PreprintPDF Available

Abstract and Figures

Tree cavities are an essential resource for cavity-dwelling mammals, birds, invertebrates and fungi, and so they are important for maintaining forest biodiversity. In North American forests, woodpeckers (Picidae) play a keystone role in cavity creation by excavating holes. However, in European forests many hole-nesting songbirds rely on non-excavated cavities that are formed by processes of fungal decay and compartmentalization after tree damage. Several factors are recognised in initiating non-excavated cavities that are used by hole-nesting birds, including loss of a tree branch or stem breakage, but this topic is poorly studied. Here, we propose that bark stripping by large herbivores (e.g. Red Deer Cervus elaphus and European Bison Bison bonasus) could be another important, and previously overlooked, mechanism for initiating tree cavities that are used by hole-nesting birds. We suggest that, after the initial damage from herbivore bark-stripping, fungal decay can create specific elongated, slit-like cavities, which are particularly important as nest sites for some common forest songbirds. We outline this idea using original observations and evidence from the literature, primarily from the primeval forest in Poland’s Białowieża National Park. We also use studies from elsewhere in Europe to show a generally low usage of slit cavities by birds where large herbivores are scarce or absent. We suggest that restoring such animals in European forests could help to restore the abundance and diversity of the tree cavity resource for hole-dwelling species. We encourage future research to investigate this proposal of large herbivores being important agents of tree cavity formation that could enhance biodiversity. A revised version is accepted by Acta Ornithologica July 2022 (in press).
Content may be subject to copyright.
Acta Ornithologica (accepted July 2022)
1
Do large herbivores have an important role in initiating tree cavities used by hole-
1
nesting birds in European forests?
2
3
Richard K Broughton 1, 2 *, Oliwia Karpińska 3, Katarzyna Kamionka-Kanclerska 3, Marta
4
Maziarz 4
5
6
1 UK Centre for Ecology & Hydrology, Maclean Building, Benson Lane, Crowmarsh Gifford,
7
Wallingford, Oxfordshire OX10 8BB, UK. ORCiD: 0000-0002-6838-9628
8
2 Senior Research Associate, Department of Biology, University of Oxford, Zoology Research
9
and Administration Building, 11a Mansfield Road, Oxford OX1 3SZ, UK.
10
3 Siedlce University of Natural Sciences and Humanities, Faculty of Exact and Natural
11
Sciences, Institute of Biological Sciences, ul. B. Prusa 14, 08-110 Siedlce, Poland. ORCiD:
12
Karpińska: 0000-0003-0926-3811; Kamionka-Kanclerska: 0000-0003-3493-7400
13
4 Museum and Institute of Zoology, Polish Academy of Sciences, Wilcza 64, 00-679 Warsaw,
14
Poland. ORCiD: 0000-0002-2921-5713
15
16
17
18
19
20
21
22
23
Acta Ornithologica (accepted July 2022)
2
ABSTRACT
24
Tree cavities are an essential resource for cavity-dwelling mammals, birds, invertebrates and
25
fungi, and so they are important for maintaining forest biodiversity. In North American forests,
26
woodpeckers (Picidae) play a keystone role in cavity creation by excavating holes. However,
27
in European forests many hole-nesting songbirds rely on non-excavated cavities that are
28
formed by processes of fungal decay and compartmentalization after tree damage. Several
29
factors are recognised in initiating non-excavated cavities that are used by hole-nesting birds,
30
including loss of a tree branch or stem breakage, but this topic is poorly studied. Here, we
31
propose that bark stripping by large herbivores (e.g. Red Deer Cervus elaphus and European
32
Bison Bison bonasus) could be another important, and previously overlooked, mechanism for
33
initiating tree cavities that are used by hole-nesting birds. We suggest that, after the initial
34
damage from herbivore bark-stripping, fungal decay can create specific elongated, slit-like
35
cavities, which are particularly important as nest sites for some common forest songbirds. We
36
outline this idea using original observations and evidence from the literature, primarily from
37
the primeval forest in Poland’s Białowieża National Park. We also use studies from elsewhere
38
in Europe to show a generally low usage of slit cavities by birds where large herbivores are
39
scarce or absent. We suggest that restoring such animals in European forests could help to
40
restore the abundance and diversity of the tree cavity resource for hole-dwelling species. We
41
encourage future research to investigate this proposal of large herbivores being important
42
agents of tree cavity formation that could enhance biodiversity.
43
44
INTRODUCTION
45
Tree cavities are essential microhabitats in forest ecosystems, providing shelter and breeding
46
sites for many mammals, birds, invertebrates and fungi (Stokland et al. 2012). Despite a large
47
literature on cavity-using species, particularly birds and bats, there is no universal definition of
48
a tree cavity, such as a typical origin or morphology. In the context of nesting birds, however,
49
Acta Ornithologica (accepted July 2022)
3
a tree cavity is broadly defined as a hole or hollow within a tree that provides a semi-enclosed
50
chamber in which a bird can nest or roost, but these can take a variety of forms (Wesołowski
51
& Martin 2017).
52
Tree cavities are classified as excavated or non-excavated. Excavated cavities are created
53
directly by animals, especially woodpeckers (Picidae), which peck or hammer into the wood
54
to excavate a nest chamber (Wesołowski & Martin 2017). Non-excavated tree cavities are
55
those formed by fungal decay of the wood following damage or infection, which can eventually
56
result in a cavity (Stokland et al. 2012). Globally, tree cavities are more abundant in humid
57
regions that promote fungal decay, although they appear to be less abundant in Palearctic
58
forests, including those of Europe (Remm & Lõhmus 2011).
59
Where forests have a history of management, as in Europe, there is typically a severe
60
reduction in the availability of tree cavities, compared to natural forest (Walankiewicz et al.
61
2014, Andersson et al. 2018). This cavity deficit is due to the logging of older and decaying
62
trees, selective thinning, and the loss of keystone animals that create holes (Remm & Lõhmus
63
2011). This reduced availability may limit the number and variety of hole-nesting animals that
64
are reliant on pre-existing cavities.
65
Providing artificial cavities, such as nest-boxes for birds or bats, is a common mitigation for
66
the reduced availability of tree holes in managed woodlands. However, nest-boxes are costly
67
and labour-intensive, requiring regular maintenance (Lindenmayer et al. 2009, Wesołowski &
68
Martin 2017). Furthermore, nest-boxes have very different microclimatic conditions from
69
natural tree cavities, which may have ecological implications, so they cannot be treated as
70
direct substitutes for tree cavities (Wesołowski & Stańska 2001, Broughton et al. 2015,
71
Maziarz et al. 2017).
72
Due to a strong bias towards nest-boxes in ornithological research, however, studies of birds
73
using tree cavities are particularly important for understanding natural behaviour (Wesołowski
74
2011). In North American forests, woodpeckers perform a keystone role by excavating most
75
Acta Ornithologica (accepted July 2022)
4
of the tree cavities that are later used by other birds and mammals (Martin & Eadie 1999). In
76
parts of Asia for where data are available, woodpeckers may be important but do not appear
77
to have a keystone role for other cavity-nesting birds (Bai et al. 2005, Baral et al. 2018). In
78
European forests, much of the literature on birds breeding in natural cavities comes from the
79
long-running studies established by Ludwik Tomiałojć, Wiesław Walankiewicz and Tomasz
80
Wesołowski, in Poland’s Białowieża National Park (NP). These studies suggested that
81
woodpeckers are generally not keystone species in European forests (reviewed in Wesołowski
82
et al. 2007a). Instead, non-excavated cavities, rather than old woodpecker holes, are far more
83
important to hole-nesting songbirds in European forests than in North America (Tomiałojć et
84
al. 1984, Wesołowski & Martin 2017).
85
Different types of non-excavated cavities were outlined by Wesołowski (2007a) and
86
Wesołowski & Martin (2017), including 1) ‘knotholes’ that form where a branch detaches from
87
a main stem, 2) ‘chimneys’ that have an upward-facing entrance on snapped stems, 3) ‘cracks’
88
formed by splits in the trunk, and 4) other ‘trunk holes’ in decaying wood, where a cavity forms
89
on the main stem. Where trunk holes have an elongated, vertical opening, these are also
90
referred to as ‘slit’ cavities (Wesołowski 2007a).
91
There is little direct observation of exactly how non-excavated tree cavities are initiated, but
92
they appear to form after damage to the protective bark through injury or disease, which
93
exposes the underlying sapwood or heartwood (Stokland et al. 2012, Kõrkjas et al. 2021). A
94
fungal infection can then take hold, leading to progressive decay of the wood, potentially
95
leading to a cavity forming in the heartwood (Boddy 2001). A living tree counters the damage
96
by compartmentalisation, which creates a protective callus around the wound or cavity (Shigo
97
1984). Compartmentalisation in living trees is a dynamic process, changing the shape of a
98
tree cavity and its opening over time, which may continue to expand and deepen, or the tree
99
may heal over the entrance and the cavity becomes unusable (Wesołowski 2012).
100
Wesołowski and Martin (2017) listed the ways that a non-excavated tree cavity could be
101
initiated, which then develops to become usable by birds. These agents comprised snow,
102
Acta Ornithologica (accepted July 2022)
5
frost, fire, lightning, insects, foraging birds and the loss of branches. Kõrkjas et al. (2021) and
103
Larrieu et al. (2018) added to this list of cavity-forming mechanisms with physical abrasion,
104
caused by falling trees or rocks, and dendrotelms, which are natural basins in the tree that
105
can deepen to hold water.
106
Here, however, we propose another means of tree damage that appears to have been largely
107
overlooked as a potential source of cavities that are important for hole-nesting birds, which is
108
bark stripping by large mammals. The larger native herbivores of European forests, such as
109
Red Deer Cervus elaphus, Eurasian Elk Alces alces and European Bison Bison bonasus, are
110
known to habitually strip bark from young trees (deciduous and coniferous), predominantly in
111
winter or early spring, by biting with their incisors and pulling off the bark in strips (Gill 1992a,
112
Verheyden et al. 2006, Kelterborn et al. 2009, Paszkiewicz & Januszczak 2010, Welch & Scott
113
2017, Kõrkjas et al. 2021, Jarnemo et al. 2022). Bark can also be damaged or stripped when
114
these animals rub their antlers or horns on tree trunks (Gill 1992a, Edvardsson et al. 2021).
115
Both activities result in exposed or damaged wood, and the opportunity for subsequent decay.
116
Kõrkjas et al. (2021) and Gill (1992a, 1992b) reviewed how bark stripping and antler rubbing
117
by large herbivores, particularly Red Deer and European Elk, exposed the underlying wood,
118
and was one of the agents of damage and microhabitat creation on living trees. Edvardsson
119
et al. (2021) and Paszkiewicz & Januszczak (2010) also showed how bark stripping and horn
120
rubbing by European Bison left elongated wounds on trees that propagated decay, including
121
stem rot, affecting up to 20% of available trees. However, despite the widespread
122
documentation of tree wounds resulting from bark stripping, we can find no proposal by
123
previous authors that this activity can lead to the formation of tree cavities that could be used
124
by hole-nesting birds.
125
Based on evidence from the natural forest of Białowieża NP, we propose that bark stripping
126
by large herbivores may be an important agent in cavity formation, specifically of slit-like tree
127
cavities that are important for communities of hole-nesting songbirds (Wesołowski 1989). To
128
outline the theory, we first document examples of tree damage observed in the Białowieża NP
129
Acta Ornithologica (accepted July 2022)
6
that we attribute to large herbivores, showing an apparent progression of decay from initial
130
damage towards slit-type cavities. We then highlight previous studies showing the importance
131
of slit cavities for hole-nesting birds in natural forest ecosystems. We then review the
132
prevalence of slit-like tree cavities in studies of hole-nesting birds from elsewhere in Europe,
133
where large herbivores are depleted or absent. Finally, we ask whether restoring large
134
herbivores to European forests through rewilding could re-establish an important component
135
of woodland ecology, by promoting the abundance and diversity of tree cavities for hole-
136
nesting species.
137
138
TREE DAMAGE AND SLIT CAVITIES IN BIAŁOWIEŻA NATIONAL PARK
139
The Białowieża NP is the principal site in Europe where the natural formation of tree cavities,
140
and their use by nesting birds, can be observed in relatively undisturbed forest. The Białowieża
141
NP is the last extensive remnant of primeval lowland temperate forest in Europe, containing
142
an almost complete assemblage of native plants and animals in unmanaged old-growth
143
stands. These stands have a multi-layered and multi-aged structure, consisting of up to a
144
dozen tree species, with abundant decaying wood, where natural processes are little affected
145
by direct human activity (Tomiałojć et al. 1984, Wesołowski 2007b). The few extirpated
146
animals missing from the ecosystem are the Brown Bear Ursus arctos (though individuals
147
sometimes occur: Diserens et al. 2020) and the globally extinct Aurochs Bos primigenius.
148
Tomiałojć et al. (1984) and Wesołowski (2007a) listed up to 31 bird species that regularly
149
breed in tree cavities in Białowieża NP, comprising nine primary cavity-excavators (including
150
seven woodpecker species), 16 obligate secondary hole-nesters, and six facultative hole-
151
nesters. As such, the tree cavity resource and hole-nesting community is virtually intact, in
152
contrast to most degraded or secondary woodlands elsewhere in Europe that have reduced
153
tree cavities and local extinctions of some cavity-nesting birds (Fuller et al. 2005, Broughton
154
et al. 2013). As such, Białowieża NP is an invaluable reference site for exploring the
155
Acta Ornithologica (accepted July 2022)
7
relationships between species in forest ecosystems, including cavity resources and their
156
users.
157
We made three sets of preliminary observations of tree damage in Białowieża NP that we
158
attributed to initial bark stripping (Table 1 and Fig. 1, with more example images in Appendix
159
1). These observations involved the photographing of 81 trees that showed bark stripping
160
injuries, elongated decay and slit-like cavities, which were opportunistically found during
161
fieldwork at various locations across the forest in 2018 (see Broughton et al. 2020 for
162
locations), largely within 187 ha of oak-lime-hornbeam Tilio-Carpinetum stands. In 2021, we
163
made further observations of 26 trees showing recent bark stripping during vegetation
164
sampling in the southern part of Białowieża NP (25 ha of Tilio-Carpinetum stands, within plot
165
EN in Figure 1 of Broughton et al. 2020). Further sampling measurements and photographs
166
of recent bark stripping and presumed subsequent decay, scars or slit-like cavities were taken
167
from 34 trees in the same area of Białowieża NP in 2022 (Table 1, Fig. 1, Appendix 1).
168
Sampling was not systematic, and so densities of trees featuring bark stripping cannot be
169
inferred.
170
We attributed these tree wounds to initial bark stripping by herbivores based on the height
171
above the ground and the nature of the damage, the pattern of decay or scarring, and their
172
apparent similarity to herbivore damage documented by Edvardsson et al. (2021),
173
Paszkiewicz & Januszczak (2010) and Kõrkjas et al. (2021). The observations involved mostly
174
young or thin trees, with a general diameter at breast height (DBH) of less of than 30 cm. The
175
damage or decay was recorded between ground level and approximately 2.5 m high. Except
176
for one Norway Spruce Picea abies, all of the trees involved were deciduous, mostly immature
177
Small-leaved Limes Tilia cordata and Common Hornbeams Carpinus betulus, which are
178
common in the area (Karpusta 2019), and also some Common Hazels Corylus avellana.
179
180
Acta Ornithologica (accepted July 2022)
8
TABLE 1. Attributes of sampled and observed trees in Białowieża National Park that exhibited marks,
181
wounds, decay and cavities as a presumed result of bark-stripping by large herbivores.
182
Sample
year
DBH
mean
cm
DBH
max
cm
Wound
height
m
Tree species %
Trees
n
Hornbeam
Hazel
Other
2018
-
~30
~2.5
63
0
2
81
2021
10
74
1.6
46
38
0
26
2022
17
57
2.3
30
12
0
34
183
The three sets of observations in Table 1 are not systematic or fully representative. However,
184
these observations are indicative of the kinds of tree wounds and decay on which we based
185
our ideas, which is the proposed progression from initial bark stripping to subsequent decay
186
and the eventual formation of some slit-like cavities that are used by hole-nesting birds.
187
In our observations, fresh wounds from bark stripping (including horn or antler rubbing)
188
appeared obvious and distinctive, consisting of damaged bark from gouging, fraying and
189
removal of strips (Fig. 1A). The dark brown discolouration of exposed inner bark, fresh yellow-
190
orange sapwood, and an absence of thickened scar tissue around the damage suggested that
191
these wounds are relatively new, probably in recent weeks/months (Jarnemo et al. 2022).
192
Wounds that appeared older were duller in colour and with thickened tissue surrounding
193
exposed wood, as the tree compartmentalised the damage (Fig. 1B). Some wounds then
194
clearly progressed to a deep elongated fissure within the bark, as it gradually closed over the
195
wound (Fig. 1C). Wounds that had apparently closed over completely were indicated by a long
196
scar on the bark (Fig. 1D).
197
However, other wounds seem to progress on a different trajectory if the heartwood was
198
degraded by fungal decay before the wound healed over (Shigo 1984). This decay appeared
199
to create a cavity behind the exposed panel of wood, with an opening at the top or bottom of
200
the fissure (Fig. 1E). Where the exposed wood had degraded completely, then the wound
201
Acta Ornithologica (accepted July 2022)
9
could become a narrow and hollow fissure within the tree, forming an elongated slit-shaped
202
cavity (Fig. 1F). In other wounds, it appears that progressive decay of extensive damage may
203
result in a large, open, elongated hollow (Fig. 1G).
204
205
FIGURE 1. Wounds, scars and slit-like cavities on trees in Białowieża National Park, showing sequence
206
of (A) initial bark stripping by a large herbivore causing an elongated wound; (B) older bark-stripping
207
wound showing compartmentalisation (thickened callus) surrounding an exposed panel of heartwood;
208
(C) wound healing to close over exposed heartwood and leaving a deep fissure; (D) successful healing
209
Acta Ornithologica (accepted July 2022)
10
that has closed over the wound and left an elongated scar; (E) failure of the wound to heal and decay
210
of an exposed panel of heartwood, creating a cavity in a slit-like wound that is used by nesting Marsh
211
Tits Poecile palustris; (F) total decay and disappearance of the exposed heartwood panel, creating an
212
elongated slit-like cavity used by nesting Marsh Tits; (G) progressive heartwood decay that has formed
213
a deep hollow in the tree.
214
215
If the type of bark stripping and tree damage observed in Białowieża NP was indeed caused
216
by large herbivores, the most likely species are Red Deer and European Bison. These species
217
typically cause more extensive damage, affecting larger trees and reaching higher above the
218
ground, compared to the smaller Roe Deer Capreolus capreolus (Gill et al. 2000, Paszkiewicz
219
& Januszczak 2010). Eurasian Elk is relatively scarce in the forest (Jędrzejewski et al. 2002),
220
and so its contribution was probably negligible. Obvious marks made by horns or antler tines
221
are visible on some images, and could only have been made by large herbivores. There is
222
currently no information for how long it takes for usable slit cavities to develop after the initial
223
tree damage, as the trajectory and rate of cavity formation are poorly understood (Stokland et
224
al. 2012). The typical lifespan of usable cavities in Białowieża NP is a median 11-13 years
225
(Wesołowski 2012), suggesting that cavities may evolve on a timescale of years or decades
226
in this forest.
227
228
THE IMPORTANCE OF SLIT CAVITIES FOR HOLE-NESTING BIRDS
229
The slit cavities depicted in Figs. 1E and 1F are distinctive among the types of tree holes
230
documented in Białowieża NP. Kapusta (2019) sampled the tree cavities available to hole-
231
nesting birds in Białowieża NP, and found that three-quarters of the cavity resource consisted
232
of oval or elongated holes, with almost half of all cavities being strongly elongated or slit-like.
233
Slit-like cavities also feature prominently in studies of nesting songbirds from Białowieża NP.
234
Of the types of non-excavated tree cavity documented by Wesołowski (2007a) and
235
Acta Ornithologica (accepted July 2022)
11
Wesołowski & Martin (2017), it is the trunk hole cavities with elongated slit-like entrances that
236
are particularly favoured by many of Białowieża NP’s hole-nesting birds. Wesołowski (1989)
237
reported that 20% of all nests of seven hole-nesting species were in slit cavities. For several
238
common species, including Blue Tits Cyanistes caeruleus, Great Tits Parus major, Marsh Tits
239
Poecile palustris and European Robins Erithacus rubecula, slit cavities are the most frequent
240
nest sites (Wesołowski 1996, Wesołowski & Rowiński 2012, Maziarz et al. 2015, Karpińska et
241
al. 2022). Slit cavities are also commonly used by Collared Flycatchers Ficedula albicollis and
242
Pied Flycatchers F. hypoleuca (Czeszczewik and Walankiewicz 2003, Walankiewicz et al.
243
2007), and even by Common Blackbirds Turdus merula (Tomiałojć 1993), so they are clearly
244
an important resource for hole-nesting songbirds in natural forests.
245
The Białowieża studies show that many slit cavities used by nesting birds partially overlap with
246
the height range of bark stripping by larger herbivores, i.e. within approximately 2 m above the
247
ground (Gill 1992a, Paszkiewicz & Januszczak 2010, Vacek et al. 2020, Edvardsson et al.
248
2021). For example, among nest sites of Great Tits and European Robins, a fifth of the slit
249
cavities used by these birds, 20% and 19% respectively, were within 2 m of the ground
250
(recalculated from raw data from Maziarz et al. (2015) and Karpińska et al. (2022)). The
251
studies of nesting birds from Białowieża NP also show that those species nesting at lower
252
average heights above the ground are more likely to use slit-like or elongated cavities than
253
those typically nesting in cavities at greater heights (Fig. 2).
254
These differences between species in cavity usage may be partially related to body size. The
255
larger European Starlings Sturnus vulgaris and Eurasian Nuthatches Sitta europaea nest at
256
the greatest mean heights and rarely use slit cavities (Fig. 2), preferring larger cavities with
257
larger entrances, such as old woodpecker holes (Wesołowski & Rowiński 2004, Wesołowski
258
2022). The larger Tawny Owl Strix aluco, which uses holes averaging 9.9 m above the ground
259
in Białowieża NP, also does not use slit cavities, but this probably reflects their requirement
260
for a much larger cavity entrance than any of the songbirds (Yatsiuk & Wesołowski 2020).
261
262
Acta Ornithologica (accepted July 2022)
12
263
FIGURE 2. Mean height of nest cavities above the ground versus the percentage of nest-cavities that
264
are elongated slit-like cavities, for European Robin (R), Marsh Tit (MT), Blue Tit (BT), Great Tit (GT),
265
Collared Flycatcher (CF), Pied Flycatcher (PF), European Starling (S) and Eurasian Nuthatch (NH). A
266
linear regression trendline is shown (R2 = 0.32). Data are derived from studies in Białowieża National
267
Park (see text).
268
269
However, a declining frequency of slit cavities among songbird nest sites at increasing heights
270
from the ground (Fig. 2) could, potentially, also reflect a declining availability of slit cavities at
271
greater heights. The evidence to test this is lacking at present, and many slit-like cavities
272
clearly occur at heights well above the range of bark stripping by herbivores. These higher
273
slits must be caused by mechanisms other than herbivores, such as abrasion from falling trees
274
(Kõrkjas et al. 2021) or initiated by bark stripping by Red Squirrels Sciurus vulgaris (Krauze-
275
Gryz & Gryz 2015). As such, large herbivores cannot be the only initiators of slit cavities, even
276
if they are potentially significant agents for initiating them closer to the ground.
277
Nevertheless, slit cavities, including those within several metres of the ground, are clearly of
278
great importance to nesting songbirds in Białowieża NP, particularly some of the tits,
279
Acta Ornithologica (accepted July 2022)
13
flycatchers and the European Robin. The frequent use of slit cavities by these species might
280
reflect selection for their specific qualities as nest sites. Narrow entrances, with a minimum
281
diameter of 16-30 mm, allows access to small songbirds but prevents medium-sized predators
282
from entering nest cavities (Wesołowski 2002, Wesołowski & Rowiński 2012). Also, an
283
elongated, slit-like entrance has a relatively large area, potentially improving gaseous
284
exchange, and letting extra light inside the cavity (Wesołowski & Maziarz 2012, Maziarz &
285
Wesołowski 2014); this would allow birds to nest at greater, safer distances from the entrance,
286
beyond the reach of larger predators unable to fully enter cavities (Walankiewicz 1991,
287
Wesołowski 2002). Consequently, slit cavities are generally safer nesting sites than other
288
types of tree holes (Maziarz et al. 2016).
289
290
EVIDENCE FROM TREE CAVITY STUDIES ELSEWHERE IN EUROPE
291
If large herbivores play a significant role in initiating slit cavities used by nesting birds, as we
292
propose, then these cavities should be less common in forests where large herbivores,
293
especially Red Deer and European Bison, are rare or absent. The European Bison has been
294
extinct across most of Europe for several centuries, whereas Red Deer have remained
295
relatively widespread and abundant, but with a more fragmented or localised distribution in
296
Scandinavia, western and southern Europe (Milner et al. 2006).
297
In British deciduous woods where Red Deer are locally absent in many areas, and European
298
Bison were never present (Kuemmerle et al. 2011), slit-shaped or elongated cavities (e.g. with
299
a vertical dimension of the entrance that is at least twice as large as the horizontal) are indeed
300
uncommon in studies of hole-nesting birds (Edington & Edington 1972, East & Perrins 1988,
301
Broughton et al. 2011, 2015). Slits or elongated cavities are similarly scarce in studies from
302
Germany (Ludescher 1973), Sweden (Nilsson 1984, Carlson et al. 1998), Estonia (Remm et
303
al. 2006) and Iberia (Camprodon et al. 2008). In The Netherlands, Van Balen et al. (1982)
304
found that cavities with oval entrances were the most common, although slits were present up
305
Acta Ornithologica (accepted July 2022)
14
to 2 m from the ground, and some could have been initiated by herbivores. However, it is
306
unclear which herbivores were present in any of these European study areas.
307
Importantly, though, based on the available information in the studies above, the proportions
308
of elongated or slit cavities used by birds in these other European forests appear far lower
309
than those reported from Białowieża NP, where slits account for a large number of nest
310
cavities used by tits, flycatchers and robins. This supports the theory that herbivores could be
311
a significant agent in initiating many slit cavities. Nevertheless, where slits are scarce, tits and
312
flycatchers elsewhere in Europe are still able to nest commonly, even abundantly, in knotholes
313
or other types of cavity outlined by Wesołowski (2007a) and Wesołowski & Martin (2017).
314
Overall, however, in forests without large herbivores, fewer trees would be affected by bark
315
stripping, and so probably fewer slit cavities would be expected to develop. As a result, the
316
availability and attributes of the cavity resource may be more limited, such as the hole
317
dimensions, height above the ground, predator defence, illumination and gaseous exchange
318
(Wesołowski 1996, Wesołowski & Maziarz 2012, Maziarz et al. 2016). The studies from
319
Białowieża NP show that, where slits are readily available, they are commonly or preferentially
320
used by many songbirds (Wesołowski 1996, Wesołowski & Rowiński 2012, Maziarz et al.
321
2015, Karpińska et al. 2022).
322
323
SUMMARY AND FUTURE CONSIDERATIONS
324
The evidence for large herbivores playing an important role as initiators of slit cavities is largely
325
circumstantial at present. However, taken together, the theory seems persuasive, linking the
326
bark stripping by large herbivores to tree wounds, decay and slit cavities, and then the
327
extensive use of slit cavities by hole-nesting birds, as shown by the Białowieża NP studies.
328
Further research is needed to provide the detailed evidence to underpin these proposed links.
329
Such studies may extend to other regions, such as North America, where bark stripping by
330
American Bison Bison bison or other large herbivores can also occur (Gill 1992a, Beschta et
331
Acta Ornithologica (accepted July 2022)
15
al. 2020). Establishing exactly how bark stripping might develop into slit cavities would be
332
valuable, including the frequency of stripping by different herbivores, which tree species are
333
most affected, and also the timescale of decay and cavity development, and how this fits
334
among other agents of cavity formation. Additionally, classifying cavity types in studies of
335
nesting birds or tree damage, similar to the nomenclature used by Wesołowski (2007a) and
336
Wesołowski & Martin (2017), would enable a more accurate assessment of the prevalence of
337
slit cavities and the role of herbivores.
338
Our theory at present is based on preliminary observations and the existing literature. A formal
339
study of the role of herbivores in tree cavity formation is yet to be undertaken, and the
340
information and hypotheses outlined here are aimed at promoting further research. If the
341
theory is correct, then the basic elements required for this mechanism of slit cavity
342
development would be the presence or large herbivores, sufficient time for the progress of
343
decay, and an absence of management interventions (such as selective thinning) that would
344
disrupt these natural processes.
345
Some of these elements are currently lacking in deciduous forests across much of Europe
346
because large mammals are depleted, management removes damaged trees, and logging
347
limits the timescale over which natural decay can operate. However, the reintroduction of large
348
native mammals and the restoration of natural processes and ecological complexity are
349
increasingly common approaches within the rewilding framework (Perino et al. 2019). There
350
is growing interest in trophic rewilding to restore large herbivores to parts of Europe from
351
where they had become extinct, including European Bison, Red Deer and Eurasian Elk (Tree
352
2017, Perino et al. 2019, Lord et al. 2020). Restoring these animals would also restore their
353
ecological functions in forest ecosystems (e.g. Nickell et al. 2018), which could include a
354
previously unappreciated role in initiating tree cavities, as we propose. Indeed, examination
355
by Edvardsson et al (2021) of preserved trees in early Holocene peat deposits in Sweden
356
suggests that there was frequent bark stripping by large herbivores in prehistory, leading to
357
the type of tree damage and subsequent decay that we observed in Białowieża NP.
358
Acta Ornithologica (accepted July 2022)
16
Meanwhile, reintroduction of European Bison to Damerower Werder and the Rothaar
359
Mountains in Germany has resulted in frequent debarking of forest trees (Kelterborn et al.
360
2009, Schröder et al. 2019), and reintroduction of Red Deer to Knepp Wildland in England
361
(Tree 2017) has also resulted in debarking and early cavity formation similar to that observed
362
in Białowieża NP (Appendix 2).
363
In conclusion, we propose that the potential role of large herbivores in increasing the
364
availability and variety of tree cavities is worthy of further exploration. The ecological function
365
of tree cavity initiation could provide further support for restoring large herbivores to European
366
forest ecosystems, with wider benefits for biodiversity.
367
368
ACKNOWLEDGEMENTS
369
We thank the Białowieża National Park authorities for access to the forest. We also thank
370
Knepp Wildland, particularly Penny Green and Ivan de Klee. The authors owe a debt of
371
gratitude to Professors Ludwik Tomiałojć, Wiesław Walankiewicz and Tomasz Wesołowski,
372
who provided valued knowledge, inspiration, support and friendship, and we dedicate this work
373
to their memory.
374
375
APPENDICES 1 & 2 FOLLOW THE REFERENCES
376
377
REFERENCES
378
Andersson J., Gomez E.D., Michon S., Roberge J.-M. 2018. Tree cavity densities and
379
characteristics in managed and unmanaged Swedish boreal forest. Scand. J. For. Res. 33:
380
233244.
381
Acta Ornithologica (accepted July 2022)
17
Bai M.-L., Wichmann F., Mühlenberg M. 2005. Nest-site characteristics of hole-nesting birds
382
in a primeval boreal forest of Mongolia. Acta Ornithol. 40: 114.
383
Baral R., Czeszczewik D., Walankiewicz W., Churski M., Bhusal P., Thapa T.B., Mikusiński
384
G. 2018. Characteristic of tree cavities in sal Shorea robusta forest, Nepal. J. For. Res. 23:
385
214220.
386
Beschta R.L., Ripple W.J., Kauffman J.B., Painter L.E. 2020. Bison limit ecosystem recovery
387
in northern Yellowstone. Food Webs 23: e00142.
388
Boddy L. 2001. Fungal community ecology and wood decomposition processes in
389
angiosperms: from standing tree to complete decay of coarse woody debris. Ecol. Bull. 49:
390
4356.
391
Broughton R.K., Bubnicki J.W., Maziarz M. 2020. Multi-scale settlement patterns of a
392
migratory songbird in a European primeval forest. Behav. Ecol. Sociobiol. 74: 128.
393
Broughton R.K., Hebda G., Maziarz M., Smith K.W., Smith L., Hinsley S.A. 2015. Nest-site
394
competition between bumblebees (Bombidae), social wasps (Vespidae) and cavity-nesting
395
birds in Britain and the Western Palearctic. Bird Study 62: 427437.
396
Broughton R.K., Hill R.A., Bellamy P.E., Hinsley S.A. 2011. Nest-sites, breeding failure and
397
causes of non-breeding in a population of British Marsh Tits Poecile palustris. Bird Study 58:
398
229237.
399
Broughton R.K., Hill R.A., Hinsley S.A. 2013. Relationships between patterns of habitat cover
400
and the historical distribution of the marsh tit, willow tit and lesser spotted woodpecker in
401
Britain. Ecol. Inform. 14: 2530.
402
Camprodon J., Salvanyà J., Soler-Zurita J. 2008. The abundance and suitability of tree cavities
403
and their impact on hole-nesting bird populations in beech forests of NE Iberian Peninsula.
404
Acta Ornithol. 43: 1731.
405
Acta Ornithologica (accepted July 2022)
18
Carlson A., Sandström U., Olsson K. 1998. Availability and use of natural tree holes by cavity
406
nesting birds in a Swedish deciduous forest. Ardea 86: 109119.
407
Czeszczewik D., Walankiewicz W. 2003. Natural nest sites of the Pied Flycatcher Ficedula
408
hypoleuca in a primeval forest. Ardea 91: 221230.
409
Diserens T.A., Churski M., Bubnicki J.W., Stępniak K., Pekach A., Selva N., Kuijper D.P.J.
410
2020. A dispersing bear in Białowieża Forest raises important ecological and conservation
411
management questions for the central European lowlands. Glob. Ecol. Conserv. 23: e01190.
412
East M.L., Perrins C.M. 1988. The effect of nestboxes on breeding populations of birds in
413
broadleaved temperate woodlands. Ibis 130: 393401.
414
Edington J.M., Edington M.A. 1972. Spatial Patterns and Habitat Partition in the Breeding
415
Birds of an Upland Wood. J. Anim. Ecol. 41: 331357.
416
Edvardsson J., Magnell O., Hansson A., Linderson H., Sjöström A., Nilsson B. 2021. Early
417
Holocene bark-stripping damages as an indicator of large herbivores: Evidence from a
418
submerged Mesolithic landscape in the Haväng area, southern Baltic basin. Holocene 31:
419
16701680.
420
Fuller R.J., Noble D.G., Smith K.W., Vanhinsbergh D. 2005. Recent declines in populations of
421
woodland birds in Britain. Br. Birds 98: 116143.
422
Gill R.M.A. 1992a. A review of damage by mammals in north temperate forests: 1. Deer.
423
Forestry: An International Journal of Forest Research 65: 363388.
424
Gill R.M.A. 1992b. A review of damage by mammals in north temperate forests: 3. Impact on
425
trees and forests. Forestry: An International Journal of Forest Research 65: 145169.
426
Gill R., Webber J., Peace A. 2000. The economic implications of deer damage. Contract
427
Report. The Deer Commission for Scotland.
428
Acta Ornithologica (accepted July 2022)
19
Jarnemo A., Widén A., Månsson J., Felton A. M. 2022. The proximity of rapeseed fields
429
influences levels of forest damage by red deer. Ecol. Solut. Evid. 3: e12156.
430
Jędrzejewski W., Schmidt K., Theuerkauf J., Jędrzejewska B., Selva N., Zub K., Szymura L.
431
2002. Kill rates and predation by wolves in ungulate populations in Białowieża primeval forest
432
(Poland). Ecology 83: 13411356.
433
Karpińska O., Kamionka-Kanclerska K., Neubauer G., Rowiński P. 2022. Characteristics and
434
selection of nest sites of the flexible cavity-nester, the European robin Erithacus rubecula, in
435
the temperate primeval forest (Białowieża National Park, Poland). Euro. Zool. J. 89: 114.
436
Kapusta A.S. 2019. Dynamika drzewostanów a zasoby dziupli w grądach Białowieskiego
437
Parku Narodowego. Unpublished PhD thesis, Siedlce University of Natural Sciences and
438
Humanities. (In Polish, with English abstract).
439
Kelterborn T., Zentner F., Zacharias K. 2009. 52 Years of European bison breeding on the
440
Wisent-Island in the heart of Mecklenburg-Vorpommern. European Bison Conservation
441
Newsletter 2: 172181.
442
Kõrkjas M., Remm L., Lõhmus A. 2021. Development rates and persistence of the
443
microhabitats initiated by disease and injuries in live trees: A review. Forest Ecol. Manag. 482:
444
118833.
445
Krauze-Gryz D., Gryz J. 2015. A review of the diet of the red squirrel (Sciurus vulgaris) in
446
different types of habitats. In: Shuttleworth C.M., Lurz P.W.W., Hayward M.W. (eds.). Red
447
squirrels: ecology, conservation & management in Europe. European Squirrel Initiative, pp.
448
3950.
449
Kuemmerle T., Radeloff V.C., Perzanowski K., Kozlo P., Sipko T., Khoyetskyy P., Bashta A.,
450
Chikurova E., Parnikoza I., Baskin L., Angelstam P., Waller D.M. 2011. Predicting potential
451
European bison habitat across its former range. Ecol. Appl. 21: 830843.
452
Acta Ornithologica (accepted July 2022)
20
Larrieu L., Paillet Y., Winter S., Bütler R., Kraus D., Krumm F., Lachat T., Michel A.K., Regnery
453
B., Vandekerkhove K. 2018. Tree related microhabitats in temperate and Mediterranean
454
European forests: A hierarchical typology for inventory standardization. Ecol. Indic. 84: 194
455
207.
456
Lindenmayer D.B., Welsh A., Donnelly C., Crane M., Michael D., Macgregor C., McBurney L.,
457
Montague-Drake R., Gibbons P. 2009. Are nest boxes a viable alternative source of cavities
458
for hollow-dependent animals? Long-term monitoring of nest box occupancy, pest use and
459
attrition. Biol. Conserv. 142: 3342.
460
Lord C.M., Wirebach K.P., Tompkins J., Bradshaw-Wilson C., Shaffer C.L. 2020.
461
Reintroduction of the European bison (Bison bonasus) in central-eastern Europe: a case
462
study. Int. J. Geogr. Inf. Sci. 34: 16281647.
463
Ludescher F.B. 1973. Sumpfmeise (Parus palustris L.) und Weidenmeise (P. montanus
464
salicarius Br.) als sympatrische zwillingsarten. Journal für Ornithologie 114: 356.
465
Martin K., Eadie J.M. 1999. Nest webs: A community-wide approach to the management and
466
conservation of cavity-nesting forest birds. For. Ecol. Manag. 115: 243257.
467
Maziarz M., Broughton R.K., Wesołowski T. 2017. Microclimate in tree cavities and nest-
468
boxes: implications for hole-nesting birds. For. Ecol. Manag. 389: 306313.
469
Maziarz M., Wesołowski T. 2014. Does darkness limit the use of tree cavities for nesting by
470
birds? J. Ornithol. 155: 793799.
471
Maziarz M., Wesołowski T., Hebda G., Cholewa M. 2015. Natural nest-sites of Great Tits
472
(Parus major) in a primeval temperate forest (Białowieża National Park, Poland). J. Ornithol.
473
156: 613623.
474
Maziarz M., Wesołowski T., Hebda G., Cholewa M., Broughton R.K. 2016. Breeding success
475
of the Great Tit Parus major in relation to attributes of natural nest cavities in a primeval forest.
476
J. Ornithol. 157: 343354.
477
Acta Ornithologica (accepted July 2022)
21
Milner J.M., Bonenfant C., Mysterud A., Gaillard J.-M., Csányi S., Stenseth N.C. 2006.
478
Temporal and spatial development of red deer harvesting in Europe: biological and cultural
479
factors. J. Appl. Ecol. 43: 721734.
480
Nickell Z., Varriano S., Plemmons E., Moran M. D. 2018. Ecosystem engineering by bison
481
(Bison bison) wallowing increases arthropod community heterogeneity in space and time.
482
Ecosphere 9: e02436.
483
Nilsson S.G. 1984. The evolution of nest-site selection among hole-nesting birds: the
484
importance of nest predation and competition. Ornis Scand. 15: 167175.
485
Paszkiewicz R., Januszczak M. 2010. Szkody powodowane przez żubry w środowisku leśnym
486
Bieszczadów w ocenie leśników. European Bison Conservation Newsletter 3: 5362.
487
Perino A., Pereira H., Navarro L.M., Fernández N., Bullock J.M., Ceaușu S., et al. 2019.
488
Rewilding complex ecosystems. Science 364: eaav5570.
489
Remm J., Lõhmus A. 2011. Tree cavities in forests The broad distribution pattern of a
490
keystone structure for biodiversity. For. Ecol. Manag. 262, 579-585.
491
Remm J., Lõhmus A., Remm K. 2006. Tree cavities in riverine forests: What determines their
492
occurrence an use by hole-nesting passerines? For. Ecol. Manag. 221: 267277.
493
Schröder F., Oldorff M.A.P., Heising K.L. 2019. Spatial relation between open landscapes and
494
debarking hotspos by European bison (Bison bonasus) in the Rothaar Mountains. European
495
Bison Conservation Newsletter 12: 516.
496
Shigo A.L. 1984. Compartmentalization: a conceptual framework for understanding how trees
497
grow and defend themselves. Annu. Rev. Phytopathol. 22: 189214.
498
Stokland J.N., Siithonen J., Jonsson B.G. 2012. Biodiversity in Dead Wood. Cambridge
499
University Press, Cambridge.
500
Acta Ornithologica (accepted July 2022)
22
Tomiałojć L. 1993. Breeding ecology of the blackbird Turdus merula studied in the primaeval
501
forest of Białowieża (Poland). Part I. Breeding numbers, distribution and nest sites. Acta
502
Ornithol. 27: 131157.
503
Tomiałojć L., Wesołowski T., Walankiewicz W. 1984. Breeding bird community of a primeval
504
temperate forest (Białowieża National Park, Poland). Acta Orn. 20: 241310.
505
Tree, I. (2017) The Knepp Wildland project. Biodiversity 18: 206209.
506
Vacek Z., Cukor J., Linda R., Vacek S., Šimůnek V., Brichta J., Gallo J., Prokůpková A. 2020.
507
Bark stripping, the crucial factor affecting stem rot development and timber production of
508
Norway spruce forests in Central Europe. For. Ecol. Manag. 474: 118360.
509
Van Balen J.H., Booy C.J.H., Van Franeker J.A., Osieck E.R. 1982. Studies on hole-nesting
510
birds in natural nest sites. Ardea 55: 124.
511
Verheyden H., Ballon P., Bernard V., Saint-Andrieux C. 2006. Variations in bark-stripping by
512
red deer Cervus elaphus across Europe. Mamm. Rev. 36: 217234.
513
Walankiewicz W. 1991. Do secondary cavity-nesting birds suffer more from competition for
514
cavities or from predation in a primeval deciduous forest? Nat. Areas J. 11: 203212.
515
Walankiewicz W., Czeszczewik D., Mitrus C. 2007. Natural nest sites of the Collared
516
Flycatcher Ficedula albicollis in lime-hornbeam-oak stands of a primeval forest. Ornis Fenn.
517
84: 155162.
518
Walankiewicz W., Czeszczewik D., Stański T., Sahel M., Ruczyński I. 2014. Tree cavity
519
resources in Spruce-Pine managed and protected stands of the Białowieża Forest, Poland.
520
Nat. Areas J. 34: 423428.
521
Welch D., Scott D. 2017. Observations on bark-stripping by red deer in a Picea sitchensis
522
forest in Western Scotland over a 35-year period. Scand. J. For. Res. 32: 473480.
523
Acta Ornithologica (accepted July 2022)
23
Wesołowski T. 1989. Nest-sites of hole-nesters in a primeval temperate forest (Białowieża
524
National Park, Poland). Acta Orn. 25: 321351.
525
Wesołowski T. 1996. Natural nest sites of Marsh Tit (Parus palustris) in a primaeval temperate
526
forest (Białowieża National Park, Poland). Die Vogelwarte 38: 235249.
527
Wesołowski T. 2002. Anti-predator adaptations in nesting Marsh Tits Parus palustris: the role
528
of nest-site security. Ibis 144: 593601.
529
Wesołowski T. 2007a. Lessons from long-term hole-nester studies in a primeval temperate
530
forest. J. Ornithol. 148 (Suppl 2): S395S405.
531
Wesołowski T. 2007b. Primeval conditions what can we learn from them? Ibis 149: 6477.
532
Wesołowski T. 2011.Reports from nestbox studies: A review of inadequacies. Acta Ornithol.
533
46: 1317.
534
Wesołowski T. 2012. “Lifespan” of non-excavated holes in a primeval temperate forest: a 30
535
year study. Biol. Conserv. 153: 118126.
536
Wesołowski T. 2022. Natural nest sites of the European Starling Sturnus vulgaris in a primeval
537
temperate forest. Bird Study 68: 145156.
538
Wesołowski T., Martin K. 2017. Tree holes and hole-nesting birds in European and North
539
American forests. In: Mikusiński G., Roberge J-M., Fuller R.J. (eds). Ecology and
540
Conservation of Forest Birds. Cambridge University Press, Cambridge. pp. 79134.
541
Wesołowski T., Maziarz M. 2012. Dark tree cavities a challenge for hole-nesting birds? J.
542
Avian Biol. 43: 454460.
543
Wesołowski T., Rowiński P. 2004. Breeding behaviour of Nuthatch Sitta europaea in relation
544
to natural hole attributes in a primeval forest. Bird Study 51: 143155.
545
Wesołowski T., Rowiński P. 2012. The breeding performance of Blue Tits Cyanistes caeruleus
546
in relation to the attributes of natural holes in a primeval forest. Bird Study 59: 437448.
547
Acta Ornithologica (accepted July 2022)
24
Wesołowski T., Stańska M. 2001. High ectoparasite loads in hole-nesting birds a nestbox
548
bias? J. Avian Biol. 32: 281285.
549
Yatsiuk Y., Wesołowski T. 2020. Diversity and abundance of large tree holes used by Tawny
550
Owls Strix aluco in lowland temperate forests. Bird Study 67: 331343.
551
552
553
554
555
556
557
558
559
560
561
562
563
564
565
566
567
568
569
Acta Ornithologica (accepted July 2022)
25
570
571
Acta Ornithologica (accepted July 2022)
26
572
573
Acta Ornithologica (accepted July 2022)
27
574
575
Acta Ornithologica (accepted July 2022)
28
576
577
Acta Ornithologica (accepted July 2022)
29
578
579
Acta Ornithologica (accepted July 2022)
30
580
581
Acta Ornithologica (accepted July 2022)
31
582
583
Acta Ornithologica (accepted July 2022)
32
584
585
Acta Ornithologica (accepted July 2022)
33
586
587
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
Deer can show transitional use between agricultural fields and forests for foraging and shelter. Such transitional use may affect forest damage as nutrient balancing theory suggests that if deer ingest large amounts of nutrient‐rich food, complementary browse, such as bark, may be required to balance the diet. We investigated the relationship between the level of red deer Cervus elaphus bark‐stripping damage in 68 Norway spruce Picea abies stands and the presence of rapeseed Brassica napus fields – an energy‐rich crop preferred by red deer – in the surroundings, hypothesizing that damage increases with decreasing distance to rapeseed fields. We also considered other potentially influencing factors, such as supplemental feeding, alternative forage availability, and deer use of spruce stands as indexed by a pellet group count. Spruce stands closer to rapeseed had a significantly higher proportion of damaged stems. The increased level of bark‐stripping damage was not explained by a higher stand use of deer closer to rapeseed fields, indicating that deer increase their consumption of bark in order to balance their diet. Similarly, spruce stands closer to supplemental feeding stations had significantly higher damage levels. In line with earlier findings, damage levels were negatively related to the amount of available browse in the forest. This emphasizes the importance of alternative forage for reducing the damage risk in forest plantations. Our study shows that the availability of fields with nutrient‐rich food, such as rapeseed, as well as supplemental feeding needs to be considered when predicting the level of forest damage. With a high availability of nutrient‐rich food in the vicinity of forest stands, a higher damage level can be expected and counteractions could be taken such as increased disturbance, harvest or changed choice of both crop and supplemental feed types. These actions may also be combined with a push–pull strategy where the deer are steered to disturbance‐free zones insensitive to damage and with alternative forage. The importance of alternative forage availability on damage levels highlights the necessity for managers to actively promote tree and shrub forage within and around their production stands.
Article
Full-text available
Despite its broad range and high abundance, nest sites of the European robin Erithacus rubecula, a small forest passerine, are rarely characterised, and most studies refer to human-transformed habitats. In this paper, we describe the species’ nest sites in the natural conditions of a primeval forest. We also investigate robin preferences to address nest site selection which can only be assessed if the availability of potential nest sites is known. We studied robins’ nest sites in Białowieża National Park, eastern Poland, on three study plots (~30 ha each) in 2016–2019. Among all nests found (n = 165), the majority (118, ~72%) were found in tree holes, followed by ground nests (25, ~15%) and root-soil plates (22, ~13%). When the availability of cavities and root-soil plates is accounted for, it appears that robins preferred tree holes over plates. Robins appeared to be weakly selective in respect to tree species, preferring hornbeam Carpinus betulus, small-leaved lime Tilia cordata and Norway spruce Picea abies over other trees. Since both cavities and root-soil plates are superabundant in the Białowieża Forest, but scarce or absent in the heavily transformed robin breeding habitats of Western Europe (parks, orchards, hedgerows or managed forests), ground-nesting may predominate there simply due to these choice limits. In summary, our results provide a basis for understanding how original nest-site choices that evolved in natural, unmodified habitats can change when a species adapts to human-transformed habitats.
Article
Full-text available
The impact of bark-stripping by red deer on an 1825 ha plantation of Picea sitchensis is reported. Monitoring began in 1978 with initially 6500 trees at 37 sites; by 2014 only 10 sites remained due to felling. Sites became vulnerable to bark-stripping once the trees reached 7 years age, and from then until felling at age c. 45 years incidence rates averaged 1% of the trees damaged yearly. Intense damage at a site in a year (> 2% trees damaged) was often followed by intense damage next year, but on average 53% of sites were undamaged in a year. Many trees suffered repeat wounding, which reduced final impact by c. 30% compared to the theoretical impact calculated from annual damage and damage duration. The trees bark-stripped were on average smaller than plot mean girths once these means exceeded 20 cm; this had only minor effect on final impact since bark-stripped small trees had similar mortality to undamaged small trees. Most wounds (> 90%) were small (< 180 cm²) and healed quickly, so were unlikely to develop decay. Larger wounds never healed in less than 8 years, but the proportion healed increased progressively from 10 to 20 years after wounding.
Article
Full-text available
Holes provide the safest nest sites for birds, but they are an underutilized resource; in natural forests there are usually more holes than birds that could use them. Some bird species could be prevented from nesting in holes because of their inability to operate in the low light conditions which occur in cavities. As no visual system can operate in complete darkness some nest cavities could be too dark to be useable even by hole-nesters. Thus, the light conditions within tree cavities could constrain both the evolution of the hole nesting habit, and the nest site choice of the hole-nesting birds. These ideas cannot be tested because little is known about the light conditions in cavities. We took an opportunity provided by ongoing studies of marsh tits Poecile palustris and great tits Parus major breeding in a primeval forest (Bialowieża National Park, Poland) to measure illumination inside their nest cavities. We measured illuminance in cavities at daybreak, which is just after the parents commenced feeding nestlings. Only ca 1% of incoming light reached the level of the nest. Illuminance at nests of both species (median =0.1-0.2 lx) fell within mesopic-scotopic range, where colour vision is impaired. Measurements in model cavities showed strong declines in illumination with distance from the entrance, with light levels typically as low as 0.01 lx at 40 cm from the cavity entrance. Thus cavities can be very dark, often too dark for the use of colour vision, and we suggest that 'lighting' requirements can affect the adoption of specific nest sites by hole nesting birds. We discuss implications of the findings for understanding the adaptations for hole-breeding in birds. © 2012 The Authors. Journal of Avian Biology
Article
Capsule European Starlings Sturnus vulgaris nested mostly in natural holes with strong walls (in live trees), typically excavated by medium-sized woodpeckers (small entrances, deep cavities), and high above the ground. Co-occurrence of these safety-enhancing features suggests that predation avoidance has been the main force shaping patterns of Starling nest site selection. Aims To describe patterns of nest site use by Starlings in a primeval forest and to assess the adaptive value of nest site choice. Methods Observations were made of Starlings breeding in undisturbed conditions in a strictly protected part of the Białowieża National Park, Poland. Intensive searches were made for nests (n = 2039) in permanent observation plots during 46 breeding seasons (1975–2020), coupled with measurements of hole attributes and observations of fate and re-use of nest sites. Results Starlings bred along forest edges in holes located in several species of deciduous tree; tree species used differed among habitats and hole location differed across tree species. The birds bred mostly in holes excavated by woodpeckers (70.3%), in trunks (77.4%) of living trees (84.5%). The median girth at breast height of these trees amounted to approximately 170 cm and median height of holes above the ground was 13 m. Starlings used holes excavated by the medium-sized woodpeckers roughly in proportion to their availability in the forest (tree species, stature, height above the ground). About 39% of holes were re-used in the consecutive years, with some holes being used over several decades. Conclusion The features of Starling nest holes (strong walls, narrow entrances, deep cavities) probably constitute adaptations to the need to evade predators. Their body size allows them to nest in excavated holes without threat of their broods being destroyed by woodpeckers.
Article
Many tree-dwelling species inhabit microhabitats that develop slowly in diseased or injured trees. Conservation planning would benefit from explicit knowledge of these processes, notably for resolving conflicts with timber production, arboricultural or public safety goals. We reviewed published rates of development of five selected common tree microhabitats and the factors affecting those rates in living trees. Most of the 71 relevant studies found globally focused on tree-cavities and exposed wood, while the development of witches’ broom, bark pocket and dendrotelm microhabitats remains poorly described. Three time parameters emerge as central: minimum tree age; rate of formation; and persistence time of the microhabitat. Among the studied microhabitats, large side cavities are formed in the oldest trees, seldom hosting large vertebrates in trees <100 years old. In contrast, the development of exposed wood, bark pockets and dendrotelms can be compatible with some approaches of even-aged production forestry. The evidence indicates that tree growth rate is a key effect modifier of microhabitat development, which supports short-term wound occlusion but can also expose the tree to chronic disease and decay. For example, side cavities usually develop more rapidly in fast-growing trees, but persist longer in slow-growing trees. Environmental exposure regulates microhabitat development by affecting these growth and degradation responses and pathogen performance, but typical ranges of natural variation in microhabitat development rates can also be distinguished. To mitigate conservation conflicts with production forestry and the management of human environments, microhabitat prone trees should be considered across multiple management cycles, notably to sustain large side-cavities and witches’ brooms. We outline retention forestry approaches, reduction of salvage logging, and veteran tree management in the countryside and urban environments as the key arenas of action. Given the high variation in tree microhabitat development, a successful strategy would combine fine-scale retention of existing microhabitats and landscape-scale prediction and planning for future microhabitat formation.
Article
Tree related Microhabitats (hereafter TreMs) have been widely recognized as important substrates and structures for biodiversity in both commercial and protected forests and are receiving increasing attention in management , conservation and research. How to record TreMs in forest inventories is a question of recent interest since TreMs represent potential indirect indicators for the specialized species that use them as substrates or habitat at least for a part of their life-cycle. However, there is a wide range of differing interpretations as to what exactly constitutes a TreM and what specific features should be surveyed in the field. In an attempt to harmonize future TreM inventories, we propose a definition and a typology of TreM types borne by living and dead standing trees in temperate and Mediterranean forests in Europe. Our aim is to provide users with definitions which make unequivocal TreM determination possible. Our typology is structured around seven basic forms according to morphological characteristics and biodiversity relevance: i) cavities lato sensu, ii) tree injuries and exposed wood, iii) crown deadwood, iv) excrescences, v) fruiting bodies of saproxylic fungi and fungi-like organisms, vi) epiphytic and epixylic structures, and vii) exudates. The typology is then further detailed into 15 groups and 47 types with a hierarchical structure allowing the typology to be used for different purposes. The typology, along with guidelines for standardized recording we propose, is an unprecedented reference tool to make data on TreMs comparable across different regions, forest types and tree species, and should greatly improve the reliability of TreM monitoring. It provides the basis for compiling these data and may help to improve the reliability of reporting and evaluation of the conservation value of forests. Finally, our work emphasizes the need for further research on TreMs to better understand their dynamics and their link with biodiversity in order to more fully integrate TreM monitoring into forest management.
Article
In forests worldwide, ∼10−40% of bird and mammal species require cavities for nesting or roosting. Although knowledge of tree cavity availability and dynamics has increased during past decades, there is a striking lack of studies from boreal Europe. We studied the density and characteristics of cavities and cavity-bearing trees in three categories of forest in a north-Swedish landscape: clearcuts with tree retention, managed old (>100 years) forest, and unmanaged old forest. Unmanaged old forests had significantly higher mean density of cavities (2.4±2.2(SD) ha⁻¹) than managed old forest (1.1±2.1 ha⁻¹). On clearcuts the mean cavity density was 0.4±2.3 ha⁻¹. Eurasian aspen (Populus tremula) had a higher probability of containing excavated cavities than other tree species. There was a greater variety of entrance hole shapes and a higher proportion of cavities with larger entrances in old forest than on clearcuts. Although studies of breeding success will be necessary to more accurately assess the impact of forest management on cavity-nesting birds, our results show reduced cavity densities in managed forest. To ensure future provision of cavities, managers should retain existing cavity-bearing trees as well as trees suitable for cavity formation, particularly aspen and dead trees.