The Characteristics and Variation of the Golden Eagle Aquila chrysaetos Home Range

Author:

Fielding Alan H.1ORCID,Anderson David2,Barlow Catherine3,Benn Stuart4,Chandler Charlotte J.5ORCID,Reid Robin6,Tingay Ruth7,Weston Ewan D.1,Whitfield D. Philip1ORCID

Affiliation:

1. Natural Research, Brathens AB31 4BY, UK

2. Dave Anderson Ecology, Callander FK17 8EU, UK

3. Southern Uplands Partnership, Galashiels TD1 3PE, UK

4. RSPB Scotland, Inverness IV2 3BW, UK

5. Department of Biological Sciences, University of Chester, Chester CH1 4BJ, UK

6. Independent Researcher, Isle of Harris HS3 3EZ, UK

7. Wild Justice, 9 Lawson Street, Raunds NN9 6NG, UK

Abstract

Satellite tracking allows for novel investigations into golden eagle home range characteristics. Understanding home range characteristics is important for conservation and for assessing the potential impact of landscape changes from forest planting, wind farms, etc. Small sample sizes, inconsistent definitions and methods restricted several previous studies. Our study involved 69 resident tagged eagles with over one year of data across five Scottish regions. Home range size was estimated from 95% isopleth contours extracted from Utilisation Distributions. Above a small threshold, estimated range size was not affected by the number of records but at least one year of data is required, largely because of the breeding and non-breeding seasonal differences. There were no significant range size differences between birds tagged as range holders and those previously tagged as nestlings. Across four regions, with considerable intra-regional variation, planar 95% isopleths did not differ (medians, km2): Argyll 58.9, Northwest Highlands 61.7, Northeast Highlands 89.3, South of Scotland 91.9. Ranges in the isolated Outer Hebrides region were exceptionally small, at 24.0 km2. Estimated range area was usually reduced to 70–80% of the planar area when restricted to usable habitat, as estimated by the Golden Eagle Topography (GET) model. Applying measures of known unsuitable habitat (closed-canopy commercial forest and wind turbines) further reduced usable open land. Loss of otherwise suitable habitat was substantially due to commercial forest. Larger ranges had larger extents of suitable habitat (according to GET), with no apparent optimum of preferred GET habitat. Range size was not different across a year between the sexes. Breeding ranges were smaller, and females’ breeding ranges were much smaller than those of males, but larger than males’ ranges in the non-breeding season. Breeding attempt duration was probably also influential. Our study provides novel insights into golden eagle home range characteristics and can guide further research and practical applications.

Funder

Natural Research

Royal Society for the Protection of Birds

Scottish Natural Heritage

Roy Dennis Wildlife Foundation

Ruth Tingay

Forest Enterprise Scotland

SSE

SSGEP

Publisher

MDPI AG

Reference51 articles.

1. Fielding, A.H., and Haworth, P.F. (2014). Golden Eagles in the South of Scotland: An Overview, SNH. Scottish Natural Heritage Commissioned Report No. 626.

2. Home-range size and examples of post-nesting movements for adult Golden Eagles (Aquila chrysaetos) in boreal Sweden;Moss;J. Raptor Res.,2014

3. Watson, J. (2010). The Golden Eagle, Poyser. [2nd ed.].

4. Measurement of Territory and Home Range Size in Birds;Odum;Auk,1955

5. Spatial distribution of undulating flight displays of territorial Golden Eagles Aquila chrysaetos in Lewis, Scotland;Reid;Bird Study,2019

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