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Abstract: NATO ASI Series
Programme: 159
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Yiou F., Raisbeck G.M., Baumgartner S., Beer J., Hammer C., Johnsen S., Jouzel J., Kubik P.W., Lestringuez J., Stievenard M., Suter & Yiou P. (1997). 10Be in the greenland Ice Core Project ice core at Summit Greenland. J. Geophys. Res., 102(c12), 26783–26794.
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Abstract: NATO ASI Ser.'Ice core studies of Global biogeochemical cycles
Programme: 322
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Carole Ferret. (2011).
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. (2023). 14 years of lidar measurements of polar stratospheric clouds at the French Antarctic station Dumont d'Urville (Vol. 23).
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Carole Ferret. (2011).
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Sowers T., Bender M., Raynaud D. & Korotkevich Y.S. (1992). 15N of N2 in air trapped in polar ice:a tracer of gas transport in the firn and a possible constraint of gas age-ice differences. J. Geophys. Res., 97, 15683–15697.
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. (2015). 167 individuals versus millions of hooks: bycatch mitigation in longline fisheries underlies conservation of Amsterdam albatrosses
. Aquatic Conservation: Marine and Freshwater Ecosystems, .
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Thiebot Jean-Baptiste, Delord Karine, Barbraud Christophe, Marteau Cédric, Weimerskirch Henri. (2015). 167 individuals versus millions of hooks: bycatch mitigation in longline fisheries underlies conservation of Amsterdam albatrosses. 1052-7613, 26(4).
Abstract: 1. Industrial fisheries represent one of the most serious threats worldwide to seabird conservation. Death of birds in fishing operations (i.e. bycatch) has especially adverse effects on populations of albatrosses, which have extremely low fecundity. 2. The single population worldwide of Amsterdam albatross (Diomedea amsterdamensis) comprises only 167 individuals and risks considerable decline over the mid-term from additional mortality levels potentially induced by fisheries. The priority actions listed in the current conservation plan for this species included characterizing the longline fisheries operating within its range, dynamically analysing the overlap between albatrosses and these fisheries, and providing fisheries management authorities with potential impact estimates of longline fisheries on the Amsterdam albatross. 3. During all life-cycle stages and year quarters the birds overlapped extensively with fishing effort in the southern Indian and Atlantic oceans. Fishing effort, and consequently overlap score (calculated as the product of fishing effort and time spent by the birds in a spatial unit) was highest in July–September (45% of the hooks annually deployed). Just three fleets (Taiwanese, Japanese and Spanish) contributed to >98% of the overlap scores for each stage (72% from the Taiwanese fleet alone, on average). Daily overlap scores were higher for the non-breeding versus the breeding stages (3-fold factor on average). 4. Based on previous bycatch rates for other albatross species, this study estimated that longline fisheries currently have the potential to remove ~2–16 individuals (i.e. ~5%) each year from the total Amsterdam albatross population, depending on whether bycatch mitigation measures were or were not systematically employed during the fishing operations. 5. Recent bycatch mitigation measures may be instrumental in the conservation of the Amsterdam albatross. This study suggests three further key recommendations: (1) to focus conservation efforts on the austral winter; (2) to require all operating vessels to report ring recoveries; and (3) to allocate special regulation of fishing operations in the areas of peak bycatch risk for the Amsterdam albatrosses. Copyright © 2015 John Wiley & Sons, Ltd.
Programme: 109
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