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Literature review to assess bird species connectivity to Special ...

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making longer movements (5 <strong>to</strong> 10km) from their natal area during their first year, but<br />

these are less common (Grant, 2007). The work by Caizergues & Ellison (2002)<br />

revealed only 9% of males had emigrated from the 836ha study area between the<br />

1990 <strong>to</strong> 1998 research period. In combination, this suggests that a small proportion<br />

of first-year males may disperse more widely.<br />

Leks comprising single <strong>bird</strong>s are more mobile and ephemeral, and may be used for<br />

just one or two years compared <strong>to</strong> the regular use of traditional leks (Cayford, 1993).<br />

The implications are that in areas with large numbers of single-<strong>bird</strong> leks (e.g. Cowal,<br />

Argyll), male black grouse movements over greater distances may be more common.<br />

2.12.9 Seasonal movements<br />

The main seasonal movements of black grouse arise from natal dispersal, of which<br />

Caizergues & Ellison (2002) identified two discreet phases; one in autumn (Oc<strong>to</strong>ber)<br />

and the other in spring (mid-April <strong>to</strong> early May). There are periods of reduced<br />

mobility between these phases. The study also showed that mean distance travelled<br />

by females exceeded that of males in autumn but not in spring. These findings tally<br />

with the dispersal patterns identified by Warren & Baines (2002). From a sample of<br />

48 radio-tagged poults they found distinct dispersal periods in late autumn (mean:<br />

10.3km) and again in early spring (mean: 5.8km).<br />

Apart from natal dispersal, both males and females remain in the same general<br />

locality throughout the year and rarely move more than a few kilometres from the lek<br />

they attend in spring (Warren & Baines, 2004).<br />

Winter home ranges of full-grown <strong>bird</strong>s are relatively small and sometimes distinct<br />

from areas used at other times of the year, with <strong>bird</strong>s congregating on particularly<br />

favoured areas (Baines et al., 2002; Calladine, 2002). Examples of favoured winter<br />

habitats are patches of birch and willow, tall vegetation where grazing is restricted,<br />

vestigial areas of ericaceous vegetation, and herb-rich meadows (Willebrand, 1988;<br />

Baines, 1994; Starling-Westerberg, 2001; Baines et al., 2002). In their study, Picozzi<br />

& Catt (1988) identified the greatest use of moorland and rough grassland <strong>to</strong> be from<br />

the spring <strong>to</strong> the late summer or early autumn, whilst most use woodland use was<br />

generally during winter.<br />

Ringing data are extremely limited. All 13 recoveries in Scotland have been of<br />

Scottish-ringed <strong>bird</strong>s, with 10 controlled within 9km of the ringing site and three within<br />

10-99km (Grant 2007).<br />

2.12.10 Post-breeding chick dispersal<br />

As reported above, brood home ranges are small and can be under 50ha (Starling,<br />

1990) equivalent <strong>to</strong> a distance of less than 400m. However, they are more typically<br />

between 10ha and 30ha (Warren & Baines, 2004) equivalent <strong>to</strong> distances between<br />

180 and 300m. Dispersal by first-year <strong>bird</strong>s is mainly confined <strong>to</strong> hens, with a mean<br />

autumn dispersal of 10.3km from the natal site <strong>to</strong> the first breeding location, and early<br />

spring movements of 5.8km (Warren & Baines, 2002).<br />

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