Although this species has a stable population, habitat changes are still occurring through continued, although much reduced, erosion and vegetation regeneration as a result of herbivore control. It qualifies as Endangered because breeding is restricted to just two colonies which may be losing burrows.
Brooke, M. de L. 2004. Albatrosses and Petrels Across the World. Oxford University Press, Oxford.
Christidis, L.; Boles, W. E. 2008. Systematics and taxonomy of Australian birds. CSIRO Publishing, Collingwood, Australia.
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.
Turbott, E. G. 1990. Checklist of the birds of New Zealand. Ornithological Society of New Zealand, Wellington.
Distribution and populationPuffinus huttoni
38 cm. Medium-sized shearwater, generally black above and white below. Uniform blackish-brown upperparts, merging at side of head below eye to whitish chin, throat. Mostly dull white underparts with brownish sides to breast, thigh patches. Greyish underwing, darker brown at trailing edge. Similar spp. Difficult to distinguish from Fluttering Shearwater P. gavia. Typically, P. huttoni has longer bill, greyer chin, throat, lateral undertail-coverts, blacker upperparts. P. gavia has sharper demarcation of dark side of head and white throat. Voice Generally quiet at sea. Noisy in flight and on ground at colony.
breeds in the Seaward Kaikoura Range, north-east South Island, New Zealand
. The population comprises two main colonies (Kowhai Valley and Shearwater Stream), sited 10-18 km inland. These were estimated to consist of c.125,000 and c.10,000 pairs (Sherley 1992), but reworking of the original data indicated c.94,000 pairs is more accurate (Taylor 2000). More recently Sommer et al.
(2009) reported 106,000 pairs at Kowhai and 8,000 pairs at Shearwater Stream. The total population is estimated to number 300,000-350,000 individuals (Brooke 2004). Numbers and distribution within the Kaikoura Ranges have decreased, with 8 of 10 known colonies having been extirpated this century (Cuthbert 1999). Six out of eight colonies discovered in the high Kaikoura mountains were extirpated by pigs, and feral pigs remain a potential threat the remaining two colonies (Harrow 2009). Since the rapid extirpation of colonies was detected, work has been underway to establish a third population on the Kaikoura peninsula through the translocation of 290 chicks (Anon 2007, Ombler 2010), and predator-proof fencing was introduced in 2010. Individuals have been returning since 2008 (Ombler 2010). For many years this species has been considered to be in a long-term decline (Sherley 1992, Heather and Robertson 1997), but a major study has indicated that the population was stable from at least 1990-2000 (Taylor 2000). Recent evidence even points to a long-term increase in the population for the Kowhai Valley, at an annual rate of 1.7% over the last 20 years, based on burrow density (Sommer et al.
2009). In the non-breeding season birds migrate to waters off southern, western and north-western Australia (Heather and Robertson 1997). Population justification
Cuthbert and Davis (2002) estimated 106,000 breeding pairs, and Brooke (2004) estimated a total population of 300,000-350,000 individuals.Trend justification
This species has been in long-term decline, probably owing to predation by introduced predators and soil erosion brought about by grazing from introduced grazers (Sherley 1992, Heather and Robertson 1997, Brook 2004), and although the population has been stable since the 1990s (Taylor 2000), declines are still suspected over 59 years (three generations). Ecology
It digs its burrows on gentle to steep mountain slopes at 1,200-1,800 m, under tussock grass or low alpine scrubland (Marchant and Higgins 1990). First breeding is thought to occur at 4-6 years of age. It feeds mostly on small fish and krill (Heather and Robertson 1997). Birds gather food for chicks as far south as the Otago Peninsula and often fish around Banks Peninsula bays (Harrow 2009). Kapiti Island and Cook Strait are common feeding areas in the north and they have been recorded near the Chatham Islands (Harrow 2009). Frequently diving to feed at c.25 m, they have been recorded as deep as 36.6 m (Harrow 2009). Burrow occupancy levels in both original colonies in 2006/2007 was found to be similar to the 1990s. In contrast, breeding success in both main colonies was thought to be due to poor at-sea feeding conditions, rather than increases in stoat predation, due to a lack of evidence pointing to the latter (Sommer et al.
2009). Annual adult survival, breeding success, and burrow occupancy averaged 93%, 47% and 71%, respectively (Sommer et al.
2009). Low levels of breeding success, particularly at Shearwater Stream colony, point to the possibility of the colony levels being maintained by immigration from the more successful Kowhai Valley colony (Sommer et al.
Introduced stoats Mustela erminea
were thought to be the primary cause of decline (Sherley 1992, Heather and Robertson 1997). Long-term research, however, has indicated that only a very small proportion of adults is taken, and breeding success is not significantly affected (Cuthbert 1999, Cuthbert and Davis 2002). A more likely cause of current poor breeding success, and a potential threat to future population stability, is the availability of high quality prey at sea (Sommer et al.
2009). Modelling has demonstrated that colonies are most vulnerable to the loss of breeding adults and therefore maintaining high survivorship is paramount (Cuthbert et al.
2001). Habitat destruction and predation by feral pigs, along with heavy browsing by a range of introduced herbivores may have been the cause of the complete destruction of some subcolonies by erosion (Sherley 1992, Heather and Robertson 1997). Feral pigs and cats are considered the greatest potential threat, but are normally absent from the two remaining colonies (Cuthbert 1999, 2002; Taylor 2000), although it is likely that predation and habitat destruction by feral pigs may have been the key factor in the range contraction of the species in the past (Sommer et al.
2009). Heavy snowfall can crush burrows, and late snow cover can delay or prevent breeding. Birds are sometimes caught in set-nets and inshore longliners, and as many as 80 have been reported to be caught in a single net (Harrow 2009). The impact of long-term over-harvesting of some inshore fish species may be severe (Taylor 2000). The species is potentially threatened by climate change because it has a geographically bounded distribution: its altitudinal distribution falls entirely within 2,000 m of the highest mountain top within its range (2,885 m) (BirdLife International unpublished data). Conservation Actions Underway
On-going control of browsing animals has resulted in a substantial improvement in vegetation cover (Heather and Robertson 1997), and a decrease in the number of burrows destroyed by trampling. A long-term project to monitor threats, and another to study population dynamics, have been established, and are on-going (Taylor 2000). Pigs are controlled on the colony boundaries (Cuthbert 1999). A third population is being established on the Kaikoura Peninsula: 10 fledglings were transferred there in 2005, 80 in 2006, c.100 in 2007 and 100 in 2008 (Anon 2007, Ombler 2010). Conservation Actions Proposed
Census the population every five years using burrow plots and photopoints. Monitor focal burrows annually and correlate results with climatic and marine fluctuations. Commence nest protection if present research indicates predation is having a significant effect. Assess the impact of local fisheries on food availability (Taylor 2000). Re-establish colonies at accessible sites along the flight path (Cuthbert 1999).
Anon. 2007. New shearwater colony for Kaikoura. Forest and Bird: 10.
Brooke, M. De L. 2004. Albatrosses and petrels across the world. Oxford University Press, Oxford.
Cuthbert, R. J. 1999. The breeding ecology and conservation of Hutton's Shearwater (Puffinus huttoni). dissertation. Ph.D., University of Otago, Dunedin.
Cuthbert, R., Davis, L.S. 2002. Adult survival and productivity of Hutton's shearwaters. Ibis 144(3): 423-432.
Cuthbert, R., Fletcher, D. and Davis, L.S. 2001. A sensitivity analysis of Hutton's shearwater: prioritizing conservation research and management. Biological Conservation 100(2): 163-172.
Harrow, G. 2009. Another chance for Hutton's Shearwater. Southern Bird: 6.
Heather, B. D.; Robertson, H. A. 1997. The field guide to the birds of New Zealand. Oxford University Press, Oxford, UK.
Marchant, S.; Higgins, P. J. 1990. Handbook of Australian, New Zealand and Antarctic birds, 1: ratites to ducks. Oxford University Press, Melbourne.
Ombler, K. 2010. Shearwaters find a new home. Forest and Bird: 56.
Sherley, G. 1992. Monitoring Hutton's Shearwater 1986-1989. Notornis 39: 249-261.
Sommer, E.; Bell, M.; Bradfield, P.; Dunlop, K.; Gaze, P.; Harrow, G.; McGahan, P.; Morriset, M.; Walford, M.; Cuthbert, R. 2009. Population trends, breeding success and predation rates of Hutton's Shearwater (Puffinus huttoni): a 20 year assessment. Notornis 56(3): 144-153.
Taylor, G. A. 2000. Action plan for seabird conservation in New Zealand. Department of Conservation, Wellington.
Further web sources of information
Alliance for Zero Extinction (AZE) species/site profile. This species has been identified as an AZE trigger due to its IUCN Red List status and limited range.
Click here for more information about the Alliance for Zero Extinction (AZE)
Explore HBW Alive for further information on this species
Search for photos and videos, and hear sounds of this species from the Internet Bird Collection
Text account compilers
Anderson, O., Benstead, P., Calvert, R., Mahood, S., Martin, R, McClellan, R., Stattersfield, A. & Taylor, J.
IUCN Red List evaluators
Butchart, S., Symes, A.
BirdLife International (2016) Species factsheet: Puffinus huttoni. Downloaded from
http://www.birdlife.org on 26/09/2016.
Recommended citation for factsheets for more than one species: BirdLife International (2016) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 26/09/2016.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.
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