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Read about recent developments and findings in procellariiform science and conservation relevant to the Agreement on the Conservation of Albatrosses and Petrels in ACAP Latest News.

THE ACAP MONTHLY MISSIVE. Michelle Risi starts her PhD on giant petrel demography

Michelle Risi Low Hump with SGP Chris JonesUnconcerned: Michelle Risi pauses while reading colour bands next to an incubating Southern Giant Petrel in the Low Hump colony on Gough Island, photograph by Chris Jones

I am sometimes asked “Which is your favourite among the 31 ACAP-listed seabirds?”  My answer might surprise, for it is not the iconic Wandering Albatross Diomedea exulans of Marion Island or the equally iconic Tristan Albatross D. dabbenena of Gough Island, both of which I have studied.  No, my co-favourites are the two giant petrels, the Northern M. halli and the Southern M. giganteus, which I have also studied on Marion (both species) and Gough (Southern) Islands. With my last island visits now over a decade ago, I am pleased that the data collected from the long-term studies of colour-banded Northerns on Marion and Southerns on Gough that I set up years back will now contribute to a PhD study by ACAP supporter, Michelle Risi – who has worked with both species in the field on Marion and Gough.  She is based in the FitzPatrick Institute of African Ornithology at the University of Cape Town, where I worked for several decades last century.

Michelle Risi writes to ACAP Latest News: “I hold an MSc in Biology from the University of KwaZulu-Natal (2015), along with BSc Honours and BSc degrees, both awarded cum laude.  Over the past decade, I have dedicated my career to wildlife conservation, with a particular focus on long-term seabird monitoring and the restoration of remote island ecosystems for threatened species.  For the past seven years, I have worked extensively on the demographic datasets for giant petrels from Gough and Marion Islands.  This has included compiling, cleaning and curating long-term monitoring data, as well as standardising records for mark-recapture and breeding success analyses.  My familiarity with these datasets and the colonies they represent provides me with a unique advantage, allowing me to conduct the planned analyses efficiently and produce high-quality outputs for my PhD thesis.”

Michelle Risi Antarctic PeninsulaMichelle guiding aboard the Roald Amundsen along the Antarctic Peninsula in summer 2025/26

A summary of Michelle’s PhD project, entitled “Understanding the drivers of seabird demography in a changing ocean: insights from long-term studies of giant petrels”, follows:

“Global climate change and human activities are transforming marine ecosystems, yet the impacts on long-lived apex predators remain poorly understood.  Seabirds, such as giant petrels Macronectes spp., are key indicators of ocean health, integrating ecological change across broad spatial and temporal scales. Northern (NGP, M. halli) and Southern Giant Petrels (SGP, M. giganteus) are large, long-lived seabirds with circumpolar distributions in the Southern Hemisphere, breeding mostly at scattered sub-Antarctic and Antarctic islands.  Males play critical ecological roles as both predators and scavengers, occupying the top of the marine food web and making them especially sensitive to ecosystem changes.  Females have a more pelagic distribution, ranging as far from their colonies as albatrosses, and consume a diverse diet that includes fish, crustaceans, squid and carrion.  Both sexes commonly scavenge behind fishing vessels and are bycaught in various longline and trawl fisheries across the Southern Ocean.  Giant petrel nestlings are impacted by heat stress, and nesting adults have also been recorded being attacked by House Mice Mus musculus on Marion Island, leading to nest abandonment.

A previous study of adult survival at Bird Island, South Georgia (Islas Georgias del Sur)*, showed that sex-specific ecological differences can lead to divergent responses to environmental drivers.  For example, females were more likely to be impacted by changes in pelagic longline effort.  However, that study did not assess how changing oceanographic conditions influence other critical demographic parameters, such as breeding probability and success.  Even less is known about the demographic drivers of populations at other sites.  As scavengers, giant petrels are at risk of secondary poisoning during rodent eradication operations, as they may forage on the carcasses of other scavenging birds.  Gough Island had a failed mouse-eradication attempt in 2021, and a mouse eradication operation is planned for Marion Island in 2029 by the Mouse-Free Marion Project.  On Macquarie Island, now free of invasive mammals, the aerial eradication campaign conducted between 2010 and 2011 had a substantial immediate impact on giant petrels, resulting in the deaths of up to 1400 NGPs over two years and an estimated 33% decline in breeding pairs.  Rodent eradication operations are generally undertaken during winter, when most seabirds are foraging at sea, and natural food availability for mice is lowest, thereby maximising bait uptake while reducing potential impacts on non-target species.  It is therefore important to establish a baseline for the number of giant petrels that remain on Marion Island during winter.

Long-term demographic datasets are available from seven Southern Ocean island groups: Signy Island in the South Orkney Islands, Bird Island at South Georgia (Islas Georgias del Sur)*, Gough Island, Marion Island in the Prince Edward Islands, Île de la Possession in the Crozet Archipelago, the Kerguelen Archipelago and Macquarie Island. These datasets include annual counts of breeding birds and fledged chicks, intensive monitoring of individual breeding attempts and, at four sites, capture-mark-recapture records that follow marked birds through their breeding histories.  Together, the sites span broad geographical, oceanographic and management gradients.  Marion Island will serve as the focal system for identifying environmental drivers of breeding success and other demographic parameters, after which the transferability of the results to other giant petrel colonies will be tested.

 

By analysing long-term demographic data from these breeding sites, the study will explore relationships between vital rates (adult and juvenile survival, breeding frequency, and breeding success) and potential oceanographic drivers (e.g. sea surface temperature, marine productivity, wind regimes).  This will provide a step change in our understanding of how these key predators respond to climate variability and other anthropogenic pressures, while also identifying implications for seabird monitoring and conservation management.

Research Questions:

1. How have breeding population size and breeding success of Northern and Southern Giant Petrels at Marion Island changed over time, and what is the relative importance of local weather and breeding-season oceanographic conditions on breeding success?

2. How does winter attendance by giant petrels vary on Marion Island, and is attendance associated with previous breeding outcome and subsequent breeding probability or success?

3. How transferable are the environmental variables identified as the best predictors of giant petrel breeding success at Marion Island to other populations across the Southern Ocean?

4. How does environmental variability influence survival, recruitment and breeding probability in giant petrels?

Methods and Impact:

Using long-term breeding counts, nest-monitoring records, winter surveys, capture-mark-recapture data and remotely sensed environmental information, the study will investigate demographic variation at both colony and individual levels.  Winter surveys will be used to determine which giant petrels attend Marion Island during the non-breeding period, whether winter attendance is associated with previous breeding outcome and subsequent breeding probability or success, and what proportion of breeding birds may be exposed during the planned winter mouse-eradication operation.  Analyses will test whether environmental relationships identified at Marion Island are transferable to other colonies.  Multi-event capture-mark-recapture analyses will then assess whether selected environmental variables explain variation in survival, recruitment and breeding probability.  The study will identify the factors associated with demographic change and provide evidence to support ACAP monitoring and conservationb management.”

OLYMPUS DIGITAL CAMERAA Northern Giant Petrel on Marion Island eyes the camera, photograph by Michelle Risi

Michelle’s study will be supervised by Associate Professor Susan Cunningham (FitzPatrick Institute), Dr Steffen Oppel (Swiss Ornithological Institute), Professor Richard Phillips (British Antarctic Survey) and Emeritus Professor Peter Ryan (FitzPatrick Institute).

Back in 2019, Michelle proposed to me that there should be a World Albatross Day.  Although I was initially somewhat reluctant, we submitted an Information Paper proposing the day to the ACAP Advisory Committee’s 11th Meeting, held in Brazil the same year.  With the committee’s approval, ACAP marked the first World Albatross Day on 19 June 2020 under the theme of Eradicating Island Pests”.  Michelle played a significant role in supporting the first “WAD” years by producing a series of photo posters, as well as entering a cake for the “Great Albicake Bake Off” competition in 2020 (click here).  Surely, now that there have been seven successful World Albatross Days held, it is past time for the two ACAP-listed giant petrels to be recognized as “honorary albatrosses” and included in the celebrations for WAD2027.


Michelle Risi and Chris Jones on SA Agulhas II 2024 09 05Husband and wife team, Chris Jones and Michelle Risi, sail from Cape Town for a year on Gough Island aboard the
S.A. Agulhas II in September 2024

Michelle and her husband Chris Jones have recently started staying with me in my home near the university for a couple of nights every other week to make their commute from their own home a distance away to campus easier.  Our dinner-table conversations often turn to Gough and Marion, their albatrosses and petrels, and stories from our respective times working with these special birds.  It will then be a pleasure to hear from time to time from Michelle how her PhD work is progressing, and I look forward to reading the peer-reviewed publications that will ensue.

John Cooper, Emeritus Information Officer, Agreement on the Conservation of Albatrosses and Petrels, 21 August 2026

* A dispute exists between the Governments of Argentina and the United Kingdom of Great Britain and Northern Ireland concerning sovereignty of the Falkland Islands (Islas Malvinas), South Georgia and the South Sandwich Islands (Islas Georgias del Sur e Islas Sandwich del Sur) and the surrounding maritime areas.

Feral cats to be removed from New Zealand’s Pitt Island, and its feral pigs controlled


Antipodean Albatross 2024 Pitt Island Flowerpot Lodge 1
Antipodean Albatross chick on Pitt Island in 2024, photograph from the Flowerpot Lodge

The New Zealand Department of Conservation has announced funding towards eradicating feral cats and controlling feral pigs on Pitt Island (Rangihaute/ Rangiauria) in the Chatham Islands.

The “Chatham Islands Landscape Restoration Trust will receive [NZ]$1,169,900 for a project to remove feral cats from Rangihaute Pitt Island.  This will protect at least 14 threatened bird species, including the Endangered Shore Plover Thinornis novaeseelandiae (tūturuatu/tchūriwat) and restore several critical ecosystems.”

“The Chatham Islands Farmers Association will receive [NZ]$543,240 to undertake pig control, reducing the impact on threatened species and critically endangered ecosystems, as well.  This work will begin on Rangihaute Pitt Island before commencing on the main Rēkohu Wharekauri Chatham Island.”

A single pair of Endangered Antipodean Albatrosses Diomedea antipodensis breeds on Pitt Island and the Vulnerable Chatham Islands Petrel Pterodroma axillaris breeds in small numbers protected by a fence.

Seven Pitt Island Cats for desexing“The last seven unsterilised pet cats on Pitt Island have been flown to neighbouring Chatham Island to be desexed, a crucial step towards eradicating feral predators.”

Pet cats living on Pitt Island have now all been sterilized (click here).

John Cooper, Emeritus Information Officer, Agreement on the Conservation of Albatrosses and Petrels, 20 August 2026

An update from OFFLU on High Pathogenicity Avian Influenza in Australia and New Zealand

OFFLUA report produced by the OFFLU Wildlife Technical Activity and released jointly by the World Organization for Animal Health (WOAH) and the Food and Agriculture Organization of the United Nations (FAO) updates the occurrence of High Pathogenicity Avian Influenza in Australia and New Zealand.  Notably, 17 infected ACAP-listed giant petrels (Macronectes sp.) have been reported from the coast of Australia (overall 231 confirmed cases) on 10 August 2026.

The report’s Executive Summary follows:

“What was long expected, has now come to pass: high pathogenicity avian influenza H5 (HPAI H5) has been detected for the first time in wild birds in Australia in June 2026 and in New Zealand in July 2026.

HPAI H5 has a high burden of disease for poultry and wildlife, as well as a zoonotic risk for humans. Since the emergence of HPAI H5 (specifically, the A/Goose/Guangdong/1/1996 lineage) in Asia in 1996, it has been detected in ever more continental regions. It spread from Europe to North America in 2021, to South America in 2022, and to the Antarctic region (Antarctica and sub-Antarctic islands) in 2023. Since its incursion in the Antarctic region, it spread nearly 6,500 km eastwards in two years, from South Georgia in the South Atlantic Ocean in October 2023 to Heard Island in the southern Indian Ocean in October 2025.

It is likely that HPAI H5 was carried from the Antarctic region to Australia and New Zealand by migratory seabirds. Between 14 June and 31 July 2026, HPAI H5 was detected in 1 Brown Skua (Stercorarius antarcticus) and 17 giant petrels (Macronectes sp.) on the coast of Australia, and 1 Brown Skua on the coast of New Zealand. These species breed in spring in the Antarctic region, here they are known to have been infected by HPAI H5. In the non-breeding period, these species may disperse widely, including northwards to waters off the coasts of Australia and New Zealand. Preliminary phylogenetic analysis shows that the HPAI H5 virus detections in wild birds in Australia are closely related to viruses from Heard Island in the Antarctic region.

HPAI H5 has subsequently spilled over from these seabirds to resident bird species in Australia and New Zealand. In Australia, HPAI H5 has been detected in 34 Greater Crested Terns (Thalasseus bergii) as of 31 July 2026. The Greater Crested Tern is a largely resident species in Australia and occurs widely along the coast and offshore islands, a habitat shared with many other seabird species. In New Zealand, HPAI H5 has been detected in one Swamp Harrier (Circus approximans) as of 31 July 2026. The Swamp Harrier is a resident species in New Zealand. In winter it feeds largely on carrion, which is a likely source of infection in avian scavengers.

Based on the sequence of events in other continents, HPAI H5 is likely to spread among wild birds and mammals in Australia and New Zealand. The main wildlife groups at risk are seabirds (e.g. gannets, terns and albatrosses), other waterbirds (e.g. ducks, swans and grebes), pinnipeds (e.g. seals and sea lions), and predatory and scavenging birds and mammals (e.g. raptors, corvids, Dingoes (Canis familiaris dingo) and quolls). From Australia and New Zealand, HPAI H5 may spread to other parts of Oceania (Melanesia, Micronesia, Polynesia), most likely via medium- or long-distance movements of wild birds.

The potential conservation impact from HPAI-H5-associated wildlife morbidity and mortality in Oceania is enormous. Oceania contains many geographically restricted and threatened wildlife populations. For susceptible species, particularly colony-nesting seabirds and pinnipeds, additional mortality associated with HPAI H5 could compound existing pressures on populations.

Although it is not possible to stop the geographical spread of HPAI H5, there are response options to reduce its spread and impact on wildlife, as well as the risk of such HPAI panzootics occurring in the future. Short-term response options include expanding and improving avian influenza surveillance in wildlife, coordination of surveillance across Oceania, removal of infected wildlife carcasses, management of human activities in regions with affected wildlife, vaccination of threatened wildlife species, and avoidance of activities that harm or disturb wildlife and their habitats. In case of HPAI H5 spillover to poultry (which has so far not been reported in Australia or New Zealand), short-term response options include rapidly controlling outbreaks and limiting concurrent infections in poultry populations, thereby reducing opportunities for continued viral evolution and recurrent spillback into local wildlife. Medium- and long-term response options include long-term monitoring of impacted wildlife populations, increasing resilience of susceptible wildlife populations (including by actively reducing other threats and promoting actions to enable recovery of populations) and reducing the risk of HPAI emergence and spillover from poultry in the future.

Post scriptum (10 August 2026): Following the drafting of this statement, further cases of HPAI H5 have been detected in wild birds in Australia. These include: a mass mortality event in Greater Crested Terns in South Australia involving over 80 sick or dead individuals. Several detections have been made in Silver Gulls (Chroicocephalus novaehollandiae), a widespread resident species in Australia and New Zealand that occurs both on the coast and inland, including wetland habitats and urban environments. A single detection has been made in an Australian Magpie (Gymnorhina tibicen), a widespread resident species in Australia, member of the Artamidae family and is omnivorous. As of 10 August 2026, there have been 231 confirmed detections of H5 HPAI in wild birds in Australia (10 in Western Australia, 163 in South Australia, 53 in Victoria, 4 in New South Wales and 1 in Queensland), while there the number of confirmed detections in New Zealand has remained at two.”

Read earlier reports on HPAI in ACAP Latest News for mainland Australia and New Zealand. Since publication of the OFFLU report, HPAI has been reported from Tasmania (10 cases, including a Brown Skua).

With thanks to David Duffy.

Reference:

OFFLU Wildlife Technical Activity 2026.  Incursion of High Pathogenicity Avian Influenza H5 into Australia and New Zealand, with potential to impact wildlife populations and to spread further in Oceania.  OFFLU Wildlife Statement IV.   WOAH/FAO.  33 pp.

John Cooper, Emeritus Information Officer, Agreement on the Conservation of Albatrosses and Petrels, 19 August 2026

Ingested plastics reduce recruitment and survival of Flesh-footed Shearwaters on Lord Howe Island – a 15-year study

Flesh footed Shearwater dissection Jennifer LaversPlastic fragments in the alimentary system of a Flesh-footed Shearwater, photograph by Jennifer Lavers

Jennifer Lavers (Gulbali Institute, Charles Sturt University, Wagga Wagga, New South Wales, Australia) and colleagues have published open access in the journal PNAS on ingested plastics affecting the the Near threatened Flesh-footed Shearwater Ardenna carneipes at the population level.

The paper’s abstract follows:

“Plastics research lags 30 y behind many other environmental crises, with population-level impacts alluded to but not yet demonstrated for any wild species.    Addressing this “Grand Challenge” requires robust data that span many years of variable exposure. Here, we use 15 y of mark-recapture data to estimate plastics’ impact on the demography of Sable Shearwaters (Ardenna carneipes). We found that the ingestion of >1 g of plastic is common and associated with at least an 11% reduction in the probability of birds surviving to return and breed at their natal island, with birds that ingested >5 g of plastic almost never seen again. In a time of unprecedented planetary change and biodiversity collapse, these results provide much- needed insight into plastics’ role in potentially driving species decline.”

Reference:

Lavers, J.L., Worthington, H. & Bond, A.L. 2026.  Ingested plastics reduce recruitment and survival of an Australian seabird.  PNAS doi/epdf/10.1073/pnas.2613782123.

John Cooper, Emeritus Information Officer, Agreement on the Conservation of Albatrosses and Petrels, 18 August 2026

The Solomon Sea is a hot spot for juvenile Flesh-footed Shearwaters

Flesh footed Shearwater 3 Kirk ZufeltFlesh-footed Shearwater at sea, photograph by Kirk Zufelt

Jennifer Lavers (Gulbali Institute, Charles Sturt University, Wagga Wagga, New South Wales, Australia) and colleagues have pre-published open access on movements of satellite-tracked fledglings of the Near threatened Flesh-footed Shearwater Ardenna carneipes in the journal Animal Biotelemetry.

The paper’s abstract follows:

“Background Juvenile survival is a critical yet poorly resolved demographic parameter in long- lived seabirds. Juvenile spatial ecology may differ remarkedly from adults in dispersal extent, habitat use, and migratory routing, as fledglings must independently and rapidly acquire foraging and navigational competency to migrate vast distances. This demographic-specific knowledge gap limits evidence-based marine spatial planning for vulnerable seabird populations. Here, we provide new data on the movement patterns of fledgling Sable Shearwaters Ardenna carneipes from Lord Howe Island, Australia to evaluate spatial ecology.

Methods Sable Shearwaters were captured by hand from the colony surface immediately prior to fledgling. Solar-powered GPS loggers were attached to three central tail feathers in 2022 (n = 15) and 2024 (n = 15). All loggers were programmed to collect GPS locations (accuracy 5 m) at one-hour intervals.

Results Juveniles departed Lord Howe Island rapidly, travelling on average 1,000 (up to > 2,500) kilometres northward within the first two weeks post-fledgling and reaching the Solomon Sea by week 3, where they moved relatively short distances from east to west during the following weeks.

Conclusion Across years, juvenile Sable Shearwaters showed consistency in migrating northward within the first two weeks of their migration, highlighting the Solomon Sea as a previously unrecognised and potentially critical stopover site for this species. By identifying this important habitat, our results provide a clear spatial focus for future conservation planning and the development of targeted area-based management measures.”

Reference:

Lavers J.L., Gilmour M.E., Jersey A.M., Rivers-Auty, J. & Bond, A.L. 2026.  Post-fledging migration of Sable Shearwaters (Ardenna carneipes) identifies the Solomon Sea as a potential conservation priority.  Animal Biotelemetry doi.org/10.1186/s40317-026-00487-9.

John Cooper, Emeritus Information Officer, Agreement on the Conservation of Albatrosses and Petrels, 17 August 2026

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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