







| Kingdom | Phylum | Class | Order | Family |
|---|---|---|---|---|
| ANIMALIA | CHORDATA | AVES | Procellariiformes | Diomedeidae |
| Scientific Name: | Thalassarche steadi | |||
| Species Authority: | Falla, 1933 | |||
Common Name/s:
|
||||
| Taxonomic Notes: | Diomedea cauta (Sibley and Monroe 1990, 1993) has been split into cauta, eremita and salvini following Brooke (2004) and steadi following Robertson & Nunn (1998), ACAP (2006) and all placed in the genus Thalassarche following Brooke (2004). | |||
| Red List Category & Criteria: | Near Threatened ver 3.1 | |||||||||||||||
| Year Assessed: | 2008 | |||||||||||||||
| Assessor/s | BirdLife International | |||||||||||||||
| Evaluator/s: | Butchart, S. (BirdLife International Red List Authority), Small, C. & Sullivan, B. (BirdLife International Global Seabird Programme) | |||||||||||||||
|
Justification: The population trend of White-capped Albatross is poorly known. It is categorised as Near Threatened because, given its longevity and slow productivity, and a high rate of mortality recorded in longline and trawl fisheries, it may be declining at a moderately rapid rate. |
||||||||||||||||
| History: |
|
|||||||||||||||
| Population: |
The global population is estimated to number c.75,000 pairs3,16, based on 72,000 pairs on Disappointment Island in 1993, 3,000 pairs on Auckland Island (unknown date), 50-100 pairs on the Antipodes Islands in 1994 (C. Robertson pers. comm.), and 100 pairs on Adams Island in 1993 (K. Walker pers. comm.). Hence, there are thought to be a minimum of 150,000 mature individuals. However, given the 10-15 years that have elapsed since these data were recorded, there is uncertainty associated with this estimate.
|
| Habitat and Ecology: | White-capped Albatross breeds annually in colonies located on rock islands. However, the breeding frequency and season for this species is poorly known17. The main foods include, fish, cephalopods, crustaceans and tunicates. It is a ship-follower and fish processing discharge comprises a significant proportion of its diet. Birds are generally surface feeders, but may undertake shallow surface dives. |
| Systems: | Marine |
| Major Threat(s): | The geographic range of T. steadi brings them into contact with a variety of longline and trawl fisheries in New Zealand, the high seas and off the coast of South Africa and Namibia15. Although T. cauta ('shy-type') comprised 15% of all seabirds returned from longlines in New Zealand waters during 1988-19976, New Zealand demersal and pelagic longline fisheries are currently considered to have a relatively low impact on T. steadi populations15. The Auckland Islands squid trawl fishery killed 2,300 adults in 1990 alone, most through collision with net monitor cables, which were phased out in 19922,6. However, birds are still killed by entanglement in nets and by collision with warp cables in trawl fisheries6,15. This species is also the most frequently caught species in pelagic tuna longline operations off South Africa8. It is estimated that 7,000-11,000 T. steadi were killed in the South African pelagic longline fishery between 1998-20008, and in 2005, an estimated 500-600 shy-type albatrosses were killed17. In the South African demersal trawl fishery, observer data from 2004-2005 produced an estimate of 7,700 shy type albatrosses killed annually. Subsequent DNA analysis indicated that these were all T. steadi16. Since the introduction of mandatory permit requirements in August 2006, whereby all vessels must deploy a bird streamer line, the bycatch rate has decreased but further data collection is required to establish a new catch estimate22. The impact of the large distant water fleets of Japan, Taiwan and Korea on T. steadi is largely unknown, but Japanese data from 2001-2002 indicate that at least 10% of recorded albatross mortalities were 'shy-type' albatrosses15. It has been estimated that 8,200 white-capped albatrosses are currently killed per annum, 75% of which are as a result of interactions with trawl fisheries in South African, Namibian and New Zealand15. Commercial exploitation of squid or fish reserves in Bass Strait could pose a threat to the species in the future by direct competition for food. On Auckland Island, the nesting area was significantly reduced during 1972-1982 because of interference by pigs, and feral cats may also take small numbers of chicks2,6,20. |
| Conservation Actions: |
Conservation actions underway: CMS Appendix II and ACAP Annex 1. A five-year aerial survey program of the Disappointment Island population commenced in 2006-2007. The New Zealand Department of Conservation has recently contracted the National Institute of Water and Atmospheric Research to conduct demographic and tracking study of the Auckland Islands populations. Conservation actions proposed: Census populations on all New Zealand islands. Conduct regular monitoring of a representative proportion of the population. Determine the at-sea distribution of the species through tracking studies and the interaction with longline and trawl fisheries13. Promote the adoption of a) monitoring of seabird bycatch associated with longline and trawl fishing and b) best-practice mitigation measures in all fisheries within the species range, including via intergovernmental mechanisms such as ACAP, the Indian Ocean Tuna Commission and FAO. |
| Citation: | BirdLife International 2008. Thalassarche steadi. In: IUCN 2009. IUCN Red List of Threatened Species. Version 2009.2. <www.iucnredlist.org>. Downloaded on 09 February 2010. |
| Disclaimer: | To make use of this information, please check the <Terms of Use>. |
| Feedback: | If you see any errors or have any questions or suggestions on what is shown on this page, please fill in the feedback form so that we can correct or extend the information provided |