Overview

Brief Summary

Biology

Laysan ducks fly when they wish to each more remote parts of the island, but otherwise, they spending much of their time walking or running along the ground. They rest at midday and begin to feed during the evening and night (11). Laysan ducks feeds principally on brine flies, shrimps, and other invertebrates such as insect larvae and moths, but it also consumes grass seeds, sedge seeds and some algae (12). They have a novel way of catching brine flies; individuals run through swarms of these flies with their bills open and necks stretched out, attempting to trap the flies in the beak (11). The breeding season of the Laysan duck extends from autumn to spring, (typically April through June) (4). Copulation occurs on land or in water, and the female then builds a nest in dense grasses, where four eggs are usually laid (4) (11).
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Comprehensive Description

Description

The Laysan duck, so-called as it occurs on the Hawaiian island of Laysan, currently has the most restricted range of any duck in the world (4). It is a small, dark duck with orange legs and a prominent white eye-ring. The amount of white around the eye and on the head varies between individuals, and some adult males also have a slight green iridescence to the dark head. The rest of the plumage is dark reddish brown plumage, heavily mottled dark brown, and an iridescent patch of colour on the wings, (the speculum) appears teal green, or blue. Male Laysan ducks have dark green bills, while the female's is brownish-pale (5) (6).
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Distribution

Range Description

Anas laysanensis is endemic to the Hawaiian Islands (USA), where it became confined to Laysan. The birds do not disperse from Laysan today, but sub-fossil remains indicate that it was widespread on the Hawaiian Islands in the past12, most recently being extirpated from Lisianski Island about 150 years ago. The species was near extinction at the beginning of the 20th century, but the population increased to 500 individuals in 19873 following the removal of introduced rabbits from Laysan. In 1993, there was a complete breeding failure and severe die-off owing to drought and disease. Poor monitoring at this time impairs accurate population estimates, but post-hoc analysis suggests that the population dropped to 82-127 adults from a peak of 743 birds prior to the drought. Since then, the population has gradually increased8; the latest population estimate is 503-682 adult birds on Laysan18. Apparent population fluctuations over the past century were previously attributed to differing methods and seasons of counts3, but are now thought to relate to genuine changes11. The Laysan population may currently have reached carrying capacity for the island, but 42 individuals were translocated to the two islands of Midway Atoll National Wildlife Refuge in 2004 and 2005; the birds bred successfully in their first year1 and the founder population increased in size to a total of 104 individuals in 200616, reaching c.200 adult and juvenile (post fledging) individuals by the end of 200717,20 and predicted to grow to a total of 380 birds20. Although being hit by an outbreak of avian botulism in 2008, killing over 160 birds (a decline of up to 40-50%)21, the preliminary estimates from Midway place the population in 2010 at c.35025.
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Geographic Range

The Laysan Duck originally resided along all of the Hawaiian archipelago but within the past two hundred years has found its range greatly diminished. At the current time the Laysan Duck can only be found on the small, 900-acre, island (Laysan Island) that is under the protection of the US Fish and Wildlife Service.

Biogeographic Regions: oceanic islands (Native ); pacific ocean (Native )

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endemic to a single state or province

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National Distribution

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: (<100 square km (less than about 40 square miles)) Resident on Laysan Island, northwestern Hawaiian Islands. Subfossils and ancient DNA indicate that this duck formerly was widespread in the Hawaiian Islands (Cooper et al. 1996).

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Historic Range:
U.S.A. (HI)

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Range

The Laysan duck, also known as the Laysan teal, is endemic to the Hawaiian Islands, USA. It was once widespread in the Hawaiian Islands, but for the last 150 years, has been restricted to just Laysan Island (7) (8). In 2004 and 2005, a number of Laysan ducks were translocated to two islands of the Midway Atoll National Wildlife Refuge (9).
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Physical Description

Morphology

Physical Description

Average weights for this long-lived duck vary with its age. An individual at age 14 can weigh 98.1 grams while an individual at age 45 can weigh 402.0 grams. There is little difference between the plumages of males and females. Both are dull, dark brown with distinctive white eye rings and white feathering on head and neck. The main difference lies with bill coloring: the male bill is yellowish green with black spotting, while the female bill is dull orange. The Laysan Duck has strong wings that allow it quick take offs but not prolonged flight. The Laysan Duck spends most of its time on its legs dabbling into the water and on land for food.

Range mass: 98 to 402 g.

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Size

Length: 41 cm

Weight: 435 grams

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
The species is non-migratory and characterised by female-only parental care and high adult survival. On Laysan, long-term pair bonds are common, and 3-4 eggs are laid per clutch. The timing of breeding varies significantly between years with the beginning of incubation varying from December to July22. It selects different habitats during different times of the day. Most adult birds use dense cover and hide in the terrestrial vegetation during the day. During the evening, and at night15, it uses the central hyper-saline lake on Laysan, but concentrates near freshwater seeps around the shore5, especially when raising young ducklings, which are less tolerant of hypersaline conditions. It nests and rests in dense stands of shrubs and grasses6. It feeds principally on invertebrates, but also grass and sedge seeds, and some algae8; brine fly Scatella sexnotata is an important prey species whose peak spring abundance is positively correlated with annual brood production of the teal22. Reintroduced birds on Midway Atoll appear to breed successfully at an earlier age and produce larger clutches, probably owing to more food and a low density population. However, duckling survival is low on both atolls.

Systems
  • Terrestrial
  • Freshwater
  • Marine
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Habitat

Grouped among the Dabbling ducks such as the Mallard, the Laysan Duck prefers land habitats to aquatic and aerial habitats. The Laysan Duck is normally observed along the coast of Laysan Island or around the inland lake found on the island. This is where they reside year round. Studies of DNA in duck bones throughout the Hawaiian Islands have shown that the Laysan Duck's range once included the entire Hawaiian Archipelago before the mass extinctions that occurred in that region after Polynesian colonization between 400 and 600 AD.

Aquatic Biomes: coastal

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Comments: Usually occurs in the island's lagoons, tidal pools, and marshes (Matthews and Moseley 1990). Feeds and drinks at inland water at night; attracted to freshwater seeps. Seeks shelter in vegetation (Pluchera, Ipomoea, and Sicyos) during heat of day.

Nests on ground in or under vegetation, mainly in clumps of grass (Eragrostis).

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Habitat

The Laysan duck selects different habitats during different times of the day. Most adult birds use dense cover and hide in the terrestrial vegetation during the day, while during the evening and at night, it can be found in the central hypersaline lake on Laysan. It favours areas in the lake near freshwater seeps around the shore, especially when raising young ducklings, which are less tolerant of hypersaline conditions. It nests and rests in dense stands of shrubs and grasses (10).
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Migration

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: No. No 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: No. No populations of this species make annual migrations of over 200 km.

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Trophic Strategy

Food Habits

The main food staple for this species is macroinvertebrates. The Laysan Duck is not a diver or swimmer and merely dips its head into the water to feed on aquatic plants, seeds and snails. They also do some filter feeding for moth larvae and pupae. A peculiar method of feeding that has been observed in this species is its tendency to run through swarms of adult brine flies with its neck extend and mouth open in order to trap the flies in its mouth. The climate in the Pacific Ocean undergoes little seasonal variation and therefore migration by this duck to follow food is unnecessary, as supplies stay constant year round.

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Comments: Eats mainly insects, including caterpillars, larvae and pupae of flies and beetles around seabird carcasses, and especially Neoscatella flies around saline lake; also crustaceans and other invertebrates in shallow tide pools.

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Population Biology

Number of Occurrences

Note: For many non-migratory species, occurrences are roughly equivalent to populations.

Estimated Number of Occurrences: 1 - 5

Comments: Only one extant occurrence in 1995 (Moulton and Marshall 1996).

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Global Abundance

50 - 1000 individuals

Comments: Population was estimated at about 400-500 in the early to mid-1980s (Moulton and Weller 1984, Scott and Kepler 1985). As of 1989, the population was holding stable (USFWS 1990) at about 500 (Matthews and Moseley 1990). Fewer than 150 survived drought conditions in 1993 (Cooper et al. 1996). In 1995, 246 were counted (Moulton and Marshall 1996). Several hundred are in breeding facilities throughout the world.

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General Ecology

Apparently reproductive rate is low and adult survival rate is high (Moulton and Weller 1984).

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Life History and Behavior

Cyclicity

Comments: Most active at twilight and at night.

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Life Expectancy

Lifespan/Longevity

Average lifespan

Status: wild:
142 months.

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Lifespan, longevity, and ageing

Maximum longevity: 12 years (wild)
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Reproduction

Reproduction

Copulation occurs on land during the late fall and winter. Nesting occurs after this with the female building a nest in a well-concealed location. Four eggs are laid usually between April and August but sometimes as early as February and as late as November. The species' overall success has been diminished by human intrusions especially because its reproductive rate is naturally low. Organizations that wish to increase the duck's population size are currently breeding the ducks in captivity.

Average eggs per season: 4.

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Eggs are laid mainly in spring and early summer, though timing of breeding may vary annually; most eggs laid May-late July according to Matthews and Moseley (1990). Clutch size is usually about 4-6. Young are tended by female. About half of adults switch mates from one year to next.

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Molecular Biology and Genetics

Molecular Biology

Barcode data: Anas laysanensis

The following is a representative barcode sequence, the centroid of all available sequences for this species. 

 
There are 2 barcode sequences available from BOLD and GenBank.  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.
 
SIBHI091-11|USNM 643458|Anas laysanensis| ------------------------------------------CTATACCTTATCTTCGGGGCATGAGCCGGAATAATTGGCACAGCACTC---AGCCTACTGATCCGGGCAGAGCTGGGCCAGCCAGGGACCCTCCTGGGCGAC---GACCAAATTTATAACGTGATCGTCACCGCTCACGCCTTCGTAATAATCTTCTTCATGGTAATGCCCATCATAATTGGAGGGTTCGGCAACTGATTGGTCCCCCTGATA---ATCGGTGCCCCCGACATAGCATTCCCACGAATAAACAACATAAGCTTCTGACTCCTCCCACCATCATTCCTCCTTCTACTCGCCTCATCCACTGTAGAAGCTGGCGCTGGTACAGGTTGAACCGTATACCCACCTCTAGCAGGCAACCTAGCCCACGCCGGAGCCTCAGTGGACCTG---GCTATCTTCTCACTTCACCTGGCCGGTGTCTCCTCCATCCTCGGAGCCATTAACTTCATTACCACAGCCATCAACATAAAACCCCCCGCACTCTCACAATACCAAACCCCACTTTTCGTCTGATCAGTCCTAATTACCGCCATCCTGCTCCTCCTATCACTCCCCGTCCTCGCCGCC---GGCATTACAATGCTACTAACCGACCGAAACCTAAACACCACATTCTTTGATCCTGCCGGAGGGGGAGACCCAATCCTGTACCAGCACCTATTTTGATTCTTCGGCCACCCAGAAGTCTATATCTTAATCCTC-------------------------------------------------------------------------------------------------------------------------------------------------------  
-- end --

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Statistics of barcoding coverage: Anas laysanensis

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 2
Species: 2
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
B1ac(iv)

Version
3.1

Year Assessed
2010

Assessor/s
BirdLife International

Reviewer/s
Calvert, R., Symes, A., Butchart, S.

Contributor/s
Morin, M., Ritchotte, G., Shallenberger, R., Reynolds, M.

Justification
This species is listed as Critically Endangered because its population exhibits extreme fluctuations within its extremely small range. Conservation action is seeking to remove existing threats or increase the species's resilience to them, and the population is currently increasing. Following the successful reintroduction of birds to Midway Atoll, this species will warrant downlisting after five years if both populations are still self-sustaining, as the species now lies above the population thresholds for listing as Critically Endangered and occurs at multiple locations; but in the meantime it retains this classification as a precautionary measure.

History
  • 2009
    Critically Endangered
  • 2008
    Critically Endangered
  • 2006
    Critically Endangered
  • 2004
    Critically Endangered
  • 2000
    Vulnerable
  • 1996
    Vulnerable
  • 1994
    Vulnerable
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Conservation Status

The population bottomed at 150 recently in 1993 following a drought in the region. Their present numbers are up to 600, which is considered a success on the part of the US Fish and Wildlife Service. Currently the Laysan Island is now a refuge for these birds, but has been maintained loosely as a Bird Sanctuary since 1909.

US Federal List: endangered

CITES: no special status

IUCN Red List of Threatened Species: critically endangered

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National NatureServe Conservation Status

United States

Rounded National Status Rank: N1 - Critically Imperiled

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NatureServe Conservation Status

Rounded Global Status Rank: G1 - Critically Imperiled

Reasons: Restricted to Laysan Island. Management has resulted in a somewhat stable wild population of several hundred, but this duck remains vulnerable to introduced species and catastrophic events.

Intrinsic Vulnerability: Moderately vulnerable

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Current Listing Status Summary

Status: Endangered
Date Listed: 03/11/1967
Lead Region:   Pacific Region (Region 1) 
Where Listed:


Population detail:

Population location: entire
Listing status: E

For most current information and documents related to the conservation status and management of Anas laysanensis , see its USFWS Species Profile

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Status

Classified as Critically Endangered (CR) on the IUCN Red List 2007 (1), and listed in Appendix I of CITES (3).
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Population

Population
Lincoln Petersen Estimate of 611 (538-714) adult individuals on Laysan in 2005 (Reynolds et al. 2006) and c.350 individuals on Midway in 2010 (M. Reynolds in litt. 2010). This gives a global population estimate of 888-1064 individuals.

Population Trend
Increasing
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Global Short Term Trend: Relatively stable (=10% change)

Comments: The recovery (1970s to early 1990s) was followed by a drought-induced decline to fewer than 100 in 1994, and then a subsequent recovery to 246+ in 1995 (Moulton and Marshall 1996).

Global Long Term Trend: Decline of 30-50%

Comments: Subfossils and ancient DNA indicate that this duck formerly was widespread in the Hawaiian Islands (Cooper et al. 1996). Has undergone two major declines in the last century. Guano mining on Laysan Island began in 1891 and continued until 1904; rabbits were introduced at this time. In 1902 Fisher (1903) estimated a population of 100. In 1912 Bailey (1956) counted 7. In April 1923 Wetmore counted 20 ducks. Remaining rabbits were killed and the island slowly regenerated. In 1950 Brock counted 33 ducks. By 1976 287 birds were counted (USFWS 1982). Population recovered to more than 450 in 1992, then crashed in 1993-1994 to fewer than 100 individuals (Moulton and Marshall 1996).

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Threats

Threats

Major Threats
Random disasters and the limited carrying capacity of the fragile tiny islands are the main threats to its persistence. Historic declines on Laysan leading to the near-extinction of the species are attributed to introduced rabbits and more recently the parasitic nematode Echinuria uncinata, coupled with drought19. Since the severe range contraction of the species from the main Hawaiian Islands after the introduction of rats, stochastic events that have already occurred include: the accidental introduction of noxious competitors, extreme weather, and disease epizootics. Additional populations on different islands are needed to reduce the extinction risk to small concentrated populations from alien predator introductions, tsunamis, and hurricanes, as the probability that disasters will affect several islands simultaneously is lower. On Laysan Island, brood rearing habitat is probably an important limiting factor. Freshwater seeps with high invertebrate abundance and adjacent dense vegetative cover are used as duckling nurseries. High incidence of duckling trauma suggests these freshwater seeps may become overcrowded. Reproductive success is sometimes related to brine fly (prey abundance) densities which, in turn, are reduced by drought and low water-levels6,7,8. During drought conditions, the birds depend more on terrestrial prey15. Introduced ants (e.g. big-headed ant Pheidole megacephala) are probably competitors for their terrestrial invertebrate prey8. Disease or parasitic infestation by the nematode Echinuria uncinata10 are perhaps one of the greatest potential threats - the catastrophic outbreak of avian botulism killed 40-50% of teal on Midway in 200821. Some alien invasive plants on Laysan have threatened nesting and wetland habitat4,5. Having a distribution on relatively low-lying islands, this species is potentially susceptible to climate change through sea-level rise and shifts in suitable climatic conditions26.
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Degree of Threat: A : Very threatened throughout its range communities directly exploited or their composition and structure irreversibly threatened by man-made forces, including exotic species

Comments: Numbers originally reduced by human predation and then species brought to near extinction as a result of habitat destruction by introduced rabbits; nest predation by introduced rats also may have also contributed to the decline (Moulton and Marshall 1996). Vulnerable to introduced species, catastrophic events, and possibly human disturbance. Scott et al. (1988) concluded that the future of the wild population seems secure if alien predators and plants can be kept off Laysan Island, and if the mobile sand dunes threatening Laysan's central lagoon are stabilized. However, USFWS (1990) stated that this may be a perennial threatened species due to limited habitat and vulnerability to natural and man-made catastrophes.

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Threats

The limited range and small, single population of the Laysan duck is the greatest ultimate threat to this species' survival at present, as it makes it is extremely vulnerable to chance events such as disease or severe weather (4). Introduced species are a potential threat to the species persistence; while mammalian predators are not currently a problem on Laysan Island, there is nothing to prevent an accidental introduction and there are no measures in place to deal with the event should it occur (6). Many non-native invertebrates have arrived on Laysan, and while not all are impacting the Laysan duck, some, (such as ants), are possibly affecting the Laysan duck's food supply as they compete for their terrestrial prey (4). An introduced grass, Cenchrus echinatus, encroached on the native bunchgrass (Eragrostis variabilis) on Laysan Island, reducing important breeding habitat, but this noxious weed was thankfully eradicated from the island (13). Infection with the parasitic nematode worm, Echinuria uncinata, is causing problems for the Laysan duck's precariously small population (2), and global sea level rise poses a constant threat to all species on the low-lying island of Laysan (4).
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Management

Conservation Actions

Conservation Actions
Conservation Actions Underway
CITES Appendix I. Laysan is part of the Hawaiian Islands National Wildlife Refuge. The alien grass Cenchrus echinatus is thought to have been eradicated5 and native bunch grass has responded positively8. Snow fences were installed 20 years ago to reduce the movement of sand and support natural revegetation6. A comprehensive restoration plan for Laysan Island has been developed, some sections of which are underway24. In 2004-2005, 42 wild birds translocated from Laysan Island were released on Midway Atoll and many bred successfully in their first season. Following the success of the releases on Midway, the next translocation is being discussed for Kure or Lisianski islands in the North West Hawaiian Islands to establish a third population, however currently held captive birds are unsuitable for translocation and this would therefore require the establishment of a new captive population from wild stock17,21. Both islands require some habitat restoration prior to duck translocation; this work is currently underway on Kure17. During the 2008 avian botulism outbreak on Midway 28 sick birds were successfully treated with anti-toxin, rehabilitated and released, and the rapid removal of sick and dead birds was thought to have prevented the impact of the outbreak becoming even worse21.

Conservation Actions Proposed
Continue to monitor the population size and health on both Midway Atoll and Laysan Island. Continue to enhance nesting habitat on Midway by planting native bunch grasses. Enhance brood-rearing habitat on Midway Atoll with small fish-free freshwater wetlands with abundant cover. Use translocation and ecosystem restoration to re-establish four additional populations of Laysan Ducks. On Laysan, continue to stabilise dunes by planting native vegetation6. Restore freshwater wetlands on Lisianski and Kure Islands prior to potential re-introduction. Ensure strict procedures to prevent the accidental introduction of exotic plants, invertebrates and animals6. Control exotic plants likely to negatively impact the species. Conduct further alien predator eradications to create potential for reintroduction to other larger higher elevation islands. After restored predator-free habitat is available, create a new genetically managed captive population within Hawaii to provide birds for reintroductions to other Hawaiian islands8.

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Restoration Potential: DNA data justify the reintroduction to other locations in the Hawaiian islands where formerly this species occurred (Cooper et al. 1996).

Management Requirements: Control of introduced plants and predators is regarded as essential.

Management Research Needs: Expand captive rearing of individuals, and develop methods for translocating individuals to other suitable islands.

Biological Research Needs: Continue research on reasons for the rapid and extreme population fluctuations.

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Global Protection: Few (1-3) occurrences appropriately protected and managed

Comments: Laysan is part of the Hawaiian Islands National Wildlife Refuge, which is actively managed by the USFWS.

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Conservation

The Laysan duck is listed under Appendix I of the Convention on International Trade in Endangered Species (CITES) and so international trade in this species is under tight control (3). Furthermore, Laysan Island and Midway Atoll are under the protection of the United States Fish and Wildlife Service as they are both National Wildlife Refuges (14), and whilst there are no measures to prevent an accidental species introduction, (for example via a ship wreck or unauthorised landing), Laysan Island has a quarantine for authorised visitors (6). Conservation action that has taken place to date includes the eradication of the introduced grass, Cenchrus echinatus (13), as well as the control of other alien plant species that threaten Laysan's wetlands (Pluchea indica) on Laysan Island, and the successful translocation of wild Laysan Ducks to Midway Atoll National Wildlife Refuge. The translocated ducks have bred successfully, creating an 'insurance' population which will reduce the chances of a catastrophic event wiping out the entire species, since it is unlikely that a disaster would strike two islands simultaneously (15). Proposed future actions include reintroducing the species to other Hawaiian islands (15), restoring or enhancing limited freshwater brood rearing habitat, along with stabilising dunes by planting vegetation, and preventing the accidental introduction of competitor and predator species, particularly new ant species and rats (2). Habitat restoration and introduced predator removal on additional islands with higher elevations are needed since Midway Atoll and Laysan Island are low lying. The Island of Kahoolawe has been proposed as a good site for reintroduction and habitat restoration (6).
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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

Their refuge is an area of high economic value to developers.

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Wikipedia

Laysan Duck

The Laysan Duck (Anas laysanensis), also known as the Laysan Teal because of its small size, is an endangered dabbling duck endemic to the Hawaiian Islands. Fossil evidence reveals that Laysan Ducks once lived across the entire archipelago, but today survive only on three small, isolated islands.

Contents

Taxonomy

Named by Lionel Walter Rothschild in 1892, the Laysan Duck is named after Laysan island, one of the Northwestern Hawaiian Islands. It is a member of the mallard clade of dabbling ducks, and is a highly behaviorally and genetically unusual species. Recent evidence suggests they evolved from an east Asian, southern hemisphere ancestor of mallards, not from stray migratory Mallards (Anas platyrhynchos) as had been reported in the past.[2]

Description

The Laysan Duck is teal-sized and dark brown, with a prominent white eye-ring. The bill is short and spatulate, dark green with variable black blotching in males, and dull orange with variable black blotching in females. The Laysan Duck usually has a ring of fat around its neck. Some males show faint iridescence on the head or neck and have slightly upturned central tail feathers. The wing has an iridescent purplish-green patch (speculum feathers) in both sexes. Leucistism, or extensive white feathering, is common on the head and neck of older birds. The legs and feet are orange, usually brighter in the male. The annual pre-basic molt is complete, and the ducks lose all their flight feathers and become incapable of flight until new feathers grow in. Wild ducks have been known to live to the age of twelve years, and captive birds have lived to the age of eighteen.

Behavior

The Laysan Duck walks and runs well, with a pelvic girdle adapted to terrestrial foraging. Energetic foraging behavior includes a fly-snapping sprint through Neoscatella sexnotata brine fly swarms. With necks outstretched, and bills close to the ground, the ducks run along a mudflat and as clouds of flies rise up in front, snap them up by rapidly opening and closing their bills. The ducks also will dabble and filter feed along lake shallows, shore, and in upland vegetation for macroinvertebrates, algae, leaves, and seeds.[3] During the day, and especially in the breeding season, they prefer to hide among the grass and shrub vegetation, helping them to avoid avian predators such as frigatebirds. They prefer to venture out in the open and feed on the lake from dusk til dawn, although there seems to be marked variation from year to year according to the availability of food items.[4]

Reproduction

Pair formation begins in fall, and nest building begins in spring. The female builds a well-concealed nest on the ground below dense vegetation, especially Eragrostis variabilis bunchgrass. The nest is a shallow bowl lined with dead grass and down feathers. Egg-laying typically occurs from April to August. Average clutch size on Laysan Island is approximately four eggs. The newly established population on Midway lays larger clutches, presumably because of better availability of food. Ducklings are precocious and feed on their own day two after hatching, but are guarded, brooded, and led to foraging sites by the hen for approximately 40 to 60 days.

Status and conservation

Decline to near-extinction

Male Laysan Duck

The decline of the Laysan Duck began 1000-1600 years ago, with the colonization of the Hawaiian Islands by Polynesians and associated non-native mammalian predators.[3] By 1860, the ducks disappeared from all but Laysan Island (the duck’s namesake), most likely due to predation by introduced rats. Like many isolated island species, the Laysan Duck evolved in an environment lacking mammalian predators, and is ill-suited to defend itself against non-native ground hunters, such as humans, rats, pigs, and Small Asian Mongooses. For example, Laysan Ducks are more likely to freeze their movement rather than flush or fly when startled— a strategy well suited for cryptic defense against Hawaiʻi’s native flying predators, but ineffective against ground predators. Although the non-migratory Laysan Duck can fly, it does not disperse between islands.[5]

The Laysan Duck found refuge through most of the nineteenth century on rat-free Laysan Island, surviving within the smallest geographic range of any duck species worldwide (415 hectares / 1.60 square miles). Laysan Island gained federal protection in 1909, with the establishment of the Hawaiian Islands National Wildlife Refuge. However, devastation of the island’s vegetation by introduced domestic rabbits brought the duck to the brink of extinction in 1912, with an all-time low population of 7 adults and five juveniles.[6]

Recovery

After many domestic rabbits starved and the remaining ones were eradicated by biologists in 1923, the ducks began to recover, increasing to a population of about 500 individuals by the 1950s.[7][8][9] Congress passed the Endangered Species Preservation Act in 1966, and in 1967 the Laysan Duck was declared an endangered species with federal protection. However, population bottlenecks occurred, such as the severe 1993 El Niño drought and food shortage, which reduced the number of ducks to about 100. Today, breeding and survival of the birds is closely tracked. Since 1998, a sample of birds have been fitted with unique leg bands or radio transmitters for monitoring reproductive success and survival, revealing that typically only 30% of ducklings on Laysan Island survive to fledge.[10] In 2004, the population grew to an estimated 576 ducks.

Laysan Ducks chasing brine flies

In October 2004 and 2005, 42 Laysan Ducks were translocated to Midway Atoll National Wildlife Refuge as a collaborative effort between the United States Geological Survey and Fish and Wildlife Service to restore a second population of ducks in the wild. The creation of a second population, since disaster is unlikely to strike both atolls simultaneously, reduces the risk of extinction by random catastrophes such as drought, hurricanes, tsunamis, disease outbreaks (like avian influenza), and accidental introductions of non-native plants and animals.[11]

The second “insurance” population of Laysan Ducks on Midway has grown quickly, more than doubling in size within the first two years (USGS 2006c). As of January 2007, 100 ducks call Midway’s Sand and Eastern Island home. Researchers monitoring the Midway population have found that the ducks are breeding at an earlier age, and laying more eggs than birds on Laysan. This suggests that the abundant habitat and food available on Midway has stimulated greater reproductive effort in the ducks, which contributes optimism for the success of this re-introduced population.[12]

Future outlook

The persistence of the Laysan Duck into the future is optimistic, though threats to the population remain. Threats include the introduction of non-native species, which may change vital rates, displace native species and adversely affect nesting and foraging opportunities. Devastation to vegetation could increase sedimentation of the lakes and seeps that serve as important foraging habitat. Human disturbance may impact nesting and brooding, and landing permits to the Laysan Island refuge are granted only for official or scientific purposes. Debris and contaminants washed ashore by ocean currents could pose a serious threat to the duck. Pesticide containers and oil spills have contaminated Laysan in the past. The island homes of the duck are especially vulnerable to a rise in sea level and extreme weather associated with global warming. Even a slight rise in sea level would destroy a large portion of the duck’s current habitat. The spread of parasites such as the nematode Echinuria uncinata could be extremely pathogenic, as well as the introduction of disease by migratory waterfowl along the Pacific Flyway (such as avian influenza, avian malaria, cholera, botulism and duck plague). Environmental catastrophes such as drought, severe storms, and tsunamis may decimate populations. The increased frequency and severity of storms are an anticipated effect of global warming.[5]

Laysan Duck Brood

A recovery plan for the Laysan Duck has been developed by the U.S. Fish and Wildlife Service.[5] The goal of the recovery program is to conserve and recover the species to the extent that it may be down-listed from endangered to threatened in the near future, and ultimately, that the population be healthy enough to no longer require federal protection under the Endangered Species Act. The emphasis of the recovery plan is the distribution of additional viable populations in the Laysan Duck’s historical and prehistorical range. The creation of multiple populations will decrease the risk that catastrophic events will result in species extinction. The increase of population size will diminish the threats from demographic and environmental uncertainties. To achieve this goal, biologists plan to establish at least five populations on a combination of predator-free Northwestern Hawaiian Islands and predator-controlled sites on Main Hawaiian Islands. This plan includes wild translocation and the establishment of a successful captive or semi-captive breeding program using wild source eggs for reintroductions to the Main Hawaiian Islands. Additionally, the plan calls for achieving gene flow between the wild source populations through long-term inter-island translocations, and island-specific management for each population to reduce threats and improve quality of habitat. If basic criteria of the recovery plan are met, the Laysan Duck could be down-listed from endangered to threatened by 2019.

Notes

  1. ^ BirdLife International (2009). "Anas laysanensis". IUCN Red List of Threatened Species. Version 2009.2. International Union for Conservation of Nature. http://www.iucnredlist.org/apps/redlist/details/141506. Retrieved 31 January 2010. 
  2. ^ Johnson and Sorenson 1999
  3. ^ a b Reynolds et al. 2006
  4. ^ Reynolds 2004
  5. ^ a b c USFWS 2004
  6. ^ Dill & Bryan 1912
  7. ^ Warner 1963
  8. ^ Moulton & Weller 1984
  9. ^ Moulton & Marshall 1996
  10. ^ USGS 2005
  11. ^ USFWS 2005
  12. ^ USGS 2006a, 2006b

References

  • Johnson, Kevin P. & Sorenson, Michael D. (1999): Phylogeny and biogeography of dabbling ducks (genus Anas): a comparison of molecular and morphological evidence. Auk 116(3): 792–805. PDF fulltext
  • Moulton, D.W. & Marshall, A.P. (1996): Laysan Duck (Anas laysanensis). In: Poole, A. & Gill, F. (eds.): The Birds of North America: 242. Academy of Natural Sciences, Philadelphia, PA & American Ornithologists' Union, Washington, D.C. Online version, retrieved 2007-FEB-08. doi:10.2173/bna.242 (requires subscription)
  • Reynolds, Michelle H. (2004): Habitat use and home range of the Laysan Teal on Laysan Island, Hawaii. Waterbirds 27(2): 183-192. DOI:10.1675/1524-4695(2004)027[0183:HUAHRO]2.0.CO;2 HTML abstract
  • Reynolds, Michelle H.; Slotterback, J.W. & Walters, J.R. (2006): Diet composition and terrestrial prey selection of the Laysan Teal on Laysan Island. Atoll Research Bulletin 543: 181-199. PDF fulltext
  • US Fish and Wildlife Service (USFWS) (2004): Draft Revised Recovery Plan for the Laysan Duck (Anas laysanensis). Portland, OR. PDF fulltext
  • US Fish and Wildlife Service (USFWS) (2005): New arrivals to Midway Atoll NWR provide “insurance” against extinction for nation’s rarest duck. News Release, Oct 28. PDF fulltext
  • US Geological Survey (USGS) (2005): Translocation of Endangered Laysan Ducks to Midway Atoll National Wildlife Refuge (2004-5). Fact sheet 2005-3128. PDF fulltext
  • US Geological Survey (USGS) (2006a): Second generation of the nation’s rarest ducks hatch after translocation. News Release, May 16.
  • US Geological Survey (USGS) (2006b): Midway Atoll national Wildlife Refuge welcomes second generation of nation’s rarest ducks. News release, May 23. PDF fulltext
  • US Geological Survey (USGS) (2006c): Endangered duck population reaches triple digits! News release, Oct 23. HTML fulltext
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Names and Taxonomy

Taxonomy

Comments: Sometimes has been regarded as subspecies of A. PLATYRHYNCHOS. Browne et al. (1993) examined allozyme variation and found that alternative alleles are fixed at six loci for mallards versus Hawaiian and Laysan ducks; in contrast, every allelic variant found in the Laysan duck was present in the Hawaiian duck (but not vice versa), suggesting that the former is an offshoot of the latter; Hawaian and Laysan ducks are genetically very close and both are genetically much closer to each other than to the mallard; allozymic data suggests that there has been extensive hybridization between mallards and Hawaiian ducks on Oahu (see also Engilis and Pratt 1993), with the near disappearance of Hawaiian duck alleles; there is only slight evidence of mallard genic introgression into the Hawaiian duck population on Kauai; the Hawaiian anatids are specifically distinct from the mallard, but further data on mating preferences, behavior, and hybrid fitness are needed to confirm that the Hawaiian duck and Laysan duck are specifically distinct from each other. Cooper et al. (1996) reported that the Laysan duck is very distinct genetically from the Hawaiian duck and mallard.

See A91LIV01NA for a phylogenetic analysis and classification (supergenera, subgenera, infragenera, etc.) of dabbling ducks based on comparative morphology.

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