Overview

Distribution

Range

Forests of Guam (s Mariana Islands). On verge of extinction.
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Range Description

Gallirallus owstoni is endemic to Guam (to USA), where it was widely distributed until 1968 when, along with most other indigenous species, it started to decline4. In 1981, the population was estimated at c.2,000, in 1983 it was reckoned to number fewer than 100 and, by 1987, it was extirpated from the wild9. It survives in captive-breeding facilities in Guam and in 14 zoos in the USA (c.180 birds in total)1. It was reintroduced to Guam in 1998 but a rapid population decline was observed during 2000-2002 and no rails have been detected since, either in the predator free zone (Area 50, 24 hectares) or the snake reduced open landscape10. From 1989-2007 853 captive reared rails were released on nearby Rota, Northern Mariana Islands (to USA), though this has experienced mixed success, with some populations rapidly declining to extinction, there is currently an expanding population of 40-60 individuals in the Duge area and another of 20 birds at Apanon10.
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Historic Range:
Western Pacific Ocean_U.S.A. (Guam)

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
This flightless species was widely distributed in most habitats on Guam, including forest, savanna, scrub, secondary grassland, fern thickets and agricultural areas5 (but not in freshwater wetland habitats8). It foraged along field edges and roadsides (never far from cover) for snails, slugs, insects, geckos, vegetable matter, seeds and flowers from low grasses and shrubs, and also the introduced giant African snail Achatina fulica which became an important part of the diet7. It breeds throughout the year (birds attaining sexual maturity at four months) with a peak period during the rains in July-November2. Nests are located on dry ground in dense grass, and clutch-size is 1-4, usually 3-47.

Systems
  • Terrestrial
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Molecular Biology and Genetics

Molecular Biology

Statistics of barcoding coverage: Gallirallus owstoni

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 0
Specimens with Barcodes: 3
Species With Barcodes: 1
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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
EW
Extinct in the Wild

Red List Criteria

Version
3.1

Year Assessed
2010

Assessor/s
BirdLife International

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

Contributor/s
Wiles, G., Amidon, F., Lepson, J., Wenninger, P.

Justification
The last individual in the wild of this species died in 1987 following catastrophic declines owing to predation by the introduced brown tree-snake. A captive population survives in a snake-proof enclosure, and it breeds well in captivity. It remains classified as Extinct in the Wild until an introduced population becomes firmly established.

History
  • 2008
    Extinct in the Wild
  • 2004
    Extinct in the Wild
  • 2000
    Extinct in the Wild
  • 1996
    Extinct in the Wild
  • 1994
    Extinct in the Wild
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Current Listing Status Summary

Status: Endangered
Date Listed: 04/11/1984
Lead Region:   Pacific Region (Region 1)   
Where Listed: except Rota

Status: Experimental Population, Non-Essential
Date Listed: 10/30/1989
Lead Region:   Pacific Region (Region 1)   
Where Listed: Rota


Population detail:

Population location: Entire, except Rota
Listing status: E

Population location: Rota
Listing status: EXPN

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

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Threats

Major Threats
Its decline and extinction in the wild is the result of predation by the introduced brown tree snake Boiga irregularis6. Reasons for the failure of some of the introduction attempts on Rota are not known, but predation by feral cats was responsible for the failure of the reintroduction attempts on Guam10.
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Management

Conservation Actions

Conservation Actions
Conservation Actions Underway
Captive breeding started in 1984. Since 1987, efforts have been under way to establish a self-sustaining, experimental population on the nearby snake-free island of Rota2. In 1999, birds bred there for the first time1; birds have since been released at four sites and success has been mixed10. In late 1998, some captive-reared birds were released in northern Guam, into a small area (24 ha) protected from snakes by a barrier and trapping, and though these birds were breeding1, this population is now extinct10.

Conservation Actions Proposed
Continue the captive-breeding programme. Control B. irregularis in additional areas on Guam so that more introductions can take place1. Continue to manage the released populations on Rota to maximise the retention of the species's genetic diversity1. Implement stringent measures to prevent the spread of B. irregularis from Guam to Rota. Before considering another reintroduction to Guam, control feral cats.

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Wikipedia

Guam Rail

The Guam Rail (Gallirallus owstoni) (Chamorro name: Ko'ko' [2]) is a flightless bird, endemic to the United States territory of Guam. The Guam Rail disappeared from southern Guam in the early 1970s and was extirpated from the entire island by the late 1980s. This species is now being bred in captivity by the Division of Aquatic and Wildlife Resources on Guam and at some mainland U.S. zoos. Since 1995, more than 100 rails have been introduced on the island of Rota in the Commonwealth of the Northern Mariana Islands in an attempt to establish a wild breeding colony. Although at least one chick resulted from these efforts, predation (largely by feral cats) and accidental deaths have been extremely high. A small number of birds potentially persists.

Nine of the 11 species of native forest-dwelling birds have been extirpated from Guam. Five of these were endemic at the species or subspecies level and are now extinct on Guam. Two of these species, the Guam Rail and the Micronesian Kingfisher, are being captively bred in zoos in the hope that they can eventually be released back into the wild. Several other native species exist in precariously small numbers, and their future on Guam is perilous. Most native forest species, including the Guam rail, were virtually extinct when they were listed as threatened or endangered by the U.S. Fish and Wildlife Service in 1984.

A recent effort to introduce rails on Guam in a 22 hectare forested area concentrated on protecting the rails by limiting snakes using a combination of trapping and a perimeter barrier to reduce re-invasion by snakes. This endeavor allowed the tentative survival of several pairs of rails released into the area. Reproduction by the rails was reported in this control area on the basis of sounds attributed to chicks. The preliminary success constitutes one of the few bright spots in the conservation of Guam's native fauna in recent years and speaks to future opportunities to recover wildlife. [1]

Background

Beginning in the mid-1960s, the Brown tree snake decimated Guam's native avifauna. The birds of Guam evolved in the absence of snake predators. They had no experience with such a predator and lacked protective behaviors against the snake. Consequently, they were easy prey for these efficient, nocturnal predators. As the snakes spread across the island, the number of snakes began to grow exponentially and bird populations plummeted.

The history of this decline starts shortly after the introduction of the Brown tree snake, although appreciable losses were not evident until the 1960s. By 1963, several formerly abundant species of native birds had disappeared from the central part of the island where snakes were most populous. By the late 1960s, birds had begun to decline in the central and southern parts of the island and remained abundant only in isolated patches of forest on the northern end of the island. Snakes began affecting the birds in the north-central and extreme northern parts of the island in the 1970s and 1980s, respectively.

Zoologist Bob Beck, a Guam Department of Agriculture Division of Aquatic and Wildlife Resources wildlife supervisor, is credited with leading the efforts to capture the remaining wild Guam rails, Micronesian Kingfishers and other native birds to save them from extinction.[2] His efforts to save the Guam rail began in 1982 and lasted more than 20 years.[2] Beck was considered to be instrumental in capturing the remaining population of Guam rails and establishing captive breeding programs for the species on Guam.[2] He later established a release site and an introduced breeding population of Guam rails on the neighboring island of Rota in the Northern Mariana Islands.[2]

Beck was also a driving force in establishing Guam rail breeding programs in zoos throughout the mainland United States.[2] Beck's Guam rail breeding program initially began with just three zoos in the U.S. - the Bronx Zoo, the Philadelphia Zoo and the National Zoo in Washington, D.C.[2] The program proved to be successful and was soon expanded to include other zoos. Seventeen zoos now participate in the Guam rail breeding program, as of 2008,[2] including the Audubon Zoo in New Orleans, the San Diego Zoo, the Santa Fe College Teaching Zoo, and zoos in Chicago, Houston and San Antonio.[2]

The efforts by Beck, and others, to save the Guam rail have been promising. There are now approximately 120 Guam rails in captivity in Guam and approximately 35 birds in captive breeding programs throughout the United States.[2] Biologist Gary Wiles, who worked on the Guam rail breeding program from 1981 through 2000, said of Beck's efforts to save the Guam rail, "Bob was one of the first to begin organizing catching the birds so they could be brought into captivity, held there and bred. He started a captive population. We still have Guam rails today because of his efforts."[2] Suzanne Medina, a wildlife biologist, also credited Beck with saving the Guam rail, "Bob Beck was the ko'ko' champion, was Guam's champion at the time for preventing the extinction of these birds."[2]

References

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