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Chelydra

Chelydra is a of large-bodied freshwater turtles in the family , commonly referred to as snapping turtles for their combative temperament and strong, hooked jaws adapted for a powerful bite. Native to aquatic environments in North, Central, and northern , the genus encompasses three extant that are primarily predators with rugged, keeled carapaces and reduced plastra, enabling them to withdraw their limbs for . These turtles are distinguished from their larger relatives in the Macrochelys by their smaller size and more streamlined morphology, playing key ecological roles as and predators in ecosystems. The taxonomic history of Chelydra reflects ongoing revisions based on molecular and morphological evidence, with the current recognition of three species stemming from elevations of former subspecies of C. serpentina. These include Chelydra serpentina (common snapping turtle, type species described by Linnaeus in 1758), Chelydra rossignonii (Yucatán snapping turtle, originally described as Emysaurus rossignonii by Bocourt in 1868), and Chelydra acutirostris (South American snapping turtle, described by Peters in 1862). The genus name derives from the Greek kheludros, meaning "water serpent," alluding to their serpentine necks and amphibious habits. Fossil records indicate Chelydra has a deep evolutionary history dating back to the Tertiary period, representing a basal lineage within the Chelydridae family. Physically, species in Chelydra exhibit a robust build with carapace lengths reaching up to 50 cm in C. serpentina males, featuring three pronounced keels and a rough, sculptured texture for in muddy substrates. Their heads are disproportionately large with sharp, beak-like tomia lacking teeth, while tails are nearly as long as the and adorned with spines. Coloration varies from dark brown to olive or black , with yellowish undersides on limbs and necks; is evident in larger male size and thicker tails. Unlike many , they possess a small, cross-shaped plastron that offers minimal ventral protection, relying instead on speed and for when on land. Chelydra species inhabit slow-moving or stagnant freshwater bodies such as rivers, lakes, swamps, and marshes with soft bottoms and abundant vegetation, tolerating brackish water but avoiding fast currents. C. serpentina has the broadest range, extending from southeastern Canada and the eastern United States to northeastern Mexico, with introduced populations in Asia and Europe; C. rossignonii is restricted to the Yucatán Peninsula and adjacent Central American countries like Belize and Honduras; C. acutirostris occurs from Honduras southward to Ecuador and western Colombia. These distributions overlap in Central America, but habitat fragmentation and climate variability influence local abundances. Conservation assessments vary, with C. serpentina listed as Least Concern globally but facing regional declines from harvesting, C. rossignonii as Near Threatened, and C. acutirostris as Near Threatened, as of 2025. Biologically, Chelydra turtles are long-lived, with lifespans exceeding 50–70 years in the wild, and exhibit during oviparous reproduction, laying 10–50 eggs in terrestrial nests during or summer. They are opportunistic omnivores, consuming , amphibians, , carrion, and vegetation, often ambushing prey from concealment in . Behaviorally solitary except during , they are docile in water but fiercely defensive on land, capable of rapid neck extension to snap at threats. Population dynamics are influenced by high juvenile mortality and slow growth rates, with ongoing research highlighting and responses to environmental stressors like and road mortality.

Taxonomy

Etymology

The genus name Chelydra is derived from the Greek words chelys, meaning "turtle" or "tortoise," and hydra, referring to a water serpent, which together evoke the turtle's aquatic lifestyle and elongated, snakelike neck. The genus was established by August Friedrich Schweigger in 1812, with the type species Chelydra serpentina originally described as Testudo serpentina by Carl Linnaeus in 1758. The specific epithet serpentina comes from the Latin serpentīnus, meaning "snake-like," alluding to the species' aggressive disposition and serpentine neck. Among the recognized species, Chelydra rossignonii, described by Marie Firmin Bocourt in 1868, bears a honoring Jules Rossignon, a Frenchman who resided in during the mid-19th century. Similarly, Chelydra acutirostris, named by Wilhelm Peters in 1862, derives its from the Latin terms acutus ( or pointed) and rostrum (beak or snout), describing the species' distinctive tapered muzzle.

Classification and phylogeny

The genus Chelydra belongs to the family Chelydridae within the order Testudines, suborder Cryptodira. Its full taxonomic hierarchy is as follows: Kingdom Animalia, Phylum Chordata, Class Reptilia, Order Testudines, Suborder Cryptodira, Family Chelydridae, Genus Chelydra. Within Chelydridae, Chelydra represents one of two extant genera, the other being Macrochelys, which encompasses the alligator snapping turtles. Phylogenetic analyses, combining molecular data such as mitochondrial DNA sequences and morphological traits like cranial and shell characteristics, position Chelydra as a basal clade relative to Macrochelys within the family. These studies indicate that the divergence between Chelydra and Macrochelys occurred during the late Eocene, approximately 39–50 million years ago, marking an early split in chelydrid evolution. The fossil record of Chelydra and its stem relatives extends back to the , providing evidence of the genus's ancient origins within . Stem-chelydrids, such as Tavachelydra stevensoni from the early (Puercan, ~66 million years ago) Denver Formation in , represent early pan-chelydrid forms with features transitional to modern snapping turtles, including robust skulls adapted for durophagy. Later fossils include remains of Chelydra species from formations in , where and plastron fragments indicate large-bodied individuals co-occurring with other chelydrids. Pleistocene records further document the genus's persistence, with Chelydra serpentina fossils from sites in southern (e.g., Glendale locality, ~20,000–10,000 years ago) and western , reflecting broader historical distributions across North and during glacial periods. Additionally, extinct pan-chelydrid species like Chelydropsis aubasi from the Middle Eocene (Bartonian, ~40 million years ago) of Chéry-Chartreuve, , highlight the family's early Eurasian presence before its modern restriction to the . Recent taxonomic revisions have elevated several former subspecies of C. serpentina to full status based on genetic evidence from analyses demonstrating deep phylogenetic divergences and limited . Specifically, Chelydra rossignonii (Yucatán snapping turtle) and Chelydra acutirostris (South American snapping turtle) were recognized as distinct following studies in the and formalized in checklists by 2017, reflecting their isolation from northern C. serpentina populations. These changes underscore the role of molecular data in refining chelydrid systematics beyond morphological variation alone.

Description

Physical characteristics

Chelydra species exhibit a robust body structure adapted for an lifestyle, characterized by a large head, elongated that retracts in an S-shaped , and powerful featuring a hooked, beak-like without teeth. The is rough-textured and keeled with three prominent longitudinal ridges, providing structural support and , while the plastron is notably small and cross-shaped, leaving much of the limbs, , and tail exposed. This facilitates bottom-walking on substrates rather than agile swimming, with stout limbs equipped with strong claws suited for digging and navigating muddy environments. The shell of Chelydra typically measures 25-50 cm in length and displays an olive to black coloration, often obscured by or for concealment. Males possess a longer tail relative to females, featuring sharp spines along its surface, which aids in balance and defense. Sensory adaptations include laterally positioned eyes for a broad field of vision and snorkel-like nostrils at the tip, enabling the to breathe while submerged with minimal exposure. Webbing on the feet is minimal compared to more pelagic , emphasizing their role as bottom-dwellers over proficient swimmers. Dorsally, the body is mottled in shades of brown to black, enhancing against substrates, while the ventral surfaces are paler for contrast in low-light conditions. This structure contributes to the genus's characteristic aggressive snapping behavior when threatened on land.

Size variation and growth

Adult individuals of the genus Chelydra typically reach lengths of 25–45 cm and weights of 5–16 kg, with variation among species; hatchlings measure 2–3 cm in length. Sexual dimorphism in Chelydra is pronounced, with males generally achieving larger linear dimensions than females, including longer tails with thicker bases at the cloacal region. Females, in contrast, develop bulkier bodies to support egg production. Larger female size correlates with increased sizes during . Growth in Chelydra is indeterminate, allowing individuals to continue increasing in size throughout their lifespan, albeit at diminishing rates after . In C. serpentina, juveniles exhibit relatively rapid growth, averaging 1–2 cm per year in length, which slows to approximately 0.5 cm per year or less in adults; similar patterns are observed in other species. These patterns are modulated by environmental factors such as temperature and food availability, with warmer conditions and abundant resources promoting faster growth. Among species in the genus, C. serpentina attains the largest sizes, with wild individuals occasionally exceeding 34 kg, whereas C. rossignonii are smaller, with maximum carapace lengths around 39 cm, and C. acutirostris reaches up to 48 cm.

Distribution and habitat

Geographic range

The genus Chelydra is native to the Americas, encompassing eastern and central North America, Central America, and northwestern South America. Chelydra serpentina, the common snapping turtle, occupies much of this northern portion, ranging from southeastern Canada—including Nova Scotia, southern Ontario, Quebec, and New Brunswick—southward through the eastern and midwestern United States to the Gulf Coast states of Florida and Texas, and westward to the eastern slopes of the Rocky Mountains in Alberta, Montana, and Colorado. In Central America, C. rossignonii is distributed across Atlantic lowland drainages from central Veracruz and Oaxaca in southern Mexico, through the Yucatán Peninsula, Belize, Guatemala, and into northeastern Honduras. Further south, C. acutirostris inhabits Caribbean and Pacific drainages from southern Honduras through Nicaragua, Costa Rica, and Panama, extending into western Colombia and Ecuador in northwestern South America. Introduced populations of C. serpentina have established beyond its native range, primarily through the pet trade and human releases. In the , populations occur in since at least the mid-, as well as in , , , and , where individuals have been documented since the 1970s but likely earlier via aquarium and food trades dating to the 1800s. In Europe, established groups are reported in , the , , , the , and , often from pet releases since the late . In Asia, introductions include ( since the 1960s), , , , and , with breeding populations in some areas potentially aided by rafting on debris or intentional releases. Fossil evidence indicates a broader historical distribution for the genus and its relatives in the pan-chelydrid clade during the and Eocene epochs. Remains from the through early are widespread in western , with the clade spreading to and by the Paleocene, including sites in during the Middle Eocene, before regional extinctions outside the . In , sympatric zones exist where C. rossignonii and C. acutirostris co-occur, particularly in , allowing for potential ecological interactions in shared drainages.

Habitat preferences

Chelydra species, particularly the (C. serpentina), primarily inhabit slow-moving or stagnant freshwater bodies such as ponds, marshes, sluggish rivers, and swamps, where muddy or sandy bottoms and dense aquatic vegetation provide ideal conditions for predation and concealment. These habitats often feature shallow depths, typically less than 1 meter, allowing the turtles to remain close to the while minimizing exposure to open water. While they generally avoid fast-flowing currents that could dislodge them from preferred resting sites, C. serpentina demonstrates tolerance for in estuarine environments, occasionally utilizing coastal marshes or tidal creeks for seasonal or dispersal. As bottom-dwellers, Chelydra individuals spend much of their time burrowed into soft mud or concealed among submerged logs and vegetation, which offers protection from predators and facilitates . Microhabitat selection varies by life stage; hatchlings and juveniles favor obstructed pools or small streams with cover, while adults prefer larger, vegetated water bodies but remain tied to muddy substrates for and resting. Overland migrations occur occasionally, particularly for nesting or relocation to new water bodies, with recorded distances up to 16 km round-trip, though most movements are shorter, under 4 km. These turtles thrive in warm-temperate climates with water temperatures ranging from 10°C to 30°C during active periods, achieving optimal activity around 28°C, though they can endure brief extremes up to 39.5°C or down to 1–2°C during overwintering. They avoid deep, open waters due to limited swimming efficiency, relying instead on habitats with structural complexity for and . Physiologically, Chelydra exhibits remarkable adaptations for hypoxic conditions prevalent in muddy, low-oxygen sediments, including enhanced buccopharyngeal respiration that allows supplemental oxygen uptake through the throat lining, enabling prolonged submergence. This tolerance supports their use of seasonally variable estuarine habitats, where fluctuations occur.

Behavior and ecology

Activity patterns and locomotion

Chelydra species are primarily active during diurnal hours, with peak activity often occurring in crepuscular periods, although some nocturnal foraging has been documented. Basking behavior is rare, limited to occasional brief exposures rather than prolonged sessions typical of many other turtles. In southern portions of their range, individuals remain active year-round, while northern populations enter dormancy when water temperatures drop below 5°C, typically from October to April, burying in mud or overwintering communally in aquatic sediments. Activity resumes in spring as temperatures rise above 7.5°C, with feeding concentrated above 15°C and maximal movement between 18°C and 28°C. Locomotion in Chelydra involves quadrupedal walking along aquatic or terrestrial substrates, with typical speeds of 0.5–1 km/h, though juveniles may achieve brief maximal bursts up to 0.3 m/s on inclines. In , they are inefficient open-water swimmers, relying instead on paddling to "walk" along the bottom in depths under 2 m. Overland travel is infrequent but purposeful, primarily by females during nesting migrations (up to 16 km) or by both sexes for dispersal, such as during droughts when individuals may cover 1–1.7 km to reach permanent bodies. Home ranges average 4–11 ha, with females exhibiting larger areas during reproductive periods. Defensive responses emphasize aggression on , where individuals lunge forward with rapid extension to at threats, striking at distances equivalent to half to two-thirds of their length using powerful jaws (bite force averaging 209 ). Unlike many turtles, they do not fully retract their head but instead face the intruder directly, elevating the hindquarters and extending limbs to maintain balance during strikes. When possible, they retreat to or bury into to evade predators. Chelydra are largely solitary, with minimal conspecific interactions outside of ; , including and clawing, may occur during resource , though synchronized overwintering in groups has been observed in some populations. The Central American snapping (C. rossignonii) exhibits comparable solitary habits and substrate-based locomotion, with tracked movements up to 20 m in forested habitats.

Diet and foraging

Chelydra species exhibit an omnivorous diet, incorporating both animal and matter in varying proportions depending on age, season, and availability. Animal components typically include , amphibians, such as and , carrion, small mammals, and , while plant material consists of aquatic vegetation like and vascular s, as well as fruits, leaves, and stems. Studies indicate that plant matter often constitutes a larger portion of the diet than animal matter in adults, though quantitative analyses show variability across populations. Foraging in Chelydra primarily involves predation, where individuals rely on in muddy or vegetated environments to lie in wait with their mouths agape, striking rapidly with neck extension to capture passing prey. They also employ opportunistic scavenging of carrion and active pursuit or ram-feeding for softer vegetation and slower prey. Their powerful jaws, adapted for crushing hard-shelled items like mollusks, facilitate consumption of a broad range of food types. Dietary habits shift ontogenetically, with juveniles being more carnivorous and targeting small and larvae in shallow waters, whereas adults increase their intake of to comprise a substantial part of their . Seasonal variations further influence composition, as consumption of matter rises in summer when is abundant, while diets lean more toward animal prey amid limited growth. In wetland ecosystems, Chelydra plays a key trophic role as a predator, helping to regulate populations of and through predation and scavenging, which influences community structure and energy flow.

Reproduction

Mating and courtship

Mating in Chelydra species occurs primarily during the active from through fall, typically spanning to November in northern populations, with peak activity in late spring and early summer when temperatures rise above approximately 15–20°C. This timing aligns with post-hibernation gonadal , where increased testicular activity in males and in females are triggered by environmental warming. Males actively search for receptive females in aquatic habitats, often pursuing them with brief chases or mutual head movements near the surface. Courtship displays in Chelydra are minimal and lack elaborate visual or acoustic signals common in other ; instead, the male mounts the female's directly, grasping it firmly with his claws while curving his tail to align cloacae for intromission. To maintain position, the male may bite the female's neck or head, prompting occasional struggles from her, though she generally remains passive during copulation, which typically lasts 10–30 minutes and occurs submerged or partially in water. Male-male interactions during the period are infrequent but can involve aggressive snapping or lunging if territories overlap, though outright combat is rare compared to more territorial chelonians. Both sexes exhibit polygamous behavior, with females often mating with multiple males over the season, as evidenced by multiple paternity in clutches detected via DNA fingerprinting, facilitated by long-term sperm storage in oviducts. Males similarly mate with multiple females, contributing to a promiscuous mating system that enhances genetic diversity. Sexual maturity is reached at 8–12 years of age, though this varies regionally; males typically mature at smaller sizes (e.g., 10–12 cm plastron length) than females due to pronounced sexual size dimorphism, where larger female body size may influence male mate selection preferences.

Nesting and development

Females of the Chelydra typically produce a single per year, consisting of 20–80 eggs, with an average of 30–50 eggs depending on female size and . Eggs are white, elliptical to spherical, and enclosed in leathery shells measuring 2.3–3.3 cm in diameter (mean 2.8 cm). In C. serpentina, larger females lay more eggs, with clutch sizes increasing northward; for example, means range from about 30 eggs in southern populations to 44 in northern ones. Comparable data for C. rossignonii and C. acutirostris are limited, but clutch sizes are presumed similar based on shared traits. Nesting occurs primarily in to (June–July in northern ranges), when gravid females migrate overland to well-drained, sandy or loamy upland sites, often 50–500 m from water bodies. They excavate flask- or bowl-shaped nests 5–20 cm deep using their hind limbs, deposit the eggs, cover the chamber with soil and vegetation, and then abandon the site without further . These migrations expose females to risks such as predation and vehicular collisions. Nest favors open, sunny areas to optimize temperatures, though females may reuse sites in subsequent years. Egg incubation lasts 9–18 weeks (typically 70–90 days), varying with environmental conditions such as and . Optimal temperatures range from 25–30°C, with higher levels in the enhancing success (up to 87.5%) and hatchling size and locomotor performance. determination is temperature-dependent, following an FMF pattern (female-male-female) where females are produced at low (below approximately 23°C) and high (above 29°C) temperatures, and males at intermediate temperatures (23–28°C), with pivotal temperatures around 23°C (lower) and 28–29°C (upper) yielding mixed sex ratios. In C. acutirostris, incubation periods extend to 55–125 days under similar thermal regimes. , about 3–4 cm in length with absorbed yolk sacs, emerge independently in late summer or fall (August–) or overwinter in the nest and emerge the following (–May). Post-hatching development involves high juvenile mortality, estimated at 80–90% before adulthood due to predation, flooding, and environmental stressors. Initial growth is slow, at approximately 1 cm per year for the first few years in C. serpentina, with reached in 10–15 years (males 10–17 years, females 11–19 years in northern populations). Survivorship improves with size, but overall recruitment remains low, supporting the genus's long-lived, late-maturing life history strategy.

Conservation

Status across species

The (Chelydra serpentina) is classified as Least Concern globally by the , with the assessment conducted in 2025. However, it holds Special Concern status in according to the on the Status of Endangered Wildlife in Canada (COSEWIC), a designation established in 2008 and maintained through ongoing reviews, with reassessment deferred in May 2025. In the United States, while generally secure at the national level, it is considered Vulnerable or of Special Concern in certain states, such as and , due to regional population pressures. The Central American snapping turtle (Chelydra rossignonii) is assessed as Vulnerable by the , with the assessment conducted in 2007 and data availability remaining limited, leading to uncertainties in population estimates. Regional conservation protections exist in parts of its range in due to habitat loss and other threats. For the South American snapping turtle (Chelydra acutirostris), the species is by the . Information on its population status is limited, particularly in portions of its distribution such as Ecuadorian wetlands. Across the Chelydra genus, populations are generally stable, reflecting wide distributions and adaptability, though localized declines occur due to . loss contributes to these regional vulnerabilities but does not threaten the genus as a whole.

Threats and protection

The genus Chelydra faces several human-induced threats that impact its populations across North and . Habitat loss, primarily from drainage for and urban development, is a primary concern, reducing suitable and riparian environments essential for these turtles. Road mortality poses a significant risk, particularly to nesting females that travel overland to lay eggs, with studies indicating annual mortality rates exceeding 5% in high-road-density areas. Harvesting for the and trades, both legal and illegal, further depletes adult populations, especially of C. serpentina, contributing to localized declines. , including water contamination and of contaminants like mercury, affects and , with agricultural runoff exacerbating these issues. Climate change introduces additional pressures on Chelydra species through altered incubation temperatures influencing temperature-dependent sex determination. Warmer nest temperatures generally produce more females, potentially skewing sex ratios toward feminization, though extreme thermal fluctuations may occasionally accelerate male production and mitigate some biases. For C. rossignonii, increased hurricane frequency facilitates oversea dispersal and introductions to new islands, such as the first documented occurrence on Utila Island, Honduras, following a 2020 storm, raising concerns about invasive establishment. Conservation protections for Chelydra include international and national measures to regulate trade and collection. C. serpentina is listed in Appendix II (since 2023) by the and several Canadian provinces, requiring export permits to monitor and prevent . In the U.S., at least 30 states prohibit or severely restrict commercial harvesting of snapping turtles, with recent bans in (2024) and (2018) targeting wild populations to curb declines. Habitat restoration efforts in focus on wetland reconstruction and nesting site enhancement, such as in Ontario's urban areas, while similar initiatives in aim to protect riparian zones in southern ranges. Monitoring programs, coordinated by the IUCN SSC and Freshwater Turtle Specialist Group, track population trends and threats through field surveys and Red List assessments to inform . Management strategies emphasize reducing mortality and bolstering . Head-starting programs, where hatchlings are reared in captivity to larger sizes before release, improve juvenile survival rates, with applications tested for Chelydra in fragmented habitats to counter road and predation losses. Nest protection measures, including fenced beaches and wire mesh enclosures, have been evaluated to shield eggs from predators and vehicles, increasing hatch success in high-risk areas. Ongoing research addresses invasive potential, such as modeling C. serpentina range expansion in under scenarios to prevent ecological disruptions.

Species

Chelydra serpentina

Chelydra serpentina, commonly known as the North American snapping turtle, is the largest species in the Chelydra, with adults typically exhibiting a carapace length of 25 to 50 and weights ranging from 4.5 to 16 , though exceptional individuals can reach up to 34 . Juveniles display more pronounced keels along the , which become less distinct with age as the shell smooths out. Like other members of the , it possesses a robust build adapted for life, but its greater size distinguishes it among snapping turtles. The native distribution of C. serpentina spans from southeastern southward to and westward to the , encompassing a wide array of temperate freshwater systems. Introduced populations have established on the of the , as well as in parts of and , often resulting from releases of pet trade animals. These non-native ranges pose ecological concerns due to potential competition with local species. In its preferred habitats of temperate ponds, rivers, and slow-moving streams, C. serpentina functions as an opportunistic , with a diet heavily featuring , carrion, and various aquatic . This scavenging aids in ecosystem cleanup, but the turtle's aggressive defensive posture, including powerful bites, frequently leads to conflicts with humans, such as injuries during handling or encounters in shared waterways. Reproduction in C. serpentina involves females laying larger clutches than other congeners, typically 25 to 80 eggs per nest, with clutch size increasing with female body size and . Nests are commonly excavated in disturbed sandy or loamy substrates, including sites like roadsides and dams, which provide suitable loose soil for burial. lasts 2 to 3.5 months, influenced by , leading to sex determination via . Conservation challenges for C. serpentina include historical overharvesting for its meat, which has been commercially exploited for soups and stews across its range, prompting regulations in some areas to limit take. Abroad, introduced populations raise concerns, potentially disrupting native in European and Asian wetlands. Fossil evidence from the Pleistocene of southern indicates the species' long presence in western , with remains suggesting continuity in distribution despite past climatic shifts. The standardized "North American Snapping Turtle" helps distinguish it from other snapping turtles and snappers in .

Chelydra rossignonii

Chelydra rossignonii, commonly known as the Central American snapping , is a moderately sized freshwater distinguished by its rounded , which measures up to 38.9 cm in length and features three pronounced longitudinal keels along with heavy posterior serrations. The shell tends to be smoother overall with more pointed marginal scutes compared to other congeners, and adults typically weigh 5-12 kg, with females reaching larger sizes. This species is distributed across southeastern Mexico, including the states of , , , , and , extending southward through and to northeastern . Its range centers on lowland tropical wetlands, with records indicating potential overwater dispersal events facilitated by hurricanes, such as the first documented occurrence on Utila Island, Honduras, following in November 2020. Inhabiting slow-moving tropical rivers, swamps, and marshy areas, C. rossignonii exhibits ecological adaptations suited to warm, humid environments, where it remains largely aquatic and displays less aggressive behavior than temperate relatives. Its diet is omnivorous, primarily consisting of , amphibians, and , supplemented by some aquatic vegetation, with foraging typically involving predation similar to other Chelydra species. Reproduction occurs seasonally, with females laying a single clutch of 20-30 eggs annually between April and June; nests are excavated in sandy substrates, often near water bodies including coastal areas, and hatchlings emerge dark gray to black with white spots on the marginal scutes. Clutch sizes may vary regionally, but limited observations suggest 15-40 eggs as a broader range based on related studies. Conservation efforts for C. rossignonii are challenged by its Vulnerable status on the , primarily due to ongoing habitat loss from deforestation, , and across its , compounded by illegal collection for the pet trade and subsistence use. Population trends are poorly documented, with sparse studies indicating potential declines and deficiencies in remote areas; protective measures include regional bans on collection in and , though enforcement remains limited. Notably, C. rossignonii was historically classified as a of C. serpentina until elevated to full status in 2016 based on genetic and morphological distinctions, and its scientific name honors Jules Rossignon, a 19th-century collector who gathered specimens in .

Chelydra acutirostris

Chelydra acutirostris, the South American snapping turtle, is the smallest in the genus, typically measuring 25–35 cm in length and weighing 3–7 kg, though maximum recorded straight lengths reach 48 cm in males and 39 cm in females. It features a broad, dark brown with three faint keels and radiating lines often obscured by , a cross-shaped plastron, a , and a robust head with a hooked and pointed adapted for probing stream substrates. This suits its role as a bottom-walker in flowing waters, emphasizing its poor swimming ability compared to more aquatic congeners. The is endemic to wetter southern ranges, distributed from in and possibly extending north to , , and , southward to northwestern including , , and , with unconfirmed records in . It inhabits rivers and lagoons in Andean foothills at elevations up to 624 m, as well as swamps, streams, and artificial ponds with sandy or muddy bottoms, favoring clearer, slow-moving freshwater environments. Ecologically, it is primarily nocturnal and territorial, with home ranges of 0.1–15 ha, functioning as an on the ; its is omnivorous but heavily features , , crustaceans, mollusks, and occasional or carrion. Reproduction occurs with underwater copulation, followed by females nesting in riverbanks up to 50 m from water during May–June, laying clutches of 10–30 eggs that incubate for 55–125 days. Conservation-wise, C. acutirostris is classified as Near Threatened globally but experiences local declines due to , , loss, , and for meat, medicinal uses, crafts, or the pet trade, with populations in and protected in reserves like Cotacachi Cayapas. Like other Chelydra species, it relies on a defensive snapping bite when threatened on land.

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