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Petroica traversi 

Scope: Global
Language: English
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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Passeriformes Petroicidae

Scientific Name: Petroica traversi (Buller, 1872)
Common Name(s):
English Black Robin, Chatham Island Black Robin, Chatham Islands Robin, Chatham Robin
Taxonomic Source(s): Turbott, E.G. 1990. Checklist of the Birds of New Zealand. Ornithological Society of New Zealand, Wellington.
Identification information: 15 cm. Small, pure black bird. Plumage of sexes alike, but female slightly smaller. Short, slender, black bill. Voice Male song simple phrase of 5-7 notes. Call notes are distinct and full.

Assessment Information [top]

Red List Category & Criteria: Endangered D ver 3.1
Year Published: 2016
Date Assessed: 2016-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Contributor(s): Aikman, H., Houston, D., Kennedy, E., Merton, D., O'Connor, S. & Massaro, M.
Facilitator/Compiler(s): Benstead, P., Khwaja, N., Mahood, S., McClellan, R., Taylor, J., Temple, H., Symes, A. & Stringer, C.
Justification:
In 1980, this robin had the smallest population of any bird species for which precise figures were known and it seemed doomed to extinction. Its spectacular recovery, following intensive management, is a renowned conservation success worldwide. Although numbers continue to increase, it still has a very small population and is therefore classified as Endangered.

Previously published Red List assessments:

Geographic Range [top]

Range Description:Petroica traversi is endemic to the Chatham Islands, New Zealand. It declined rapidly during the late 1800s, and by 1980 the population had fallen to five birds, comprising two males and three females. A convalescent pedigree confirms that all birds alive today are descendants from a single breeding pair (Old Blue and Old Yellow). Intensive management by the New Zealand Wildlife Service (later Department of Conservation) has resulted in a continuous increase in numbers: from seven adults pre-breeding in 1981 (12 post-breeding), to 93 in 1990 (128 birds post-breeding), 142 in 1995 (200 post-breeding) and 197 adults in 1998 (270 individuals post-breeding) (Kennedy 2009). The population is now restricted to Mangere (1 km2) and Rangatira (= South East, 2 km2) islands. Intensive monitoring of the species by the Department of Conservation was ceased in 1998.
Countries occurrence:
Native:
New Zealand
Additional data:
Estimated area of occupancy (AOO) - km2:3Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:29
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:2Continuing decline in number of locations:No
Extreme fluctuations in the number of locations:No
Upper elevation limit (metres):280
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:Full population surveys in Oct-Nov 2011 found 200 mature individuals on Rangatira Island, and 39 on Mangere Island (Massaro et al. 2013a). During the 2015 pre-breeding census (Oct-Nov), 246 adult birds were counted on Rangatira (M. Massaro, unpublished data) and 43 birds on Mangere (T. Bliss, unpublished data, Department of Conservation).

Trend Justification:  Intensive conservation efforts boosted population sizes rapidly between 1980 and 1989 only. After intervention ceased, population sizes increased naturally though at a slower rate.. The most recent population estimate is higher than any since the population bottleneck of 1980 (E. S. Kennedy in litt. 2012).
Current Population Trend:Increasing
Additional data:
Number of mature individuals:230Continuing decline of mature individuals:No
Extreme fluctuations:NoPopulation severely fragmented:Yes
No. of subpopulations:2Continuing decline in subpopulations:No
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No
No. of individuals in largest subpopulation:1-89

Habitat and Ecology [top]

Habitat and Ecology:The species lives in low-altitude forest remnants. It is entirely insectivorous, and feeds on the forest floor and low branches. It usually lays two eggs, and re-lays if a clutch is lost. Young normally begin to breed at one year of age (Kennedy 2009). Survivorship under natural conditions between 1990 and 1998 indicates mean life-expectancy of 4.2 years for males, and 3.74 for females (both means are lower than for the intensively managed years, though not by much for males; Kennedy 2009). Some individuals may live up to 16 years. A recent study investigating pair distribution across the forested habitat on Rangatira Island shows that black robins prefer lower elevations (Chick, Kennedy and Massaro, in review). The underlying drivers causing this skewed distribution are currently being studied.
Systems:Terrestrial
Continuing decline in area, extent and/or quality of habitat:Unknown
Generation Length (years):7
Movement patterns:Not a Migrant

Threats [top]

Major Threat(s):

The introduction of rats Rattus spp. and cats, following human settlement, extirpated the birds from all but Little Mangere Island (Butler and Merton 1992). Since black robins are insectivores feeding mainly on the ground and have not evolved any anti-predator behaviours, they cannot co-exist with invasive mammalian predators. Any accidental introduction of mammalian predators to the islands where the species currently survives will cause extinction on the island. Introduced Common Starlings Sturnus vulgaris, which now number over 1,000 pairs on Rangatira, are a serious threat to black robin reproduction (Massaro et al. 2013a). Black robins nesting in cavities experienced a significantly higher rate of predation (36.33%) than open nesters (10.82%) (Massaro et al. 2013a). Nest height also influenced predation, with predation risk increasing from 4.88% for nests below 1 m to 31.89% for nests above 3 m (Massaro et al. 2013a). A potential future threat to this highly inbred species is the arrival of new pathogens. Fire, catastrophic storm events and natural processes of forest recovery, exacerbated perhaps by climate change, are key extrinsic threats to habitat quality and extent. For example, severe storms in the winter of 2015, caused higher than normal winter mortality rates, especially for males in the Top Bush. The extensive loss of genetic diversity through genetic drift and chronic inbreeding since the severe population bottleneck in 1980, compromises reproductive output and juvenile survival (Massaro et al. 2013b; Kennedy et al. 2014; Weiser et al. 2016) and is threatening the long-term viability of this species.

Hybridisation with congeneric Chatham Island Tomtits P. macrocephala chathamensis remains a concern, although the probability of recurrence may be low. A recent paper has shown that there is no evidence of recent hybridisation with the sympatric Chatham Island Tomtit P. macrocephala chathamensis (Cubrinovska et al. 2016). The species remains susceptible to outright loss owing to stochastic events (E. S. Kennedy in litt. 2012).


Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
In 1976, following forest deterioration on Little Mangere Island, the seven surviving birds were relocated to Mangere Island. Prior to reintroduction, thousands of trees were planted to provide future habitat. In 1979, productivity failed to offset losses for the first time, and the population declined to five adults. In 1980-81, eggs and chicks were cross-fostered to the Chatham Island Warbler Gerygone albofrontata in order to induce Black Robin females to renest. Supplementary feeding commenced, along with protection of nests from seabirds and Common Starlings. The warblers proved unsuitable as foster-parents. In 1981-82, Old Blue’s eggs were cross-fostered to congeneric Tomtits P. macrocephala chathamensis on Rangatira Island. The chicks were returned to Mangere Island to assist future breeding there. Fostering to Tomtits proved successful, and in 1983 a permanent population of Black Robins was founded on Rangatira Island (E. S. Kennedy in litt. 2012). Intensive management ceased after 1989 (Heather and Robertson 1997). Annual monitoring of numbers, reproductive success and distribution within habitats continues in both island populations. Reforestation on both islands is on-going, and both island habitats are subject to strict quarantine measures to avoid introducing predators, pathogens and other threats. In 2014, 100 nest boxes were installed on Rangatira Island, to test whether a) nest boxes decrease starling predation on robin nests and b) the availability of nest boxes in the upper part of the bush on Rangatira Islands will increase densities of pairs in Top Bush. This study is ongoing (M. Massaro, in litt. 2016). A recent study investigating genetic diversity and differentiation in the two island populations has shown that a) genetic diversity is very low in both populations and b) that due to strong genetic drift genetic differentiation between the two populations has taken place (Forsdick et al. in review). Reciprocal translocations between the two islands are currently being considered.
Conservation Actions Proposed
Continue to monitor population and demographic trends. Expand populations sizes through reforestation of Mangere Island and infill planting on Rangatira Island. Protect populations on Mangere and Rangatira Islands from biosecurity threats. Establish a third population within the Chatham Islands. Reintroduce birds to Little Mangere Island with landowners' support (H. Aikman in litt. 1999). Continue to work with landowners and Department of Conservation to provide safe habitat on Chatham Island.


Citation: BirdLife International. 2016. Petroica traversi. The IUCN Red List of Threatened Species 2016: e.T22704831A93987480. . Downloaded on 21 July 2018.
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