Roost selection by barbastelle bats (Barbastella barbastellus, Chiroptera: Vespertilionidae) in beech woodlands of central Italy: consequences for conservation
Introduction
Roosts play a crucial role in bat biology (e.g. Kunz, 1982), and their availability affects both the geographic occurrence of bat species and the diversity of bat communities (e.g. Findley, 1993). Many of the nearly 850 microchiropteran species roost in trees (e.g. Kunz, 1982, Brigham et al., 1997, Sedgeley & O'Donnell, 1999a, Boonman, 2000, Lakci & Schwierjohann, 2001, Menzel et al., 2002). Deforestation is regarded as a specially serious threat to conservation of these mammals (Hutson et al., 2001). Because old and dead trees are richer in cavities suitable for roosting, they may be particularly important for bats (Hutson et al., 2001, Parsons et al., 2003). The roosting requirements of tree-dwelling bat species represent a major conservation issue, and investigation of roost selection is needed to set up appropriate guidelines for forest management.
The barbastelle bat (Barbastella barbastellus (Schreber, 1774)) is a medium-sized vespertilionid (forearm length=36.5–43.5 mm, body mass=6–13.5 g.; Schober and Grimmberger, 1997) occurring in Europe, North Africa and Asia (Hutson et al., 2001, Urbanczyk, 1999). It is recorded over much of Europe, except in the highest latitudes (Iceland, Northern Ireland, Estonia and most of Scandinavia; Urbańczyk, 1999). B. barbastellus is classified as ‘Vulnerable’ at a global scale (Hutson et al., 2001), ‘Endangered’ in Italy (Bulgarini et al., 1998) and is threatened in many areas of Europe, especially in the west where it may be one of the rarest bat species (Urbańczyk, 1999). The species is protected by European law under Annexes II and IV of the Habitats Directive 92/43/EEC.
B. barbastellus shows roosting preferences that should be regarded as a key point in conservation protocols (Hutson et al., 2001). The species has been described as roosting mainly in human-made structures in summer, with trees being regarded as of secondary importance (Harrington et al., 1995, Schober & Grimmberger, 1997). However, radio-tracking studies have recently shown that B. barbastellus largely selects tree cavities as roosts (Greenaway, 2001, Steinhauser et al., 2002).
Few studies have dealt with roosting preferences in B. barbastellus: Greenaway (2001) examined roosting behaviour and activity of the species in Britain, while observations in continental Europe are limited to Germany (Steinhauser et al., 2002). Nothing is known about roost selection of B. barbastellus in southern Europe.
We examined roost selection in a breeding population of B. barbastellus from central Italy at three levels: woodland structure and management type; tree characteristics; and cavity characteristics. Our aim was to contribute to drawing up guidelines for conservation of this sensitive bat species in southern Europe.
Section snippets
Study area
The study was carried out at the Abruzzo, Lazio and Molise National Park (Lat 41°48′ N, Long 13°46′ E; Fig. 1), where Issartel (2001) first documented the occurrence of B. barbastellus. To our best knowledge, the area is home to the only breeding population documented for peninsular Italy. For data analysis, the area hereafter named ‘study area’, of 700 ha, was delimited after locating roosts by choosing limits corresponding to main mountain ridges and other topographic features to encompass
The bats and their roosting behaviour
We tagged 31 adult B. barbastellus, 10 lactating females in 2001 and 21 (19 lactating females, one pregnant female and one male) in 2002. No juvenile was observed, probably because most of them were not volant at the time captures were made. The male we captured was the only one ever recorded in the study area (Issartel, 2001; D. Russo, unpublished data). Forearm length was 39.8±1.0 mm, and body mass was 8.2±1.1 g; on average, the tag weighed 6.0±0.7% of the bat's body mass (range 4.0–7.2%).
B. barbastellus roosting preferences
In this study, B. barbastellus made a great use of dead trees for roosting as observed in northern Europe (Greenaway, 2001, Steinhauser et al., 2002), as also found for other tree-dwelling bat species (Brigham et al., 1997, Sedgeley & O'Donnell, 1999a, Law & Anderson, 2000, Weller & Zabel, 2001, Lumsden et al., 2002, Kurta et al., 2002). In the study area, dead trees occurred most frequently in unmanaged woodland, where the number of roosts we located was higher than expected from the
Acknowledgments
We gratefully acknowledge the Nando Peretti Foundation and the Abruzzo, Lazio and Molise National Park for funding the study. Francesco Garofano and Giovanni Mastrobuoni helped in capture operations and radio-tracking. Cinzia Sulli and Carmelo Gentile provided information on woodland management at the Abruzzo, Lazio and Molise National Park. Colin O'Donnell and Jane Sedgeley gave precious advice on data collection and analysis, Mark Weir kindly made some linguistic improvements to the ms. and
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