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Featuring ACAP-listed species and their photographers: Buller’s Albatross by Jean-Claude Stahl

 1 Solander May 2013 0459
A pair of non-breeding Buller’s Albatrosses preen on Solander Island, the female (left) devoting all her attention to a rather contented-looking male, May 2013

NOTE: This post continues an occasional series that features photographs of the 31 ACAP-listed species, along with information from and about their photographers.  Here, Jean-Claude Stahl writes on the globally Near Threatened Buller’s Albatross Thalassarche bulleri that he has studied and photographed over many years.

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Jean-Claude Stahl (right) and Dominique Filippi (Sextant Technology) at a sealers’ shelter on Solander Island; photograph by Michael Hall

Realistically, I have the French military service to thank for my involvement in albatross research.  My choice back in 1977 was between mud crawling on mock battlefields, or a civilian option to study King Penguins Aptenodytes patagonicus on the sub-Antarctic Crozet Islands.  I chose the latter after a nanosecond hesitation, unaware then that the penguin option would have its fair share of mud crawling.  Begging for more, I returned to the Crozets for two more seasons, with research undertaken on a community of 16 petrel species on East Island with Pierre Jouventin, Jean-Louis Mougin and Henri Weimerskirch.  We also undertook the first surveys of Penguin and Apostle Islands where we discovered new breeding localities of Indian Yellow-nosed Albatrosses T. carteri.

While roaming the penguin beaches on the main Possession Island (Île de la Possession), I got the attention of a rather exotic (to French eyes) visiting bird curator from the Museum of New Zealand, Sandy Bartle.  He invited me to his home country and museum; I went there “for a year” in 1986 and I still live in New Zealand.  I soon got involved in seabird research, briefly on the Auckland Islands with Graham Elliott and Kath Walker and more in-depth on Southern Buller’s Albatrosses T. b. bulleri with programme leader Paul Sagar of the National Institute of Water and Atmospheric Research (NIWA), with whom I have enjoyed working for many years.  The research programme was prompted by worries about interactions with fisheries when little was then known about the bird’s at-sea distribution.

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A two and half month-old Buller’s Albatross chick

Buller’s Albatross (known as Buller’s Mollymawk in New Zealand) is one of the smallest albatrosses.  The Southern nominate subspecies breeds only on the Snares Islands/Tine Heke (8700 pairs, 2002) and Solander Islands/Hautere (4900 pairs, 2002) south of New Zealand.  Northern Buller’s Albatrosses T. b. platei breed on the Chatham Islands east of New Zealand (17 500 pairs, 1970s) and the Three Kings Islands north of New Zealand (13 pairs, 1985).  Annually breeding Southern Buller’s Albatrosses start returning ashore in December and lay their single eggs in January-February. The egg hatches after 68-72 days, and chicks are reared for an average of 167 days through the southern winter, fledging mainly in August-September.  Northern Buller’s Albatross breeds about three months earlier.  Adults and chicks migrate to seas off Chile and Peru at the end of the breeding season.

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Paul Sagar in a Buller’s Albatross study colony under Subantarctic Tree Daisies on the Snares

During our shared stint of research, Paul Sagar concentrated on demography and the Snares some 100 km south of Stewart Island, complete with a cosy hut.  My focus was on the telemetry of foraging birds, and on a study colony on the Solander Islands, which the New Zealand Department of Conservation wishes to keep a wilderness (so no hut, although I sympathise with the policy).  Solander (1.6 km long, 33 m high) is the largest eroded remnant of an andesitic volcano, a bleak landmark some 40 km south of the Fiordland coast and 60 west of Stewart Island.  Hautere, the Māori name of the island, means “swift winds”, a rather apt description for an outpost close to the windiest weather station in New Zealand at South-west Cape.  Europeans first sighted the island in 1770, when Captain James Cook named them after Daniel Solander, the Swedish naturalist on Cook’s first voyage.  As did many southern islands, Solander had its share of sealing gangs and castaways, with one gang of five stranded there between 1808 and 1813, presumably plenty of time to hone their Buller’s Albatross recipes.  Solander is partly covered by “muttonbird scrub” Brachyglottis rotundifolia and Veronica elliptica scrub, below or adjacent to wind-blasted slopes of Poa foliosa and P. astonii tussock and a taller forest patch of Subantarctic Tree Daisies Olearia lyallii on the summit plateau and Brachyglottis stewartiae, more widespread and down to sea level on the Snares.

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The safest if horizontally challenged camping spot on Solander

Access to Solander is by permit only and after strict quarantine procedures by the Department of Conservation.  A helicopter can only land on the boulder beaches at low tide, and the first time we were left stranded was an eerie experience in misty weather, surrounded by fish bins of food and gear and hundreds of New Zealand Fur Seals Arctocephalus forsteri and desperately looking for a camping spot on the side of a pyramid.  Over time, we sampled various “promising” spots that turned out to be a waterfall base, a gravity-assisted boulder field, a seal haulout and a Weka Gallirallus australis playground, all accompanied by the deafening heavy swell.  Wekas (a flightless rail) were presumably introduced by sealers and have seriously depleted the burrowing petrel populations but seem to have little affected the Buller’s Albatrosses.

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Part of a study colony (foreground) among
Poa astonii tussock and Veronica elliptica scrub vegetation on the north-west corner of Solander

Apart from the storms, the greatest spectacle on the Solander Islands was the synchronised return of non-breeding Buller’s Albatrosses to their prospective colonies - I had become particularly interested in non-breeders, which account for close to half of the birds coming ashore.  This was most spectacular in summer during incubation when flocks of over a thousand birds started wheeling off the cliffs at dawn before returning ashore and literally awakening the place (and us) with their piercing wails.  The by-then presumably exhausted birds trickled out to sea in mid-morning to form large rafts just offshore, with an eerie silence returning to the colonies of snoozing incubators.  In mid-afternoon, whole squadrons of non-breeders returned ashore, and all wailing hell broke loose once again, bodies circling each other, heads bobbing, tails fanning, fights and all, until the final dusk exodus.  Except at full moon, when the racket went on well into the night.

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Non-breeding birds ready to take off into a wild Tasman Sea

Speaking of storms, one truly epic day was when collecting diet samples from chicks in the teeth of a massive winter storm in July.  In between sheets of sea spray ascending right past the top of the island, we fought our best to “stabilize” the collecting bucket bobbing frantically in the wind. During a relative lull, the knack was to get the near vomiting chick’s bill somehow aligned with the bucket before “release”.  Needless to say a few samples shot past the rim of the bucket on their way to outer space.

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Non-breeding birds displaying, attending nests and preening chicks in a study colony on Solander in May 2013

All in all, I made 11 trips to Solander (three-week trips in February and two-week trips in May and July), as well as eight trips to the Snares.  In the compact Solander study colony, I came to know quite a few birds personally; the placid incubators hardly moving when their bands were checked, the neurotic ones on the verge of nervous breakdowns.  I got particularly fond of a banded non-breeder, although getting close to it would be an overstatement.  From the top of his house-sized rock perch, this particular male kept a near daily watch on my wanderings in the colony - and presumably on passing Buller’s females.  I tried everything: slithering around the rock, whistling in mock disinterest, sprinting to beat the odds.  The cool bird just slid off its perch in a nonchalant glide, returning within sometimes seconds of me giving up the chase (French expletives omitted here).

Telemetry of breeding and non-breeding birds from the Snares and Solanders has revealed a dynamic stage, sex, age and locality dependant pattern which, on present evidence, seems broadly consistent from year to year.  Breeding Southern Buller’s Albatrosses forage up to 1800 km from their colonies, from Tasmania in the west to the Chatham Rise east of New Zealand, and from the Auckland Islands north to the Cook Strait (usually) or top the northern tip of New Zealand (one bird).  Breeders of both sexes undertake mostly long trips during the incubation period, mostly short trips during the brood-guard stage, and a mix of short and long trips during the post-guard stage to mid-June (males, which revert to short trips later in the season) or late July at least (females).  The mid-June change coincides with the dispersal of White-capped Albatrosses T. steadi, although this may not indicate a causal relationship.  Males undertake more short trips than do females, and, during long trips, disperse less far along the New Zealand slope.  When heading into the Tasman Sea they forage over the Tasmanian slope, whereas females stay in the oceanic mid-Tasman.  Females also mostly forage in the mid-Tasman during the pre-laying period, when males undertake mostly short trips. Compared to Snares breeders, Solander breeders, especially females, disperse more frequently to the slope west of New Zealand, both during long and short trips.  Tracked six-to-seven year-old prebreeders dispersed to a staging area off Tasmania after their only documented visit ashore.  Older prebreeders (aged eight to nine years) either made mostly long trips to the same areas as breeders (Tasman Sea and New Zealand slope), or mostly undertook short trips throughout the season.

6 Solander May 2013 0446Actively displaying non-breeders; the right-hand bird makes its piercing “wail” call.  Wails echoing in the cliffs are one of the great soundscapes of Buller’s Albatross colonies

Dietary studies (with Gavin James, also from NIWA) have revealed that fisheries discards (mostly of Jack Mackerel, Hoki and macrourids) accounted for two thirds of solid food by weight during the post-guard period at both Solander and the Snares.  The proportion of discards was greater during long trips, that of squid, salps and non-food items (wood and plastic gloves!) greater during short trips, suggesting that the latter are perhaps aimed at filling up the chick with just about anything.  One item that literally stood out from a chick regurgitation was the beak of a cephalopod subsequently identified as that of a giant squid.  An addiction to discards may well have been associated with the population increase observed on the Snares until about 2005, but the recent decline in adult casts some shadows on this sunny picture.  Watch this space.

Acknowledgements

As well as Sandy Bartle and Paul Sagar, I would like to acknowledge all who have contributed to our research, especially the New Zealand Department of Conservation, Dominique Filippi, Graeme Taylor, Alan Tennyson, Susan Waugh, Bernard West and Chrissie Wickes.  They have all facilitated my trips and made them great memories, despite the sometimes-testing conditions.

Selected Publications:

BirdLife International 2004.  Tracking Ocean Wanderers: the Global Distribution of Albatrosses and Petrels.  Results from the Global Procellariiform Tracking Workshop, 1–5 September, 2003, Gordon’s Bay, South Africa.  Cambridge: BirdLife International.  pp. 26-27.

Broekhuizen, N., Stahl, J.-C. & Sagar, P.M. 2003.  Simulating the distribution of southern Buller’s Albatross using an individual-based population model.  Journal of Applied Ecology 40: 678-691.

James, G.D & Stahl, J.-C. 2000.  Diet of southern Buller’s albatross (Diomedea bulleri bulleri) and the importance of fishery discards during chick-rearing.  New Zealand Journal of Marine and Freshwater Research 34: 435-454.

Sagar, P. M. & Stahl, J.-C. 2001.  Unusual items fed to southern Buller’s albatross chicks.  Water and Atmosphere 9: 5.

Sagar, P.M. & Stahl, J.-C. 2005.  Increases in the numbers of breeding pairs in two populations of Buller’s Albatross (Thalassarche bulleri bulleri).  Emu 105: 49-55.

Sagar, P.M., Stahl, J.-C. & Molloy, J. 1998.  Sex determination and natal philopatry of Southern Buller’s Mollymawks (Diomedea bulleri bulleri).  Notornis 45: 271-278.

Sagar, P.M., Stahl, J.-C. & Molloy, J. 2002.  The influence of experience, pair bond duration, and partner change on breeding frequency and success in southern Buller's mollymawk (Thalassarche bulleri bulleri).  Notornis 49: 145-152.

Sagar, P.M., Stahl, J.-C., Molloy, J., Taylor, G.A. & Tennyson, A.J.D. 1999.  Population size and trends within the two populations of Southern Buller’s Albatross Diomedea bulleri bulleri.  Biological Conservation 89: 11-19.

Sagar, P.M., Unwin, M.J., Stahl, J.-C. & Warham, J. 2005.  Variation in the size of Buller's albatross (Thalassarche bulleri) eggs.  New Zealand Journal of Zoology 32: 171-180.

Stahl, J.-C., Bartle, J.A., Cheshire, N.G., Petyt, C. & Sagar, P.M. 1998.  Distribution and movements of Buller’s albatross (Diomedea bulleri) in Australasian seas.  New Zealand Journal of Zoology 24: 109-137.

Stahl, J.-C. & Sagar, P.M. 2000. Foraging strategies of southern Buller's albatrosses Diomedea b. bulleri breeding on The Snares, New Zealand.  Journal of the Royal Society of New Zealand 30: 299-318.

Stahl, J.-C. & Sagar, P. 2000.  Foraging strategies and migration of southern Buller’s albatrosses Diomedea b. bulleri breeding on the Solander Is, New Zealand.  Journal of the Royal Society of New Zealand 30: 319-334.

Stahl, J.-C. & Sagar, P.M. 2006.  Behaviour and patterns of attendance of non-breeding birds at the breeding colony in a Buller’s albatross Thalassarche bulleri population at The Snares.  Notornis 53: 327-338.

Stahl, J.-C. & Sagar, P.M. 2006. Long and short trips in nonbreeding Buller’s albatrosses: relationships with colony attendance and body mass. The Condor 108: 349-366.

Van Bekkum, M., Sagar, P.M.; Stahl, J.-C. & Chambers, G.K. 2006.  Natal philopatry does not lead to population genetic differentiation in Buller’s albatross (Thalassarche bulleri bulleri).  Molecular Ecology 125: 73-79.

Waugh, S.M., Poupart, T.A., Miskelly, C.M., Stahl, J.-C. & Arnould, J.P.Y. 2017.  Human exploitation assisting a threatened species?  The case of muttonbirders and Buller’s albatross. PLoS ONE 12: e0175458.

Jean-Claude Stahl, Museum of New Zealand Te Papa Tongarewa, Wellington, New Zealand, 25 February 2022

The Commission for the Conservation of Southern Bluefin Tuna advertises for a Seabird Project Manager

ccsbt 

The Commission for the Conservation of Southern Bluefin Tuna (CCSBT) is an intergovernmental organization responsible for the global conservation and management of Southern Bluefin Tuna.

The CCSBT is inviting applications for a three-year part-time position of Seabird Project Manager for the CCSBT’s Project for Enhancing the Implementation of Ecologically Related Species Seabird Measures within CCSBT Fisheries.

The Seabird Project Manager will be responsible for the management and reporting of the CCSBT Seabird Project, the main objective of which is to reduce seabird bycatch in CCSBT fisheries.  This will be achieved through a combination of educational outreach, capacity-building, and technical innovation to enhance the implementation and monitoring of the functional deployment of seabird bycatch mitigation measures by CCSBT Members.

Deadline for applications is 31 March 2022.  Read more here.

John Cooper, ACAP Information Officer, 25 February 2022

Bird-scaring lines and reducing discards together will bring seabird mortality in an Uruguayan trawl fishery to negligible levels.


Black-browed Albatrosses gather behind a Uruguayan trawler deploying twin bird-scaring lines either side of the warp cable; photograph by Pablo Troncoso

Sebastián Jiménez (Laboratorio de Recursos Pelágicos, Dirección Nacional de Recursos Acuáticos, Montevideo, Uruguay) and colleagues have published in the journal Biological Conservation on reducing seabird mortality due to warp cable collisions in a demersal trawl fishery in the South Atlantic.

The paper’s abstract follows:

“The incidental mortality in trawl fisheries is considered a conservation threat for many seabirds. We simulate management scenarios, combining bird scaring lines (BSL; zero, one and two) and variables describing discards (occurrence, levels, type, and mode), to predict the total seabird collisions with warp cables potentially produced by a demersal trawl fleet operating in a region and season of high seabird abundance. A total of 2067 collisions, including 439 heavy collisions and 53 fatal collisions, were recorded on five trips aboard the Uruguayan trawl fleet. One BSL reduced collisions and heavy collisions by 89%, and the associated mortality by 94%. Best management scenarios in terms of reducing collisions were those without discards, where the models with BSL outperformed the scenarios without BSL. Scenarios with two BSL presented slight improvements, likely caused by the small sample size. Under a scenario without discards, the mortality caused by the entire fleet is likely to be negligible. Given the inability to eliminate discards in most situations, we simulated scenarios of discharge produced in batches with BSL. This could drive mortality to negligible levels. We provide six recommended scenarios (S) ordered by expected reduction in seabird mortality. Fisheries implementing BSL as a single mitigation measure should present a strong reduction in seabird mortality. However, the ability to hold discards on board, at least partially, can drive mortality to negligible levels. This should occur without discards and BSL use (S1), without discards and without BSL (S2), and with batch discharge and BSL use (S3).”

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Black-browed Albatrosses behind a trawler in the South Atlantic, photograph by Graham Parker

With thanks to Sebastián Jiménez.

Reference:

Jiménez, S., Páez E., Forselledo, R., Loureiro, A., Troncoso, P. & Domingo, A. 2022.  Predicting the relative effectiveness of different management scenarios at reducing seabird interactions in a demersal trawl fishery.  Biological Conservation 267.  doi.org/10.1016/j.biocon.2022.109487.

John Cooper, ACAP Information Officer, 23 February 2022

Wandering Albatross interactions with fishing vessels mimic natural foraging

graph abstract v3 

Ana Carneiro (BirdLife International, Cambridge, UK.) and colleagues have published open access in the journal Animal Conservation on studying Wandering Albatross Diomedea exulans - fishing vessel interactions with immersion loggers.

The paper’s abstract follows:

“Advances in biologging techniques and the availability of high-resolution fisheries data have improved our ability to understand the interactions between seabirds and fisheries and to evaluate mortality risk due to bycatch.  However, it remains unclear whether movement patterns and behaviour differ between birds foraging naturally or scavenging behind vessels and whether this could be diagnostic of fisheries interactions.  We deployed novel loggers that record the GPS position of birds at sea and scan the surroundings to detect radar transmissions from vessels and immersion (activity) loggers on wandering albatrosses Diomedea exulans from South Georgia.  We matched these data to remotely sensed fishing vessel positions and used a combination of hidden Markov and random forest models to investigate whether it was possible to detect a characteristic signature from the seabird tracking and activity data that would indicate fine-scale vessel overlap and interactions.  Including immersion data in our hidden Markov models allowed two distinct foraging behaviours to be identified, both indicative of Area Restricted Search (ARS) but with or without landing behaviour (likely prey capture attempts) that would not be detectable with location data alone.  Birds approached vessels during all behavioural states, and there was no clear pattern associated with this type of scavenging behaviour.  The random forest models had very low sensitivity, partly because foraging events at vessels occurred very rarely, and did not contain any diagnostic movement or activity pattern that was distinct from natural behaviours away from vessels.  Thus, we were unable to predict accurately whether foraging bouts occurred in the vicinity of a fishing vessel, or naturally, based on behaviour alone.  Our method provides a coherent and generalizable framework to segment trips using auxiliary biologging (immersion) data and to refine the classification of foraging strategies of seabirds.  These results nevertheless underline the value of using radar detectors that detect vessel proximity or remotely sensed vessel locations for a better understanding of seabird–fishery interactions.”

With thanks to Richard Phillips.

Reference:

Carneiro, A.P.B., Dias, M.P., Oppel, S., Pearmain, E.J., Clark, B.L., Wood, A.G., Clavelle, T. & Phillips, R.A. 2022.  Integrating immersion with GPS data improves behavioural classification for wandering albatrosses and shows scavenging behind fishing vessels mirrors natural foraging.  Animal Conservation doi.org/10.1111/acv.12768.

John Cooper, ACAP Information Officer, 22 February 2022

Eye in the sky spots over a hundred pairs of Short-tailed Albatrosses on the Senkaku Islands

 Short tailed Albatrosses by Hiroshi Hasegawa1
Short-tailed Albatross, photograph by Hiroshi Hasegawa

Nigel Brothers (Marine Ecology & Technology, Wonga Beach, Queensland, Australia) and colleagues have published in the open-access journal Marine Ornithology on using satellite imagery to count Vulnerable Short-tailed Albatrosses breeding on the Senkaku Islands.

The paper’s abstract follows:

“Accurate monitoring of vulnerable albatross populations is essential to their conservation. Herein, we explore the prospect of monitoring one particular remote albatross population with a view to promoting accurate worldwide monitoring of vulnerable albatross populations. We used very high-resolution (VHR) satellite images to count nesting Short-tailed Albatrosses Phoebastria albatrus on two islands of the Senkaku group, western North Pacific Ocean, where conventional monitoring has not occurred for 19 years due to a geopolitical territory dispute. Despite count uncertainties across rocky terrain, many birds were clearly discernible using the highest resolution image available of Minami-kojima. The result was a count of 132 (109­-162) nesting pairs in the 2020/21 breeding season (the timing of the count indicates the presence of nesting birds); this compares to a count of 52 when the population was last surveyed in 2002. On Kita-kojima, no birds were counted in images available for the 2019/20 and 2020/21 breeding seasons; one bird (a chick) was counted in 2002. If accurate, these counts are inconsistent with existing projections of increasing abundance of this species at the Senkakus (190 breeding pairs by 2018/19). Based on our findings, we suggest that reliable satellite image-based counts, independent of ground verification, is an achievable goal for albatrosses. Images must be of the highest possible resolution, with angle and timing optimized appropriately for the breeding site.  There is a need for standardization of specific procedures and methodologies, a task that is well-suited to The Working Group of the Agreement on the Conservation of Albatrosses and Petrels.”

Senkaku Maxar
WorldView-3 30-cm resolution satellite image of Minami-kojima and Kita-kojima, Senkaku Islands, western North Pacific Ocean
on 27 November 2020, with inset showing primary (P) and secondary (S) nest count areas of Short-tailed Albatrosses; ©2020 Maxar Technologies

Read about the taxonomic status of the Senkaku Short-tailed Albatrosses here.

With thanks to Nigel Brothers.

Reference:

Brothers, N., Bone, C. & Wellbelove, A. 2022.  Albatross population monitoring using satellite imagery, a case study:. Marine Ornithology 50: 7-12.

John Cooper, ACAP Information Officer, 21 February 2022

The Agreement on the
Conservation of Albatrosses and Petrels

ACAP is a multilateral agreement which seeks to conserve listed albatrosses, petrels and shearwaters by coordinating international activity to mitigate known threats to their populations.

About ACAP

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Hobart TAS 7000
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Email: secretariat@acap.aq
Tel: +61 3 6165 6674