1832
  • Chelonia bicarinata
    Lesson, 1834
  • Chelonia marmorata
    A.M.C. Duméril & Bibron, 1835
  • Chelonia (Chelonia)
    cepedeana [sic]
    Fitzinger, 1835
    (ex errore)
  • Chelonia viridis
    Temminck & Schlegel, 1835
  • Mydas mydas
    Cocteau, 1838
  • Mydasea mydas
    Gervais, 1843
  • Euchelonia mydas
    Tschudi, 1846
  • Megemys mydas
    Gistel, 1848
  • Chelonia lacrymata [sic]
    Agassiz, 1857
    (ex errore)
  • Chelonia formosa
    Girard, 1858
  • Chelonia tenuis
    Girard, 1858
  • Euchelys macropus
    — Girard, 1858
  • Chelone macropus
    Strauch, 1862
  • Chelone maculosa
    — Strauch, 1862
  • Chelone marmorata
    — Strauch, 1862
  • Chelone virgata
    — Strauch, 1862
  • Chelone viridis
    — Strauch, 1862
  • Chelonia albiventer
    Nardo, 1864
  • Thalassiochelys albiventer
    Günther, 1865
  • Chelonia agassizii
    Bocourt, 1868
  • Mydas viridis
    — Gray, 1870
  • Chelone midas
    Cope, 1871
  • Chelonia lata
    Philippi, 1887
  • Chelone mydas
    Boulenger, 1889
  • Chelonia mydas mydas
    Mertens & L. Müller, 1928
  • Caretta thunbergi [sic]
    H.M. Smith, 1931
    (ex errore)
  • Chelonia mydas agassizii
    Carr, 1952
  • Chelonia mydas agassizi [sic]
    Schmidt, 1953
    (ex errore)
  • Chelonia mydas carrinegra
    Caldwell, 1962
  • Chelonia agazisii [sic]
    Tamayo, 1962
    (ex errore)
  • Testudo nigrita
    Tamayo, 1962
  • Chelonia agassizi
    — Carr, 1967
  • Chelonia mydus [sic]
    Nutaphand, 1979
    (ex errore)
  • Chelonia mydas carinegra [sic]
    Nutaphand, 1979
    (ex errore)
  • Testudo chloronotus [sic]
    H.M. Smith & R.B. Smith, 1980
    (ex errore)
  • Chelone albiventer
    — Márquez, 1990
  • Caretta thumbergii [sic]
    Sharma, 1998
    (ex errore)
  • Chelonia mydas viridis
    Karl & Bowen, 1999

The green sea turtle (Chelonia mydas), also known as the green turtle, black sea turtle, and Pacific green turtle,[5] is a species of large sea turtle of the family Cheloniidae. It is the only species in the genus Chelonia.[6] Its range extends throughout tropical and subtropical seas around the world, with two distinct populations in the Atlantic and Pacific Oceans, but it is also found in the Indian Ocean.[7][8] The common name refers to the usually green fat found beneath its carapace, due to its diet strictly being seagrass,[9] not to the color of its carapace, which is olive to black.

The dorsoventrally flattened body of C. mydas is covered by a large, teardrop-shaped carapace; it has a pair of large, paddle-like flippers. It is usually lightly colored, although in the eastern Pacific populations, parts of the carapace can be almost black. Unlike other members of its family, such as the hawksbill sea turtle, C. mydas is mostly herbivorous. The adults usually inhabit shallow lagoons, feeding mostly on various species of seagrasses.[10] The green sea turtle is the only aquatic turtle species which is herbivorous when fully grown.

Like other sea turtles, green sea turtles migrate long distances between feeding grounds and hatching beaches. Many islands worldwide are known as Turtle Island due to green sea turtles nesting on their beaches. Females crawl out on beaches, dig nests, and lay eggs during the night. Later, hatchlings emerge, and scramble into the water. Those that reach maturity may live to 90 years in the wild.[7]

C. mydas was listed as endangered by the IUCN and CITES and is protected from exploitation in most countries.[11] It is illegal to collect, harm, or kill them. In addition, many countries have laws and ordinances to protect nesting areas. However, turtles are still in danger due to human activity. In some countries, turtles and their eggs are still hunted for food. Pollution indirectly harms turtles at both population and individual scales. Many turtles die after being caught in fishing nets. In addition, real estate development often causes habitat loss by eliminating nesting beaches.

Taxonomy

[edit]

The green sea turtle is a member of the tribe Cheloniini.[12] A 1993 study clarified the status of genus Chelonia with respect to the other marine turtles. The carnivorous Eretmochelys (hawksbill), Caretta (loggerhead) and Lepidochelys (ridley) were assigned to the tribe Carettini. Herbivorous Chelonia warranted their status as a genus, while Natator (flatback) was further removed from the other genera than previously believed.[13]

The species was originally described by Carl Linnaeus in his landmark 1758 10th edition of Systema Naturae as Testudo mydas.[14] In 1868, Marie Firmin Bocourt named a particular species of sea turtle Chelonia agassizii,[15][16] in honor of Swiss-American zoologist Louis Agassiz.[17] This "species" was referred to as the "black sea turtle".[18] Later research determined Bocourt's "black sea turtle" was not genetically distinct from C. mydas, and thus taxonomically not a separate species.[19] These two "species" were then united as Chelonia mydas and populations were given subspecies status: C. mydas mydas referred to the originally described population, while C. mydas agassizi referred only to the Pacific population known as the Galápagos green turtle.[20][21] This subdivision was later determined to be invalid and all species members were then designated Chelonia mydas.[6] The oft-mentioned name C. agassizi remains an invalid junior synonym of C. mydas.

The species' common name does not derive from any particular green external coloration of the turtle. Its name comes from the greenish color of the turtles' fat, which is only found in a layer between their inner organs and their shell.[22] As a species found worldwide, the green turtle has many local names. In the Hawaiian language it is called honu,[23][24] and it is locally known as a symbol of good luck and longevity.[25]

Description

[edit]
Drawing of turtle carapace and plastron showing respectively, vertebral, costal, marginal, and supracaudal and intergular, gular, pectoral, abdominal, humeral, femoral, anal, axillary (anterior inframarginal), and inguinal (posterior inframarginal) shields
Escalation of carapace and plastron
Taxidermied shell of Chelonia mydas

Its appearance is that of a typical sea turtle. C. mydas has a dorsoventrally flattened body, a beaked head at the end of a short neck, and paddle-like arms well-adapted for swimming.[26] Adult green turtles grow to 1.5 metres (5 ft) long.[27] The average weight of mature individuals is 68–190 kg (150–419 lb) and the average carapace length is 78–112 cm (31–44 in).[28] They are considered the second largest sea turtle in the United States, after the leatherback sea turtle.[29] Exceptional specimens can weigh 315 kg (694 lb) or even more, with the largest known C. mydas having weighed 395 kg (871 lb) and measured 153 cm (60 in) in carapace length.[30]

Anatomically, a few characteristics distinguish the green turtle from the other members of its family. Unlike its close relative the hawksbill turtle, the green turtle's snout is very short and its beak is unhooked. The neck cannot be pulled into the shell.[31] The sheath of the turtle's upper jaw possesses a denticulated edge, while its lower jaw has stronger, serrated, more defined denticulation. The dorsal surface of the turtle's head has a single pair of prefrontal scales. Its carapace is composed of five central scutes flanked by four pairs of lateral scutes. Underneath, the green turtle has four pairs of inframarginal scutes covering the area between the turtle's plastron and its shell. Mature C. mydas front appendages have only a single claw (as opposed to the hawksbill two), although a second claw is sometimes prominent in young specimens.[32]

The carapace of the turtle has various color patterns that change over time. Hatchlings of Chelonia mydas, like those of other marine turtles, have mostly black carapaces and light-colored plastrons. Carapaces of juveniles turn dark brown to olive, while those of mature adults are either entirely brown, spotted or marbled with variegated rays. Underneath, the turtle's plastron is hued yellow. C. mydas limbs are dark-colored and lined with yellow, and are usually marked with a large dark brown spot in the center of each appendage.[7][33]

Distribution

[edit]
Green sea turtle nesting populations

The range of the green sea turtle extends throughout tropical and subtropical oceans worldwide. The two major subpopulations are the Atlantic and the eastern Pacific subpopulations. Each population is genetically distinct, with its own set of nesting and feeding grounds within the population's known range.[7] One of the genetic differences between the two subpopulations is the type of mitochondrial DNA found in individual's cells. Individuals from rookeries in the Atlantic Ocean and Mediterranean Sea have a similar type of mitochondrial DNA, and individuals from the Pacific and Indian Oceans have another type of mitochondrial DNA.[34] Their native range includes tropical to subtropical waters along continental coasts and islands between 30°N and 30°S. Since green sea turtles are a migrating species, their global distribution spans into the open ocean. The differences in mitochondrial DNA more than likely stems from the populations being isolated from each other by the southern tips of both South America and Africa with no warm waters for the green sea turtles to migrate through. The green sea turtle is estimated to inhabit coastal areas of more than 140 countries, with nesting sites in over 80 countries worldwide throughout the year. In the United States Atlantic coast, green sea turtles can be found from Texas to Massachusetts. In the United States Pacific coast, they have been found from southern California north to the southernmost tip of Alaska. The largest populations of green sea turtles within the United States coastline are in the Hawaiian Islands and Florida. Globally, the largest populations of sea turtles are in the Great Barrier Reef in Australia, and the Caribbean Sea.[35] Recently these Turtles were discovered within Rangaunu Harbour in New Zealand.[36]

Atlantic subpopulation

[edit]

The green sea turtle can generally be found throughout the Atlantic Ocean. Although the species is most abundant in tropical climates, green sea turtles can also be found in temperate climates, and individuals have been spotted as far north as Canada in the western Atlantic, and the Cimbrian peninsula in the east. The subpopulation's southern range is known until past the southern tip of Africa in the east and Argentina in the western Atlantic. The major nesting sites can be found on various islands in the Caribbean, along the Atlantic coast of Florida in the United States, the eastern coast of the South American continent and most notably, on isolated North Atlantic islands.

In the Caribbean, major nesting sites have been identified on Aves Island, the U.S. Virgin Islands, Puerto Rico, the Dominican Republic, and Costa Rica. In recent years, there are signs of increased nesting in the Cayman Islands.[37] One of the region's most important nesting grounds is in Tortuguero in Costa Rica.[38] In fact, the majority of the Caribbean region's C. mydas population hails from a few beaches in Tortuguero.[39] Within United States waters, minor nesting sites have been noted in the states of Georgia, North Carolina, and South Carolina. Florida's east coast is the largest nesting site in the United States. Hutchinson Island in particular is a major nesting area in Florida waters. Florida has several annual nesting periods when local beaches are closed or cordoned off to protect nesting sites. According to Green Sea Turtle Watch, in 2015 more than 37,000 green sea turtle nests were documented in Florida, a record number. In addition to sporadic distribution of nesting sites, feeding grounds are much more widely distributed throughout Florida. Important feeding grounds in Florida include Indian River Lagoon, the Florida Keys, Florida Bay, Homosassa, Crystal River, and Cedar Key.[26][40]

Notable locations in South America include secluded beaches in Suriname and French Guiana.[41] In the Southern Atlantic Ocean, the most notable nesting grounds for Chelonia mydas are found on the island of Ascension,[26] hosts 6,000–13,000 turtle nests.[42][43][44]

Indo-Pacific subpopulation

[edit]
Photo of turtle swimming towards surface with diver in background
About to break the surface for air at Kona, Hawaii

In the Pacific, its range reaches as far north as the southern coast of Alaska and as far south as Chile in the east. The turtle's distribution in the western Pacific reaches north to Japan and southern parts of Russia's Pacific coast, and as far south as the northern tip of New Zealand and a few islands south of Tasmania. Significant nesting grounds are scattered throughout the entire Pacific region, including Mexico, the Hawaiian Islands, the South Pacific, the northern coast of Australia, and Southeast Asia. Major Indian Ocean nesting colonies include India, Pakistan, Sri Lanka and other coastal countries.[45]

The turtles can also be found throughout the Indian Ocean; the east coast of the African continent hosts a few nesting grounds, including islands in the waters around Madagascar.[45]

Specific nesting grounds

[edit]
Photo of swimming turtle at twilight in a coral reef near Mexico

Nesting grounds are found all along the Mexican coast. These turtles feed in seagrass pastures in the Gulf of California.[46] Green turtles belonging to the distinct Hawaiian subpopulation nest at the protected French Frigate Shoals some 800 kilometers (500 mi) west of the Hawaiian Islands.[24]

In the Philippines, green turtles nest in the Turtle Islands along with closely related hawksbill turtles.[47] In December 2007, fishermen using a hulbot-hulbot (a type of fish net) accidentally caught an 80 kg (180 lb), 93 cm (37 in) long and 82 cm (32 in) wide turtle off Barangay Bolong, Zamboanga City, Philippines. December is breeding season near the Bolong beach.[48]

An annual presence is recorded in the Gulf of Panama, on the Isla Parida island. Local activists also moving some turtle nests to the coast, in the vicinity of the small town of Malena, to save and increase the turtle population in the safe place.[49]

Indonesia has a few nesting beaches, one in the Meru Betiri National Reserve in East Java.[50]

Off the north-eastern and northern coasts of Australia, the Great Barrier Reef has two genetically distinct populations; one north and one south. Within the reef, 20 separate locations consisting of small islands and cays were identified as nesting sites for either population of C. mydas. Of these, the most important is on Raine Island.[51][52] In the Torres Strait there is a large rookery on Bramble Cay.[53][54] The Coral Sea has nesting areas of world significance.[55]

Major nesting sites are common on either side of the Arabian Sea, both in Ash Sharqiyah, Oman, and along the coast of Karachi, Pakistan. Some specific beaches there, such as Hawke's Bay and Sandspit, are common to both C. mydas and L. olivacea subpopulation. Sandy beaches along Sindh and Balochistan are nesting sites. Some 25 kilometers (16 mi) off the Pakistani coast, Astola island is another nesting beach.[10][56][57]

Galápagos green turtle

[edit]
Green Sea Turtle Swimming in the Galápagos

The population that has often been known as the Galápagos green turtle have been recorded and observed in the Galápagos as far back as the 17th century by William Dampier.[58] Not much attention has been paid to them due to the overwhelming research done on the Galápagos giant tortoises.[59] Only over the last 30 years have extensive studies been performed covering the behaviors of the Galápagos green turtles. Much of the debate that has surrounded them recently is over the binomial classification of the species.[60] At one point the name Chelonia agassizii was applied to this population as a separate species.[19] Analysis of mitochondrial and nuclear DNA of 15 nesting beaches,[60] however, has demonstrated that there is not only no significant distinction of this population but that it would be paraphyletic to recognise it. As such the species name Chelonia agassizzii is considered a junior synonym of Chelonia mydas[60] as such it is considered as a local variant of the populations of the East Pacific waters and those of other nesting areas.[60]

The morphological distinctiveness of the Galápagos green turtle has given rise to the debate,[19] but evidence of taxonomic distinctiveness is best served using the combination of multiple datasets. The two most notable morphological distinctions are the considerably smaller adult size and the much darker pigmentation of the carapace, plastron, and extremities.[19] Other distinctions are the curving of the carapace above each hind flipper, the more dome-shaped carapace, and the very long tail of adult males.[61] Three possibilities have arisen from their unique characteristics: agassizii is a separate species from C. mydas, it is a subspecies of green sea turtle, or it is simply a color mutation.[61] These facts have led to the debate over binomial separation however due to the significance of the DNA testing results there have been no distinctions made at this time.[60] At a meeting for sea turtle scientists and their collaborators in 2000, the evidence for the taxonomic position of the Galápagos green turtle was reviewed and a majority among the participants supported treating it as a population or subspecies of the green turtle (instead of a separate species).[62] However, this is possibly a case of political taxonomy. As such the three major international checklists that cover turtles of the world Reptile Database[63] the checklist of Fritz and Havas (2007)[4] and the IUCN Checklist (TTWG 2017)[64] all consider this a junior synonym.

Habitat

[edit]
Green sea turtle on Punaluu black sand beach of Big Island, Hawaii.

Green sea turtles move across three habitat types, depending on their life stage. They lay eggs on beaches. Mature turtles spend most of their time in shallow, coastal waters with lush seagrass beds. Adults frequent inshore bays, lagoons, and shoals with lush seagrass meadows. Entire generations often migrate between one pair of feeding and nesting areas.[26] Green sea turtles, Chelonia mydas, are classified as an aquatic species and are distributed around the globe in warm tropical to subtropical waters. The environmental parameter that limits the distribution of the turtles is ocean temperatures below 7 to 10 degrees Celsius.[65] Within their geographical range, the green sea turtles generally stay near continental and island coastlines. Near the coastlines, the green sea turtles live within shallow bays and protected shores. In these protected shores and bays, the green sea turtle habitats include coral reefs, salt marshes, and nearshore seagrass beds. The coral reefs provide red, brown, and green algae for their diet and give protection from predators and rough storms within the ocean. The salt marshes and seagrass beds contain seaweed and grass vegetation, allowing ample habitat for the sea turtles.[35]

Turtles spend most of their first five years in convergence zones within the bare open ocean that surround them.[10][66] These young turtles are rarely seen as they swim in deep, pelagic waters.[67][68] Green sea turtles typically swim at 2.5–3 km/h (1.6–1.9 mph).[69]

Ecology and behavior

[edit]
Turtle swimming toward surface
Swimming, Hawaii

As one of the first sea turtle species studied, much of what is known of sea turtle ecology comes from studies of green turtles. The ecology of C. mydas changes drastically with each stage of its life history. Newly emerged hatchlings are carnivorous, pelagic organisms, part of the open ocean mininekton. In contrast, immature juveniles and adults are commonly found in seagrass meadows closer inshore as herbivorous grazers.

Diet

[edit]
Green sea turtle grazing on seagrass

The diet of green turtles changes with age.[70] Juveniles are carnivorous, but as they mature they become omnivorous.[71] Young sea turtles eat fish and their eggs, sea hare eggs, hydrozoans, bryozoans, molluscs, jellyfish, small invertebrates, echinoderms, tunicates, insects, worms, sponges, algae, sea grasses, leaves, tree bark, and crustaceans.[72][73][35][74] Green sea turtles have a relatively slow growth rate because of the low nutritional value of their diet. Body fat turns green because of the consumed vegetation.[71] This diet shift has an effect on the green turtle's skull morphology.[75] Their serrated jaw helps them chew green and red algae (such as filamentous red alga (Bostrychia), red moss (Caloglossa), freshwater red algae (Compsopogon), lobster horns (Polysiphonia), sea lettuce (Ulva lactuca), green seaweed (Gayralia), and crinkle grass (Rhizoclonium)) and sea grasses.[73][76] They also consume large quantities of wetland plants such as Avicennia schaueriana and Sporobolus alterniflorus, which are commonly found in salt marshes.[73] Most adult sea turtles are strictly herbivorous.[71]

Predators and parasites

[edit]

Only some human beings and the larger sharks feed on C. mydas adults. Specifically, tiger sharks (Galeocerdo cuvier) hunt adults in Hawaiian waters.[77] The tiger shark is the main predator of the green turtle as it will prey on green turtles of all sizes. The tiger shark has often been seen feeding on green turtles near their nesting beaches because they are restricted in the area of their nesting beaches and vulnerable to predation.[78] Juveniles and new hatchlings have significantly more predators, including crabs, small marine mammals and shorebirds.[7] Additionally, their eggs are vulnerable to predation by scavengers like red foxes and golden jackals.[79]

Green sea turtles have a variety of parasites including barnacles, leeches, protozoans, cestodes, and nematodes. Barnacles attach to the carapace, and leeches to the flippers and skin of the turtles, causing damage to the soft tissues and leading to blood loss. Protozoans, cestodes and nematodes lead to many turtle deaths because of the infections in the liver and intestinal tract they cause. The greatest disease threat to the turtle population is fibropapilloma, which produces lethal tumor growth on scales, lungs, stomach, and kidneys. Fibropapilloma is caused by a herpesvirus that is transmitted by leeches such as Ozobranchus branchiatus, a species of leech which feeds almost entirely on green sea turtles.[65][80]

Life cycle

[edit]
Photo of newly hatched turtle held in human hand
Hatchling

Green sea turtles migrate long distances between feeding sites and nesting sites; some swim more than 2,600 kilometres (1,600 mi) to reach their spawning grounds. Beaches in Southeast Asia, India, islands in the western Pacific, and Central America are where green sea turtles breed.[8] Mature turtles often return to the exact beach from which they hatched. Females usually mate every two to four years. Males, on the other hand, visit the breeding areas every year, attempting to mate.[81] Mating seasons vary between populations. For most C. mydas in the Caribbean, mating season is from June to September.[26] The French Guiana nesting subpopulation nests from March to June.[41] In the tropics, green turtles nest throughout the year, although some subpopulations prefer particular times of the year. In Pakistan, Indian Ocean turtles nest year-round, but prefer the months of July to December.[56]

Returning tracks from a female green sea turtle
Returning tracks from a female green sea turtle that had nested on Ilha do Fogo, Mozambique

Sea turtles return to the beaches on which they were born to lay their own eggs. The reason for returning to native beaches may be that it guarantees the turtles an environment that has the necessary components for their nesting to be successful. These include a sandy beach, easy access for the hatchlings to get to the ocean, the right incubation temperatures, and low probability of predators that may feed on their eggs. Over time these turtles have evolved these tendencies to return to an area that has provided reproductive success for many generations. Their ability to return to their birthplace is known as natal homing.[82] The males also return to their birthplaces in order to mate. These males that return to their homes know they will be able to find mates because the females born there also return to breed. By doing this, the green sea turtles are able to improve their reproductive success and is why they are willing to expend the energy to travel thousands of miles across the ocean in order to reproduce.

Mating behaviour is similar to other marine turtles. Female turtles control the process. A few populations practice polyandry, although this does not seem to benefit hatchlings.[83] After mating in the water, the female moves above the beach's high tide line, where she digs a hole 28–56 centimetres (11–22 in) in depth with her hind flippers and deposits her eggs. The hole is then covered up again.[84] Clutch size ranges between 85 and 200, depending on the age of the female. This process takes about an hour to an hour and a half. After the nest is completely covered, she returns to the sea. The female will do this 3 to 5 times in one season.[8]

Green sea turtle hatchlings on the beach

The eggs are round and white, and about 45 mm (1.8 in) in diameter. The hatchlings remain buried for days until they all emerge together at night.[84] The temperature of the nest determines the sex of the turtles at around the 20–40 day mark. Green Sea Turtles are type 1a, meaning males develop at cooler temperatures while females are produced under hot temperatures.[85][86] At around 50 to 70 days,[87] the eggs hatch during the night, and the hatchlings instinctively head directly into the water. This is the most dangerous time in a turtle's life. As they walk, predators, such as gulls and crabs, feed on them. A significant percentage never make it to the ocean. Little is known of the initial life history of newly hatched sea turtles.[26] Juveniles spend three to five years in the open ocean before they settle as still-immature juveniles into their permanent shallow-water lifestyle.[67][68] It is speculated that they take twenty to fifty years to reach sexual maturity. Individuals live up to eighty years in the wild.[7] It is estimated that only 1% of hatchlings reach sexual maturity.

Hatchling on beach going towards Indian Ocean, Dar es Salaam, Tanzania

Each year on Ascension Island in the South Atlantic, C. mydas females create 6,000 to 25,000 nests. They are among the largest green turtles in the world; many are more than 1 metre (3 ft 3 in) in length and weigh up to 300 kilograms (660 lb).[88]

Breathing and sleep

[edit]

Sea turtles spend almost all their lives submerged, but must breathe air for the oxygen needed to meet the demands of vigorous activity. With a single explosive exhalation and rapid inhalation, sea turtles can quickly replace the air in their lungs. The lungs permit a rapid exchange of oxygen and prevent gases from being trapped during deep dives. Sea turtle blood can deliver oxygen efficiently to body tissues even at the pressures encountered during diving. During routine activity, green and loggerhead turtles dive for about four to five minutes, and surface to breathe for one to three seconds.

Turtles can rest or sleep underwater for several hours at a time, but submergence time is much shorter while diving for food or to escape predators. Breath-holding ability is affected by activity and stress, which is why turtles quickly drown in shrimp trawlers and other fishing gear.[32] During the night while sleeping and to protect themselves from potential predators, the adults wedge themselves under rocks below the surface and under ledges in reefs and coastal rocks. Many green sea turtles have been observed in returning to the same sleeping location night after night.[35]

Physiology and sensory modalities

[edit]
Diver with a Green Sea Turtle at Arraial do Cabo, Brasil

Green sea turtles tend to have good vision, well adapted to a life at sea. The turtles can see many colors, but are most sensitive to light from violet to yellow or wavelengths of 400 to 600 nanometers. They do not see many colors in the orange to red portion of the light spectrum. On land, however, the sea turtles are nearsighted because the lenses in the eyes are spherical and adjusted to refraction underwater.[35] Sea turtles have no external ear and only one ear bone, called the columella. With one ear bone, the turtles can hear only low frequency sounds, from 200 to 700 Hz. Sounds can also be detected through vibrations of the head, backbone, and shell. The nose of the turtle has two external openings and connects to the roof of the mouth through internal openings. The lower surface of the nasal passage has two sets of sensory cells called the Jacobson's organ. The turtle can use this organ to smell by pumping water in and out of its nose.[65]

Since green sea turtles migrate long distances during breeding seasons, they have special adaptive systems in order to navigate. In the open ocean, the turtles navigate using wave directions, sun light, and temperatures. The sea turtles also contain an internal magnetic compass. They can detect magnetic information by using magnetic forces acting on the magnetic crystals in their brains. Through these crystals, they can sense the intensity of Earth's magnetic field and are able to make their way back to their nesting grounds or preferred feeding grounds.[65]

Natal homing is an animal's ability to return to its birthplace in order to reproduce. Natal homing is found in all species of sea turtles and in other animals such as salmon. How these turtles are able to return to their birthplace is an interesting phenomenon. Many researchers believe that sea turtles use a process called imprinting, which is a special type of learning that occurs when turtles first hatch that allows them to recognize their native beach. There are two types of imprinting that are thought to be the reason turtles can find these beaches. The first is the chemical imprinting hypothesis. This hypothesis states that much like salmon, sea turtles are able to use olfactory cues and senses to smell their way home. However, a problem with this hypothesis is that some turtles travel thousands of miles to return to their native beaches, and the scents from that area are not likely to travel and be distinguishable from that distance. The second hypothesis is the geomagnetic. This hypothesis states that as it hatches, a young turtle will imprint on the magnetic field of the beach they are born on. This hypothesis strongly correlates to the method which sea turtles use to navigate the earth.[82]

In order to tolerate the constant heat loss in the water, sea turtles have the ability to shunt blood away from tissues that are tolerant of low oxygen levels toward the heart, brain, and central nervous system. Other mechanisms include basking on warm beaches and producing heat through their activity and movements of their muscles. Basking turtles sometimes look like they are crying because behind the turtles eye is the lachrymal gland which stores excess salt from the sea water, which then expels through the turtles eye. In the winter months, turtles living at higher latitudes can hibernate for a short period in the mud.[89]

Unique characteristics and features

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A tracked nesting sea turtle

Green sea turtles can reach up to 40 miles per hour when swimming, making them the fastest sea turtle.[90] The green sea turtles exhibit sex differences by their development and appearance. As adult turtles, males are easily distinguishable from the females by having a longer tail (visibly extending past the shell) and longer claws on the front flippers. The hatching time and sex of the turtles are determined by the incubation temperature of the nest. Hatchings occur more quickly in nests that are warmer than nests that are in cooler conditions. Warm nesting sites above 30 degrees Celsius favor the development of females, whereas nesting sites below 30 degrees Celsius produce males. The position of the egg in the nest also affects sex-determination. Eggs in the center tend to hatch as females due to the warmer conditions within the nest.[35]

Green sea turtles play an essential role in the ecosystem in which they live. In the seagrass beds, the turtles feed on the seagrass by trimming only the top and leaving the roots of the plant. Through their feeding technique, the turtles help to improve the health and growth of the seagrass beds. The healthy seagrass beds that the turtles provide give habitat and feeding grounds for many species of fish and crustaceans. On the nesting beaches, the green sea turtles provide key nutrients for the ecosystem through their hatched egg shells. In their coral reef habitat, the green sea turtles have a symbiotic interaction with reef fish, including the yellow tang. The yellow tang fish swims along with the turtle and feeds on the algae, barnacles, and parasites on its shell and flippers. This species interaction provides food for the yellow tang and provides a necessary cleaning and smoothing of the turtle's shell. This cleaning helps the turtles swim by reducing the amount of drag and improves their health.[65]

Importance to humans

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Black-and-white photo of several turtles set on their backs
Harvested green turtles on a wharf at Key West, Florida

Historically, the turtles' skin was tanned and used to make handbags, especially in Hawaii.[24] Ancient Chinese considered the flesh of sea turtles a culinary delicacy, including and especially C. mydas.[91] Particularly for this species, the turtle's fat, cartilage, and flesh, known as calipee, are sought as ingredients for making turtle soup, a popular 19th-century English and American dish.[92][93][22]

In Java, Indonesia, sea turtle eggs were a popular delicacy. However, the turtle's flesh is regarded as ḥarām or "unclean" under Islamic law (Islam is Java's primary religion). In Bali, turtle meat was a prominent feature at ceremonial and religious feasts. Turtles were harvested in the remotest parts of the Indonesian archipelago.[94] Bali has been importing sea turtles since the 1950s, as its own turtle supplies became depleted.[95] The mostly Hindu Balinese do not eat the eggs, but sell them instead to local Muslims.

Green Sea Turtle skeleton in the collection of the Museum Alexandre-Franconie, Cayenne, French Guiana

Commercial farms, such as the Cayman Turtle Farm in the West Indies, once bred them for commercial sale of turtle meat, turtle oil (rendered from the fat), turtle shell, and turtle leather made from the skin. The farm's initial stock was in large part from "doomed" eggs removed from nests threatened by erosion, flooding, or in chemically hostile soil.[96] The farms held as many as 100,000 turtles at any one time. When the international markets were closed by regulations that did not allow even farm-bred turtle products to be exported internationally, the surviving farm became primarily a tourist attraction, supporting 11,000 turtles.[97] Initially started as Mariculture Ltd., then Cayman Turtle Farm Ltd and subsequently branded Boatswain's Beach, in 2010 the farm's brandname was changed to Cayman Turtle Farm: Island Wildlife Encounter.[98]

Sea turtles are integral to the history and culture of the Cayman Islands. When the islands were first discovered by Christopher Columbus in 1503, he named them "Las Tortugas" because of the abundance of sea turtles in the waters around the islands.[99] Many of the earliest visitors came to the Cayman Islands to capture the turtles as a source of fresh meat during long voyages. The green turtle is a national symbol displayed as part of the coat of arms of the Cayman Islands, which also forms part of the national flag of the Cayman Islands. The country's currency uses a turtle as the watermark in its banknotes.[100] A stylised sea turtle nicknamed "Sir Turtle" is the mascot of the national airline Cayman Airways[101] and is part of the livery of its aircraft.

A ki'i pōhaku (petroglyph) of a green sea turtle (or honu) can be found on the Big Island of Hawaii in the Pu'u Loa lava fields. The green sea turtle has always held a special meaning for Hawaiians and this petroglyph shows its importance; it may date to when the Hawaiian Islands first became populated. The turtle symbolizes a navigator that can find his way home time after time. This symbol mirrors the real life of the green Hawaiian turtle as it will swim hundreds of miles to lay its eggs at its own place of birth. Though there are other myths as well, some Hawaiian legends say the honu were the first to guide the Polynesians to the Hawaiian Islands. Hawaiians revere the turtle and the legend of Kailua, a turtle who could take the form of a girl at will. In human form, she looked after the children playing on Punaluʻu Beach.[102]

Conservation

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Photo from front of swimming turtle
In a public aquarium

Sea turtles have moved from unrestricted exploitation to global protection, with some individual countries providing additional protection, although serious threats remain.[103][104] In 2025, the International Union for Conservation of Nature (IUCN) reclassified the global population of green sea turtles from endangered to least concern, though some sub-populations remain a conservation concern.[104][105]

Threats

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Human action presents both intentional and unintentional threats to the species' survival. Intentional threats include continued hunting, poaching and egg harvesting. More dangerous are unintentional threats, including boat strikes, fishermen's nets that lack turtle excluder devices, pollution and habitat destruction. Chemical pollution may create tumors;[106] effluent from harbors near nesting sites may create disturbances; and light pollution may disorient hatchlings. With chemical pollution present, there is a development of tar balls that is often eaten by green sea turtles in a confusion of their food. Tar balls cause the green sea turtle to ingest toxins that can block their guts and cause swelling of the tissue, displacing the liver and intestines.[107] Habitat loss usually occurs due to human development of nesting areas. Beach-front construction, land "reclamation" and increased tourism are examples of such development.[7][10] An infectious tumor-causing disease, fibropapillomatosis, is also a problem in some populations. The disease kills a sizeable fraction of those it infects, though some individuals seem to resist the disease.[24][108][109] In addition, at least in the Southwestern Atlantic (Río de la Plata, Uruguay), exotic invasive species such as the rapa whelk Rapana venosa, were reported massively bio-fouling immature green turtles, reducing buoyancy, increasing drag, and causing severe injuries to the carapace.[110] Because of these threats, many populations are in a vulnerable state.

A poached green turtle in Costa Rica

Pacific green turtles' foraging habitats are poorly understood and mostly unknown.[111] These foraging grounds are most likely along the coast of Baja California, Mexico and southern California,[112] in which these turtles have a high risk of incidental capture by coastal fisheries. The main mortality factor for these turtles is the shrimp trawlers in Mexico, in which many of these turtles go undocumented.[112] The only foraging area that has been identified is San Diego Bay, but it is heavily polluted with metals and PCBs.[112] These contaminants have a negative effect on the ocean environment, and have been shown to cause lesions and sometimes mortality.[112] Green turtles also are threatened by entanglement and ingestion of plastic.[112] In San Diego Bay, an adult green turtle was found dead with monofilament netting tightly packed in its esophagus.[112] In addition there are indications that global climate change is affecting the ability of green turtle populations in Australia to produce males due to their temperature-dependent sex determination and the rising temperatures in the northern Great Barrier Reef region.[113] Construction of new thermal power stations can raise local water temperature, which is also said to be a threat.[114]

Green sea turtles are the most commonly traded species along Java's south coast and are sold in the form of whole, stuffed animals or turtle oil, locally known as "minyak bulus".[115]

The geographer James J. Parsons' book titled The Green Turtle and Man played a special role in the conservation movement to save the species from extinction.[116]

Global initiatives

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A confiscated musical instrument made from the shell of a green turtle, on display at Narita International Airport, Tokyo.

The International Union for Conservation of Nature (IUCN) has repeatedly listed green sea turtles in its Red List under differing criteria. In 1982, they officially classified it as an endangered species.[117] The 1986,[118] 1988,[119] 1990,[120] 1994,[121] and the landmark 1996 edition of the IUCN Red List, retained the listing.[122]

In 2001, Nicholas Mrosovsky filed a delisting petition, claiming some green turtle populations were large, stable and in some cases, increasing. At the time, the species was listed under the strict EN A1abd criteria. The IUCN Standards and Petitions Subcommittee ruled that visual counts of nesting females could not be considered "direct observation" and thus downgraded the species' status to EN A1bd—retaining the turtle's endangered status.[123]

In 2004, the IUCN reclassified C. mydas as endangered under the EN A2bd criteria, which essentially states the wild populations face a high risk of extinction because of several factors. These factors include a probable population reduction of more than 50% over the past decade as estimated from abundance indices and by projecting exploitation levels.[124]

On 3 May 2007, C. mydas was listed on Appendix I of the Convention on International Trade in Endangered Species (CITES) as a member of the family Cheloniidae.[125] The species was originally listed on Appendix II in 1975. The entire family was moved to Appendix I in 1977, with the exception of the Australian population of C. mydas. In 1981, the Australian population joined the rest. The Appendix I listing prohibits commercial international trade in the species (including parts and derivatives).[126] The Zoological Society of London has listed the reptile as an EDGE species.[127]

The Mediterranean population is listed as critically endangered.[7][22] The eastern Pacific, Hawaiian and Southern California subpopulations are designated threatened. Specific Mexican subpopulations are listed as endangered. The Florida population is listed as endangered. The World Wide Fund for Nature has labeled populations in Pakistan as "rare and declining".[57]

Since 1999, the Florida Aquarium has led extensive sea turtle rehabilitation efforts and visitor and community education & conservation platforms to advance sea turtle protection. Over a 20-year period, the aquarium received 200 sea turtles, and while not all could be released due to the nature of their injuries or illnesses, 180 were successfully released. In 2019, they opened a state-of-the-art Sea Turtle Rehabilitation Center in Apollo Beach, Florida. In the first year, The Florida Aquarium Animal Response Team managed the care of 21 sea turtles, initiated new foraging-readiness testing for release candidates in deep-dive tank, and released 14 animals. In 2020, they also initiated a study to better understand how micro-plastics are impacting the sea turtles in their care. In 2016, Florida enacted extensive protection measures. Florida statutes (F.A.C. Rule 68E-1) restrict the take, possession, disturbance, mutilation, destruction, selling, transference, molestation, and harassment of marine turtles, nests or eggs. Protection is also afforded to marine turtle habitat. A specific authorization from commission staff is required to conduct scientific, conservation, or educational activities that directly involve marine turtles in or collected from Florida, their nests, hatchlings or parts thereof, regardless of applicant's possession of any federal permit.

In the State of Hawaii, specifically on the Island of Hawaiʻi (Hawaii County), state representative Faye Hanohano, a Native Hawaiian rights activist, pressed for a measure to delist C. mydas from protected status so that Native Hawaiians could legally harvest the turtles and possibly their eggs as well. The bill, HCR14, was largely overlooked by the media since at that point it was only a local issue. While the bill was passed in the United States House of Representatives, the United States Senate's Committee on Energy and Environment refused to hear it, which meant that the bill did not go on to be heard by the Senate.[128]

Country-specific initiatives

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At the Osaka Aquarium, profile photo of turtle resting on bottom

In addition to management by global entities such as the IUCN and CITES, specific countries around the world have undertaken conservation efforts.

The Indonesian island of Bali has traditional uses that were considered sustainable, but have been questioned considering greater demand from the larger and wealthier human population. The harvest was the most intensive in the world.[94] In 1999, Indonesia restricted turtle trade and consumption because of the decreasing population and threat of a tourist boycott. It rejected a request made by Bali Governor I Made Mangku Pastika in November 2009 to set a quota of 1,000 turtles to be killed in Hindu religious ceremonies. While conservationists respect the need for turtles in rituals, they wanted a smaller quota.[129]

Multiple protected areas of the Philippines have significant green sea turtle nesting and feeding sites. The most notable is Turtle Islands Wildlife Sanctuary, an UNESCO tentative site which encompasses an entire municipality and one of Southeast Asia's most important green sea turtle nesting sites.[130] Other notable sites include the UNESCO tentative site of El Nido-Taytay Management Resource Protected Area and the UNESCO World Heritage Site of Tubbataha Reefs Natural Park. The species is protected under Republic Act 9147 or the Wildlife Resources Conservation and Protection Act, while the sites where they live and nest are protected under the National Integrated Protected Areas System Act.[131]

Ecotourism is one initiative in Sabah, Malaysia. The island of Pulau Selingan is home to a turtle hatchery. Staff people place some of the eggs laid each night in a hatchery to protect them from predators. Incubation takes around sixty days. When the eggs hatch, tourists assist in the release of the baby turtles into the sea.[132]

The Hawaiian subpopulation has made a remarkable comeback and is now one focus of ecotourism and has become something of a state mascot. Students of Hawaii Preparatory Academy on the Big Island have tagged thousands of specimens since the early 1990s.[24]

In the United Kingdom the species is protected by a Biodiversity Action Plan, due to excess harvesting and marine pollution.[133] The Pakistani-branch of the World Wide Fund for Nature has been initiating projects for secure turtle hatching since the 1980s. However, the population has continued to decline.[10]

In the Atlantic, conservation initiatives have centered around Caribbean nesting sites. The Tortuguero nesting beaches in Costa Rica have been the subject of egg-collection limits since the 1950s. The Tortuguero National Park was formally established in 1976, in part, to protect that region's nesting grounds.[38] On Ascension Island, which contains some of the most important nesting beaches, an active conservation program has been implemented.[134] Karumbé has been monitoring foraging and developmental areas of juvenile green turtles in Uruguay since 1999.[135]

In Mozambique, there are a number of initiatives to protect sea turtles. In the Primeiras e Segundas, WWF Mozambique has established a turtle tagging and protection program. The archipelago is a vital nesting area for green turtles, including Ilha do Fogo where Earth Legacy Foundation[136] manage a turtle monitoring programme, and at Celdeira Island, where several nesting females have been tagged.

Cayman Turtle Farm located in Grand Cayman in the northwest Caribbean Sea is the first farm to have achieved the second generation of green sea turtles bred, laid, hatched, and raised in captivity.[137] Since its beginning in 1968, the farm has released over 31,000 turtles into the wild,[99] and each year more captive-bred turtles are released into the Caribbean Sea from beaches around the island of Grand Cayman.[138] Captive-bred turtles released from the farm as hatchlings or yearlings with "living tags," have now begun to return to nest on Grand Cayman as adults.[139][140] On February 19, 2012 the farm released the first 2nd-generation captive-bred green sea turtle equipped with a Position Tracking Transponder, or PTT[141] (also known as a satellite tag).[142] In addition, the farm provides turtle meat products to the local population for whom turtle has been part of the traditional cuisine for centuries. In so doing, the farm curtails the incentive to take turtles from the wild,[143] which over the years in addition to the Cayman Turtle Farm's release of captive-bred turtles has enabled an increase in the number of turtles sighted in the waters around the island of Grand Cayman and nesting on its beaches.[144]

United States Fish and Wildlife Service measures sea turtle eggs

In the Pacific, green sea turtles nest on the motu (islets) in the Funafuti Conservation Area, a marine conservation area covering 33 square kilometers (12.74 square miles) of reef, lagoon and motu on the western side of Funafuti atoll in Tuvalu.[145]

On Raine Island, up to 100,000 nesting females have been observed in a season, with the cay producing 90% of the region's green turtles. However, the hatching rate declined in the 1990s, and a further decline in the population was threatened by the deaths of thousands of females as they struggled to climb the small sandy cliffs. In addition, as the shape of the island had changed over time, the spread of the beaches outwards had led to greater risk of inundation of the turtle nests. Between 2011 and 2020, a collaborative project by the Queensland Government, BHP (as corporate sponsor), the Great Barrier Reef Marine Park Authority, Great Barrier Reef Foundation, and Wuthathi and Meriam traditional owners, reshaped the island using heavy machinery in a way that gave the female turtles a smoother passage and reduced the risk of nest inundation. A sophisticated monitoring and research system, using 3D modelling, satellite technology and drones was employed, and monitoring continues.[146]

As of June 2020, a project called "The Turtle Cooling Project" is being undertaken by scientists from the World Wildlife Fund Australia, University of Queensland, Deakin University and the Queensland Government. It is looking at the effect of global warming on northern green turtle breeding, in particular the effect of producing more male turtles owing to the higher temperatures. They are working in the area around Raine Island, Heron Island and Moulter Cay.[147]

Genetics

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The genome of Chelonia mydas was sequenced in 2013 to examine the development and evolution of the turtle body plan.[148]

See also

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References

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[edit]
Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
The green sea turtle (Chelonia mydas) is a large marine reptile in the family Cheloniidae, distinguished as the only primarily herbivorous sea turtle species, with adults feeding mainly on seagrasses and algae.
Inhabiting tropical and subtropical coastal waters and open oceans worldwide, it undertakes extensive migrations, particularly females returning to natal beaches for nesting.
Adults typically reach a carapace length of 3 to 4 feet (0.9 to 1.2 meters) and weigh 300 to 350 pounds (136 to 159 kilograms), with sexual maturity attained after 20 to 50 years and a lifespan estimated at 50 to 100 years.
Reproduction involves females emerging onto beaches at night to excavate nests and deposit clutches averaging 110 eggs, which incubate for 50 to 70 days before hatchlings instinctively head to sea.
Although historically threatened by egg harvesting, bycatch in fisheries, habitat loss, and pollution, global populations have rebounded sufficiently that the IUCN Red List downgraded its status from Endangered to Least Concern in 2025, crediting sustained conservation measures.

Taxonomy

Classification and Nomenclature

The green sea turtle (Chelonia mydas) belongs to the family Cheloniidae, which comprises the hard-shelled sea turtles, within the order Testudines of reptiles. Its full taxonomic classification is as follows:
  • Kingdom: Animalia
  • Phylum: Chordata
  • Class: Reptilia
  • Order: Testudines
  • Suborder: Cryptodira
  • Superfamily: Chelonioidea
  • Family: Cheloniidae
  • Subfamily: Cheloniinae
  • Genus: Chelonia
  • Species: Chelonia mydas
The binomial nomenclature Chelonia mydas reflects Linnaeus's original 1758 description of the species as Testudo mydas, with the genus Chelonia later formalized by Brongniart in 1800 to distinguish sea turtles from terrestrial tortoises. The genus name derives from the Ancient Greek chelōnē (χελώνη), denoting a turtle or tortoise. The specific epithet mydas originates from Linnaeus's usage, likely drawing on Greek roots associated with moisture, though its precise connotation in this context remains tied to early descriptive conventions rather than direct morphological traits. The common name "green sea turtle" refers to the greenish hue of the species' subcutaneous fat, resulting from its herbivorous diet rich in algae and seagrasses, rather than the typically olive-brown carapace. Other regional common names include "green turtle" and, in some contexts, distinctions like "black turtle" for darker variants, but these do not alter the primary nomenclature. Chelonia mydas serves as the type species for its monotypic genus, with no other species currently recognized within Chelonia.

Subspecies and Genetic Variants

The green sea turtle (Chelonia mydas) is classified by some authorities as monotypic, lacking formally recognized subspecies, while others distinguish two based on morphological and geographic differences. The proposed subspecies C. m. mydas encompasses populations in the Atlantic Ocean, Mediterranean Sea, Indo-West Pacific, and central Pacific, characterized by a typically olive-green carapace in adults. In contrast, C. m. agassizii, known as the black turtle or East Pacific green turtle, occurs primarily along the eastern Pacific coast from Baja California to Peru, featuring a darker blackish carapace and plastron, smaller adult size (typically under 100 cm curved carapace length), and a diet shifted toward more crustaceans and mollusks compared to the herbivorous tendencies of C. m. mydas. The distinction remains debated, with genetic evidence supporting divergence but insufficient for full species status; some researchers elevate agassizii to species level (Chelonia agassizii) due to observed isolation and morphological adaptations, though this is not widely accepted in major taxonomic databases. Genetic analyses reveal significant variation within C. mydas, primarily through mitochondrial DNA (mtDNA) haplotypes in the control region, which define distinct evolutionary significant units (ESUs) and management units (MUs) for conservation. Eleven major mtDNA haplotypes have been identified globally, with clustering into Atlantic, Indo-Pacific, and East Pacific lineages; for instance, East Pacific populations exhibit unique haplotypes like CM-CMP2, reflecting isolation dating back approximately 1-3 million years based on coalescent models. Nuclear DNA studies further indicate low gene flow between ocean basins, with fixation indices (F_ST) exceeding 0.5 for East Pacific versus Atlantic/Indo-Pacific groups, underscoring adaptive divergence potentially linked to environmental pressures such as upwelling-driven productivity in the eastern Pacific. Color morphs—green, black, and yellow—observed in foraging aggregations, particularly in Australia, show partial genetic correlations with SNPs under selection for pigmentation and immunity genes, though these are not fixed subspecies traits and likely result from phenotypic plasticity or local adaptation rather than deep phylogenetic splits. Population-level variants are evident in rookery-specific genetics, with high haplotype diversity (h > 0.8) in some Indo-Pacific sites like São Tomé and Príncipe, indicating ancient refugia, contrasted by lower diversity in bottlenecked Atlantic populations. These variants inform stock delineation; for example, mixed-stock analyses using mtDNA assign over 90% of East Pacific foragers to agassizii-like origins, aiding targeted protection amid ongoing hybridization risks from human-mediated translocations. Overall, while subspecies taxonomy emphasizes my das and agassizii, genetic data prioritize finer-scale units for preserving adaptive potential against threats like climate-induced shifts in nesting fidelity.

Physical Description

Morphology and External Features

The green sea turtle (Chelonia mydas) has a streamlined, dorsoventrally flattened body adapted for efficient swimming in marine environments, characterized by a rigid shell formed by the fusion of dermal bones and keratinous scutes. The carapace is heart-shaped, low-domed, and smooth-surfaced, typically exhibiting dark brown, olive, or gray coloration in adults, with five central vertebral scutes and four pairs of costal scutes that do not overlap and whose first pair does not contact the nuchal scute; the posterior marginal scutes may form a serrated or scalloped edge. The plastron is lighter, ranging from yellowish to white, and consists of paired gular, humeral, pectoral, abdominal, and femoral scutes, often with an intergular scute present. The head is small and rounded with a short neck, featuring a single pair of prefrontal scales between the eyes and a beak with serrated, cutting-edge margins specialized for cropping seagrass and algae. Limbs are modified into four flippers: the foreflippers are long, paddle-shaped, and equipped with a single prominent claw for propulsion during swimming, while the shorter hindflippers, used for steering, bear one or two claws. The skin is thick, leathery, and scaled, providing protection against abrasion and pathogens in the aquatic habitat. Hatchlings differ markedly, possessing a black carapace, white plastron, and pale marginal regions on the flippers and shell edges, which darken with age.

Size, Growth, and Sexual Dimorphism

Hatchling green sea turtles (Chelonia mydas) measure approximately 5 cm in curved carapace length (CCL) and weigh less than 25 grams upon emergence from the nest. Adults typically reach 91 to 122 cm in CCL and weigh 110 to 190 kg, though exceptional individuals exceed 150 cm and 300 kg. Growth occurs primarily during the pelagic juvenile stage, with rates varying by habitat, diet, and population density; juveniles under 90 cm CCL exhibit median annual increases of about 4.9 cm, while overall rates across sizes average 1.03 cm per year in temperate foraging grounds. Post-maturity somatic growth slows markedly, averaging 0.14 to 0.25 cm per year in nesting populations, reflecting density-dependent factors and reduced metabolic demands in adults. Somatic growth variance decreases with increasing body size, as slower-growing individuals at smaller sizes contribute to stabilized adult cohorts. Sexual dimorphism in C. mydas is minimal overall but manifests in size and secondary traits; adult females are larger than males, with nesting females averaging greater CCL and mass to support egg production. Males exhibit longer tails and curved claws adapted for mating, while females have shorter tails and straight claws; these differences emerge post-maturity and aid in reproductive behaviors without substantial overall size divergence.

Distribution and Populations

Global Range and Subpopulations

The green sea turtle (Chelonia mydas) occupies tropical and subtropical marine waters across all major ocean basins, including the Atlantic, Pacific, and Indian Oceans, as well as the Mediterranean Sea. Its range extends from approximately 30°N to 30°S latitude, with individuals foraging in coastal bays, estuaries, and coral reefs, while nesting occurs on sandy beaches in over 80 countries. Major nesting concentrations are documented in regions such as Ascension Island in the Atlantic, French Frigate Shoals in Hawaii for the central Pacific, and Berau Islands in Indonesia for the Indo-Pacific. Subpopulations are delineated primarily through mitochondrial DNA analyses, revealing matriarchal genetic structure with limited gene flow between distant rookeries due to natal homing. Genetic studies identify distinct clades: a widespread Indo-Pacific lineage, an Atlantic lineage, and an eastern Pacific lineage corresponding to the subspecies C. m. agassizii. Globally, 76 management units (MUs) have been defined from genetic sampling of 164 rookeries, facilitating targeted conservation. In the Atlantic, key subpopulations nest at Ascension Island (up to 25,000 females annually) and Suriname/French Guiana; in the Pacific, Hawaii hosts the largest central Pacific aggregation with over 90% nesting at French Frigate Shoals; and in the Indian Ocean, Chagos Archipelago and Oman support significant numbers. Population segments under frameworks like the U.S. Endangered Species Act recognize 11 distinct population segments (DPSs), reflecting genetic and demographic isolation, such as the endangered Central South Pacific DPS and threatened North Pacific DPS. Recent genomic analyses confirm isolation in areas like the Red Sea, with approximately 5,000 nesting females showing differentiation across five subpopulations. These delineations underscore the species' metapopulation dynamics, where local rookeries contribute to broader oceanic stocks through juvenile dispersal.

Migration Patterns and Philopatry

Adult green sea turtles (Chelonia mydas) undertake long-distance migrations between distant foraging grounds and specific nesting beaches, often covering thousands of kilometers. These migrations are primarily undertaken by mature females every 2–4 years to breed, with post-nesting routes leading back to resident foraging areas rich in seagrass or algae. Satellite telemetry has documented varied routes; for example, females nesting in Montserrat, West Indies, follow two principal pathways: one northeast toward the Azores and another along the Lesser Antilles, with total migration distances exceeding 2,000 km in some cases. In the Gulf of Mexico, tracked individuals migrate to foraging sites off the Florida Keys, Cape Sable, or Mexican coasts, highlighting regional connectivity between nesting and feeding zones. Males exhibit sex-specific migration patterns, often shorter than those of females, as observed in West African breeding populations where post-breeding movements to foraging grounds averaged less than 1,000 km. Juveniles and subadults also disperse widely post-hatch, entering oceanic "lost years" before recruiting to neritic habitats, though their migrations are less precisely mapped due to tagging challenges. Global analyses of satellite data indicate aggregation in marine protected areas, suggesting migratory corridors overlap with conservation hotspots. Philopatry, or natal homing, is a defining behavioral trait, with females exhibiting strong fidelity to their birth beaches for nesting, as evidenced by mitochondrial DNA (mtDNA) structuring across rookeries. Genetic studies reveal finer-scale homing to isolated islands versus continental sites, driven by matrilineal inheritance and minimal gene flow between populations. This behavior, potentially guided by geomagnetic imprinting during the open-sea migration from hatchling to nesting site, maintains distinct genetic stocks despite occasional straying. Precise philopatry is not absolute; some gene flow occurs, but it is insufficient to homogenize populations, as shown in rookeries like Tortuguero, Costa Rica, where lineages remain differentiated. Male philopatry is less studied but inferred from breeding site returns, contributing to overall population structuring. The global population of green sea turtles (Chelonia mydas) has increased by approximately 28% since the 1970s, reflecting successful conservation interventions such as protected nesting beaches and reduced bycatch, which contributed to the species' downlisting from Endangered to Least Concern by the IUCN in 2025. This rebound follows historical overexploitation that decimated populations, including a 95% reduction in the Caribbean from pre-colonial estimates of 19–33 million individuals. However, aggregate trends obscure variability across distinct population segments (DPS), with three DPS listed as Endangered and eight as Threatened under the U.S. Endangered Species Act, and ongoing declines in hatchling production at key sites like Raine Island, Australia, due to nest inundation from sea-level rise. In the Hawaiian Archipelago, the once-depleted endemic population has demonstrated a robust recovery, with nesting abundance rising at an average rate of 5.4% annually since 1973 after harvesting bans were enacted. At East Island in French Frigate Shoals, the primary nesting site, the population has grown at 5.7% per year, though over 90% of Hawaiian nesting remains concentrated at this vulnerable location. Similarly, the resident green turtle population in southern Great Barrier Reef waters, Australia, expanded by 11% annually from 1984 to 1992, reaching an estimated 1,300 individuals. Regional successes contrast with persistent challenges elsewhere; for example, nesting at Tortuguero, Costa Rica—one of the largest rookeries—has declined in recent years despite earlier stabilization efforts. In the western Indian Ocean, such as at Aldabra Atoll, nesting numbers rose from around 4,000 to 16,000 annually between 1980 and 2018. At Raine Island, the world's largest green turtle rookery, peak seasons attract up to 64,000 females, underscoring its critical role, yet environmental pressures like rising sea surface temperatures have correlated with shifts in nesting behavior and reduced body sizes even amid abundance gains. These empirical patterns highlight that while overall numbers are trending upward, subpopulation-specific monitoring remains essential for addressing localized threats including climate impacts and fisheries interactions.

Habitat Preferences

Marine and Coastal Environments

Green sea turtles (Chelonia mydas) inhabit tropical and subtropical marine waters across the Atlantic, Pacific, and Indian Oceans, with adults predominantly utilizing neritic zones characterized by coastal shelf waters up to approximately 200 meters in depth. Juveniles exhibit an ontogenetic habitat shift, initially occupying pelagic environments in the open ocean following hatching before transitioning to neritic habitats as they grow larger and shift foraging strategies. This shift typically occurs at carapace lengths of 25-40 cm, aligning with increased reliance on benthic resources in shallower coastal areas. These turtles favor water temperatures between 20°C and 32°C, as colder conditions below 20°C can induce metabolic stress or cold-stunning events, particularly in northern extents of their range. Salinity levels in their preferred habitats approximate full marine conditions at around 35 parts per thousand, though they tolerate minor fluctuations in estuarine-influenced coastal zones without significant osmotic disruption. Depths utilized range from surface waters to 50 meters or more, but most activity concentrates in shallow platforms under 20 meters where light penetration supports algal and seagrass productivity essential for their ecology. Coastal environments, including bays, lagoons, and reef-adjacent platforms, provide protected waters that mitigate wave action and predation risks while facilitating access to productive benthic communities. In the southeastern Pacific, for instance, green turtles demonstrate flexible use of nearshore habitats influenced by upwelling, adapting to seasonal variations in water quality and temperature. Such areas often feature soft substrates like sand or mud overlying hard bottoms, promoting stable conditions for extended residency. Anthropogenic alterations, including warming trends, are projected to expand suitable thermal habitats poleward but compress equatorial ranges, potentially intensifying competition in coastal refugia.

Foraging and Nesting Sites

Green sea turtles forage in shallow, protected coastal waters, typically at depths less than 20 meters, where seagrass beds and algal communities predominate. These habitats include bays, lagoons, estuaries, and reef platforms supporting their herbivorous diet of seagrasses such as Thalassia testudinum and macroalgae. Juveniles recruit to these nearshore areas from pelagic stages, with individuals as small as 16.2 cm straight carapace length documented foraging in the northwestern Gulf of Mexico. Key foraging grounds span tropical and subtropical regions, including Bahía de los Angeles in Mexico's Gulf of California, seagrass meadows around Mayotte Island in the Indian Ocean, Martinique in the Caribbean, and coastal areas of New Caledonia. Turtles display strong site fidelity to these areas, with residency durations ranging from 2 to 74 years in some populations and home ranges overlapping persistent seagrass patches. Nesting sites for green sea turtles are predominantly sandy beaches in tropical and subtropical latitudes, selected for their loose substrate suitable for egg-laying and proximity to the sea for post-nesting emergence. Females exhibit natal philopatry, migrating thousands of kilometers to specific beaches where they were born, with nesting seasons varying by region—typically May to September in the Atlantic and November to March in the Indo-Pacific. Major global nesting aggregations include Ascension Island (6,000–13,000 nests annually), Aves Island, Tortuguero in Costa Rica, Suriname, Raine Island in Queensland, Australia, and French Frigate Shoals in Hawaii, the latter hosting about 90% of Hawaiian nesting activity. Additional significant sites occur in New Caledonia and over 80 countries worldwide, reflecting the species' broad distribution but with population-specific threats like erosion and predation influencing site viability. For example, at Akyatan Beach in Turkey, annual nest counts averaged 387 over a decade from 2012–2021. Conservation efforts prioritize these beaches, as they support the bulk of reproduction despite varying densities—major sites defined as exceeding 20 nests per year or 10 nests per kilometer.

Ecology

Diet and Trophic Role

Adult green sea turtles (Chelonia mydas) are primarily herbivorous, consuming seagrasses and marine algae as the dominant components of their diet. In foraging grounds such as the Gulf of California, dietary analysis from esophageal lavages revealed that larger individuals (>40 cm curved carapace length) fed almost exclusively on red algae like Gracilaria spp. and Chondracanthus canaliculatus, comprising over 90% of consumed biomass. Seagrasses such as Thalassia testudinum and Halodule wrightii form a staple in regions with extensive meadows, like the Caribbean and Indo-Pacific, where they provide high-fiber forage supporting the turtle's foregut fermentation physiology. Juvenile green turtles exhibit an ontogenetic dietary shift, incorporating more animal matter early in neritic stages before transitioning to herbivory. In subtropical bays, immature turtles (<30 cm straight carapace length) consumed a mix including sponges, hydrozoans, and crustaceans alongside algae, with animal items averaging 20-40% of diet volume, reflecting opportunistic foraging in pelagic-to-neritic habitats. Stable isotope analysis in the southwestern Atlantic confirmed this progression, with δ¹³C values shifting toward seagrass signatures in larger juveniles, indicating habitat-specific adaptation to plant-based nutrition by 40-60 cm carapace lengths. As megaherbivores, green turtles play a key trophic role in maintaining seagrass ecosystem structure and function. Their grazing reduces blade length and biomass, stimulating lateral growth and nutrient turnover in meadows, akin to large mammalian herbivores on terrestrial grasslands, which enhances overall productivity and prevents senescence. In recovering populations, such as those off Florida since the 1980s, increased turtle densities have cropped seagrasses to 20-30% of ungrazed heights, altering macroalgal assemblages and promoting diverse, short-blade communities that support higher biodiversity. This top-down control positions them as ecosystem engineers, recycling nutrients via feces that enrich surrounding waters with nitrogen and phosphorus, bolstering primary production in oligotrophic coastal systems. In algal-dominated habitats, they contribute significantly to herbivore biomass, consuming up to 95% of epiphytic cover and influencing competitive dynamics between seagrasses and invasives.

Predators, Parasites, and Competitors

Adult green sea turtles (Chelonia mydas) face predation primarily from large sharks, such as tiger sharks (Galeocerdo cuvier), which target them in foraging areas, though overall predation rates on mature individuals remain low due to their size and defensive behaviors. Juveniles encounter higher risks from sharks and large predatory fish in pelagic waters. Nesting eggs suffer extensive predation, with studies in Turkey reporting over 75% of green turtle nests destroyed by red foxes (Vulpes vulpes) and other canids. Hatchlings face immediate threats on beaches from crabs, birds, mammals like dogs and raccoons, and nearshore fishes, with empirical predation rates by fishes averaging 31% (range 0-85%) during initial swims to deeper water. Additional beach predators include mongoose, rats, and pigs, exacerbating nest failure rates. Green sea turtles host diverse parasites, including spirorchiid trematodes (blood flukes) that infest vascular systems, causing circulatory disorders, thromboembolism, and tissue damage leading to mortality in stranded individuals. Gastrointestinal helminths, such as nematodes and cestodes, are prevalent in juveniles, with dissections of stranded Brazilian specimens revealing multiple species but variable impacts on host condition. Protozoan parasites like Caryospora cheloniae induce disseminated coccidiosis, resulting in systemic lesions unique to green turtles as natural hosts. Trematodes such as Learedius learedi can cause ocular infections leading to blindness, as documented in Red Sea cases. Protozoans like Toxoplasma gondii have been detected in tissues of Brazilian green turtles, marking initial reports of this pathogen in the species. While many infections are subclinical, heavy burdens weaken hosts, increasing susceptibility to secondary stressors. Competitors for green sea turtles include sympatric sea turtle species sharing foraging grounds, such as loggerheads (Caretta caretta), Kemp's ridleys (Lepidochelys kempii), and hawksbills (Eretmochelys imbricata), where interspecific interactions influence resource partitioning in bays and coastal habitats. In seagrass meadows, green turtles' herbivorous diet of grasses and algae overlaps with potential competitors like dugongs (Dugong dugong), though empirical data on direct competitive exclusion remains limited; niche differentiation by depth or patch use mitigates intense rivalry. Overgrazing in dense turtle aggregations can degrade habitats, indirectly heightening competition pressures.

Behavior and Life Cycle

Reproductive Biology

Green sea turtles (Chelonia mydas) reach sexual maturity at ages ranging from 20 to 50 years, with females typically attaining a straight carapace length (SCL) of 80 to 100 cm. Males mature at similar ages and sizes, though precise determination is challenging due to their pelagic lifestyle post-maturity. Maturity is influenced by growth rates, which slow after juvenile stages, with coastal juveniles growing steadily until approximately 28 to 30 years. Mating occurs in shallow coastal waters near nesting sites, often weeks prior to oviposition, exhibiting a polygynandrous system where individuals mate multiply. Courtship involves males approaching females, nuzzling the head or neck, circling, gentle biting of flippers, and mounting, with copulations lasting up to 6 hours. Females may store sperm from multiple males, enabling fertilization of clutches laid over the season. Nesting females, emerging nocturnally on sandy beaches, excavate a body pit followed by an egg chamber 40-60 cm deep. Clutch sizes average 110 eggs (range 75-200), with leathery, spherical eggs approximately 4.5 cm in diameter. Females typically produce 2-5 clutches per season, with internesting intervals of 12-15 days, and remigrate every 2-4 years contingent on nutritional status. Observed clutch frequencies often range 2-4, though estimates accounting for missed nests suggest up to 6 in some populations. Incubation lasts 45-75 days, varying with sand temperature and depth. Sex determination is temperature-dependent, with pivotal temperatures around 29°C yielding 1:1 male-female ratios; temperatures below 28.5°C produce mostly males, while above 30°C yield predominantly females. Warmer, higher-beach nests favor female production, potentially skewing population sex ratios under rising global temperatures. Hatchlings emerge en masse at night after pipping, using lunar cues and wave sounds for orientation to the sea, though only about 1% survive to maturity.

Development Stages and Longevity

The development of the green sea turtle (Chelonia mydas) progresses through distinct ontogenetic stages, beginning with embryonic incubation in nests buried on sandy beaches. Females typically lay clutches of 70–150 eggs, which incubate for 45–70 days, with duration influenced by sand temperature; warmer conditions accelerate development and produce predominantly female hatchlings due to temperature-dependent sex determination. Upon emergence, hatchlings measure approximately 5 cm in curved carapace length (CCL) and weigh 20–25 grams; they synchronize piping from eggs over 1–7 days before collectively excavating the nest and crawling to the sea, often at night to minimize predation risk. Post-hatchlings enter a pelagic juvenile phase in open habitats, lasting several years (typically 3–5 or more), during which they grow to 20–40 cm straight (SCL) while feeding opportunistically on and gelatinous organisms. This "lost years" period involves drifting with currents and association with floating mats, with high mortality from predation and environmental factors. Recruitment to neritic foraging grounds occurs at sizes of 25–42 cm SCL, marking an ontogenetic habitat shift to shallow coastal waters where juveniles adopt a primarily herbivorous diet of seagrasses and algae, supporting slower somatic growth rates of 2–5 cm per year in CCL. Subadult greens continue growth in these benthic habitats, reaching sexual maturity variably between 20–50 years of age, depending on nutrition, population genetics, and environmental conditions; maturation sizes range from 80–110 cm CCL. Adults migrate to natal breeding sites every 2–4 years for reproduction, with growth ceasing or minimal thereafter. Longevity exceeds 70 years in the wild, as evidenced by tag-recapture studies and skeletochronological analysis of humeri revealing growth rings consistent with ages over 60–80 years, though precise maximum lifespan remains uncertain due to infrequent observations of senescence.

Daily and Seasonal Behaviors

![Green sea turtle grazing seagrass][float-right] Green sea turtles (Chelonia mydas) display primarily diurnal activity, with foraging concentrated during daylight hours in shallow seagrass beds and algal habitats where they graze on vegetation such as Thalassia testudinum. Dives during the day are typically shallower (averaging 2-5 meters) and shorter (5-20 minutes) to facilitate feeding, followed by brief surfacing for air every few minutes. At night, individuals shift to resting behavior on the seafloor, exhibiting longer submergence intervals and deeper nocturnal dives (up to 20-30 meters) with reduced activity. This diel pattern minimizes energy expenditure overnight while maximizing foraging efficiency by day, though some populations show occasional nocturnal activity influenced by environmental factors. In certain foraging grounds, such as those in Hawaii, subadult green turtles incorporate daytime basking on beaches into their routines, emerging from water to rest on land for thermoregulation, particularly in cooler conditions; these episodes last 1-4 hours and occur sporadically. Daily movements cover home ranges of 1-10 square kilometers, centered on key foraging and resting sites, with turtles traveling up to 1-2 km between patches. Submergence times vary by size and health, but healthy juveniles average 80-90% of time submerged, surfacing 10-20 times per hour during active periods. Seasonally, non-breeding green turtles maintain residency in foraging habitats year-round, but activity adjusts to temperature and prey cycles; juveniles in temperate reefs perform deeper, longer dives in winter (reaching 30+ meters) compared to shallower summer patterns, reflecting adaptations to cooler waters and reduced metabolic rates. Feeding rhythms on seagrass show peaks aligned with optimal growth periods, with higher intake during warmer months when biomass is abundant. Breeding adults undertake migrations spanning thousands of kilometers to nesting sites during reproductive seasons, typically May-October in tropical Atlantic populations, returning post-nesting to foraging grounds; these movements synchronize with photoperiod and sea surface temperatures exceeding 25°C. Juveniles in subtropical areas may exhibit short seasonal displacements during cold fronts to avoid lethal temperatures below 10°C.

Physiology

Sensory Systems and Navigation

Green sea turtles possess sensory adaptations suited to their marine environment, including enhanced underwater vision, acute olfaction, moderate hearing capabilities, and magnetoreception. Their eyes are adapted for aquatic vision with a high density of cone photoreceptors sensitive to blue-green wavelengths (approximately 400-550 nm), enabling color discrimination and prey detection in turbid coastal waters, though visual acuity diminishes in low-light deep-sea conditions. Olfaction is particularly acute, facilitated by a nasal cavity housing three independent sensory epithelia: the main olfactory epithelium for volatile odorants, the vomeronasal organ for water-soluble cues, and the Jacobson’s organ for additional chemosensory processing, allowing detection of chemical gradients for foraging and orientation over long distances. Hearing sensitivity in juveniles extends to underwater frequencies of 50-1600 Hz and aerial frequencies of 50-500 Hz, with auditory evoked potentials indicating responsiveness to low-frequency sounds relevant for detecting predators or conspecifics, though thresholds are higher than in many fish species. Magnetoreception, mediated by putative magnetite-based receptors in the head and possibly cryptochrome photopigments, enables perception of Earth's geomagnetic field for directional and positional information. Navigation in green sea turtles integrates these senses, particularly during oceanic migrations spanning thousands of kilometers and natal homing to breeding beaches. Geomagnetic cues form a primary "magnetic map," where turtles imprint on the unique inclination and intensity signatures of their natal sites during hatching—such as the 30-60 μT field strength and 50-70° inclination typical of tropical beaches—and later use these to guide returns after 10-30 years at sea. Laboratory conditioning experiments demonstrate that juveniles can distinguish and orient toward specific magnetic field parameters mimicking distant locations, correcting for drift during open-ocean phases. Olfactory cues supplement geomagnetism near shorelines, with turtles responding to natal beach odors in displacement tests, potentially via pheromone-like chemical signatures persisting in currents. Wave direction and celestial cues may provide coarse initial orientation post-hatch, but empirical displacement studies, such as those relocating adults 100-500 km offshore, confirm reliance on multi-modal integration, with magnetic disruption increasing path lengths by up to 50%. This system ensures precise philopatry, with tracking data showing adults returning to within 5-10 km of natal sites after migrations exceeding 2000 km.

Respiration, Diving, and Metabolism

Green sea turtles (Chelonia mydas) are air-breathing reptiles equipped with lungs located beneath their carapace, ventilating through contraction of muscles attached to the pelvic and shoulder girdles as well as the plastron. Their pulmonary system features a large tidal volume relative to functional residual capacity, facilitating rapid gas exchange during brief surface intervals. Oxygen is predominantly stored in the lungs, comprising up to 72% of total dive oxygen reserves. During dives, turtles exhibit physiological adaptations including extreme bradycardia, where heart rate slows progressively to conserve oxygen, interrupted only by surfacing events. Typical foraging dives last 20 to 40 minutes, while resting or sleeping dives can extend to several hours, with breath-holding capacity influenced by activity level, stress, and water temperature. In internesting periods, U-shaped dives average 40.8 minutes at depths of 18.2 meters, with many seabed dives remaining shallow, under 20 meters. Metabolic rates in C. mydas are strongly temperature-dependent, increasing with warmer water and activity, which inversely affects dive duration. Resting metabolic rates during dives rise significantly in higher temperatures, while swimming elevates oxygen consumption further. These ectothermic traits enable efficient energy use for prolonged submersion, though prolonged stress or entrapment can lead to rapid oxygen depletion and drowning due to impaired breath-holding.

Thermoregulation and Health

Green sea turtles (Chelonia mydas) are ectothermic reptiles that primarily regulate body temperature through behavioral means, such as selecting warmer water masses and engaging in terrestrial or aquatic basking to elevate core temperatures above ambient seawater levels. Circulatory adjustments, including regional blood flow variations to the front flippers, enable heat retention or dissipation, allowing turtles to transport heat into the body core or release excess during warming. In cooler conditions, such as winter sea surface temperatures below 23°C, turtles increase basking frequency on beaches to facilitate thermoregulation, digestion, and immune function. Physiological responses to temperature extremes include reduced activity and torpor when water drops below 15°C, conserving energy by minimizing metabolic demands. Adult turtles exhibit inactivity in water temperatures of 26–28°C, which supports passive warming akin to basking behaviors. Rising sea surface temperatures linked to climate change are reducing basking opportunities in some populations, potentially altering thermal profiles and habitat suitability. Access to haul-out sites for basking is critical, as unobstructed land emergence supports effective heat gain in populations like the Central North Pacific distinct population segment. A primary health concern for green sea turtles is fibropapillomatosis (FP), a neoplastic disease characterized by fibroepithelial tumors on skin, eyes, mouth, and internal organs, often leading to impaired vision, mobility, feeding, and increased mortality. Caused by chelonid herpesvirus 5 (ChHV5), FP prevalence is highest in green turtles, with temporal increases noted in regions like Hawaii and Florida, where tumor burdens can exceed 50% in some foraging aggregations. Environmental cofactors, including pollutants and warmer waters, exacerbate tumor development and regression, with sunlight exposure aiding healing post-surgical removal in rehabilitated individuals. Basking behaviors may indirectly support FP resistance by bolstering immune responses through elevated body temperatures. Prevalence varies geographically, with lower rates in open ocean versus coastal habitats, suggesting density-dependent transmission dynamics.

Human Interactions

Historical Harvesting and Utilization

Green sea turtles (Chelonia mydas) have been harvested by humans across tropical and subtropical regions for their meat, eggs, fat, and shells, with exploitation documented since prehistoric times and intensifying during European colonization of the Americas. In the colonial Caribbean, turtles served as a vital protein subsidy, where their meat, eggs, and rendered fat (calipash and calipee) were consumed fresh or preserved, supporting both free and enslaved populations in urban centers like Jamaica and the Cayman Islands from the 17th to 19th centuries. Commercial fleets, such as those operating from the Cayman Islands, captured thousands annually by overturning turtles at sea, leading to overexploitation that depleted local stocks by the early 1800s. Meat from green turtles was prized for its flavor, often featured in soups, stews, and as a veal substitute in dishes across Europe and the Americas, with historical records noting exports from Caribbean fisheries peaking in the 18th century. Eggs were systematically collected from nesting beaches, providing a seasonal resource; for instance, in regions like the Dominican Republic, harvesting reduced populations to levels where commercial operations became unprofitable by the late 19th century. Turtle fat was boiled for oil used in lighting, cooking, and leather preservation, while shells were crafted into combs, spectacles, and decorative items, though less valued than hawksbill tortoiseshell. In Florida, intensive fisheries from the late 1800s targeted greens for meat and eggs, crashing local populations and prompting early regulatory attempts by the 1890s. Indigenous and local communities in areas like the Pacific Islands and Southeast Asia historically practiced more sustainable take, focusing on eggs and occasional adults for subsistence, but global trade amplified pressure, with documented annual egg harvests exceeding 200,000 in some locales through the mid-20th century. Overall, this utilization contributed to widespread declines, as nesting aggregations were particularly vulnerable to beach-based exploitation, reducing reproductive output before international protections emerged in the 1970s.

Cultural Significance and Economic Value

In Hawaiian culture, the green sea turtle (honu) embodies symbols of longevity, wisdom, endurance, and good fortune, often linked to ancestral spirits and deities emerging from the realm of (darkness of creation). Turtles were historically regarded as property of the ali'i (chiefs), raised in coastal fishponds (loko i'a), and consumed selectively during ceremonies under kapu (traditional prohibitions) to regulate access and sustain populations. Among Indigenous Pacific Islander groups, including those in the Northern Mariana Islands and Yap (Micronesia), green sea turtles hold ceremonial importance, with harvesting integrated into traditional practices tied to navigation lore, feasts, and social structures, though regulated to prevent depletion. In Indonesian Hindu traditions, the species features symbolically in rituals, representing fertility and cosmic balance, with live turtles sometimes released as offerings. Historically, green sea turtles provided substantial economic value through commercial and subsistence harvesting of meat, eggs, fat (for oil), and calipee (cartilage for soup), with 19th-century fisheries in regions like the Cayman Islands exporting up to 2,600 turtles annually to markets in Europe and North America. Shells were crafted into combs, eyeglass frames, and jewelry, contributing to trade networks valued in thousands of dollars per turtle in peak eras. Today, subsistence harvests in Asia-Pacific communities yield approximately US$800,000 annually, primarily for local consumption, while illegal trade persists despite international bans under CITES since 1975. Shifting to non-consumptive uses, ecotourism centered on turtle viewing generates revenue exceeding harvest values in protected areas; for instance, nesting beach tours in Costa Rica and Australia produce millions in annual income, with willingness-to-pay studies estimating non-use values (e.g., existence and bequest) at US$1,000–3,000 per respondent household in surveyed regions. These incentives have reduced poaching in some villages by compensating former harvesters, though effectiveness varies due to enforcement challenges and opportunity costs of forgone protein sources.

Modern Conflicts and Ecotourism

Fisheries bycatch constitutes a primary modern conflict for Chelonia mydas, with entanglement in gillnets and longlines causing substantial mortality, particularly among juveniles and adults in foraging areas. In the central Pacific, genetic analyses of bycaught turtles reveal origins from and eastern Pacific stocks, highlighting the transboundary nature of this issue. Global assessments identify as the leading anthropogenic threat, outpacing other factors in scope due to the ubiquity of commercial fishing operations. Vessel strikes exacerbate conflicts during reproductive migrations and nearshore activities, as adult females aggregate in predictable coastal zones, increasing collision risks with boating traffic. In regions like Hawaii, population recoveries have intensified human-turtle interactions, with basking turtles on public beaches prompting disturbances from recreationists, necessitating volunteer patrols to enforce setbacks and mitigate harassment. Ecotourism centered on nesting observations and snorkeling encounters generates economic value exceeding that of traditional harvesting, with studies estimating three-fold revenue gains from sustainable viewing over egg or meat sales. In locales such as Tortuguero, Costa Rica, regulated tours fund conservation while curbing poaching, though rapid visitor growth has historically elevated trampling risks to nests and females. Compensation schemes in fishing communities link tour income to forgone turtle harvests, fostering local stewardship. Unregulated ecotourism, however, induces behavioral disruptions, including elevated stress responses from close human approaches during foraging or surfacing. In Barbados, frequent encounters correlated with altered diving patterns and potential injury from propellers. Provisioning with non-natural foods, such as animal matter outside the herbivorous diet, accelerates growth but risks nutritional imbalances and dependency. Nesting site overcrowding from mass tourism erodes dunes, compacts sand, and exposes eggs via artificial lighting disorientation, with post-COVID-19 data indicating tourism cessation allowed expanded access to optimal habitats. Mitigation through caps on visitor numbers and timed access preserves benefits while addressing these causal pressures.

Conservation

Primary Threats and Causal Factors

The primary threats to Chelonia mydas populations stem from anthropogenic activities that disrupt their life cycle stages, including nesting, foraging, and migration. Fisheries bycatch remains a leading cause of mortality, with incidental captures in gillnets, longlines, and trawls affecting juveniles and adults globally; a 2023 analysis highlighted its role in hidden demographic impacts, exacerbating population declines through repeated gear interactions that cause injury or drowning. Directed harvest for meat, eggs, and shells has historically decimated numbers, with an estimated 1.1 million illegal exploitations occurring between 1990 and 2020 across 65 countries, predominantly involving green turtles, despite international prohibitions. Habitat degradation compounds these pressures by reducing nesting beaches and seagrass foraging grounds essential for herbivorous adults. Coastal development drives habitat loss through beach armoring, artificial lighting that disorients hatchlings, and erosion from seawalls, directly limiting nesting success; in the Pacific, such alterations have fragmented critical sites, with vehicle traffic and urbanization further compacting sand and destroying eggs. Climate change intensifies these effects via rising sea levels that erode nesting beaches and warmer incubation temperatures that skew primary sex ratios toward females—peer-reviewed monitoring at Australia's Great Barrier Reef documented near-total feminization in juveniles by the 2010s due to sand temperatures exceeding 29°C. Ocean warming also shifts foraging distributions, increasing overlap with high-risk areas like vessel traffic zones, as modeled in a 2025 global assessment projecting redefined hotspots under continued emissions. Marine pollution, including plastics and derelict fishing gear, causes entanglement and ingestion, with Hawaiian strandings data from 2016 identifying fishing line as the predominant injury source, often leading to fibropapillomatosis-linked debilitation. Chemical contaminants from runoff and oil spills degrade seagrass beds, a core diet component, while boat strikes from growing coastal boating traffic inflict blunt trauma, particularly during surfacing. Predation by invasive species on eggs and hatchlings amplifies losses at degraded sites, though these are secondary to human-induced factors; overall, cumulative mortality from these threats has driven regional declines, with recovery hinging on addressing root causes like unregulated fisheries and land-use expansion.

Protective Measures and Initiatives

The green sea turtle (Chelonia mydas) is afforded protection under the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES), with the species listed in Appendix I since June 6, 1981, which prohibits commercial international trade to prevent further population declines from exploitation. In the United States, the species is protected under the Endangered Species Act (ESA) of 1973, with three distinct population segments (DPSs) classified as endangered and eight as threatened, a status revised in April 2016 to reflect regional variations in recovery. These listings mandate federal actions to conserve habitats and minimize incidental harm, including prohibitions on take without permits. National and international initiatives emphasize habitat safeguarding, particularly nesting beaches and foraging grounds. NOAA Fisheries, in collaboration with partners, implements recovery plans that prioritize protecting key sites through marine protected areas, shoreline stabilization, and restrictions on coastal development to maintain suitable sand temperatures for sex determination and incubation success. Efforts also include reducing artificial lighting on beaches, which disorients hatchlings, and conducting patrols to deter egg poaching and predation, as seen in programs across Hawaii and Florida where thousands of nests are monitored annually. Bycatch mitigation forms a core component of fisheries-focused protections, addressing incidental capture in commercial operations. Techniques such as turtle excluder devices (TEDs) in shrimp trawls, which allow turtles to escape while retaining catch, and circle hooks in longline fisheries, which reduce hooking rates compared to J-hooks, have been promoted through regulations and gear incentives. Community-based programs in regions like Costa Rica and the Pacific islands involve local enforcement against egg harvesting and unsustainable take, supplemented by satellite tracking to map migration routes and inform protected corridors. These measures, combined with bans on direct harvest, contributed to the species' downlisting from Endangered to Least Concern on the IUCN Red List in October 2025, reflecting global population rebounds in monitored nesting aggregations.

Recovery Data and Debates on Effectiveness

Population estimates for Chelonia mydas have shown signs of recovery in several key regions following implementation of protective measures since the 1970s and 1980s, including bans on commercial harvesting and egg collection. In Hawaii, nesting abundances increased from fewer than 100 females annually in the early 1970s to over 1,000 by the 2010s, attributed to federal protections under the Endangered Species Act of 1973 and reduced poaching. Similarly, at Ascension Island, annual nesting emerged counts rose from approximately 5,000 in the 1980s to over 20,000 by 2020, linked to habitat management and anti-poaching enforcement. A 40-year study in Florida's Sarasota Bay documented sustained increases in juvenile recruitment and adult sightings, confirming localized effectiveness of nest relocation and predator control programs. Globally, the International Union for Conservation of Nature (IUCN) reassessed the species in October 2025, upgrading its status from Endangered to Least Concern based on aggregated data from over 50 rookeries showing overall population growth rates exceeding 1% annually in many monitored sites. This downlisting reflects empirical trends where conservation reduced direct mortality, allowing demographic recovery through higher survivorship of juveniles and adults; for instance, genetic studies indicate expanding effective population sizes in the Indo-Pacific. However, the assessment notes variability, with some subpopulations—such as the Central South Pacific (Endangered)—continuing to decline due to uneven enforcement. Debates persist on the long-term effectiveness of these efforts, as recovery metrics often rely on nesting beach data, which may overlook foraging ground declines from bycatch in industrial fisheries, estimated to kill tens of thousands annually despite gear regulations. Critics argue that optimistic IUCN projections underweight climate-induced threats, such as beach erosion and sex-ratio skews from warmer incubation temperatures, potentially stalling rebounds; for example, at Tortuguero, Costa Rica, nesting trends reversed downward after 2016 peaks, correlating with fishery expansions. Proponents counter that causal links from protections to observed increases demonstrate efficacy, but emphasize needs for expanded marine protected areas and international bycatch mitigation, given that sources like government reports (e.g., NOAA) show persistent strandings tied to fisheries. Regional biases in data collection—favoring well-studied Atlantic and Pacific sites over under-monitored Indian Ocean populations—further complicate global assessments.

References

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