Natural History Sciences. Atti Soc. it. Sci. nat. Museo civ. Stor. nat. Milano, 10 (1): 87-90, 2023 DOI: 10.4081/nhs.2023.647
Short communication
Arboreal behaviour of the wood mouse Apodemus sylvaticus (Rodentia:
Muridae): a study in the Venetian plain
Alessandro Nardotto
Via Guizze 55/3, Villorba (TV), Italia.
E-mail: info.wildlifeservices@gmail.com
© 2023 Alessandro Nardotto
Received for publication: 21 September 2022
Accepted for publication: 18 November 2022
Online publication: 20 April 2023
Abstract - The arboreal activity of the wood mouse is known,
but mostly based on anecdotal evidence or single records. This study
reports on field observations carried out systematically during an indi-
rect survey conducted in the Venetian plain using hair tubes positioned
at different heights in the shrub layer. The research confirmed that in
the study area the wood mouse moves not only at ground level, but at
also a few meters above the ground reaching heights up to 2.30 m (1.54
m on average).
Keywords: Arboreal behaviour, hair tube, small mammals.
Riassunto - Comportamento arboricolo del topo selvatico Apode-
mus sylvaticus (Rodentia: Muridae): uno studio nella pianura veneta.
L’attività arboricola del topo selvatico è nota, ma basata soprattutto
su testimonianze aneddotiche o singole osservazioni. Il presente studio
riporta osservazioni di campo effettuate sistematicamente durante
un’indagine indiretta condotta nella pianura veneta, mediante l’utilizzo
di hair tube posizionati a varie altezze nello strato arbustivo. Lo studio
ha confermato che il topo selvatico si muove non solo a livello del
suolo, ma anche ad alcuni metri dal terreno, raggiungendo altezze fino
a 2,30 m nell’area di studio (1,54 m in media).
Parole chiave: Comportamento arboricolo, hair tube, piccoli mam-
miferi.
INTRODUCTION
The wood mouse Apodemus sylvaticus (Linnaeus
1758) is a small rodent widely spread throughout Europe,
from the Iberian Peninsula to Western Russia, reaching
to the north Sweden, Norway and even Iceland (Amori
et al., 2008). In Italy, the species populates most of the
peninsula and some islands like Sicily, Sardinia, Elba,
Giglio, Capri and Pantelleria (Amori, 1993; Capizzi &
Santini, 2007), thanks to its broad capacity to adapt to
different ecological conditions (Amori et al., 2008). The
species is present throughout the Veneto region, from sea
level up to quite high elevations, even beyond 2000 m
(Bon, 2017). Although most of the species’ activities are
carried out at ground level (Jennings, 1975; Flowerded,
1991), the wood mouse also has a marked aptitude for
climbing, reaching up to 3-4 meters in height on shrubs
(Montgomery, 1980; Gurnell, 1985). Although this be-
haviour has been frequently reported, arboreality of the
species has been little investigated and this information
often remains anecdotal (Buesching et al., 2008). As a se-
condary result of a monitoring of small mammals carried
out in a protected area of the Veneto plain, it was possible
to collect quantitative data on this little-studied behaviour
in a systematic way.
MATERIALS AND METHODS
Study area
The present study was conducted in the Regional
Natural Park of the River Sile, sited between the loca-
lities of Canizzano (TV) and Quinto di Treviso (TV)
(45°38’47.8”N, 12°11’35.6”E). This is a riparian area
adjacent to the River Sile and close to the Treviso airport,
consisting of mixed-species hedges with Rubus ulmifo-
lius Schott, Cornus sp. and to a lesser extent Morus alba
L., Corylus avellana L. and other shrub and tree species,
and woods with Ulmus minor Mill., Alnus glutinosa (L.)
Gaertn., Quercus robur L., Robinia pseudoacacia L.
Reedbeds are also present in some areas.
Data collection and analysis
Data were collected during a monitoring survey con-
ducted with hair tubes (Pocock & Jennings, 2006; Chiron
et al., 2018) and targeted at the hazel dormouse Muscardi-
nus avellanarius (Linnaeus 1758). In this case, the choice
fell on tubes 20 cm long and 3.5 cm in diameter, in order
to facilitate entry only to target species and those of simi-
lar size, as has already been successfully experimented
in other studies (Tioli & Zocca, 2010). In particular, 30
tubes arranged in two transects of 15 tubes each were tied
at a distance of 5-10 m apart on the branches of trees and
shrubs at a height ranging from 100 cm to about 250 cm,
depending on the shrubs. Horizontal branches have been
favoured to enhance the stability of the hair tubes. The
placement height of each hair tube was then recorded
rounding the measurement down to the nearest ten cen-
88
timetres. The hair tubes were left in place for about two
and a half months, from 25 May to 2 August 2022, and
were checked periodically (5 times) every two weeks to
collect any samples, replace the double-sided tape and put
the tubes back in place. The collected samples were first
removed from the double-sided tape and then cleaned of
impurities by immersion first in acetone and then in water.
The hair was then identified under an optical microscope
at 100× and 400× magnification through the diagnostic
microstructures of the cuticle (outermost layer, formed by
the overlapping of transparent keratin scales) and the me-
dulla (inner part, formed by dead cells).
Identification was performed by visual comparison
with figures in specialist texts (Debrot et al., 1982; Tee-
rink, 1991; Paolucci & Bon, 2022).
In order to obtain a statistical description of the arboreal
behaviour of the wood mouse in relation to the height at-
tained in the shrub layer, a weighted average of the heights
of the frequented hair tubes was calculated, taking into ac-
count the height of placement and the number of positi-
ve controls per hair tube (i.e. those in which hairs of the
species are present). In addition, the range (minimum and
maximum heights) of occurrence of the wood mouse in the
arboreal environment is reported. The mean for each con-
trol and the confidence intervals were also calculated. The
chi-square test was performed to check whether there were
differences between the various sampling sessions. All sta-
tistical analyses were performed in the R environment (R
Core Team, 2022).
RESULTS
During the survey, only wood mouse samples we-
re collected. The average placement height of the hair
tubes frequented by the wood mouse is 1.54 m ± 0.36
(S.D.). The hair tube positioned at the height of 2.30 m
was frequented 4 times, the highest recorded height. In-
stead, the lowest tube used was located at 1.10 m. With
the exception of the first sampling session, in which no
hair samples of the species were found, in the subsequent
ones the average height of the frequented tubes is around
1.50 m in height, not showing significant differences
between one sampling session and another (χ2= 2.1204,
p=0.9992).
DISCUSSION
The information reported in this work testifies and
confirms the arboreal habits of the wood mouse (Bue-
sching et al., 2008). Although the arrangement of the tu-
bes may have probably influenced the results obtained, it
can be said that the species appears to move skilfully from
the ground level up to the height of 2.30 m. The findings
are consistent with the observations reported in other
European contexts (Gurnell, 1985), even if they do not
reach the record height of 23.37 m exceptionally recor-
ded in Poland for A. flavicollis (Melchior 1834), a species
that shows similar arboreal behaviour (Borowski, 1962;
Montgomery, 1980). The reason for this behaviour seems
to be attributable to a combination of factors such as the
SHORT COMMUNICATION
Fig. 1 - Averages and confidence intervals of the heights of the hair tubes used by the wood mouse during the sampling sessions. / Valori
medi e relativi intervalli di confidenza delle altezze degli hair tube utilizzati dal topo selvatico durante le sessioni di campionamento.
89NAT U R A L HISTORY SCIENCES. ATTI SOC. IT. SCI. NAT. M USEO CI V. STOR. NAT. MILA NO, 10 (1): 87-90, 2023
search for additional food sources and the possibility of
escaping predators (Buesching et al., 2008). Furthermo-
re, the presence of the species also in the shrub layer can
represent a disturbing factor for the hazel dormouse, as
the two species can potentially compete for resources. In
Germany, for example, it was observed that the absence
(or the presence at low densities) of A. sylvaticus and A.
flavicollis has a positive effect on the abundance of the
hazel dormouse (Villing & Horst, 2021). Given the Com-
munity interest of the hazel dormouse (Habitats Directive
92/43/CEE), in-depth investigations into the ecological
implications of the coexistence of this two rodent species
in this study area are recommended.
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SHORT COMMUNICATION