Tree cavity density is a limiting factor for a secondary cavity nester in second-growth Andean temperate rainforests

Cavity-nesting bird populations are most frequently limited by the number of tree cavities available in second-growth forests. However, this possible limitation of a key resource is less clear in old-growth forests. We compared forest attributes (i.e., basal area, density of larger trees, density of...

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Veröffentlicht in:Ornithological Applications 2024-12, Vol.126 (4), p.1
Hauptverfasser: Altamirano, Tomás A, Novoa, Fernando, Ibarra, José Tomás, Navarrete, Sergio A, Bonacic, Cristián, Martin, Kathy
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container_issue 4
container_start_page 1
container_title Ornithological Applications
container_volume 126
creator Altamirano, Tomás A
Novoa, Fernando
Ibarra, José Tomás
Navarrete, Sergio A
Bonacic, Cristián
Martin, Kathy
description Cavity-nesting bird populations are most frequently limited by the number of tree cavities available in second-growth forests. However, this possible limitation of a key resource is less clear in old-growth forests. We compared forest attributes (i.e., basal area, density of larger trees, density of dead trees, and tree cavity density) in second-growth and old-growth stands in Andean temperate rainforests in southern Chile. To examine the role of nest-site availability in limiting the populations of Aphrastura spinicauda (Thorn-Tailed Rayadito), we monitored their populations in both forest types during a 5-year period (2008-2013), while we conducted an experiment in which nest boxes were added and then, after two years, removed by blocking cavity entrances. In old-growth forests, as compared to second-growth forests, we found a more than double basal area (99.6 vs. 43.7 m2 ha−1), a 3 times higher density of larger trees (88.2 vs. 36.4 trees ha−1), and a 1.5 times higher number of small cavities (25.9 vs. 10.3 cavities ha−1). The density of cavities also strongly increased with tree diameter and basal area. In second-growth forests, A. spinicauda showed a strong response to the addition, and later to the removal of nest boxes, with population abundance increasing by 13% and then decreasing by 50%, respectively. In contrast, we found no impact on old-growth stands. Our experiment emphasizes the importance of maintaining large and dead trees in second-growth, disturbed, and managed forests. These trees provide suitable cavities for A. spinicauda, and likely many other secondary cavity nesters, increasing their abundance in a Globally significant Biodiversity Hotspot in southern South America. A Spanish translation of this manuscript is available as Supplementary Material.
doi_str_mv 10.1093/ornithapp/duae031
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In second-growth forests, A. spinicauda showed a strong response to the addition, and later to the removal of nest boxes, with population abundance increasing by 13% and then decreasing by 50%, respectively. In contrast, we found no impact on old-growth stands. Our experiment emphasizes the importance of maintaining large and dead trees in second-growth, disturbed, and managed forests. These trees provide suitable cavities for A. spinicauda, and likely many other secondary cavity nesters, increasing their abundance in a Globally significant Biodiversity Hotspot in southern South America. 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source Oxford University Press Journals All Titles (1996-Current); Free E- Journals
subjects Availability
Biodiversity hot spots
Bird populations
Boxes
Cavities
Cavity nesters
Cavity nesting
Dead wood
Density
Forest management
Forests
Holes
Limiting factors
Nest boxes
Nesting
Populations
Rainforests
Trees
title Tree cavity density is a limiting factor for a secondary cavity nester in second-growth Andean temperate rainforests
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