Trawl fisheries cause staggering levels of seabird bycatch, particularly large-bodied albatrosses and petrels. These beautiful migratory birds undertake epic journeys and are attracted to the easy meals that discarded fish offal from commercial trawl fisheries present. This feeding prospect lures them dangerously near to boats where they often collide with warp cables or become entangled in nets during the later stages of hauling. Up to 40 species are thought to be affected, with tens of thousands estimated to be dying each year.
While seabird bycatch in long-line fishing has been known since the 1980s, the threat posed by trawl fisheries has only become apparent in more recent years (Bartle 1991, Weimerskirch et al. 2000, Sullivan et al. 2006). No global review of the impact of trawl fishing on seabirds has been undertaken, but there are a number of regional and national levels studies that highlight the significance of the problem (Wilson et al. 2004). Currently, BirdLife International’s Albatross Task Force is working with fishermen and local communities worldwide to test mitigation strategies that will reduce the unsustainable levels of seabird bycatch. Albatrosses are especially hard-hit as they lay a single egg every one or two years and take 7 – 13 years to reach sexual maturity.
The Humboldt Current and turbid waters of the southern cone are incredibly productive upwelling zones, supporting a wealth of biodiversity. In Argentina, studies (Gonzalez-Zevallos et al. 2007, Yorio et al. 2010) on Magellanic Penguin Spheniscus magellanicus and Imperial Shag Phalacrocorax atriceps breeding at a newly designated marine park in Golfo San Jorge assessed the potential spatial conflict between these seabirds and commercial hake and shrimp trawl fisheries. The observed foraging patterns suggest a high probability of spatial conflict and incidental mortality was regularly recorded in both fisheries, at rates that varied between 0.02 and 0.34 individuals per haul depending on species and fishery (Yorio et al. 2010).
In the Falklands/Malvinas, Sullivan et al. (2006) estimated that >1,500 seabirds, predominantly Black-browed Albatross Thalassarche melanophris (pictured above), were killed by demersal (bottom) finfish trawlers in 2002/2003. A chick like the one pictured will be incubated and nurtured for seven to eight months until it is ready to fledge, during which time parents will take turns between foraging for food and protecting their chick. As such, chicks are left incredibly vulnerable if either parent is killed. Data released in 2017 has revealed the sheer extent of bycatch in Argentinian and Chilean fisheries; approximately 25,000 seabirds, predominantly albatrosses, are drowned by trawl fisheries in South America each year. The Albatross Task Force has demonstrated through trials that this figure could be reduced by 85% if the same mitigation strategies that have been so successful in South Africa can be applied in South America. The signing of the Valdivia Declaration in January 2017 marks the beginning of new regulations and increased monitoring efforts to reduce the senseless volume of seabird deaths in these fisheries.
Historically the Bengula Current (covering the Exclusive Economic Zones of South Africa, Namibia, Angola, and adjacent international waters) has had high levels of seabird bycatch in trawl fisheries (Petersen et al. 2007, 2008). In 2005/06 it was estimated that 18,000 seabirds were killed in the South African hake trawl fishery, one of the first trawl fisheries in which this problem was identified (Watkins et al. 2008). In South Africa, it was estimated that 85% of birds were killed by the powerful warp cables that attach the trawl net to the fishing vessel, entangling particularly the long-winged albatrosses and dragging them under the water. The remaining 15% died entangled in nets during shooting and hauling (Watkins et al. 2008). Of the birds killed, 70% were Shy Albatross T. cauta and Black-browed Albatross T. melanophrys, 14% were Cape Gannet Morus capensis, and 9% White-chinned Petrel Procellaria aequinoctialis. All of these species are globally threatened or near-threatened. BirdLife International’s Albatross Task Force has been working with the trawl fleet in South Africa since 2006 to reduce this bycatch, and began work in Namibia in 2008. This work has succeeded in greatly reducing the scale of the problem in these areas; albatross bycatch has reduced by 99% in South Africa’s hake trawl fishery. Meanwhile the same simple, cost-effective mitigation strategies are saving an estimated 30,000 seabirds per year in Namibia and helping to empower women in the process.
Related Case Studies in other sections
Bartle, J. A. (1991) Incidental capture of seabirds in the New Zealand Subantarctic Squid trawl fishery, 1990. Bird Conservation International 1, 351–359.
Gonzalez-Zevallos, D., Yorio, P., and Caille, G. (2007) Seabird mortality at trawler warp cables and a proposed mitigation measure: a case of study in Golfo San Jorge, Patagonia, Argentina. Biological Conservation 136: 108–116.
Petersen, S. L., Honig, M. B. and Nel, D. C. (2007) The impact of longline fisheries on seabirds in the Benguela Current Large Marine Ecosystem. Pp 9–31 in S. Petersen, D. Nel and A. Omardien, eds, Towards an ecosystem approach to longline fisheries in the Benguela: an assessment of impacts on seabirds, sea turtles and sharks. WWF South Africa Report (Series - 2007/Marine/001).
Petersen, S. L., Nel, D. C., Ryan, P. G., and Underhill, L. G. (2008) Understanding and mitigating vulnerable bycatch in southern African trawl and longline fisheries. WWF South Africa Report Series, 2008/Marine/002.
Sullivan, B. J., Reid, T. A., and Bugoni, L. (2006) Seabird mortality on factory trawlers in the Falkland Islands and beyond. Biological Conservation 131: 495–504.
Watkins, B. P. Petersen, S. L. and Ryan, P. G. (2008) Interactions between seabirds and deep-water hake trawl gear: an assessment of impacts in South African waters. Anim. Conserv. 11: 247–254.
Weimerskirch, H., Capdeville, D. and Duhamel, G. (2000) Factors affecting the number and mortality of seabirds attending trawlers and long-liners in the Kerguelen area. Polar Biology 23: 236–249.
Wilson, B., Rivera, K., Fitzgerald, S. and Rose, C. (2004) Discussion paper on seabird interactions with trawl vessel gear. North Pacific Fishery Management Council, Protected Resources Report No.2, Anchorage, Alaska.
Yorio P., Quintana F., Dell’arciprete P. and Gonzalez-zevallos D. (2010) Spatial overlap between foraging seabirds and trawl fisheries: implications for the effectiveness of a marine protected area at Golfo San Jorge, Argentina. Bird Conservation International 20: 320–334.
Zador, S. G., Parrish, J. K., Punt, A. E., Burke, J. L. and Fitzgerald, S. M. (2008) Determining spatial and temporal overlap of an endangered seabird with a large commercial trawl fishery. Endang. Species Res. 5: 103–115.
Compiled: 2008 Last updated: 2017
BirdLife International (2017) Trawl fisheries cause significant mortality to albatrosses . Downloaded from http://www.birdlife.org on 29/11/2021