Global Range: (>2,500,000 square km (greater than 1,000,000 square miles)) BREEDING: Formerly throughout North America from central Alaska to western Hudson Bay (James Bay), southeast to Nova Scotia, with the southern limit extending to northwest Mississippi and eastern Arkansas in the east and possibly California in the west. Present breeding range includes Alaska (Interior, Southcentral, Gulf of Alaska, and Chilkat basin), Yukon, British Columbia, Alberta, Washington, Oregon, Nevada, Montana, Idaho, Wyoming, South Dakota, Minnesota, Wisconsin, Michigan, Saskatchewan, and Ontario (Mitchell 1994). Alaska contains over 85% of the world's breeding population, and breeding areas outside of Alaska are very localized (Mitchell 1994).
NONBREEDING: Formerly from the present range in southeast Alaska (a few small flocks along the Gulf of Alaska), along the British Columbia coast, Washington, Oregon, and occasionally California but historically extending to southern California, possibly Arizona and New Mexico, along Gulf Coast to central Florida, and along Alantic coast as far as ice free waters existed (Mitchell 1994). Present range includes the Gulf of Alaska coast, southeast Alaska, British Columbia, western Washington, western Oregon, occasionally California, eeastern Nevada, western Utah, southern Montana, eastern Idaho, northwestern Wyoming, southwestern South Dakota, and small resident populations in the midwestern states, Saskatchewan, and Ontario (Mitchell 1994). In the contiguous United States and adjacent Canada, the highest winter densities occur in western Wyoming, western British Columbia (coast and interior lakes), southeastern Oregon, and southwestern Montana, mainly on wildlife refuges (Root 1988).
Interior population (resulting from transplants and captive propagation) consists of flocks in Lacreek National Wildlife Refuge, South Dakota, and Hennepin County Park Reserve District, Minnesota; these gradually are exhibiting southward movement in fall but still are dependent on supplemental feeding.
Rocky Mountain population nests in the Rocky Mountains of Canada and the United States (Idaho, Montana, Wyoming) and winters primarily in the Greater Yellowstone Ecosystem (Spahr et al. 1991). Breeding areas in Canada include Peace River area of Alberta and British Columbia and Toobally Lakes area of Yukon, plus some areas farther north in Northwest Territories (Johnson and Herter 1989). U.S. flocks of the Rocky Mountain population currently summer in three locations (1) the Tri-state Area of eastern Idaho, southwestern Montana, and western Wyoming, (2) the Ruby Lake National Wildlife Refuge, and (3) Malheur NWR and Summer Lake area of Oregon. Trumpeter swans at Ruby Lake and Malheur NWRs were derived primarily from swans that were transplanted from Red Rock Lakes NWR, beginning in 1941 (Pacific Flyway Study Committee 2002).
Trumpeter swans are found throughout the Nearctic Region, mainly in Alaska, Canada, and the northern United States. A large percentage is found in Alaska, specifically in Prince William Sound and the Copper River Delta. Some trumpeter swans have even taken up residence in Yellowstone Park, Wyoming.
Biogeographic Regions: nearctic (Native )
- Grant, T., P. Henson. 1994. Feeding ecology of trumpeter swans breeding in south central Alaska. Journal of Wildlife Management, 58/4: 774.
- Henson, P., J. Cooper. 1993. Trumpeter Swan incubation in areas of differing food quality. Journal of Wildlife Management, 57/4: 709-716.
- Mills, J. 1991. The Swan That Would Not Fly. National Wildlife, 29/6: 4.
- Schmidt, J., M. Lindberg, D. Johnson, J. Schmutz. 2009. Environmental and human influences of trumpeter swan habitat occupancy in Alaska. Condor, 111/2: 266/275.
- Squires, J. 1995. Trumpeter swan (Cygnus buccinator) food habits in the greater Yellowstone ecosystem. American Midland Naturalist, 133/2: 274.
- Squires, J., S. Anderson. 1997. Changes in trumpeter swan (Cygnus buccinator) activities. American Midland Naturalist, 138/1: 208.
occurs (regularly, as a native taxon) in multiple nations
Regularity: Regularly occurring
Type of Residency: Year-round
Regularity: Regularly occurring
Type of Residency: Year-round
- Clements, J. F., T. S. Schulenberg, M. J. Iliff, D. Roberson, T. A. Fredericks, B. L. Sullivan, and C. L. Wood. 2014. The eBird/Clements checklist of birds of the world: Version 6.9. Downloaded from http://www.birds.cornell.edu/clementschecklist/download/
Their breeding range extended from Alaska east to Ontario and south to
Oregon, the Rocky Mountains, Nebraska, and northern Missouri . Now
only two major populations remain [4,17,20]. The Pacific population
breeds in Alaska and British Columbia, and winters along the Pacific
Coast from Alaska to northern Oregon [20,23]. The mid-continental
population nests in Alberta, British Columbia, Yukon, Northwest
Territories, Saskatchewan, and the Greater Yellowstone region [20,23].
Overhunting of trumpeter swans destroyed most of their traditional
migration patterns to southerly winter habitats. As a result, virtually
all mid-continental trumpeter swans, regardless of their summer range,
now winter in the Greater Yellowstone Ecosystem .
Trumpeter swans have been transplanted from Red Rock Lakes National
Wildlife Refuge, Montana, to several other National Wildlife Refuges
(NWR): Malheur NWR in Oregon, Ruby Lake NWR in Nevada, Lacreek NWR in
South Dakota, and Turnbull NWR in Washington. A small number of
breeding swans occur on all four refuges . In Canada, attempts are
underway to reintroduce trumpeter swans in southern Ontario and in Elk
Island National Park .
Regional Distribution in the Western United States
This species can be found in the following regions of the western United States (according to the Bureau of Land Management classification of Physiographic Regions of the western United States):
1 Northern Pacific Border
2 Cascade Mountains
5 Columbia Plateau
8 Northern Rocky Mountains
9 Middle Rocky Mountains
Occurrence in North America
As the largest North American swans, these birds can weigh up to 13.5 kg and measure approximately 1.6 m in length. Wingspan can often exceed 2 m. When they are young "cygnets", the bill features some degree of pink but is always black at the base. The feet and tarsi (portion of the foot that makes up the ankle region) may be a grey-yellow. The body is light to dark grey, and will gradually whiten with age. At age two, most but not all of their feathers have turned white, except for a few on the upper portion of the body.
At adulthood their feet, bill, and tarsals are black. They have pink to red mouths which can be seen as a small pink or red line (a 'grin') on the bill. Their feathers are completely white. There is also a small percentage of trumpeter swans that have a grey-white tint for feather color instead of pure white.
They appear very similar to tundra swans (Cygnus columbianus), with the most reliable differences found near the beak. Viewed face-forward or top-down, trumpeter swans have an angular, v-shaped forehead at the base of the beak. Tundra swans have a curved or straight forehead. Most tundra swans have a yellow-white 'teardrop' on their black beak, however this is not always a reliable field mark.
Range mass: 9.5 to 13.5 kg.
Range length: 1.4 to 1.6 m.
Range wingspan: 2.0 to 2.4 m.
Other Physical Features: endothermic ; homoiothermic; bilateral symmetry
Sexual Dimorphism: sexes alike
- Slater, G. 2006. "Trumpeter Swan (Cygnus buccinator): a technical conservation assessment" (On-line pdf). US Forest Service. Accessed February 16, 2010 at http://www.fs.fed.us/r2/projects/scp/assessments/trumpeterswan.pdf.
Length: 152 cm
Weight: 11900 grams
Trumpeter swans live on land but always in close proximity to water. They are found in wetlands with open water and areas with many rivers or streams. Waters can be salt water, fresh water, or brackish water. Their climate ranges from temperate to polar. Reasons for their choice of environment have to do with their diet and nesting habits. Cygnus buccinator feeds off many plants native to those areas. They are also known for laying their eggs near or on the water. They seek out the same habitat type for wintering grounds.
Habitat Regions: temperate ; polar ; terrestrial
Terrestrial Biomes: tundra
Aquatic Biomes: lakes and ponds; rivers and streams; coastal ; brackish water
Other Habitat Features: riparian ; estuarine
- Proffitt, K. 2009. Trumpeter Swan Abundance and Growth Rates in Yellowstone National Park. Journal of Wildlife Management, 73/5: 728-736.
Habitat and Ecology
Central Pacific Coastal Forests Habitat
This taxon is found in the Central Pacific Coastal Forests ecoregion, as one of its North American ecoregions of occurrence. These mixed conifer rainforests stretch from stretch from southern Oregon in the USA to the northern tip of Vancouver Island, Canada. These forests are among the most productive in the world, characterized by large trees, substantial woody debris, luxuriant growths of mosses and lichens, and abundant ferns and herbs on the forest floor. The major forest complex consists of Douglas-fir (Pseudotsuga menziesii) and Western hemlock (Tsuga heterophylla), encompassing seral forests dominated by Douglas-fir and massive old-growth forests of Douglas-fir, Western hemlock, Western red cedar (Thuja plicata), and other species. These forests occur from sea level up to elevations of 700-1000 meters in the Coast Range and Olympic Mountains. Such forests occupy a gamut of environments with variable composition and structure and includes such other species as Grand fir (Abies grandis), Sitka spruce (Picea sitchensis), and Western white pine (Pinus monticola).
Characteristic mammalian fauna include Elk (Cervus elaphus), Black-tailed Deer (Odocoileus hemionus), Coyote (Canis latrans), Black Bear (Ursus americanus), Mink (Mustela vison), and Raccoon (Procyon lotor).
The following anuran species occur in the Central Pacific coastal forests: Coastal tailed frog (Ascaphus truei); Oregon spotted frog (Rana pretiosa VU); Northern red-legged frog (Rana pretiosa); Pacific chorus frog (Pseudacris regilla); Cascade frog (Rana cascadae NT), generally restricted to the Cascade Range from northern Washington to the California border; Foothill yellow-legged frog (Rana boylii) and the Western toad (Anaxyrus boreas NT). A newt found in the ecoregion is the Rough skinned newt (Taricha granulosa).
Salamanders within the ecoregion are: Del Norte salamander (Plethodon elongatus NT); Van Dyke's salamander (Plethodon vandykei); Western redback salamander (Plethodon vehiculum); Northwestern salamander (Ambystoma gracile); Olympic torrent salamander (Rhyacotriton olympicus VU), whose preferred habitat is along richly leafed stream edges; Long-toed salamander (Ambystoma macrodactylum), whose adults are always subterranean except during the breeding season; Dunn's salamander (Plethodon dunni), usually found in seeps and stream splash zones; Clouded salamander (Aneides ferreus NT), an aggressive insectivore; Monterey ensatina (Ensatina eschscholtzii), usually found in thermally insulated micro-habitats such as under logs and rocks; Pacific giant salamander (Dicamptodon tenebrosus), found in damp, dense forests near streams; and Cope's giant salamander (Dicamptodon copei), usually found in rapidly flowing waters on the Olympic Peninsula and Cascade Range.
There are a small number of reptilian taxa that are observed within this forested ecoregion, including: Pacific pond turtle (Emys marmorata); Common garter snake (Thamnophis sirtalis), an adaptable snake most often found near water; Northern alligator lizard (Elgaria coerulea); and the Western fence lizard.
Numerous avian species are found in the ecoregion, both resident and migratory. Example taxa occurring here are the Belted kingfisher (Megaceryle alcyon); Wild turkey (Meleagris gallopavo); and the White-headed woodpecker (Picoides albolarvatus) and the Trumpeter swan (Cygnus buccinator), the largest of the North American waterfowl.
Comments: Ponds, lakes, and marshes, breeding in areas of reeds, sedges or similar emergent vegetation, primarily on freshwater, occasionally in brackish situations, wintering on open ponds, lakes and sheltered bays and estuaries (AOU 1983). In the intermountain western U.S., winters in areas of geothermal activity, springs, and dam outflows (Spahr et al. 1991). Primarily breeds in freshwater, on edges of large inland waters; typically in emergent marsh vegetation, or on a muskrat house, beaver lodge, or island. The nest is a large mass of plant material. Uses same nesting sites in successive years.
See Pacific Flyway Study Committe (2004) for a summary of nesting, migration, and winter habitat requirements for the Rocky Mountain population.
Tall emergent vegetation provides shelter and cover for trumpeter swans
. Adults may remove vegetation around the nest until the nest is
surrounded by open water. This provides good visibility and protection
from land predators . During winter, trumpeter swans prefer open
sites with few trees or shrubs to obscure their vision while feeding
Breeding habitat - Trumpeter swans nest on the margins of interconnected
shallow marshes and lakes, lakes within forest or sagebrush habitat,
and oxbows of rivers . They prefer stable, quiet, shallow waters
where small islands, muskrat houses, or dense emergent vegetation
provide nesting and loafing sites. Nutrient-rich waters, with dense
aquatic plant and invertebrate growth, provide the best habitat [3,23].
Nests are built in water 1 to 3 feet deep . Trumpeter swans build a
platform nest made of emergent vegetation. The nest is often located on
a muskrat house, beaver lodge, or small island . In Alaska,
trumpeter swan nests are built 10 to 600 feet (3-183 m) from shore,
depending upon cover and water depth. Occasionally, a nest is located
on or near the shoreline of a small inlet in a large lake .
Winter habitat - Winter habitat must provide extensive beds of aquatic
plants and water that remains ice-free. In the Greater Yellowstone
region, cold temperatures and ice restrict trumpeter swans to sites
where geothermal waters, springs, or outflow from dams maintain ice-free
areas. In winter, trumpeter swans use shallow lakes, streams, and ponds
that do not entirely freeze over during the winter months [18,23].
Pacific Coast trumpeter swans use both esuaries and freshwater habitats,
and feed in pastures and croplands . Good winter habitat also
contains a certain amount of level and open terrain, allowing these large
birds to loaf or fly without restriction of movement or visibility .
This species is known to occur in the following ecosystem types (as named by the U.S. Forest Service in their Forest and Range Ecosystem [FRES] Type classification):
FRES24 Hemlock-Sitka spruce
FRES26 Lodgepole pine
FRES28 Western hardwoods
FRES36 Mountain grasslands
FRES37 Mountain meadows
FRES38 Plains grasslands
Associated Plant Communities
emergent vegetation. In Montana, they commonly build their nests in
extensive beds of sedges (Carex spp.), bulrushes (Scirpus spp.),
cattails (Typha spp.), and reeds (Juncus spp.). In Alaska, they use
horsetails (Equisetum spp.) and sedges for nesting [4,10]. Plants found
in most trumpeter swan habitats include willow (Salix spp.), alder
(Alnus spp.), cottonwood (Populus spp.), water milfoil (Myriophyllum
exalbescens), arrowhead (Sagittaria latifolia), and pondweed
(Potamogeton spp.) [3,10].
Habitat: Cover Types
This species is known to occur in association with the following cover types (as classified by the Society of American Foresters):
204 Black spruce
205 Mountain hemlock
218 Lodgepole pine
222 Black cottonwood - willow
223 Sitka spruce
224 Western hemlock
225 Western hemlock - Sitka spruce
226 Coastal true fir - hemlock
227 Western redcedar - western hemlock
228 Western redcedar
235 Cottonwood - willow
253 Black spruce - white spruce
254 Black spruce - paper birch
Habitat: Plant Associations
This species is known to occur in association with the following plant community types (as classified by Küchler 1964):
K001 Spruce - cedar - hemlock forest
K004 Fir - hemlock forest
K008 Lodgepole pine - subalpine forest
K015 Western spruce - fir forest
K020 Spruce - fir - Douglas-fir forest
K021 Southwestern spruce - fir forest
K025 Alder - ash forest
K063 Foothills prairie
K064 Grama - needlegrass - wheatgrass
Depth range (m): 0 - 0
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.
Locally Migrant: Yes. At least some populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).
Locally Migrant: Yes. At least some populations of this species make annual migrations of over 200 km.
Wyoming-Montana-Idaho breeders nonmigratory; interior breeders in British Columbia, Yukon, Alberta, and Northwest Territories migrate. Arrives in northern nesting areas in early May, departs northern latitudes by late September or early October. Uses traditional migration routes.
Yellowstone population consists of a resident year-round population and a migratory winter population. Migrants that visit Yellowstone in the winter are a combination of swans from the Yellowstone/Greater Yellowstone area and swans from Canada (primarily Grande Prairie, Alberta).
As cygnets, trumpeter swans' diets are mostly comprised of aquatic invertebrates. At five weeks of age, most cygnets have converted to a nearly herbivorous diet. This diet consists mostly of tubers, roots, stems, leaves and occasionally insects. In Alaska during mating season, the wetland plants commonly known as horsetail (genus Equisetum) and Lyngbye's sedge (Carex lyngbyei) are consumed in great quantities. However, because of the wide distribution of the species there are some variations of their diet such as duck potato (Sagittaria latifolia), water weeds (genus Elodea), pondweeds (genus Potamogeton) and sago pondweed (Potamogeton pectinatus) tubers.
Trumpeter swans attain their food by foraging underwater with tails bobbing in the air. They also yank plants out of the damp ground, with most of the plant intact.
Animal Foods: aquatic or marine worms
Plant Foods: leaves; roots and tubers
Primary Diet: herbivore (Folivore )
Comments: Adults feed mostly on aquatic vegetation; young first eat aquatic insects and crustaceans but in 5 weeks begin feeding on aquatic plants. Also may graze in fields (McKelvey and Verbeek 1988). Prefers shallow, slow-moving water for feeding.
of aquatic vegetation, and they occasionally eat insects .
Initially, young cygnets eat large aquatic insects and snails. Cygnets
feed on the water's surface and often depend on the adults to stir up
the water around them. Within 2 to 3 weeks the cygnets start to eat
aquatic plants .
Trumpeter swans feed on the following: the tubers of duck potato and
sago pondweed (Potamogeton pectinatus); the stems and leaves of sago and
other pondweeds (Potamogeton spp.), water milfoil (Myriophyllum
verticullatum), muskgrass (Chara spp.), waterweed (Elodea canadensis),
and duckweed (Lemna triscula); the seeds of yellow pond lily (Nuphar
polysepala), water shield (Bransenia schreber), smartweed (Polygonum
spp.), sedges (Carex spp.), and spikerush (Eleocharis spp.); and the
stems and roots of grasses and sedges [2,3,4,17].
Trumpeter swans' main role in the ecosystem is linked to their diet. Trumpeter swans eat many insects when they are young. As they grow they switch to roots and aquatic plants, digging around to get them which in many cases allows water to fill the remaining holes supplying a very valuable nutrient to the plants. Cygnus buccinator can also be a host to a small number of parasites including tapeworms (Anoplocephala perfoliata), caecal paramphistomids (Zygocotyle lunata), trematode flukes (Echinostoma revolutum), another type of trematode (Orchipedum tracheicola), filarial worms (a nematode found in the heart) of the species Sarconema eurycerca, and other forms of tapeworms (Hymenolepis).
Ecosystem Impact: soil aeration
- Tapeworms (Anoplocephala perfoliata)
- Caecal paramphistomids (Zygocotyle lunata)
- Trematode flukes (Echinostoma revolutum)
- Trematodes (Orchipedum tracheicola)
- Filarial worms (Sarconema eurycerca)
- Tapeworms (Hymenolepis)
- Cowan, I. 1946. Death of a Trumpeter Swan from Multiple Parasitism. The Auk, 63/2: 248-249.
Although adults aggressively defend their nests, ground nests are easy targets for land predators. Many predators, such as bears, wolves and coyotes, wolverines, raccoons, and common ravens are known to snatch eggs. Post-hatchlings and adults are prey to fast predators such as coyotes, bobcats, red foxes, and golden eagles. The main predator of adult trumpeter swans is mankind. Humans have hunted more of these swans than anything else.
Trumpeter swans are aggressive towards predators, and at 12 kg with a 2 m wingspan, they can potentially inflict serious damage. Trumpeter swans do exhibit warning behaviors before they attack, including head bobbing and hissing.
- Man (Homo sapien sapiens)
- Bears (Ursus)
- Wolves (Canis)
- Coyotes (Canis latrans)
- Wolverines (Gulo luscus)
- Red Fox (Vulpes vulpes)
- Raccoons (Procyon lotor)
- Bobcat (Lynx rufus)
- Ravens (Corvus corax)
- Golden Eagle (Aquila chrysaetos)
- Kraft, F. 1946. The Flying Behemoth is Coming Back. Saturday Evening Post, 219/6: 6.
Predation is of little consequence in determining overall trumpeter swan
population levels, but may be an important cause of death to preflight
cygnets . Except for man, trumpeter swans have few natural enemies
after flying age is reached. Coyotes (Canis lutrans), river otters
(Lutra canadensis), minks (Mustela vison), and golden eagles (Aquila
chrysaetos) have been blamed for cygnet deaths in Yellowstone National
Park and Red Rock Lakes National Wildlife Refuge . The following
species also occur in trumpeter swan habitat and could potentially prey
on trumpeter swans: black bears (Ursus americanus), grizzly bears (U.
arctos), lynx (Lynx canadensis), bald eagles (Haliaetus leucocephalus),
greathorned owls (Bubo virgianus), mountain lions (Felis concolor),
bobcats (Lynx rufus), striped skunk (Mephitis mephitis), red fox (Vulpes
vulpes), raccoons (Procyon lotor), and gulls (Larus spp.) .
Number of Occurrences
Note: For many non-migratory species, occurrences are roughly equivalent to populations.
Estimated Number of Occurrences: 21 - 80
Comments: There are three regional populations (Pacific Coast, Rocky Mountain, and Interior) recognized by the USFWS (Mitchell 1994). An unknown number of breeding areas exist within the range of these populations (estimated at between 20 and 50 in all regions). Occurences have been searched for extensively, continent-wide survey was conducted in 1990 (Mitchell 1994).
10,000 - 100,000 individuals
Comments: In 2000, the total North American population was about 24,000 birds (USFWS 2003).
The 1995 Canadian subpopulation of the Rocky Mountain population recorded 2,076 swans, while the Tri-state subpopulation (Wyoming, Idaho, Montana) of the Rocky Mountain population counted 441 swans. In September 2001, the U.S. segment of the Rocky Mountain population collectively contained 416 adults, including 362 in the Tri-state Area, 23 in Oregon, and 31 in Nevada. Observers counted 417 swans (white birds and cygnets) in the U.S. Breeding Segment of the Rocky Mountain population of trumpeter swans during fall of 2004, a count identical to that from comparable areas in 2003 (USFWS 2004). Observers counted 4,584 swans (white birds and cygnets) in the Rocky Mountain population of trumpeter swans during February 2004, an increase of 15% from the 3,974 counted in February 2003 and a record-high count for the mid-winter survey (Pacific Flyway Study Committee 2004, USFWS 2004).
In the Yellowstone region, there are basically two trumpeter swan flocks: a resident year-round population and a migratory winter population. The winter population varies from 75-119 swans. In 2000, the resident population included 20 adults and 7 cygnets (National Park Service).
The 1995 Interior Population census counted 927 swans (Subcommittee on the Interior Population of Trumpeter Swans 1997).
In summer, nonbreeding flocks of 20-100 individuals may occur on large lakes and reservoirs. Defends breeding territory of about 5-10 acres.
Habitat-related Fire Effects
No specific information was found in the literature regarding
fire-related effects on trumpeter swan habitat. Fire occuring in wetland
habitats, however, often removes excessive accumulations of fast-growing
hydrophytes, permitting better waterfowl access and growth of more
desirable trumpeter swan foods such as pondweed and duckweed [19,21].
There may be some negetive effects of burning waterfowl habitat.
Large-scale autumn burning may have a detrimental effect upon marshes by
reducing the retention of drifting snow. The ability of marsh vegetion
to catch and hold snow is vital to marsh survival .
Timing of Major Life History Events
Pair formation - Trumpeter swans most often form pair bonds when they
are 2 or 3 years old, and first nest when they are 4 or 5 years old.
Most pairs remain together year-round and bond for life [2,18,23].
Nesting - In the Copper River area of Alaska, the Greater Yellowstone
area, and Red Rock Lakes National Wildlife Refuge, egg laying normally
begins in late April or early May and is completed about mid-May [4,17].
In interior Alaska, egg laying begins later than in the above areas
. In Alberta, the eggs are layed in mid-May .
Clutch size and incubation - Each breeding pair uses only one nest and
the female lays five to six eggs [2,14,17]. If the eggs are destroyed
the pair will probably not renest . The incubation period is 33 to
37 days [3,4,18].
Cygnet development and fledging - Trumpeter swan cygnets grow rapidly
. They are fully feathered in 9 to 10 weeks, but are unable to fly
until 13 to 15 weeks in Alaska and 14 to 17 weeks in Montana [4,17].
Cygnets remain with their parents throughout their first winter. They
separate from their parents the following spring, but siblings may
remain together into their third year. Family bonds are strong;
subadult siblings may rejoin with parents after nesting ends or in
subsequent winters .
Molt - Nonbreeding subadults molt first. Most nonbreeders in Alaska
begin their molt in late June or early July. At Red Rock Lakes, the
molt may be completed as early as June . It is rare for both members
of a breeding pair to be flightless at the same time. The male of the
pair usually molts first. Some paired birds may begin to molt as early
as nonbreeders. Many, however, delay a month or longer. Some trumpeter
swans are flightless until early September in Alaska and until October
in Montana. Trumpeter swans are normally flightless for about 30 days
Migration - The seasonal movements of trumpeter swans in the Greater
Yellowstone region are limited to local flights between breeding habitat
and contiguous wintering areas. No molt migration is known. Breeders
molt in the general vicinity of nesting territories .
In Alaska, trumpeter swan populations migrate south in shifts. This
occurs from September until very late in the year, with times and
distances varying depending on severity of the weather. Trumpeter swans
move from interior regions in September, as total freeze-up occurs by
the first week in October. By mid-October, they have usually left
Kenai, located on the coast. On the Copper River Delta, many swans
remain until about mid-November. They arrive at Lonesome Lake, British
Columbia, beginning October 20 through October 25 .
Life span - Trumpeter swans may live up to 35 years in captivity but
usually do not live more than 12 years in the wild .
Life History and Behavior
Trumpeter swans produce a variety of sounds, but they are known for their low bugle call. In addition to the bugle call, they also use motions such as head bobbing to alert others of disturbances or in preparation for flight. Trumpeter swans are very social creatures except for in times of mating, when they become quite territorial. Pheromones are also used in mating rituals. The female emits pheromones when she is ready to mate. Breeding pairs perform visual, synchronous displays which likely reinforce the pair-bond. Trumpeter swans call to warn the flock of impending danger. Trumpeter swans perceive their environment through visual, auditory, tactile, and chemical stimuli.
Communication Channels: visual ; tactile ; acoustic ; chemical
Other Communication Modes: duets ; pheromones
Perception Channels: visual ; tactile ; acoustic ; chemical
Comments: Staging and breeding individuals may be active day and night (Henson and Cooper 1994).
Young trumpeter swans often have survival estimates from 40% to 100%, adult swan survival increases to 80% to 100%. The oldest captive trumpeter swan on record was 33 years old. In the wild, the oldest known individual was 24.
Status: wild: 24 (high) years.
Status: captivity: 33 (high) years.
- Krementz, D., R. Barker, J. Nichols. 1997. Sources of Variation in Waterfowl Survival Rates. The Auk, 114/2: 93-102.
Lifespan, longevity, and ageing
Trumpeter swans are monogamous and mate for life. During mating season, trumpeter swans reunite with their former mates or begin a process of courtship to secure a mate. Courtship displays consist of pairs simultaneously spreading or raising wings, wing quivering, head bobbing and trumpeting.
Mating System: monogamous
Adults begin mating at 4 to 7 years of age. Mating usually occurs from March to May. Nest-building can take 2 to 5 weeks to complete, and both parents are involved in construction. The nests range from 1.2 to 3.6 m in diameter and are usually surrounded by water. The materials used in nests building include various aquatic vegetation, grasses, and sedges.
After copulation and fertilization, the females lay 4 to 6 eggs. Incubation lasts for 32 to 37 days, done mainly by the female. The young, precocial cygnets spend their first 24 hours in the nest, then begin to swim. They fledge after 91 to 119 days and are independent after one year.
Breeding interval: Trumpeter swans breed once yearly.
Breeding season: Trumpeter swans breed from March to May.
Range eggs per season: 4 to 6.
Range time to hatching: 32 to 37 days.
Range fledging age: 91 to 119 days.
Average time to independence: 1 years.
Range age at sexual or reproductive maturity (female): 4 to 7 years.
Range age at sexual or reproductive maturity (male): 4 to 7 years.
Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; oviparous
Both parents contribute to nest building which lasts 2 to 5 weeks. The female will perform the majority of incubation. Unlike many birds, trumpeter swans do not have a specialized brood patch and instead will incubate the eggs using their feet. Upon hatching, the young are precocial but still require significant parental care. Both parents care for the cygnets throughout their first year.
Parental Investment: precocial ; male parental care ; female parental care ; pre-fertilization (Provisioning, Protecting: Female); pre-hatching/birth (Provisioning: Male, Female, Protecting: Male, Female); pre-weaning/fledging (Provisioning: Male, Female, Protecting: Male, Female); pre-independence (Provisioning: Male, Female, Protecting: Male, Female); post-independence association with parents; extended period of juvenile learning
- Slater, G. 2006. "Trumpeter Swan (Cygnus buccinator): a technical conservation assessment" (On-line pdf). US Forest Service. Accessed February 16, 2010 at http://www.fs.fed.us/r2/projects/scp/assessments/trumpeterswan.pdf.
Nesting begins in late April or early May in the intermountain western U.S. Clutch size is 2-9 (usually about 5). Incubation, mainly by female, lasts 33-37 days (Harrison 1978). Hatching occurs in latter half of June in southern Alaska, June in the intermountain Western U.S. Nestlings are precocial but remain with adults until subsequent spring. Fledging occurs at 100-120 days. Young remain with parents through winter; siblings may stay together for a few years, may rejoin parents after the nesting period. First nests at 4-5 years (may form pair bonds earlier). Life-long pair bond. Rarely more than one pair nests on a single body of water.
Molecular Biology and Genetics
Barcode data: Cygnus buccinator
Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species.
See the BOLD taxonomy browser for more complete information about this specimen and other sequences.
-- end --
Download FASTA File
Statistics of barcoding coverage: Cygnus buccinator
Public Records: 2
Specimens with Barcodes: 5
Species With Barcodes: 1
Historically, birds were heavily harvested for decorative feathers and skins. Many birds continue to be hunted illegally. If birds are illegally shot and do not die immediately, an embedded bullet may cause lead poisoning and eventual death. Today, habitat destruction is likely the greatest threat to trumpeter swans. Efforts are being made to protect trumpeter swans and their wetland habitat, with many states involved in reintroduction programs. As migratory birds, they are protected under the United States Migratory Bird Act.
Trumpeter swans are also affected by recent population increases of invasive mute swans. Mute swans are markedly more aggressive and will often chase trumpeters away from their shared wetland habitats. Some states are involved in mute swan control programs with the goal of reducing populations to allow for native swans to return.
US Migratory Bird Act: protected
US Federal List: no special status
CITES: no special status
State of Michigan List: threatened
IUCN Red List of Threatened Species: least concern
IUCN Red List Assessment
Red List Category
Red List Criteria
National NatureServe Conservation Status
Rounded National Status Rank: N4B,N5N : N4B: Apparently Secure - Breeding, N5N: Secure - Nonbreeding
Rounded National Status Rank: N4B,N4N : N4B: Apparently Secure - Breeding, N4N: Apparently Secure - Nonbreeding
NatureServe Conservation Status
Rounded Global Status Rank: G4 - Apparently Secure
Reasons: Although Pacific Coast population is increasing, the Rocky Mountain population has moderately increased, and the Interior population of midwestern, northern, and Canada subpopulations have expanded, serious threats to winter habitat availability and quality are present for all three major populations. The Pacific Coast population continues to lose wintering habitat in Washington and British Columbia. Some areas of Alaska breeding habitat are open to development; no overall swan management plan has been enacted for the state. Serious potential for disease outbreaks on reduced winter ranges exist. Species is sensitive to disturbance and pollution.
Intrinsic Vulnerability: Highly to moderately vulnerable.
Other Considerations: Water quality important for aquatic and emergent plant species utilized as forage and nesting materials.
United States and Canada is available at NatureServe, although recent changes
in status may not be included.
Global Short Term Trend: Increase of 10 to >25%
Comments: Increasing mainly in Alaska; other continent-wide expansion due to regional and local reintroduction programs (Mitchell 1994).
Global Long Term Trend: Decline of 30-50%
Comments: Great loss of historical breeding and wintering habitat, hunting (primarily market hunting) reduced contiguous U.S. population to less than 100 individuals by 1935, but undocumented populations smaller than their present levels existed in Alaska and Canada (Mitchell 1994).
In North America the species increased from less than 4,000 birds in 1968 to nearly 24,000 birds in 2000, which represents an average annual population growth of 5.9 percent. The Rocky Mountain population increased from approximately 800 birds in 1968 to more than 3,600 birds in 2000; average population growth rate was 4.8 percent per year. See USFWS (2003).
Degree of Threat: Low
Comments: Pacific Coast population (Mitchell 1994) faces a serious threat of winter habitat loss to development. Rocky Mountain population faces a serious threat due to declining winter habitat, overcrowding on existing winter habitat, and potential for widespread disease introduction. Threats to Interior population may be the same winter habitat and disease threats that the Rocky Mountain population faces.
Trumpeters swans are sensitive to human disturbance (boating, float-plane use, photography, etc.) (Mitchell 1994)and pollution. They are unusually sensitive to lead poisoning due to habitat and foraging behavior. White Phosphorus from military operations has caused death at Eagle River Flats, Alaska (Mitchell 1994). Human activity near nest site may cause nest failure or cygnet loss by disturbing adults (responses by pairs varies) (Mitchell 1994). Vulnerable to illegal hunting or malicious shooting due to their conspicuousness and large size (Mitchell 1994).
Rocky Mountain population:
From 1935-1992, the trumpeters were fed grain during winter at Red Rock Lakes National Wildlife Refuge, 20 miles northwest of Harriman State Park, Idaho. Large sanctuaries in Yellowstone and Grand Teton National Parks and at Harriman State Park also protected the swans from human disturbance. Artificial feeding and sanctuaries saved the population from extinction but discouraged southward migration, which is essential to long-term recovery. Artificial feeding at Red Rock Lakes ceased in 1992.
In eastern Idaho, lack of dispersal southward has created a severe "bottleneck" as increasing numbers of trumpeters arrive from Canadian nesting areas to spend the winter within Harriman State Park on the Henry's Fork of the Snake River in eastern Idaho. At this site, which receives the greatest amount of swan use, the aquatic plants can no longer provide enough winter food to support the increasing flocks of swans, Canada geese, and ducks (U.S. Fish and Wildlife Service).
In the Yellowstone region, nest flooding is the primary cause of nest failure, and coyote predation is the major cause of swan mortality in the winter.
Management Requirements: North American Trumpeter Swan Management Plan has been prepared (USFWS and Canadian Wildlife Service 1986). Henson and Grant (1991) recommended the following management guidelines for nesting areas that receive heavy use by humans: restrict sources of loud noises (e.g., airboats) during breeding season; discourage (e.g., through posting) human activity (such as cars stopping and passengers getting out to view swans nesting along roads); if wildlife viewing areas are desired, such sites should be more than 300 m from a nest and should be designed to minimize noise and visibility of observers.
Current/recent management includes ensuring adequate river flows, protecting and restoring nesting and winter habitat, restoring southward migration pathways to suitable wintering areas, and transplanting of swans to suitable winter habitat along the Snake River in southern Idaho (Spahr et al. 1991).
Rocky Mountain Population:
USFWS (http://www.r6.fws.gov/redrocks/rrl3.htm) reported the following information:
Since 1988, over 1,300 trumpeter swans have been captured at Harriman State Park and Red Rock Lakes National Wildlife Refuge and transplanted to new habitats in Oregon, southern Idaho, and Wyoming. Several were also moved to Utah.
Transplanted swans were neck collared and dyed, and closely monitored through a network of observers.
The disturbance from trapping and occasional planned disturbance has reduced the number of swans at high risk sites in the vicinity of Harriman State Park. Reduced swan use at Harriman has allowed some increase of aquatic plants which has improved habitat for both fish and waterfowl.
Transplanted swans have been sighted in all western states and are slowly increasing use of other wintering sites as far west as Oregon and California. Serious problems remain in eastern Idaho, however, as wintering swans continue to increase.
Up through 1995, biologists attempted to establish trumpeter swan migrations that would avoid tundra swan hunting areas. This was done to minimize the potential for a legal tundra swan hunter to accidentally harvest a trumpeter.
Beginning in 1994, tundra swan hunting regulations in Utah, Nevada, and Montana were changed to reduce the potential harvest of trumpeters, and to protect legal tundra swan hunters from legal action should they accidentally harvest a trumpeter. These changes enabled biologists to transplant trumpeters into areas where they have a greater potential to follow migrating tundra swans to southern wintering areas where food resources are plentiful.
Unless the present "bottleneck" can be opened, trumpeters from across western Canada will continue to end their southward migration in the tri-state area. They must either be persuaded to migrate through this region and continue south or they will exceed the carrying capacity of winter habitat and die there. The tri-state's local nesting swans, forced to share marginal sites with the growing Canadian flocks, will also be at risk.
Management options are limited. Substantial mortality is likely unavoidable; the problem has developed over decades and will not be easily solved. Additional transplants may help create use of other wintering areas but cannot possibly remove enough swans from eastern Idaho. Artificial feeding can no longer meet the needs of the increasing flocks. Feeding would concentrate swans as well as ducks and geese, creating a high risk of disease and discouraging any migration.
A well-organized program to systematically haze trumpeters offers another option to increase the number of birds that continue southward, but success is by no means a certainty. Fall hazing efforts will be increased; various techniques will be tried, and results will be closely monitored. Best results are likely if hazing occurs during the peak migration while the swans are still in good condition. To keep swans moving, hazing must be frequent and consistent over a broad area.
Regardless of hazing intensity and translocation efforts, some swans will likely remain in eastern Idaho and face harsh winters and limited food supplies. Our goal is to disperse as many swans as possible from the area.
Long-term population security will depend upon the survival of trumpeters in a wide variety of wintering sites. Currently, the Pacific Flyway Council is emphasizing monitoring over translocation in order to better understand the migration corridors used by the Rocky Mountain trumpeter swans.
Biological Research Needs: There are three research needs at present (Mitchell 1994):
1. Determine gene flow among subpopulations.
2. Obtain information on nutritional requirements of various age and sex classes, including the differences in foraging ecology and nutritional needs between migratory and sedentary poulations.
3. Investigate differences in foraging ecology and nutritional needs of swans foraging on agricultural crops versus aquatic vegetation on their wintering ares.
Global Protection: Many to very many (13 to >40) occurrences appropriately protected and managed
Comments: Localized migratory and nonmigratory populations in Canada and contiguous United States are very small (< 500 individuals) and are protected (to varing levels) in reserves. Alaska populations have varying levels of protection on their breeding grounds, but overwintering and migration habitats (occurrences with no protection) in British Columbia and Washington are declining.
Needs: Protection of winter areas (winter use EOs), resting and foraging habitat is needed (particularly in Washington, British Columbia, and Oregon as well) (Mitchell 1994). Non-point source pollution needs to be eliminated from breeding and wintering wetlands used by swans. Lost, reduced, or contaminated wetlands need to be restored. Further wetland loss needs to be prevented.
Use of Fire in Population Management
habitat . Fire can be used to convert forested uplands adjacent to
aquatic habitats to grasses and sedges, which are more suitable for
trumpter swan nesting . Additionally, removal of dense vegetation
and prevention of woody species encroachment is vital to prairie marsh
maintenance . Less dense vegetation allows more space for waterfowl
activities . Ward  reported that spring burning in marshlands
is primarily done to remove vegetation and create more nesting edge for
waterfowl. Summer fires are used to create more permanent changes in
the plant community. Prescribed burning during the nesting season
should be avoided so as not to disturb nesting females and/or destroy
The commercial swanskin trade, coupled with sport hunting and habitat
destruction, reduced the species to near extinction by 1920. The
trumpeter swans' traditional migration patterns and knowledge of
important winter and spring habitats were lost as the swans neared
extinction. Although recovery efforts have increased swan numbers,
historic migratory paths have not yet been restored. As a result,
virtually all the breeding trumpeter swans of Canada and the Greater
Yellowstone Ecosystem share the same high-elevation winter habitat in
the Greater Yellowstone Ecosystem. Increasing numbers of wintering
swans, concentrating on this limited, harsh winter habitat are
vulnerable to catastrophic losses. Reduced flows during drought, heavy
ice formation, unusually severe winter weather, disease, or
environmental pollution could destroy a large portion of the
mid-continental population during a single winter .
Trumpeter swans are sensitive to human activities on their breeding
grounds. Intrusions by humans at nesting wetlands have caused temporary
and permanent nest abandonment as well as movements from breeding and
staging areas [2,11]. Trumpeter swans will not nest on lakes
intensively developed for recreation. The swans are most sensitive to
disturbance from mid-April to mid-June .
Cygnet survival is associated with spring weather and favorable water
levels. It is extremely important to properly manage water levels so
that nest flooding is avoided and growth of aquatic vegetation is
encouraged through nutrient cycling .
Management efforts currently focus on ensuring adequate stream flows,
protecting and enhancing nesting and wintering habitat, and restoring
southward migration to lower elevation habitats .
Relevance to Humans and Ecosystems
Trumpeter swans are very territorial animals, especially during mating season, and humans that enter their territory may be attacked.
Trumpeter swans used to be a commercial hunting target for feathers and skins, but over-hunting led to their marked decline. Today, only illegal hunting occurs.
Positive Impacts: body parts are source of valuable material
The trumpeter swan (Cygnus buccinator) is a species of swan found in North America. The heaviest living bird native to North America, it also is on average, the largest extant species of waterfowl. It is the American counterpart and a close relative of the whooper swan of Eurasia, and even has been considered the same species by some authorities.
The trumpeter swan is the largest extant species of waterfowl. Adults usually measure 138–165 cm (4 ft 6 in–5 ft 5 in) long, though large males can exceed 180 cm (71 in) in total length. The weight of adult birds is typically 7–13.6 kg (15–30 lb). Possible due to seasonal variation based on food access and variability due to age, average weights in males have been reported to range from 10.9 to 12.7 kg (24 to 28 lb) and from 9.4 to 10.3 kg (21 to 23 lb) in females. It is one of the heaviest living birds or animals capable of flight. Alongside the mute swan (Cygnus olor), Dalmatian pelican (Pelecanus crispus) and Andean condor (Vultur gryphus) and the kori bustard (Ardeotis kori), it is one of the handful to scale in excess of 10 kg (22 lb) between the sexes and one survey of wintering trumpeters found it averaged second only to the condor in mean mass. The trumpeter swan's wingspan ranges from 185 to 250 cm (6 ft 1 in to 8 ft 2 in), with the wing chord measuring 60–68 cm (24–27 in). The largest known male trumpeter attained a length of 183 cm (72 in), a wingspan of 3.1 m (10 ft 2 in) and a weight of 17.2 kg (38 lb). It is the second heaviest wild waterfowl ever found, as one mute swan was found to weigh a massive 23 kg (51 lb), but it has been stated that was unclear whether this swan was still capable of flight due to its bulk.
The adult trumpeter swan is all white in plumage. As with a whooper swan, this species has upright posture and generally swims with a straight neck. The trumpeter swan has a large, wedge-shaped black bill that can, in some cases, be minimally lined with salmon-pink coloration around the mouth. The bill, measuring 10.5–12 cm (4.1–4.7 in), is up to twice the length of a Canada Goose's (Branta canadensis) bill and is the largest of any waterfowl. The legs are gray-pink in color, though in some birds can appear yellowish gray to even black. The tarsus measures 10.5–12 cm (4.1–4.7 in). The cygnets (juveniles) are grey in appearance, becoming white after the first year.
The mute swan, introduced to North America, is scarcely smaller. However, it can easily be distinguished by its orange bill and different physical structure (particularly the neck, which is always curved down as opposed to straight in the Trumpeter). The mute swan is often found year-around in developed areas near human habitation in North America, whereas Trumpeters are usually only found in pristine wetlands with minimal human disturbance, especially while breeding. The tundra swan (C. columbianus) more closely resembles the Trumpeter, but is significantly smaller. The neck of a male Trumpeter may be twice as long as the neck of a tundra swan. The tundra swan can be further distinguished by its yellow lores. However, some trumpeter swans have yellow lores; many of these individuals appear to be leucistic and have paler legs than typical Trumpeters. Distinguishing tundra and trumpeter swans from a distance (when size is harder to gauge) can be challenging without direct comparison but it is possible thanks to the trumpeter's obviously longer neck (the great length of which is apparent even when the swan is not standing or swimming upright) and larger, wedge-shaped bill as compared to the tundra swan.
Range and habitat
Their breeding habitat is large shallow ponds, undisturbed lakes, pristine wetlands and wide slow rivers, and marshes in northwestern and central North America, with the largest numbers of breeding pairs found in Alaska. They prefer nesting sites with enough space for them to have enough surface water for them to take off, as well as accessible food, shallow, unpolluted water, and little or no human disturbance. Natural populations of these swans migrate to and from the Pacific coast and portions of the United States, flying in V-shaped flocks. Released populations are mostly non-migratory. In the winter, they migrate to the southern tier of Canada, the eastern part of the northwest states in the United States, especially to the Red Rock Lakes area of Montana, the north Puget Sound region of northwest Washington state; they have even been observed as far south as Pagosa Springs, Colorado. Historically, they range as far south as Texas and southern California. Since 1992, trumpeter swans have been found in Arkansas each November – February on Magness Lake outside of Heber Springs.
These birds feed while swimming, sometimes up-ending or dabbling to reach submerged food. The diet is almost entirely aquatic plants. They will eat both the leaves and stems of submerged and emergent vegetation. They will also dig into muddy substrate underwater to extract roots and tubers. In winter, they may also eat grasses and grains in fields. They will often feed at night as well as by day. Feeding activity, and the birds' weights, often peaks in the spring as they prepare for the breeding season. The young feed on insects, small fish, fish eggs and small crustaceans along with plants initially, providing additional protein, changing to a vegetation-based diet over the first few months.
Trumpeter swans often mate for life, and both parents participate in raising their young, but primarily the female incubates the eggs. Most pair bonds are formed when swans are 5 to 7 years old, although some pairs do not form until they are nearly 20 years old. "Divorces" have been known between birds, in which case the mates will be serially monogamous, with mates in differing breeding seasons. Occasionally, if his mate dies, a male trumpeter swan may not pair again for the rest of his life. Most egg laying occurs between late April and May. The female lays 3–12 eggs, with 4 to 6 being average, in a mound of plant material on a small island, a beaver or muskrat lodge, or a floating platform on a clump of emergent vegetation. The same location may be used for several years and both members of the pair help build the nest. The nest consists of a large, open bowl of grasses, sedges and various aquatic vegetation and have ranged in diameter from 1.2 to 3.6 m (3.9 to 11.8 ft), the latter after repeated uses. The eggs average 73 millimetres (2.9 in) wide, 113.5 millimetres (4.5 in) long, and weigh about 320 grams (11.3 oz). The eggs are quite possibly the largest of any flying bird alive today, in comparison they are about 20% larger in dimensions and mass than those of an Andean condor (Vultur gryphus), which attains similar average adult weights, and more than twice as heavy as those of kori bustards (Ardeotis kori). The incubation period is 32 to 37 days, handled mainly by the female, although occasionally by the male as well. The young are able to swim within two days and usually are capable of feeding themselves after, at most, two weeks. The fledging stage is reached at roughly 3 to 4 months. While nesting, trumpeter swans are territorial and harass other animals, including conspecifics, who enter the area of their nest.
Adults go through a summer moult when they temporarily lose their flight feathers. The females become flightless shortly after the young hatch; the males go through this process about a month later when the females have completed their moult.
In captivity, members of this species has survived to 33 years old and, in the wild, have lived to at least 24 years. Young trumpeter swans may have as little as 40% chance of survival due variously to disturbance and destruction by humans, predation, nest flooding, and starvation. In some areas, though, the breeding success rate is considerably greater and, occasionally, all cygnets may reach maturity. Mortality in adults is quite low, usually being 80–100% annually, unless they are hunted by humans. Predators of trumpeter swan eggs include common raven (Corvus corax), common raccoon (Procyon lotor), wolverine (Gulo gulo), American black bear (Ursus americanus), brown bear (Ursus arctos), coyote (Canis latrans), gray wolf (Canis lupus), and northern river otter (Lontra canadensis). Nest location can provide partial protection from most mammalian nest predators, especially if placed on islands or floating vegetation in deep waters. Most of the same predators will prey on young cygnets, as will common snapping turtle (Chelhydra serpentina), California gull (Larus californicus), great horned owl (Bubo virginianus) and American mink (Mustela vison). Larger cygnets and, rarely, nesting adults may be ambushed by golden eagle (Aquila chrysaetos), bobcat (Lynx rufus), red fox (Vulpes vulpes) and coyote. When their eggs and young are threatened, the parents can be quite aggressive, initially displaying with head bobbing and hissing. If this is not sufficient, the adults will physically combat the predator, battering with their powerful wings and chomping down with their large bills, and have managed to kill predators equal to their own weight in confrontations. Predation of adults when they are not nesting is rare, although they may possibly be hunted by golden and bald eagles. Photos of a bald eagle (Haliaeetus leucocephalus) exceptionally attacking an adult trumpeter swan in mid-flight were taken recently, although the swan managed to survive the predation attempt.
In the 19th and early 20th centuries, the trumpeter swan was hunted heavily, both as game and a source of feathers. This species is also unusually sensitive to lead poisoning while young. These birds once bred in North America from northwestern Indiana west to Oregon in the U.S., and in Canada from James Bay to the Yukon, and they migrated as far south as Texas and southern California. The trumpeter was rare or extinct in most of the United States by the early twentieth century. Many thousands survived in the core range in Canada and Alaska, however, where populations have since rebounded. One of the largest conservation sites for the Trumpeter Swan is located in Lois Hole Provincial Park. It is located adjacent to the renamed Trumpeter subdivision of Edmonton, Alberta within Big Lake.
Early efforts to reintroduce this bird into other parts of its original range, and to introduce it elsewhere, have had only modest success, as suitable habitats have dwindled and the released birds do not undertake migrations. More recently, the population in all three major population regions have shown sustained growth over the past thirty-year period. Data from the US Fish and Wildlife Service show 400% growth in that period, with signs of increasing growth rates over time.
The Ontario Trumpeter Swan Restoration Group started a conservation project in 1982, using eggs collected in the wild. Live birds have also been taken from the wild. Since then, 584 birds have been released in Ontario. Despite lead poisoning in the wild from shotgun pellets, the prospects for restoration are considered good.
- Grande Prairie, Alberta, Canada — 'The Swan City'
- Ralph Edwards, a leading Canadian conservationist of trumpeter swans
- The Trumpet of the Swan, a 1970 children's novel by E. B. White.
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- Slater, G. (2006). "'Trumpeter Swan (Cygnus buccinator): a technical conservation assessment". U.S. Forest Service.
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The largest of North American waterfowl, the Trumpeter Swan is resident throughout much of its range, but migratory in other parts. Its was reduced to near extinction by the early 20th century, but it is relatively common today.
The Trumpeter Swan was hunted for its feathers throughout the 1600s - 1800s, causing a tremendous decline in its numbers. Its largest flight feathers made what were considered to be the best quality quill pens.
Swans can live a long time. Wild Trumpeter Swans have been known to live longer than 24 years, and one captive individual lived to be 32.
Trumpeter Swans form pair bonds when they are three or four years old. The pair stays together throughout the year, moving together in migratory populations. Trumpeters are assumed to mate for life, but some individuals do switch mates over their lifetimes. Some males that lost their mates did not mate again.
Names and Taxonomy
Comments: C. cygnus and C. buccinator have been considered conspecific by some authors (AOU 1983). See Meng et al. (1990) for information on variability of DNA fingerprints in C. cygnus, C. olor, and C. columbianus.
Cygnus buccinator Richardson [1,4,17]. There are no recognized
subspecies or races.