Overview

Brief Summary

Biology

During winter, superb parrots live in pairs or small flocks of up to 30 birds (7). Nesting begins by September and continues through to November or December (2) (7). Nests are situated in the hollow limb or hole in a tree (2), and loose nesting colonies are often found around clusters of suitable nesting trees (7). Four to six eggs are laid per clutch and incubated by the female for about 20 days, with chicks fledging at around five weeks of age (2) (7). Flocks of males can be seen feeding together and collecting food for the nesting females, which they feed two to three times a day over a month or more while the eggs and new hatchlings are developing (6) (7). The superb parrot is mostly active in the early morning and late afternoon, when it feeds on the seeds of grasses and plants, fruits, berries, nectar flowers and occasionally insects, foraging on the ground, in shrubs, the understorey and in trees (7). These social birds often feed in pairs or small parties (6).
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Comprehensive Description

Description

This is a brilliant green parrot with a distinctively long, slender, graduated tail (4) and a swift and graceful flight (5). One of the diagnostic features of the superb parrot is the bright yellow face of the male, sharply demarcated by a scarlet band across the upper breast (4). The female is a duller green than the male with a bluish-green face, red thighs and rose-pink edges to the tail feathers (2) (4) (5). Both have a red iris and bright pinkish-red bill, and the juvenile is similar to the adult female (4) (5). In flight, their sleek bodies, long pointed tails and backward swept wings give superb parrots a distinctive silhouette (6).
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Distribution

Range Description

Polytelis swainsonii is endemic to Victoria and New South Wales, Australia. It has undergone a substantial range contraction. Bioclimatic modelling of suitable climatic conditions within its range supports this and suggests that it now occupies a relatively small part of its former range3. In Victoria, it is now largely confined to the Nathalia area, especially Barmah State Forest, birds having disappeared from central and southern areas in the early 1900s, and it has substantially declined in northern Victoria by 1930. In New South Wales, it has declined in the Parkes district since the 1960s. However, its range may have extended to Deniliquin and in northern New South Wales over the same period. The breeding population was estimated at fewer than 5,000 pairs in the early 1990s and, owing to a likely decline, was thought to number c.6,500 mature individuals in 2000. It is suspected that the population continues to decline. Variation in the recorded abundance of the species, due to its movements, may mask population trends, and compounds the reliability of population estimates6. High local and temporal abundance may indicate movements in response to habitat deterioration, rather than the recovery of populations6. The South-West Slopes of New South Wales appear to have become the most important area for the species, perhaps as habitat in other areas deteriorates6.
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Range

Native to eastern inland New South Wales, parts of the Australian Capital Territory, and north-central Victoria, Australia (7). Populations migrate northward during the non-breeding season in winter (5), although some birds remain in their breeding areas (7).
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
It nests in the New South Wales and Victorian Riverina in loose colonies in riparian woodland of river red gum Eucalyptus camaldulensis and forages in box woodland. On the slopes of the Great Dividing Range, it forages and nests in box-gum woodland, preferring highly modified, open habitat such as scattered paddock trees on private agricultural land2,5. Nesting birds on the South-West Slopes show clear preferences for Blakely's red gum trees E. blakelyi, dead and aging trees in general, and larger trees, as all of these factors are correlated with the presence of suitable nest hollows2. The species also shows a preference for lower elevations in this area, which are dominated by agriculture5, in contrast to the poorer soils and lower temperatures of higher elevations6. In the Riverina, it feeds on the seeds of herbaceous plants, switching to lerp, mistletoe berries, eucalypt flowers and grass seed in winter, and forages up to 15 km from the nest. In contrast, it appears that the most important habitats for breeding birds on the South-West Slopes are within 3 km of nest-sites5.

Systems
  • Terrestrial
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Habitat

In Victoria and parts of New South Wales, populations nest in riverine eucalypt woodland dominated by red gum (Eucalyptus camaldulensis) and forage in box woodland, whilst those on the slopes of the Great Dividing Range in New South Wales forage and nest in box woodland (4) (5).
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Life History and Behavior

Life Expectancy

Lifespan, longevity, and ageing

Maximum longevity: 15.1 years (captivity) Observations: One specimen lived 15.1 years in captivity (Brouwer et al. 2000).
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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Polytelis swainsonii

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 0
Species: 2
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
C2a(ii)

Version
3.1

Year Assessed
2008

Assessor/s
BirdLife International

Reviewer/s
Taylor, J., Butchart, S., Dutson, G., Garnett, S.

Contributor/s
Weston, M., Manning, A., Tzaros, C.

Justification
This species has a small population that has been declining for over a century, primarily owing to loss, degradation and fragmentation of habitat from agricultural clearance. It is therefore classified as Vulnerable.

History
  • 2007
    Vulnerable
  • 2004
    Vulnerable
  • 2000
    Vulnerable
  • 1996
    Vulnerable
  • 1994
    Vulnerable
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Status

Classified as Vulnerable (VU) on the IUCN Red List 2006 (1) and listed on Appendix II of CITES (3).
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Population

Population
The species's population has been estimated at c.6,500 mature individuals (Garnett and Crowley 2000).

Population Trend
Decreasing
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Threats

Threats

Major Threats
Range contraction is largely the result of clearing for agriculture. Decreases in the species's abundance are linked to land clearing that does not leave scattered trees in the landscape6. Remaining habitat is often fragmented, with feeding and breeding habitats divided. Regeneration is commonly prevented by high grazing levels by stock and rabbits or inappropriate fire regimes. Scattered box-gum woodland is threatened by limited regeneration, rural tree dieback, removal of trees and firewood collection6. In breeding areas the majority of nest trees are often on private land, with scattered paddock trees in mixed agricultural land of vital importance on the South-West Slopes. Nest-site fidelity means that birds continue to use traditional breeding sites despite habitat loss and degradation4. Many nest trees are dead, particularly on inland slopes, and have no replacements when they fall or are cut for firewood, potentially resulting in competition with other species, particularly the Common Starling Sturnus vulgaris. There are limited provisions for the protection of dead trees, and due to continued illegal removal and natural loss of old trees a decline in nest site availability is inevitable2. In areas of low occupancy, the availability of food in the breeding season, and not that of nest hollows, may limit population size4. In the Riverina, altered flooding regimes may compromise the health and extent of riparian woodlands where this species nests1. Illegal trapping occurs, but is a far less significant threat than habitat loss. Birds are also killed on roadsides and possibly suffer from pesticide poisoning. The abundance and distribution of the species appears to be affected by changes in plant productivity, as influenced by climate6. It is therefore susceptible to climate change and its interaction with fragmentation6.
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Threats

The superb parrot's population has been declining for over a century, largely as a result of habitat loss and deforestation, particularly of box woodlands, for farming and grazing purposes and urban development (4) (8) (9). Regeneration is often prevented due to high levels of grazing by livestock and rabbits or inappropriate fire regimes (4). It takes a gum tree about 100 years to develop tree hollows, which the parrots need to nest in (8). When the dead trees, which often provide the hollows needed for nesting, fall or are cleared for firewood, there may be no replacements (4) (6). Furthermore, the superb parrot must compete with feral bees and native and exotic hollow-nesting birds for what few tree hollows remain (10). Additional, but less significant, threats include illegal trapping, road mortality as the birds feed on grain spills, and possibly pesticide poisoning (4) (8).
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Management

Conservation Actions

Conservation Actions
Conservation Actions Underway
CITES Appendix II. All populations were surveyed in the 1980s, and regular surveys of Barmah State Forest and along Murray, Murrumbidgee and Edward Rivers have been instigated. Annual community-based surveys occur in northern Victoria and southern New South Wales1. Guidelines have been developed for forestry in riparian breeding habitat, but these have sometimes been inadvertently ignored.

Conservation Actions Proposed
Refine monitoring techniques. Extend surveys of nest trees. Determine the extent of trade. Protect all known breeding and feeding habitat from clearance, including scattered paddock trees on private agricultural land7. Reduce firewood collection. Promote good habitat management and revegetation on private land5. Coordinate land management on the scale of landscapes and centuries2, and involve all stakeholders5. Develop regional operations groups. Research the potential benefits of nest boxes2. Conduct research into methods of regenerating scattered trees5 and develop grazing regimes suitable for eucalypt regeneration2. Initiate research into population demography and communal behaviour4. Research importance of woodland, and potential new plantings, adjacent to breeding sites, and relationship to mortality of immatures4. Conduct research on local and landscape-scale movement patterns7. Study nest-site fidelity7. Carry out further investigations into, and monitoring of, the effects of climate variation on the species's abundance and distribution and the interaction with habitat loss and modification7.

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Conservation

Regular surveys are conducted in much of the superb parrot's range (4), and an Action Plan has been developed for the species (7). Forestry operations in riparian breeding habitat have also been given guidelines to help conserve the species, but these have sometimes been ignored (4).
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Wikipedia

Superb Parrot

A juvenile in a pet shop. Note brown iris

The Superb Parrot (also known as Barraband's Parrot, Barraband's Parakeet, or Green Leek Parrot),[1][2][3] (Polytelis swainsonii) is a parrot native to southeastern Australia. It is a monomorphic species and one of three species in the genus Polytelis.

The Superb Parrot is mostly bright green with darker flight feathers and is about 40 cm (16 in) long with a long pointed tail. Adult males have continuous yellow foreheads, and throats, with a red horizontal band across the border of the throat.

Contents

Taxonomy

First described by French naturalist Desmarest in 1826, the Superb Parrot, a monomorphic species,[4] is one of three species in the genus Polytelis of long-tailed parrots. Common names include Superb Parrot and, in avicultural circles, Barraband's Parrot or Parakeet,[5] or Green Leek (although the last is applied to several unrelated species).[6] Its closest relative is the Regent Parrot.[citation needed]

Description

The Superb Parrot is a medium-sized bright green parrot, approximately 40 cm (16 in) long, with long tail feathers, yellow-green below and yellow-orange irises. The adult male has a scarlet band upper chest, bright yellow face and throat. The adult female has a pale blue-green face, greyish-green throat, a variable tinged russet-pink fore-throat, and orange thighs. Juveniles have brown irises and otherwise resemble females.[7] The male has adult coloured plumage at the age of about one year.[2]

Distribution and habitat

An Australian endemic, the Superb Parrot is restricted to the dry (sclerophyll) woodlands of New South Wales and Victoria. There is estimated to be 6500 adult individuals in the wild.[8]

Behaviour

It nests on hollow limb or a hole in a tree.During breeding season, small flocks of males often forage for food alone. Pairs may nest in a loose colonial system of as many as 6 pairs, so hens are in the neighborhood at this time. The diet consists mainly of eucalypt flowers, fruits, nectar and pollen. It consumes seeds and green heads of the Yellow Box (Eucalyptus melliodora).[9][10]

Conservation status

An adult male at Taronga Western Plains Zoo, Australia

International

Due to ongoing habitat loss in Australia, small population size and limited range, the Superb Parrot is evaluated as Vulnerable on the IUCN Red List of Threatened Species.[1] It is listed on Appendix II of CITES.

Australia

Superb Parrots are listed as vulnerable on the Australian Environment Protection and Biodiversity Conservation Act 1999. Their conservation status also varies from state to state within Australia; for example, the Superb Parrot is listed as threatened on the Victorian Flora and Fauna Guarantee Act (1988).[11] Under this Act, an Action Statement for the recovery and future management of this species has been prepared.[12]

Threatening processes

During February–June 2005, logging in the Barmah State Forest destroyed 60 per cent of the nesting colonies of the Superb Parrot (6000 tonnes of river red gums): with fewer than 150 breeding in Victoria this has severely compromised their chances of survival.[13][14]

In December 2008, dozens of reports were filed of Superb Parrots being hit by cars.[15] NPWS wildlife officials speculated that the parrots had gorged on grain spilled from an uncovered truck and became unable to move, eventually being hit by automobiles.

References

  1. ^ a b c BirdLife International (2008). Polytelis swainsonii. In: IUCN 2008. IUCN Red List of Threatened Species. Downloaded on 18 March 2009.
  2. ^ a b Juniper, Tony; Parr, Mike (1998). Parrots; A Guide to Parrots of the World. Pica Press. Chapter 121: Superb Parrot. ISBN 1-873403-40-2. 
  3. ^ Alderton, David (2003). The Ultimate Encyclopedia of Caged and Aviary Birds. London, England: Hermes House. p. 187. ISBN 1-84309-164-X. 
  4. ^ "Zoological Nomenclature Resource: Psittaciformes (Version 9.020)". www.zoonomen.net. 2009-03-05. http://www.zoonomen.net/avtax/psit.html. 
  5. ^ Lendon, p. 117
  6. ^ Lendon, p. 114
  7. ^ Forshaw, Joseph M. (2006). Parrots of the World; an Identification Guide. Illustrated by Frank Knight. Princeton University Press. plate 51. ISBN 0-691-09251-6. 
  8. ^ "BirdLife Species Factsheet - Polytelis swainsonii". BirdLife International. 2008. http://www.birdlife.org/datazone/species/index.html?action=SpcHTMDetails.asp&sid=1456&m=0. 
  9. ^ Lendon, p. 116
  10. ^ David Alderton, Birds of the World p. 426
  11. ^ List of threatened fauna on the FFG Act, Department of Sustainability and Environment, Victoria
  12. ^ List of Approved Action Statements, Department of Sustainability and Environment, Victoria
  13. ^ Minchin, Liz (2005-08-06). "Blunder gives loggers wrong area, rare parrot loses nesting trees". The Age (Melbourne): p. 11. 
  14. ^ "Homeless Parrots in the Fire logging has been taking place in the Barmah forests for over 150years - they are what they are today as a result of Forest management - logging increases the health of the forest and reduces the risk of fire - therefore increasing the health of all fauna that live there.". http://www.melbourne.foe.org.au/news/news16_barmahbreach.htm. 
  15. ^ Sydney Morning Herald. Gorged Parrots at Risk (bottom of page). Retrieved December 31, 2008.

Cited text

  • Lendon, Alan H. (1973). Australian Parrots in Field and Aviary (2nd. ed). Sydney: Angus and Robertson. ISBN 0-207-12424-8. 
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