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

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

ANNEX 3 ALBATROSS TRACKING AND UTILISATION DISTRIBUTIONS FROM KERNELS<br />

Introduction<br />

The exploration of kernelling Royal Albatross data arose<br />

because there were strong differences on methods of analysis<br />

and the presentation of the results of satellite tracking. The<br />

Workshop faces similar challenges. Our satellite telemetry<br />

methodology differed between the various individuals<br />

within the single species. The differences were intentional at<br />

the time, but it requires careful analysis if we are to achieve<br />

valid comparisons and summaries. These complications are<br />

directly relevant to procedures combining datasets.<br />

Definitions<br />

The kernel is the shape placed over each observation. The<br />

process of summing the kernels creates a measure of<br />

abundance, either as a density, or the probability of<br />

occurrence across the range.<br />

Utilisation distribution is the grid or contour map of the<br />

occurrence.<br />

Home range is the area used by an animal in its normal<br />

daily activities. Home range for an albatross that has<br />

migrated to the other side of the world is arguably a<br />

contradiction, so we used range.<br />

Methods<br />

The homogenous data set is of a single northern royal<br />

albatross (abandoned breeding, migrated via the Pacific<br />

<strong>Ocean</strong> to the Patagonian Shelf; bird was present from<br />

March to 30 June, totalling 558 selected Argos locations;<br />

transmission regime: on-period 25 hours, off-period 23<br />

hours, i.e. exactly two days. The kernels, utilisations<br />

distributions and maps were prepared in Animal<br />

Movements Extension 2.0 in ESRI ArcView 3.2.).<br />

Results<br />

Smoothing produces different forms of the Utilisation<br />

Distributions. The user must decide the form depending on<br />

their hypothesis. There is no single choice, and no one other<br />

than the user can decide. Different kinds of subsets of the<br />

data do affect the range and Utilisation Distributions. These<br />

differences may be deeply hidden in the data. We tested the<br />

sample size and its effects on the area of the range. Small<br />

samples underestimated the range, but indicated a measure<br />

of by how much the range might be underestimated. It<br />

cannot of course show the places where an underestimate<br />

might be occurring.<br />

Subsets<br />

With subsets, such as day versus night, or, night, dawn, day,<br />

dusk, accuracy of locations and speed, the area of the<br />

ranges was close to the range area expected for the sample<br />

size. However for transmission regime, or, for seasonal time<br />

periods of the time spent on the Patagonian Shelf namely,<br />

early, middle and late, the range areas emphatically did not<br />

match the range for the complete data set.<br />

Conclusions<br />

Choosing the smoothing is subjective. The activity at hot<br />

spots is speculative. Concentrations may only in a limited<br />

sense indicate risk. Combining results and comparing maps<br />

from different datasets, other than at the most superficial<br />

levels, needs care but the exploration described here<br />

provides methods to ensure valid use.<br />

David Nicholls, Christopher Robertson<br />

and Beat Naef-Daenzer<br />

79

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