Procellaria parkinsoni 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Procellariiformes Procellariidae

Scientific Name: Procellaria parkinsoni Gray, 1862
Common Name(s):
English Black Petrel, Black (Parkinson's) Petrel, Black Petrel
Taxonomic Source(s): Turbott, E.G. 1990. Checklist of the Birds of New Zealand. Ornithological Society of New Zealand, Wellington.
Identification information: 46 cm. Large, black petrel, becoming more brown as plumage ages. Undersides of primaries may appear silvery. Yellow-white bill on adults, blue-white on juveniles, has black tip. Black legs, feet. Similar spp. Smallest Procellaria species. Smaller, especially bill, than Westland Petrel P. westlandica and has less laboured flight. Large, all-dark Flesh-footed Shearwater P. carneipes have pink feet and distinctive flight. Voice Varied calls at colony after dark.

Assessment Information [top]

Red List Category & Criteria: Vulnerable D2 ver 3.1
Year Published: 2017
Date Assessed: 2016-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Contributor(s): Bell, E., Debski, I., Taylor, G.A. & Weeber, B.
Facilitator/Compiler(s): Anderson, O., Bird, J., Black, A., Calvert, R., Martin, R, Moreno, R., Small, C., Symes, A., Taylor, J.
This species qualifies as Vulnerable because it breeds on just two very small islands where introduced predators are a potential threat. The population is assumed to be stable, but if a decline is detected, the species should be uplisted to Endangered.

Previously published Red List assessments:

Geographic Range [top]

Range Description:

Procellaria parkinsoni breeds on Great and Little Barrier Islands, New Zealand, where the populations number c.880 pairs (in the 35-ha study site) and 620 pairs respectively (E. A. Bell et al. 2016a,b). It once bred in the mountains of the North and South Islands, but had disappeared from the mainland by the 1960s. On Little Barrier, it was abundant in the late 1800s but the population was decimated, mainly by feral cats, until predators were eradicated in 1980. The trend obtained from census grid data for Great Barrier Island estimated a population growth rate between -2.3% and 2.5% per year, depending on juvenile annual survival. Assuming a juvenile annual survival rate of 88%, the population growth rate was estimated to be -1.1% per year (Bell et al. 2014). Nevertheless, there is considerable uncertainty in the model and further research is needed to clarify the population trend. It migrates to the eastern Pacific Ocean between the Galápagos Islands, southern Mexico and northern Peru (Heather and Robertson 1997).

Countries occurrence:
Australia; Colombia; Cook Islands; Costa Rica; Ecuador; Fiji; French Polynesia; Mexico; New Caledonia; New Zealand; Nicaragua; Niue; Panama; Peru; Tonga
Present - origin uncertain:
El Salvador; French Southern Territories; Kiribati
Additional data:
Estimated area of occupancy (AOO) - km2:70Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:54300000
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:2Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:No
Upper elevation limit (metres):726
Range Map:Click here to open the map viewer and explore range.

Population [top]


There are c.880 pairs in the 35-ha study site of Great Barrier Island and 620 pairs in Little Barried Island (E. A. Bell et al. 2016a,b). A recent assessment of the whole population derived from band recoveries from fisheries bycatch estimates 2750 breeding pairs and 11,000 individuals (Richard and Abraham 2015).

Trend Justification:  

The trend obtained from census grid data for Great Barrier Island estimated a population growth rate between -2.3% and 2.5% per year, depending on juvenile annual survival. Assuming a juvenile annual survival rate of 88%, the population growth rate was estimated to be -1.1% per year (Bell et al. 2014).Nevertheless, there is considerable uncertainty in the model and further research is needed to clarify the population trend.

Current Population Trend:Stable
Additional data:
Number of mature individuals:5500Continuing decline of mature individuals:Unknown
Extreme fluctuations:NoPopulation severely fragmented:No
No. of subpopulations:2Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No

Habitat and Ecology [top]

Habitat and Ecology:

Behaviour It is a colonial burrow-nesting, annually-breeding species (ACAP 2009). Most eggs are laid in mid-November/late-December, hatch in late January/February and chicks fledge in May/June at about three months old. Chick provisioning can continue until June (Bell et al. 2009). The youngest recorded bird returning to a colony was two years of age, and the age of first breeding has been recorded at four years of age (Bell et al. 2016a). Feeding behaviour is characterised by surface feeding and shallow diving in groups of up to 300 individuals that are frequently seen to associate with fishing vessels and cetaceans. Black petrels have been recorded diving up to 34 m, but over 85% of all dives were less than 5 m and over 90% were during the day (Bell 2016). Preliminary geolocator data suggest that it preferentially forages on the continental shelf or at seamounts (ACAP 2008), with most foraging trips taking at least 15 days (Bell et al. 2009). Further data suggest foraging areas are highly variable, although birds travel mainly west and east of northern New Zealand (Bell et al. 2009). Habitat Breeding It nests in virgin podocarp and mixed broadleaf forest above 500 m. On the mainland, it reportedly bred up to 1,200 m, mostly in tall forest, but also in alpine tussock grasslands (Marchant and Higgins 1990). Diet Its diet is dominated by squid and supplemented by tunicates, crustaceans and cyclostomes (Bell et al. 2009). 

Systems:Terrestrial; Marine
Continuing decline in area, extent and/or quality of habitat:No
Generation Length (years):34
Movement patterns:Full Migrant
Congregatory:Congregatory (and dispersive)

Threats [top]

Major Threat(s): Introduced cats decimated the Little Barrier population, killing up to 100% of fledglings in some years (Imber 1987), and taking adults. Introduced cats cause minor interference on Great Barrier, but breeding success is high (77% in 2007/2008) (Bell et al. 2011). Pacific rat Rattus exulans is present on Great Barrier Island but has little effect on this species. Pacific rats were eradicated from Little Barrier Island in 2004. Black rat R. rattus, stray dogs, feral cats and feral pigs may also be a threat on Great Barrier. The species is a common scavenger of fishing boat waste, and is caught by commercial longliners and recreational fishers, and may be at greater risk during migration to the east Pacific off Ecuador and Peru where it is a near-obligate associate of small crustaceans (Pitman and Ballance 1992). El Niño fluctuations may also affect the population in this zone (Taylor 2000). The species is potentially threatened by climate change because it has a geographically bounded distribution: its altitudinal distribution falls entirely within 1,000 m of the highest mountain top within its range (621 m) (BirdLife International unpublished data).

Conservation Actions [top]

Conservation Actions:

Conservation Actions Underway
CMS Appendix II and ACAP Annex 1. Cats were eradicated on Little Barrier Island by 1980. Between 1986 and 1990, 249 fledglings were transferred from Great Barrier to Little Barrier in an attempt to boost population size. Follow-up monitoring indicates mixed results (Imber et al. 2003). The population on Little Barrier has been studied since 2014/15 (Bell et al. 2016b). A long-term population study was initiated on Great Barrier in 1996 to study populations annually to determine trends and assess breeding success (Taylor 2000, Bell et al. 2007). Tracking research has been completed on both Little Barrier and Great Barrier (E. Bell in litt. 2012). Feral cat trapping was undertaken on Great Barrier Island in 2011/2012 and is scheduled to continue in future breeding seasons, along with a rodent control programme (per E. Bell in litt. 2012). Rattus exulans was eradicated from Little Barrier in 2004 (E. Bell in litt. 2012).

Conservation Actions Proposed
Complete an accurate census of Little Barrier Island. Monitor Great Barrier study populations annually to determine trends, and assess breeding success. Monitor the effectiveness of increased mitigation application in the main fisheries threat in NZ from bottom longlining through electronic monitoring project. (Black Petrel Working Group, 2016). Continue and expand control at Great Barrier if monitoring indicates that any predators are causing a population decline (Taylor 2000). 

Amended [top]

Amended reason: Edited: Geographic Range, Elevation Upper Limit, Countries of Ocurrence, Trend justification, Habitats and Ecology, Generation Length, Continuing Decline in Habitat, Threats, Conservations Actions.The estimated number of mature individual were altered. Added references and also a new Facilitator.

Citation: BirdLife International. 2017. Procellaria parkinsoni (amended version of 2016 assessment). The IUCN Red List of Threatened Species 2017: e.T22698150A111472389. . Downloaded on 18 August 2018.
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