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Capercallie: A Review of Research Needs

 

Table 1 - Contents of capercaillie crops from two studies in north-east Scotland. Items other than conifers and dwarf shrubs are excluded

Plant species

1965-66 (Zwickel, 1966)

1977-80 (Jones, 1982)

Conifers

Scots pine

90.0

69.2 (M2)

63.1 (F3)

Sitka spruce

T1

2.4 (M)

39.1 (F)

Norway spruce

T

T

Douglas fir

3.0

0

Dwarf shrubs

Blaeberry

T

12.5 (M)

3.2 (F)

Cow berry

T

T

Heather

T

9.6 (M)

13.7 (F)

Erica spp.

0

T

Crow berry

0

T

1trace. 2male. 3female

Table 2 - Some densities of capercaillie (both sexes) from autumn/winter counts in Scotland

Year

Locality

Habitat

Mean density
(birds per 100 ha)

Source

1965/66

Black Wood of Rannoch

Native pinewood

14-20

(Johnstone & Zwickel, 1966)

1975/76

Glen Tanar

Native pinewood

10.1-11.0

(Moss et al., 1979)

1975/76

Kinveachy

Native pinewood

16.9-17.8

(Moss et al., 1979)

1976/77

Kinveachy

Native pinewood

23.3-36.2

(Moss et al., 1979)

1976/77

Black Wood of Rannoch

Native pinewood

28.1-31.5

(Moss et al., 1979)

1976/77

Abernethy

Native pinewood

13.6-24.0

(Moss et al., 1979)

1976/77

Monaughty

Pine plantation

9.0-17.5

(Moss et al., 1979)

1976/77

Culbin

Pine plantation

1.4-8.3

(Moss et al., 1979)

1975-83

Glen Tanar

Native pinewood

11-23

(Moss & Oswald, 1985)

1975-85

Kinveachy

Native pinewood

6-34

(Moss & Weir, 1987)

1992-94

Scotland

Native pinewood

2.67-5.0

(Catt et al., 1998)

1992-94

Scotland

Other woodland

0.39-0.94

(Catt et al., 1998)

1998-99

Scotland

Native pinewood

1.69

(Wilkinson et al., 1999)

1998-99

Scotland

Other woodland

0.43

(Wilkinson et al., 1999)

 

Table 3 - Criteria to evaluate re-establishment proposals (IUCN, 1987)

  • There should be good historical evidence of former natural occurrence
  • There should be clear understanding of why the species was lost to the area. In general, only those lost through human agency and unlikely to recolonise naturally should be regarded as suitable candidates
  • The factors causing extinction should have been rectified
  • There should be suitable habitats of sufficient extent to which the species can be re-established
  • The individual taken for re-establishment should be from a population as close as possible to that of the native population
  • The loss should not prejudice the survival of the population from which they were taken

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