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Greater rhea

The Greater rhea (Rhea americana) is a large, flightless bird and the largest species in the , endemic to open South American habitats where it serves as an ecological engineer through and . Adults stand 1.3–1.7 m (4.3–5.6 ft) tall at the shoulder, weigh 20–40 kg (44–88 lb), and exhibit with males larger than females; their is shaggy and gray-brown, with blacker tones on the head, neck, and back, while the underparts are whitish. They possess long, powerful legs ending in three-toed feet for rapid sprinting up to 60 km/h (37 mph), a long neck for foraging, and vestigial wings that aid in balance and display but preclude flight, classifying them within the ancient lineage alongside ostriches and emus. Native to a vast range spanning northeastern and eastern , eastern , , , and northern and central , the greater rhea inhabits lowland , savannas, grasslands, and semi-open scrublands, often near water sources like rivers or marshes during breeding. These birds are highly adaptable to human-modified landscapes, including agricultural fields and pastures, though they prefer areas with low vegetation for visibility and escape. Outside their native range, introduced populations exist in southeastern , an established population of about 600 in , and small groups in the United States, primarily from escaped or released captives. Greater rheas are social, diurnal omnivores that form loose flocks of 10–30 individuals outside breeding season, foraging on grasses, seeds, fruits, roots, and occasionally insects, small vertebrates, or even carrion, aided by ingested stones for grinding in their gizzard. Breeding occurs from July to January in the Southern Hemisphere summer, with polygynandrous mating where dominant males court multiple females (up to 12), construct shallow ground nests, and solely incubate clutches of 10–60 large, yellowish eggs for 35–40 days before raising precocial chicks for up to six months. When threatened, they rely on speed and zigzagging runs rather than confrontation, producing low-frequency booming calls primarily from males during courtship. Currently classified as Near Threatened by the IUCN, greater rhea populations are declining across their range due to habitat loss from and , as well as illegal for , eggs, and feathers; the global has not been quantified, but the is described as uncommon to fairly common. Conservation efforts include protected areas in key habitats like the Argentine and regulated quotas in countries such as and , where the holds cultural and economic value in ranching communities.

Taxonomy

Etymology

The genus name Rhea was introduced in 1752 by the German naturalist Paul Heinrich Gerhard Möhring for the South American ratites, drawing from the name of the Titaness Rhea in Greek mythology, who was the mother of the gods and symbolized fertility and the earth; this choice likely reflected the bird's large size and ground-dwelling nature as a flightless species. The specific epithet americana was coined by Carl Linnaeus in 1758, when he described the species as Struthio americanus in Systema Naturae, with "americana" denoting its origin in the New World to distinguish it from African ostriches. Over time, the binomial nomenclature evolved, and by the early 19th century, the bird was reclassified under the genus Rhea as Rhea americana, solidifying its current scientific name. In , the greater rhea is known as ñandú, derived from the Guaraní term ñandú guazú, which literally translates to "big spider" and may allude to the bird's sprawling legs or the way it spreads its wings in displays, resembling a spider's . European explorers and naturalists initially misclassified the greater rhea as a relative of the African due to superficial similarities in appearance and flightlessness, leading to common names like "American ostrich" or "South American ostrich," as noted by during his voyages. This nomenclature persisted in early , highlighting the bird's role as the largest native in the before more precise taxonomic distinctions were established.)

Classification

The greater rhea ( americana) is classified within the order and the family Rheidae, belonging to the paleognathous birds, a group characterized by ratite-like features such as reduced wings and a keelless . It was first described by in 1758 under the binomial name Struthio americanus in the 10th edition of Systema Naturae, later reclassified into the genus . Phylogenetically, the greater rhea is most closely related to the lesser rhea (Rhea pennata), with both forming the monophyletic family Rheidae, as confirmed by genetic analyses of nuclear and mitochondrial DNA sequences. Rheas are part of the broader ratite clade, which includes ostriches (Struthio), emus (Dromaius), cassowaries (Casuarius), and kiwis (Apteryx), though recent phylogenomic studies indicate ratites are polyphyletic, with flightless evolution occurring multiple times independently. The divergence between the Palaeognathae (encompassing ratites and tinamous) and other birds occurred around 110 million years ago, while the split between tinamous (Tinamidae) and ratites is estimated at 60–70 million years ago, following the Cretaceous–Paleogene extinction event. The evolutionary history of rheas is tied to the ancient ancestors that originated in the during the , with the rhea lineage diversifying in after the continent's separation from approximately 100 million years ago. The fossil record of Rheidae dates back to the Eocene epoch around 40 million years ago, with multiple species identified from deposits (about 12–2 million years ago) in , supporting the family's through shared morphological traits in hindlimb bones. Genetic studies, including analyses of complete mitochondrial genomes, further affirm the of Rheidae as a distinct South American clade within .

Subspecies

The greater rhea (Rhea americana) is classified into five recognized , primarily distinguished by subtle morphological variations and geographic isolation within their South American ranges. These were delineated based on early 20th-century taxonomic assessments, with ongoing recognition in modern ornithological references despite limited genetic data.
SubspeciesDistributionKey Features
R. a. americana (nominate)Northern and eastern Typical gray plumage; moderate size (males up to 1.5 m tall); standard bill shape.
R. a. nobilisEastern , in semi-arid Chaco woodlands and grasslandsSlightly larger body; darker neck feathering; adapted to dry, open habitats.
R. a. araneipesSouthwestern (Mato Grosso region), eastern , western Robust build; variations in leg feathering; inhabits savannas and floodplains.
R. a. intermediaSoutheastern (Rio Grande do Sul), , central Intermediate size; balanced plumage tones; prefers and grassy lowlands.
R. a. albescensSouthern ( to Río Negro region)Largest subspecies (up to 1.7 m tall); paler, grayish-white plumage; straighter bill.
Morphological distinctions among these subspecies are minor but include body size gradients (increasing southward), plumage coloration (paler tones in southern populations like albescens due to lighter feathering on the flanks and underparts), and subtle bill curvature variations, with northern forms showing slightly more curved bills for foraging in varied vegetation. These traits reflect adaptations to local habitats, such as open grasslands for intermedia and albescens, or semi-arid scrub for nobilis. Genetic studies, including analyses of mitochondrial DNA, indicate low inter-subspecies divergence, supporting their validity as diagnosable units but highlighting potential for future taxonomic review; no significant revisions have occurred since 2023.

Description

Physical characteristics

The greater rhea (Rhea americana) is the largest bird native to , distinguished by its tall, robust frame and flightless form. Measuring 127–140 cm (50–55 in) in length from beak to tail, it stands 1.4–1.7 m (4.6–5.6 ft) tall at the shoulder, with an average adult weight of 20–27 kg (44–60 lb). Individuals in captivity may reach up to 40 kg due to ample and protection from predators. The bird's is fluffy and shaggy, giving a tattered appearance, primarily in to with considerable individual variation. Both sexes have feathered heads, , rumps, and thighs, along with white underparts, but lack true tail feathers. Males exhibit darker overall coloration than females, which are paler, and develop a prominent dark at the base during the breeding season. Key structural features include a long, flexible neck, powerful elongated legs, and three-toed feet suited for . The wings are long and vestigial, functioning primarily for , while the overall build supports rapid running speeds of up to 60 km/h (37 mph). Sexual dimorphism is evident in males' greater size and intensified pigmentation, though both sexes share a comparable body structure. Greater rheas typically live 10–15 years , where environmental pressures limit , but can survive up to 30–40 years in captivity under optimal conditions.

Adaptations

The , a flightless , exhibits a reduced on its , which minimizes the attachment sites for flight muscles and supports its to terrestrial life. Instead of relying on flight, it has evolved powerful, long legs optimized for locomotion, enabling sustained running speeds up to 60 km/h to evade predators across open grasslands. Its long wings, though incapable of sustaining flight, function as stabilizers and rudders, aiding balance and sharp turns during high-speed chases. Sensory adaptations in the greater rhea prioritize detection of threats in expansive habitats, with excellent eyesight allowing vigilant scanning for predators while . Its is poor, consistent with most species that depend little on olfaction for . Acute hearing complements these traits, as evidenced by the male's booming calls, which can be detected up to 1 km away, facilitating communication over distances. Physiologically, the greater rhea conserves water efficiently, lacking sweat glands like other birds and minimizing evaporative loss through low respiratory water expenditure, which suits its semi-arid environment. Its omnivorous digestive system features a muscular that grinds tough plant material, aided by ingested pebbles, enabling it to process a diet dominated by grasses, seeds, and occasional or small vertebrates. For thermoregulation, the greater rhea's , with looser feathers on the neck and body compared to flying birds, facilitates heat dissipation in hot conditions by allowing air circulation; it also pants and spreads its wings to enhance evaporative cooling when ambient temperatures exceed 36°C. These mechanisms, observed across ratites, help maintain body temperature without excessive loss. Recent studies have revealed evidence of problem-solving in ratites, including greater rheas, with individuals demonstrating innovative behaviors such as manipulating objects to access rewards, suggesting cognitive adaptations beyond basic instinctual responses.

Distribution and habitat

Native range

The greater rhea (Rhea americana) is native to eastern and southern , with its range encompassing northeast , east and northeast , , , and north and east south to approximately 40°S in Río Negro province. This primarily spans open and ecoregions, including the , chaco, and campos, with serving as the core of its occurrence across much of the country's eastern and southern regions. The total extent of occurrence is estimated at 8,740,000 km², reflecting a broad but uneven coverage shaped by historical availability. Historically, the greater rhea's range was more continuous and extensive prior to European colonization, when vast expanses of unmodified grasslands supported larger, interconnected populations across these regions. Intensive agricultural expansion and ranching since the have fragmented this range, converting grasslands into croplands and pastures, leading to local extirpations such as in the Brazilian states of and , though reintroductions have since recolonized parts of these areas with small populations. Today, the persists in a patchwork of remaining natural and semi-natural areas, with ongoing habitat loss continuing to isolate populations. Five subspecies are recognized, each tied to specific ecoregions within the native range: R. a. americana in northeastern Brazil's caatinga and cerrado; R. a. nobilis along eastern Brazil's coastal lowlands; R. a. intermedia in central Brazil, eastern Bolivia, and the Paraguayan chaco; R. a. murbergii in northern Argentina and Uruguay's pampas; and R. a. albescens in the Patagonian steppes of southern Argentina south to northeastern Río Negro. These distributions align with regional biome variations, from tropical savannas in the north to temperate grasslands in the south. Recent observations indicate range expansion into altered landscapes, particularly degraded edges of forested areas like Brazil's , where habitat modification from and has created suitable open conditions, allowing incursions up to 500 km beyond traditional savanna-forest transitions. This shift, documented through and probabilistic mapping in southern Brazil's , reflects adaptation to anthropogenic changes rather than natural migration. The species occurs from up to 1,650 m in elevation, primarily in lowland plains but extending into the Andean foothills where suitable grassy habitats persist.

Introduced populations

The greater rhea has established a population in northeastern , primarily in the region around the . This population originated from escapes of farmed birds around 2000, beginning with a small group of one male and five females from a farm near Groß Grönau in . By late 2018, the population had grown to approximately 560 individuals despite initial challenges, and estimates reached over 550 by 2020, with continued expansion reported into adjacent areas. As of mid-2025, the population remains stable despite ongoing management efforts, aided by mild summers and suitable open habitats resembling their native . These introduced rheas have demonstrated notable adaptability to the of , tolerating cold winters with temperatures as low as -20°C by seeking shelter in wooded areas and forming groups for warmth. However, they face conflicts with local , as their behavior leads to crop damage, particularly to corn, soybeans, and fields, prompting their classification as potentially invasive by authorities in 2020. The dominant in this population is likely Rhea americana americana, derived from South American farm stock commonly used in aviaries. Management efforts in include targeted programs initiated by farmers' associations and local authorities to control numbers and mitigate agricultural impacts, with hunting permitted since 2018. No self-sustaining populations have established elsewhere outside ; attempts in the United States, such as in , and other parts of have resulted in only transient escapes without long-term success post-2023. Small, unconfirmed groups have occasionally been reported in , but these have not persisted.

Behavior and ecology

Social behavior

The greater rhea exhibits a gregarious outside the , forming mixed-sex flocks typically ranging from 10 to 100 individuals that roam open grasslands in a loosely cohesive manner. These larger flocks provide benefits such as enhanced vigilance, with group size influencing individual scanning to detect potential threats. Following the breeding period, flocks fragment into smaller family units consisting of a single male accompanied by 20 or more of his , which remain together for several months until the young reach independence. Greater rheas are diurnal, maintaining active routines during daylight hours characterized by leisurely ambling across their range, covering home areas averaging approximately 4.5 square kilometers (450 hectares) in some populations, with maximums exceeding this based on radiotracking studies. When evading perceived dangers, they employ swift zig-zag running patterns, utilizing their vestigial wings alternately for balance and sharp turns at speeds up to 60 km/h. Vocalizations are minimal outside contexts, with adults generally remaining silent; only low booming calls occur during displays. Males display territorial defense solely during the breeding season, aggressively protecting defined areas, whereas outside this period, the species adopts a with fluid group movements across expansive habitats. Recent research highlights in greater rheas, as evidenced by a 2025 study where one individual innovated solutions to a novel puzzle by rotating a 10 times and twice removing a securing bolt to access food compartments, suggesting capacity for trial-and-error among ratites. Within flocks, social interactions reveal a subtle hierarchy, where dominant adults—often larger males—tend to lead group movements and influence spatial positioning, though overall cohesion remains loose without rigid dominance structures.

Diet and foraging

The greater rhea (Rhea americana) is omnivorous, with its diet dominated by plant matter comprising approximately 80–99% of intake, including broad-leaved foliage, grasses, leaves, fruits, seeds, roots, and clover. Animal matter supplements this, consisting of insects (such as beetles and grasshoppers), small vertebrates like lizards, frogs, snakes, rodents, and occasionally fish or birds. In agroecosystems, it preferentially consumes wild dicots like black medic (Medicago lupulina) and thistles over cultivated crops such as wheat or oats, with dicots making up 60–70% of fecal samples in studies from the Argentine Pampas. Foraging occurs primarily in open grasslands and field borders, where the bird uses its strong, flat beak to graze and pluck vegetation throughout the day, often in groups for vigilance. It opportunistically preys on mobile animals like or small reptiles encountered during , and may gather at carrion to consume flies. Seasonal variations influence composition, with higher animal matter intake during dry periods; for instance, in Brazil's Três Marias Reservoir, rheas consumed stranded when water levels dropped in . In introduced populations in , foraging extends to agricultural fields, leading to crop damage estimated at tens of thousands of euros annually. The digestive system features a in the esophagus for temporary and a muscular that grinds tough material, aided by ingested pebbles, , or seashells acting as gastroliths. This supports efficient processing of fibrous , with gut times averaging 61.6 hours, which facilitates by enhancing rates of large-fruited tree species in ecosystems like the Argentine Chaco. However, in farmlands creates conflicts, as rheas consume weeds and pests beneficially but also raid , contributing to their in agricultural regions.

Reproduction

The greater rhea exhibits a complex combining female-defense and sequential , where males court and defend groups of multiple females, while females may lay eggs in several males' nests. Males typically mate with 5 to 12 females, with harems often comprising up to seven, leading to communal es in a single nest. Clutch sizes range from 8 to 56 eggs, with an average of 25 eggs per nest, though most completed nests contain 20–30 eggs laid by multiple females over 7–10 days. Breeding occurs seasonally in the spring, from August to January, often triggered by increasing photoperiod and rainfall patterns that signal favorable conditions. Peak egg-laying aligns with moderate temperatures (14.8–20.8°C) and low rainfall (<11.3 mm/day), with activity ceasing during heavy rains exceeding 35 mm. Eggs are pale green to greenish-yellow, measuring approximately 13 cm in length and 9 cm in width, and are laid in a simple ground scrape nest constructed by the male, often in open grassy areas. Following laying, females abandon the nest and may contribute to other males' clutches, leaving and parental duties entirely to the male. Males incubate the eggs for 29–43 days (averaging 36–42 days), beginning full coverage 5–7 days after the first egg, with nest attendance reaching 97.5% during late ; they leave the nest briefly during the hottest midday hours to . demands significant energy reserves, equivalent to 53,202 kcal or 15–20% of the male's body weight in , limiting breeding to fewer than 20% of males annually. Post-hatching, males provide exclusive , aggressively defending the brood against intruders—primarily through displays and chases—and leading up to 20 surviving for 4–6 months until independence. occupies over 20% of daylight hours initially, decreasing as age, with about 60% of surviving the first 40–50 days. In , rates are high, with below 50% due to nutritional, behavioral, and environmental factors, though egg production can reach 30 per female per season under optimal conditions.

Predators and defense

The greater rhea faces predation across all life stages, with adults primarily threatened by large carnivores such as pumas (Puma concolor), jaguars (Panthera onca), and occasionally feral dogs. Eggs and chicks are more vulnerable, preyed upon by foxes (e.g., , Lycalopex gymnocercus), armadillos (e.g., big hairy armadillo, Chaetophractus villosus), and such as the (Caracara plancus). Humans also pose a significant predation risk through , though this is addressed in conservation contexts. To counter these threats, greater rheas rely on swift evasion tactics, capable of reaching speeds up to 60 km/h in open grasslands while running in a pattern to confuse pursuers; their wings aid in and balance during these maneuvers. When cornered, individuals—particularly s—may charge and kick with powerful legs to deter attackers. Chicks employ by hiding in tall grass under the vigilant protection of the brooding male, who leads the group away from danger. Predation exacts a heavy toll on chick survival, with approximately 40% mortality in the first few months post-hatching, largely attributable to attacks by foxes, caracaras, and other small carnivores; overall first-year losses can exceed this due to ongoing risks. As a key prey in South American grasslands, the greater rhea supports populations of these carnivores, contributing to balance.

Conservation

Population status

The greater rhea (Rhea americana) is classified as Near Threatened on the , with this status reflecting ongoing concerns over its dynamics across its native range in eastern and southern . The global size has not been precisely quantified, though the is described as uncommon to fairly common in suitable s, encompassing an estimated range of approximately 6.5 million km². Population trends indicate a decline, primarily driven by habitat degradation, though exact rates remain uncertain due to limited comprehensive surveys. Monitoring efforts rely on data compiled by , supplemented by local field surveys and regional assessments in countries like , Brazil, and Paraguay. These indicate stable to decreasing numbers in core native areas, with some populations facing heightened vulnerability from fragmented habitats and localized pressures. No significant change in overall IUCN status has occurred since the last major assessment in 2016, though ongoing evaluations incorporate modern techniques like camera trapping to track density and distribution. Outside its native range, an introduced feral population in , established from escaped captives around 2000, has shown stability and modest growth despite management efforts, numbering over 500 individuals as of 2020, with the population remaining stable as of 2025. This non-native group contrasts with native trends and contributes negligibly to global numbers but highlights the species' adaptability in novel environments.

Threats and measures

The greater rhea faces significant threats from activities, primarily habitat loss due to the expansion of and ranching, which has converted significant portions of its native range into croplands and pastures. This fragmentation reduces available foraging areas and increases isolation of populations, exacerbating vulnerability in regions like the Argentine and Brazilian campos. Additionally, illegal for meat and eggs persists, particularly in parts of where such practices are prohibited, leading to substantial population declines in hunted areas. Egg collection by rural communities further impacts , as rheas lay large clutches that are targeted for . Vehicle collisions also pose a growing risk, with rheas frequently struck on roads traversing their open habitats, contributing to adult mortality in both native and introduced ranges. Emerging threats include disease outbreaks, such as avian pox reported in in 2024, which caused 69% mortality among juveniles in affected flocks, highlighting the species' susceptibility to pathogens in altered environments. compounds these issues by drying grasslands through altered precipitation patterns, reducing vegetation cover and food availability in core habitats like the Chaco and . Conservation measures for the greater rhea include its listing under Appendix II since 1975, which regulates international trade in skins, meat, and eggs to prevent . The species is protected within reserves such as the Iberá Wetlands in , where habitat efforts safeguard breeding sites and migration corridors. Reintroduction programs draw from models like the 2025 lesser rhea translocation initiative in Patagonia, adapting techniques for greater rhea releases to bolster wild populations in fragmented areas. Community-based ranching bans and sustainable land-use policies in and have reduced by promoting and legal alternatives to hunting. Successes in conservation include feral population management in , where non-lethal deterrents and fencing have minimized conflicts with farmers since , preventing culls and aiding local ecosystem balance. Captive breeding programs, such as those at the Smithsonian National Zoo, have produced chicks for release into protected areas, contributing to and population recovery in declining regions.

Relationship with humans

Economic uses

The greater rhea is raised on farms primarily in and , where it serves as a source of multiple products including , , and . The is lean and red, with a fat content lower than that of or , making it a healthier alternative to traditional red meats while offering a similar and profile. Each rhea is substantially larger than a , weighing approximately 500–600 grams and equivalent in volume to about 10 , allowing for high-yield under captive conditions where females can lay up to 40 annually. The hide yields durable valued for its strength and suppleness, contributing to the bird's overall economic viability as nearly 95% of the is usable for products like these. Farming operations remain small-scale globally, though exact current numbers are unclear; for example, production has declined to fewer than 2,000 birds in recent years, focused on sustainable rearing to meet niche markets for meat and specialty goods. In addition to primary products, feathers are harvested for use in dusters due to their soft, effective dust-trapping qualities, while the oil extracted from the birds has historically been incorporated into and soaps for its moisturizing properties in South American formulations. Traditional hunting of greater rheas for and feathers persists in some South American countries such as and , where it is regulated through quotas and commercial permits to balance harvest with population sustainability. Escapes from farms have occasionally led to established feral populations, such as in , where birds introduced via agricultural operations in the early now number in the hundreds and pose management challenges. These economic activities provide supplementary income for rural communities in , where rhea products contribute to local protein sources and diversification of agricultural revenue, accounting for a notable portion of wild-sourced in some areas. However, such can with broader efforts, as unregulated or excessive harvesting in agricultural landscapes exacerbates pressures on wild populations already vulnerable to habitat loss.

Cultural and ecological impacts

The greater rhea holds notable cultural significance among , particularly in Patagonia. Rock art at , a in , features depictions of rheas alongside guanacos and hunting scenes, with paintings dating between 13,000 and 9,500 years ago, providing evidence of the bird's importance in early societies. In Guarani and Tehuelche traditions, the bird is known as "ñandú" and appears in as a swift, elusive creature emblematic of the open landscape. Ecologically, the greater rhea contributes to the maintenance of ecosystems in its native range. As an effective seed disperser, it consumes and excretes seeds from various plants, often enhancing rates in Neotropical savannas and , thereby supporting plant diversity and regeneration. Its behavior helps control overgrowth, promoting the health and structure of open . The species also serves as an indicator of pampa ecosystem integrity, with declining populations signaling habitat degradation from and . Interactions with humans often involve conflicts, particularly where populations overlap with developed areas. In , feral greater rheas have caused agricultural damage, including to crop fields, due to foraging by groups of up to 20 birds. In native , road vehicle collisions pose a significant threat, with frequent roadkills documented on routes traversing pampas habitats, such as Provincial Route 17 near the Ansenuza Reserve. The greater rhea enjoys popularity in captivity and media, appearing in zoos as an engaging exhibit of South American wildlife. In 2025, several facilities introduced young rheas, including the in , which welcomed three juveniles to educate visitors on species. Unlike some animals with deep religious connotations, the greater rhea holds no major symbolic role in global faiths. For conservation education, the bird features prominently in initiatives within Argentina's Iberá , where guided tours allow observation of wild rheas amid wetlands and grasslands, fostering public appreciation for and supporting local economies through sustainable viewing opportunities.

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