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Tracking Ocean Wanders (PDF, 5 MB) - BirdLife International

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e examined. Several of the New Zealand albatrosses are<br />

known to frequent the coastal shelf off South America<br />

(Nicholls et al. 2002, Spear et al. 2003), making Argentina,<br />

Chile, Peru and Uruguay crucial for their conservation.<br />

64<br />

<strong>Tracking</strong> ocean wanderers: the global distribution of albatrosses and petrels – Discussion<br />

Figure 5.16. Regional maps of global utilisation distributions (UD’s) of breeding albatrosses in relation to EEZs. Important breeding sites for<br />

albatrosses in each region are shown. A. North Pacific; B. Australasia; C. Southern Atlantic and Indian <strong>Ocean</strong>s. These composites were created<br />

by calculating the utilisation distributions for each species and combining them giving each species equal weighting.<br />

The geographical designations employed do not imply the expression of any opinion whatsoever on the part of <strong>BirdLife</strong> <strong>International</strong> concerning the legal status of any country, territory or area, or<br />

concerning the delimitation of its frontiers or boundaries. At the time of going to press it was noted that the EEZ surrounding South Georgia does not extend as far west as indicated in the map. A dispute<br />

exists between the Governments of Argentina and the United Kingdom of Great Britain and Northern Ireland concerning the sovereignty over the Falkland Islands (Malvinas).<br />

Frances Taylor<br />

5.3 ESTABLISHMENT, MAINTENANCE AND USE<br />

OF A GIS TRACKING DATABASE<br />

The workshop participants acknowledged the importance<br />

and uniqueness of the integrated perspective of global<br />

Procellariiform distributions achieved at this workshop, and<br />

agreed to maintain the tracking database assembled for the<br />

Important Bird Area (IBA) delineation exercise beyond this<br />

meeting. However, participation in this exercise does not<br />

imply the contribution of the tracking data into a<br />

permanent database, nor does it give <strong>BirdLife</strong> <strong>International</strong><br />

the permission to use the contributed data indefinitely. The<br />

data sets used in this workshop will not be automatically<br />

incorporated into a permanent database at the end of this<br />

exercise. Instead, the workshop participants will be given<br />

the opportunity to re-submit their data sets into a<br />

permanent repository, on the basis of agreed-upon terms of<br />

use to be ratified at a later date. Alternatively, users may<br />

choose to withdraw their data from the tracking database<br />

once the IBA exercise has been completed.<br />

Many important issues concerning data ownership and<br />

the longevity of this database will be determined in future<br />

discussions. Nonetheless, the participants decided to<br />

proceed with the establishment of the Procellariiform<br />

tracking database at this time, acknowledging the need to<br />

Table 5.7. Comparison of the importance of overlapping EEZs to the breeding albatrosses for which satellite tracking data was submitted to the<br />

workshop. (The EEZ area includes territorial and contiguous waters.)<br />

New South United High<br />

Argentina Australia Brazil Chile Canada France Mexico Norway Zealand Africa Kingdom Uruguay USA seas<br />

No. of albatross species tracked within<br />

EEZ during breeding (out of 16 total)<br />

% time spent in EEZ by tracked breeding birds:<br />

3 9 2 3 1 7 1 2 7 3 4 2 2 16<br />

– species given equal weight 1 9 0 1 0 12 0 0 27 1 9 0 3 36<br />

– species weighted by threat status 2 4 0 1 0 16 0 0 29 1 9 0 3 34<br />

Rank of importance of EEZ to satellite tracked<br />

breeding albatrosses, taking the no. of species<br />

and time spent in the EEZ into account<br />

6 3 10 8 13 2 9 12 1 7 4 11 5

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