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Ruddy duck

The ruddy duck (Oxyura jamaicensis) is a small, compact stiff-tailed diving duck native to the Americas, characterized by its thick neck, buoyant body, and long stiff tail frequently held upright. Breeding males display vivid chestnut plumage, a black cap and nape, white cheeks, and a bright sky-blue bill, contrasting with the duller grayish-brown females and juveniles that feature a dark crown stripe. These ducks breed in freshwater marshes, ponds, and lakes across prairie regions of , preferring areas with dense emergent vegetation for nesting, and migrate southward to winter in shallow coastal bays and protected waters from to . Primarily diving foragers, they consume aquatic plants, seeds, and invertebrates such as insects and crustaceans, often feeding at night in some regions. Populations remain stable across their extensive range, earning a Least Concern status from the IUCN, with no major threats identified in native habitats. However, introduced populations in pose a significant conservation challenge through aggressive hybridization with the endangered (Oxyura leucocephala), prompting eradication efforts in the and elsewhere to prevent genetic swamping.

Taxonomy

Classification and Phylogeny

The ruddy duck (Oxyura jamaicensis) is classified within the order Anseriformes, family Anatidae (waterfowl), subfamily Oxyurinae (stiff-tailed ducks), genus Oxyura, and species jamaicensis. The subfamily Oxyurinae is characterized by morphological adaptations such as stiffened tail feathers for underwater swimming, and it is sometimes ranked as a tribe (Oxyurini) within the larger subfamily Anatinae, though molecular and morphological evidence supports its distinct subfamily status. Phylogenetic analyses of , incorporating mitochondrial genes (e.g., and ND2) and hybridization data, place Oxyurinae as a monophyletic group sister to other diving duck clades within , with divergence estimated around 10–15 million years ago based on calibrations. Within Oxyurinae, the Oxyura (encompassing eight ) forms a clade distinct from Nomonyx (), supported by synapomorphies including elongated central tail rectrices and specialized nasal structures; O. jamaicensis clusters with other taxa like O. vittata, forming a basal to Oxyura (O. australis, O. leucocephala, O. maccoa), reflecting vicariant divergence tied to continental isolation. Morphological phylogenies corroborate mtDNA results, with Oxyura monophyly upheld by three unambiguous synapomorphies (e.g., reduced hind toe and modified tarsal scutes), though incomplete lineage sorting in mtDNA control regions has complicated subspecies-level resolution for O. jamaicensis and allies. Hybridization potential across Oxyura , observed in and inferred from patterns, suggests reticulate but does not undermine the core structure.

Subspecies and Genetic Variation

The ruddy duck (Oxyura jamaicensis) is treated as monotypic by major taxonomic authorities, with no subspecies formally recognized. Previously proposed divisions, such as O. j. rubida (Wilson, 1814) for continental North American breeding populations and the nominate O. j. jamaicensis (Gmelin, 1789) for West Indian birds, were based on minor differences in male facial plumage intensity and body size, but these vary clinally and lack sufficient genetic or morphological discontinuity to justify subspecific status. South American populations formerly included under O. jamaicensis, such as O. j. ferruginea and O. j. andina, have been elevated to full species (Oxyura ferruginea and related taxa) due to consistent plumage, vocal, and genetic distinctions. Geographic variation within the native range (western from to , plus the ) is minimal, manifesting primarily as slight increases in body mass and bill length toward northern latitudes, consistent with rather than discrete boundaries. Genetic analyses of native n populations indicate moderate , including 23 mitochondrial DNA s (haplotype Hd = 0.824, π = 0.00345) and microsatellite expected heterozygosity (H_E) of 0.50 across 11 loci, with evidence of historical population expansion. This contrasts with introduced populations, such as the one founded by approximately seven captive individuals in the 1940s–1950s, which show drastically reduced variation (single mtDNA , H_E = 0.37, allelic richness ~3.3 per locus) due to bottlenecks and subsequent isolation from native (F_ST = 0.274). Such low in non-native ranges raises concerns for long-term adaptability but does not reflect native conditions.

Description

Physical Morphology

The ruddy duck (Oxyura jamaicensis) is a compact, stocky duck characterized by a thick neck, short wings, and a long, stiff tail frequently held cocked upward. Its body plan reflects adaptations for , with a relatively heavy build and low-slung posture on water. Adults measure 35–43 cm in total length, with males averaging slightly larger at 37–43 cm compared to females at 35–41 cm; wingspan ranges from 56–62 cm. Weight varies seasonally and by sex, typically 300–850 g, with females averaging around 550 g and males 600 g. Breeding males exhibit striking , featuring a bright body , black crown and , bright white cheeks, and a vivid sky-blue bill that intensifies during the breeding season. The tail consists of stiff, black feathers, and the upperwing shows black secondaries and coverts contrasting with paler tertials. In non-breeding , males molt to a duller gray-brown overall, retaining the white cheeks but with a less vibrant bill. Females are more cryptically colored year-round, with warm brown upperparts, paler underparts, a dark cap, and a distinctive dark stripe through the eye on buffy cheeks; their bill is dark or grayish. Juveniles resemble females but with finer streaking and softer feathering. The bill is stout and broad at the base, widening into a flattened, scoop-like tip suited for in sediments. Legs are short and set toward the rear, with lobed toes for , though the relies more on wing-assisted than foot . is dense and waterproof, with males showing seasonal dichromatism linked to testosterone-driven molts, while females exhibit minimal variation.

Vocalizations and Displays

Ruddy ducks (Oxyura jamaicensis) produce few vocalizations and are generally silent outside the breeding season. Males generate mechanical ticking, clapping, or popping during by rapidly pressing and beating their inflated blue against the distended neck feathers, which creates a vibrating resonance akin to bill-drumming. These displays often conclude with a belch-like or sputtering call, described as a rapid "chuck-chuck-chuck" or guttural hoot. Females occasionally emit low growls, hisses, or nasal calls near the nest to deter intruders or communicate with ducklings, while ducklings produce a soft, double-noted for contentment and harsher distress calls. Courtship displays occur primarily on grounds, where males perform elaborate, stiff-tailed routines to attract females and form temporary monogamous pairs. A core element involves the male raising its black vertically while pumping its head forward and backward in quick succession, often tilting the over the back or submerging the head to beat it against the neck, producing a trail of bubbles from the vigorous motion. These displays, which emphasize the male's bright blue and chestnut body during , can last several minutes and are punctuated by the aforementioned mechanical sounds. Females respond selectively, sometimes chasing or ignoring persistent males, with displays intensifying in shallow waters where visibility aids assessment of traits like stiffness and coloration. Outside , both sexes rarely , though males may exhibit mild aggression via head-forward rushes.

Distribution and Habitat

Native Range

The ruddy duck (Oxyura jamaicensis) is native to , where its breeding range spans from , including prairie provinces and , southward through the western and —particularly the prairie pothole region of the northern —and into northern and central . Within this area, breeding occurs primarily in shallow freshwater wetlands, marshes, and ponds with emergent vegetation, from elevations near up to montane basins. Populations in the southern portions of the native range, including southern , , , the islands (such as the Greater and ), and Andean regions of (e.g., , , and ), are largely resident year-round, occupying similar habitats without extensive migration. Northern breeding populations are partially migratory, with birds departing and interior wetlands by late summer or fall to winter in coastal bays, estuaries, and ice-free lakes across the (from to ), , and occasionally as far south as . Winter concentrations can number in the thousands at protected saline or brackish waters, such as those along the Gulf and Pacific coasts. The species is absent from arid desert interiors unsuitable for its wetland preferences, including southeastern and western Arizona.

Introduced Populations

The ruddy duck (Oxyura jamaicensis) established its primary introduced populations in Europe following escapes from captive wildfowl collections imported to the United Kingdom from North America in the 1950s. The first wild individuals were recorded in Great Britain in 1952, with confirmed breeding in Gloucestershire (then part of Avon county) beginning in 1960. The UK breeding population grew to encompass most suitable habitats by the late 20th century, peaking at approximately 6,000 individuals in 2001 before targeted culling reduced it to fewer than 100 birds continent-wide by the 2020s. From the , ruddy ducks naturally dispersed across the western Palaearctic, colonizing 21 countries by the early 2000s, including , , the (where numbers fell to about 70 by 2023), (reached in the late 1980s), , , , , , , , (with breeding populations), , and . Eradication programs coordinated under the Bern Convention have nearly extirpated breeding pairs in the (confined to scattered English sites), , , and , with remnant non-breeding flocks persisting in low single figures in and as of 2024. In these non-native ranges, ruddy ducks preferentially inhabit eutrophic freshwater bodies such as ponds, lakes, reservoirs, and slow-moving rivers with emergent and submerged aquatic vegetation, mirroring native habitat preferences but exploiting wetlands altered for agriculture and recreation. No other self-sustaining introduced populations are established outside , though vagrant individuals have appeared casually in locations including and .

Behavior

Breeding and Reproduction

The ruddy duck (Oxyura jamaicensis) breeds seasonally from May to August in , primarily in prairie pothole regions of and the , with males arriving first to establish territories before females join for pair formation. The mating system combines , , and , where most pairs are initially monogamous but some males form bonds with up to three females, often abandoning the first mate once begins to pursue additional pairings. Courtship displays involve males submerging their heads and rapidly beating their bills against inflated necks to produce bubble trails in the water, a that signals and attracts females. Nests are constructed by females in dense emergent vegetation over shallow water in marshes or wetlands, typically consisting of woven plant material lined with down; platform nests may also form from floating . Clutch sizes range from 3 to 13 eggs, with averages of 6–10, representing a substantial energetic investment as eggs are the largest relative to body size among ducks, comprising up to 96% of a female's late- mass for a full of seven. Eggs are white to buffy white, often staining to cream or tan during , which lasts 20–26 days and is performed solely by the female after the male departs. Females may relay up to four times per season if clutches are lost, though typically only 1–2 broods succeed annually. Hatchlings are precocial and nidifugous, emerging covered in down and capable of and shortly after under female care, which continues for feeding and protection. Fledging occurs after 52–66 days, during which young may disperse from the brood; females lead broods but provide limited post-hatching support beyond initial guidance. First typically happens at one year of age, with annual productivity varying by quality and predation pressure in native wetlands.

Foraging and Diet

Ruddy ducks (Oxyura jamaicensis) almost exclusively by in shallow freshwater habitats, propelling themselves underwater with powerful feet and using their broad, spatulate bills to sift and strain from muddy substrates. This technique allows them to access benthic prey in ponds and marshes, with dives typically lasting 10–30 seconds, though they rarely dabble at the surface or skim water for . Adults exhibit patch-depletion , systematically exploiting localized concentrations of prey before moving to new areas, as observed in controlled aquarium studies where they prioritized high-density patches. The diet is predominantly animal matter, comprising over 90% of intake in many populations, with aquatic invertebrates such as chironomid larvae, crustaceans (including fairy shrimp), mollusks, and zooplankton forming the bulk. Plant material, including seeds of pondweeds (Potamogeton spp.), tubers, and submerged vegetation, constitutes a minor component (typically 2–8%), serving supplementary nutrition rather than a primary energy source. In vernal pools, for instance, spike-rush seeds and fairy shrimp dominate, reflecting opportunistic selection based on local abundance. Dietary composition varies by season, age, and ; adults and females during emphasize protein-rich to support production and periods, while ducklings initially consume smaller before transitioning to benthic larvae. In prairie wetlands, exceed 94% of esophageal contents, underscoring the ' specialization as a reliant on shallow, eutrophic waters for sustained prey availability.

Social Structure and Migration

Ruddy ducks display seasonal shifts in . On grounds, males assemble in parties of 2–15 individuals on larger ponds to display and form pairs, after which pairs disperse to smaller, isolated wetlands and maintain solitary habits. males do not defend fixed territories but remain in close proximity to their mates, aggressively repelling rivals and even heterospecifics such as mammals from nearby areas. The exhibits high intraspecific aggression year-round, with young birds particularly noted for combative interactions. In non-breeding periods, ruddy ducks shift to more gregarious behavior, forming flocks ranging from small groups of 8–12 to large aggregations of hundreds or thousands on open waters. They rarely associate with other waterfowl , preferring to and in monospecific groups. Northern populations undertake medium- to long-distance migrations, with southward departure from breeding areas beginning in late and extending into at southern wintering sites such as and the . Northward return migration initiates in early from and southern U.S. wintering grounds, continuing through mid-May in northern latitudes. Flights occur mainly at night in small flocks, following primary corridors southwest, south, and southeast from breeding habitats in and the northern U.S. Southern and populations are largely non-migratory or perform only local movements, remaining year-round in suitable wetlands.

Ecology in Native Range

Interspecific Interactions

In their native North American range, ruddy ducks (Oxyura jamaicensis) primarily interact agonistically with American s (Fulica americana), especially during brood-rearing. In wetlands, brood-rearing ruddy ducks engaged in an average of 6.2 interspecific agonistic interactions per hour, with coots comprising 85% of these encounters; ruddy duck hens with broods frequently initiated attacks, though adult coots often dominated outcomes, while younger coots were typically repelled. for nesting sites intensifies when coot densities are high, potentially limiting ruddy duck in shared prairie pothole habitats. During winter, ruddy ducks may loosely associate with coots on open water but seldom integrate with other duck species. Breeding males display territorial aggression, chasing conspecifics and other waterfowl from display areas, though ruddy ducks do not maintain fixed all-purpose territories year-round. Ducklings exhibit precocial aggression toward heterospecifics as early as one day post-hatching, diving and confronting intruders at foraging sites. Foraging overlaps with diving ducks for aquatic invertebrates and plants, but direct competition remains undocumented as a primary limiter of ruddy duck populations. Hybridization occurs rarely in the native range, with no evidence of widespread genetic affecting North American congeners; limited reports suggest possible ancient admixture with Andean populations of Oxyura ferruginea in northwestern , but this does not extend to core northern breeding grounds.

Predators and Parasites

Ruddy ducks face predation primarily from mammalian and avian species targeting eggs, nestlings, and ducklings, with adults less vulnerable due to their diving behavior and aggression. Mammalian predators include raccoons (Procyon lotor), (Neovison vison), and red foxes (Vulpes vulpes), which raid nests and consume eggs or young. Avian predators such as crows (Corvus brachyrhynchos), red-tailed hawks (Buteo jamaicensis), great horned owls (Bubo virginianus), and great blue herons (Ardea herodias) prey on eggs, ducklings, and occasionally adults. Ducklings are additionally susceptible to large and snapping turtles ( serpentina). Nest predation contributes significantly to reproductive losses, though flooding and desertion often exceed predation as causes of egg failure. Ruddy ducks serve as intermediate or definitive hosts for various helminth parasites, particularly acanthocephalans residing in the intestinal tract, including Polymorphus obtusus and Corynosoma constrictum. Documented helminth communities in populations include trematodes, cestodes, and nematodes, with one trematode and four cestode reported overall. These parasites are acquired through of infected intermediate hosts like amphipods or crustaceans during in wetlands. Ectoparasites such as lice and mites occur but are less studied; varies by and , with higher intensities in breeding grounds. No major viral or bacterial pathogens unique to ruddy ducks have been identified as significant population regulators in native ranges.

Invasive Status

History of Introduction

The ruddy duck (Oxyura jamaicensis), native to North and , was first imported to the in the late 1940s for inclusion in wildfowl collections and . By the mid-1950s, escapes from captivity had occurred, leading to of a breeding population; the first confirmed wild sighting in was in 1952, followed by nesting in the former county of in 1960. This introduced population grew rapidly due to the species' adaptability to habitats, expanding from a few individuals to an estimated 6,000 birds in the UK by 2000, with breeding pairs numbering around 1,000. From the , ruddy ducks dispersed naturally across via vagrant individuals and short-distance flights, colonizing sites in , the , , and by the 1970s and 1980s. The first records in occurred in 1983, with breeding attempts following in the early 1990s, marking the onset of significant invasive establishment on the continent. These introductions were unintentional, stemming primarily from the expanding UK feral flock rather than deliberate releases elsewhere in , though earlier ornamental imports to western in the 1930s have been noted but did not lead to self-sustaining populations until the UK-derived spread. Outside , no major feral populations have established from direct introductions, with the species remaining largely confined to its native range in the . The rapid proliferation in non-native regions was facilitated by the ruddy duck's tolerance for varied freshwater and brackish wetlands, high reproductive rates (clutch sizes of 6–10 eggs), and aggressive mating behavior, which allowed it to outcompete or hybridize with local congeners. By the late , the population exceeded 10,000 individuals, prompting international concern over its invasive potential, particularly in Iberia where it threatened the endangered (Oxyura leucocephala) through hybridization.

Hybridization Threats

The ruddy duck (Oxyura jamaicensis), introduced to from , poses a primary hybridization threat to the endangered (Oxyura leucocephala) through interbreeding that produces fertile offspring, risking genetic and potential swamping of the native species' gene pool. The European ruddy duck population traces to a small founder group of seven captive birds imported to the in 1948, with escapes occurring between 1953 and 1973, leading to breeding by 1960 and expansion to approximately 5,000 individuals in the UK by 2000; this limited genetic diversity has not hindered hybridization success with the white-headed duck. In , where the white-headed duck population numbered about 2,500 individuals in 2004—representing roughly 25% of the global total—ruddy ducks were first detected in 1984, with initial hybrids appearing in 1991. Between 1993 and 2003, 29 presumed hybrids were collected, including 18 first-generation (F1) hybrids (89% carrying ruddy duck ) and 10 backcrosses (all with white-headed duck ), confirming ongoing . Genetic analysis of 63 morphologically identified white-headed ducks revealed no ruddy duck alleles, with estimated at 0–0.7% of alleles (95% ) and affecting 0–6% of individuals, indicating that control measures have so far constrained widespread but underscore the latent risk without sustained intervention. F1 hybrids demonstrate fertility, yielding viable backcrosses with both parental species, though female hybrids inheriting ruddy duck exhibit potentially reduced fertility. This reproductive compatibility enables multi-generational , eroding species-specific genetic adaptations in the and elevating risk via demographic and genetic swamping, particularly in overlapping habitats across and . Aggressive mating behavior by male ruddy ducks further exacerbates the threat, as they preferentially pair with female white-headed ducks during seasons, amplifying hybrid production in the absence of barriers to . Continued eradication efforts are essential to avert irreversible genetic dilution, as evidenced by the low but detectable hybridization rates under partial control.

Broader Ecological and Economic Impacts

The invasive ruddy duck (Oxyura jamaicensis) poses its most severe ecological threat in through interspecific hybridization with the endangered (Oxyura leucocephala), whose Spanish population represents approximately 25% of the global total. Aggressive mating by male ruddy ducks with female white-headed ducks produces fertile hybrids, including backcrosses that facilitate genetic of ruddy duck alleles into the native . This process risks swamping the white-headed duck's genetic identity, eroding its distinctive behavioral and ecological traits—such as diving adaptations and habitat preferences—and potentially driving the species toward effective as a distinct entity if unchecked. Sustained control efforts have curtailed these genetic impacts; in , where hybrids first appeared in 1991, culling of ruddy ducks since 1984 and removal of 68 hybrids by shooting (plus two in ) has averted widespread , with few hybrids observed after 2004. Continent-wide population reductions—UK numbers dropping 98% from a 2000 peak of ~6,000 to near-eradication levels by 2013, and overall to <7% of 2000 estimates—have correspondingly limited hybrid detections and preserved genetic purity. Secondary effects include resource with s, though hybridization dominates as the risk. Economic consequences center on the high costs of , with Western control programs exceeding US$28 million (in 2017-adjusted terms) for ongoing , , and eradication to avert hybridization-driven losses. These expenditures fund multi-decade, multinational operations, including the UK's intensified efforts from 1993 (scaling post-2005) and Spain's since 1984, underscoring the invasive's role in driving budgets without direct agricultural or infrastructural damages.

Management and Conservation

Native Population Status

The ruddy duck (Oxyura jamaicensis) is native to , where it breeds across wetlands from and southward to , with the core breeding range concentrated in the Prairie Pothole Region spanning the northern of the and . Approximately 86% of the continental breeding population occurs in this region, which provides essential pothole wetlands for nesting and brood-rearing. The species is classified as Least Concern on the , reflecting its large overall population size and lack of major threats leading to rapid decline in the native range. Global breeding population estimates stand at approximately 1.3 million individuals, with the vast majority in ; Canadian estimates alone range from 430,000 to 500,000–1,000,000 birds. North American populations have shown stability or slight increases over the past 40 years, based on data from the North American Breeding Bird Survey and continental waterfowl surveys, with no statistically significant long-term decline observed. Historical reductions in the early , attributed to unrestricted and drainage for , have been offset by habitat protection under programs like the North American Waterfowl Management Plan and regulated sport , which maintains populations below without causing overharvest. Wintering occurs primarily in the , , and the , with annual harvest estimates in the U.S. averaging around 50,000 birds (ranging from 7,544 to 118,637 between 1961 and recent years), primarily in the Mississippi Flyway, indicating sustainable levels under current management. In , the species holds Secure status under national assessments, with stable or increasing trends monitored through surveys like the Canadian Wildlife Service's waterfowl indices. No face elevated risks, and the population's resilience is supported by high reproductive potential in favorable conditions, though localized fluctuations can occur due to or loss in the prairies.

Eradication and Control Efforts

Control efforts against the invasive ruddy duck (Oxyura jamaicensis) in began in the in the early , prompted by the species' hybridization with the endangered (Oxyura leucocephala), which threatened the latter's genetic integrity. Initial targeted pairs and wintering flocks, with systematic surveys and shooting operations reducing the population from an estimated peak of around 6,000 birds in the late to fewer than 100 by March 2011. Over 6,800 ruddy ducks were culled in alone by 2010, achieving a 95% population decline through coordinated efforts involving licensed marksmen, nest destruction, and public reporting of sightings. A projected that deploying 14-15 control officers could reduce the ruddy duck population by 97% within 3-5 years, emphasizing the need for intensive, sustained shooting during key seasons to account for the birds' mobility and low detectability. The LIFE-Nature project (LIFE05 NAT//000142), funded by the from 2005 to 2011, supported these activities and extended surveillance to prevent re-establishment, though full eradication was not achieved by the project's end due to persistent low-level detections. Post-2011, ongoing monitoring and targeted removals continued under national and international frameworks, with one adult female shot in January 2022 and one adult male located and scheduled for removal in June 2023. Broader European coordination, guided by the Bern Convention and a 2014 action plan, aimed for of ruddy ducks across the continent by 2025 to eliminate hybridization risks. In , a LIFE-Nature program initiated in 2018 reduced estimated numbers from 160 to approximately 20 birds by 2024 through similar and genetic monitoring to detect hybrids. and other countries implemented parallel controls, with overall ruddy duck counts declining significantly between 2000 and 2013 due to intensified efforts in source populations like the . By 2024, the was nearing eradication, with coordinated actions preventing recolonization and minimizing gene flow to habitats.

Controversies and Effectiveness

The eradication efforts targeting invasive ruddy ducks (Oxyura jamaicensis) in , particularly in the UK and , have sparked significant controversy over ethical, financial, and practical grounds. organizations, including groups in the UK, have criticized the primary control method of as inhumane, arguing it causes unnecessary suffering to non-native but established birds, and have protested planned culls at sites like Scottish lochs. Conservation bodies such as the Royal Society for the Protection of Birds faced internal and public backlash for supporting the program, with detractors questioning the prioritization of one (the , Oxyura leucocephala) over the ruddy duck's right to existence in its introduced range. Critics also highlighted potential opposition to coordinated on lands and the risk of incomplete eradication leading to prolonged efforts. Financial scrutiny has intensified debates, with the UK program costing approximately £3.3 million by , equating to over £700 per bird culled at that stage, prompting claims of inefficiency and waste given the species' persistence. Proponents counter that these expenses pale against the ecological value of safeguarding the , whose genetic integrity was threatened by hybridization rates exceeding 10% in some populations prior to interventions. Despite controversies, control measures have demonstrated high effectiveness in population reduction. In the UK, coordinated under the LIFE-Nature (2005–2011) reduced ruddy duck numbers from around 6,000 in 2000 to 120 by 2011, with over 4,400 birds removed in the final years alone; by 2021, estimates indicated only 10–15 individuals remained, primarily males incapable of breeding without females. achieved local eradication by 2015, with no breeding females detected. Modeling studies predicted that sustained efforts by 14–15 trained operatives could achieve 97% reduction in 3–5 years, a largely met through targeted winter flock shooting, which culled 20–60% of birds per site visit. In , proactive prevented significant genetic into white-headed ducks, stabilizing their populations. Europe-wide coordination under the Bern Convention has advanced toward continental eradication, though isolated detections necessitate ongoing vigilance. Overall, these programs underscore that intensive, evidence-based can effectively mitigate invasive hybridization threats, albeit at substantial short-term cost and ethical contention.

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