Nest site selection by the hazel dormouse Muscardinus avellanarius: is safety more important than food?
© Juškaitis et al.; licensee Springer. 2013
Received: 25 March 2013
Accepted: 10 July 2013
Published: 9 December 2013
Vegetation parameters determining nest site selection by the hazel dormouse Muscardinus avellanarius were studied in a typical habitat where dormice are relatively common in Lithuania, the northern periphery of its distributional range.
Dormice preferred nest sites with a better-developed understory, particularly with a good cover of hazel shrubs taller than 4 m and plentiful bird cherry trees, a high diversity of woody plant species in the understory and overstory, and better connectivity of the nest tree with its surroundings. They avoided sites with a high number of mature Norway spruce trees in the canopy and a high density of young trees. In a stepwise multiple regression analysis, three vegetation parameters of the number of shrub species, the cover of hazel shrubs, and the number of Norway spruce trees in the canopy determined over 85% of the index of nestbox use by M. avellanarius. The number of shrub species in the surroundings of the nest site had the highest impact of all. Nest sites used by dormice for breeding were distinguished by a better-developed understory, particularly by a significantly higher number of bird cherry trees and a lower number of Norway spruce trees in the canopy, as well as a higher diversity of plants in the understory and overstory.
Selection of nest sites by M. avellanarius is a combination of safety from predators and the presence of food. A well-developed inter-connected understory ensures the safety of nest sites from predators, and the diversity of understory and overstory species guarantees continuity of the food supply in the vicinity of nest sites.
KeywordsCommon dormouse Vegetation parameters Breeding Nestboxes Lithuania
Nest site selection by animals is understood to be a choice of certain features of the environment that differ from generally available sites (Skórka et al. 2011). Nests provide a place for individuals to rest, raise young, avoid predators, and escape inclement weather. When selecting a nest site, animals have to find the best compromise between the risk of encountering predation, the availability of food nearby the nest, and microclimatic requirements (Cudworth and Koprowski 2011; Rosalino et al. 2011). Knowledge of habitat characteristics important to nest placement is critical for managing species of conservation concern (Bright and Morris 1990; Cudworth and Koprowski 2011; Skórka et al. 2011; Atiénzar et al. 2012).
The hazel dormouse Muscardinus avellanarius is considered an endangered species in many European countries and is listed in Annex IV of the EU Habitat Directive (Amori et al. 2008; Juškaitis 2008). Habitat loss and fragmentation, and forest management practices unfavorable for this species are the major reasons for the decline of M. avellanarius (Bright et al. 2006; Juškaitis 2007a; Juškaitis and Büchner 2013). Particular attention to the conservation of M. avellanarius is being given in some countries of Western Europe, e.g., Great Britain, Germany, Denmark, the Netherlands, and Belgium (Juškaitis and Büchner 2013). In contrast, in Lithuania, which is situated on the northern periphery of the species’ distributional range, M. avellanarius is widespread and relatively common (Juškaitis 2007a 2008).
M. avellanarius has been the subject of many studies carried out in different parts of its distributional range (reviewed in Juškaitis 2008), including investigations into habitat and nest site selection. General habitat preferences of M. avellanarius were studied in several countries, e.g., in Great Britain, Italy, Lithuania, and Germany (Bright and Morris 1990; Capizzi et al. 2002; Juškaitis 2007b; Wuttke et al. 2012). Nest site selection by this species was studied in two different landscapes in southern Sweden (Berg and Berg 1998), in two habitat types in central Italy (Panchetti et al. 2007), and in a specific hedgerow habitat by (Wolton 2009). This was also done in mature 75- to 180-year-old mixed forest stands in Lithuania, which are typical habitats for the fat dormouse Glis glis, but not for M. avellanarius (Juškaitis and Šiožinytė 2008).
Results of previous studies on site selection of nest sites and resting places by dormice and other small mammals indicated that it may be related to safety from predators (Bertolino 2007; Panchetti et al. 2007; Rosalino et al. 2011), the availability of continuous suitable food supplies (Sherman 1984; Kopij 2009), or a possible combination of both factors (Bertolino et al. 2011; Cudworth and Koprowski 2011).
The diet of M. avellanarius was investigated at our study site, and the main feeding plants important for this species are known (Juškaitis and Baltrūnaitė 2013). This allowed us to assess whether safety of nest sites from predators is more important to M. avellanarius than food presence near their nest sites. Nest site selection should correlate with environmental variables securing nest sites (e.g., vegetation cover or connectivity) in the first case and with the presence of the main food plants in the vicinity of nest sites in the second case. However, some woody plants may be important for both secure movement and feeding.
Another issue we tested was related to breeding by M. avellanarius. In Sweden, no significant differences were found in the habitat composition of natural nests used for breeding and those used only for resting (Berg and Berg 1998). However, we hypothesized that nest sites used for breeding should be of somewhat better quality compared to other nest sites.
Thus, the two aims of the present study were to: identify vegetation parameters which determine nest site selection by M. avellanarius and determine differences between nest sites of M. avellanarius used for breeding and not used for breeding.
The dormouse study site is situated in Šakiai District, southwestern Lithuania (55°03′N, 23°04′E). The study site covers an area of 60 ha and contains 272 standard wooden nestboxes for small hole-nesting birds spaced in a grid system at 50-m intervals between boxes. Most nestboxes were put up at a height of 3 to 4 m off the ground. The study site incorporates a typical Lithuanian habitat of M. avellanarius, i.e., a mixed deciduous-coniferous forest dominated by birches Betula pendula and Betula pubescens and Norway spruce Picea abies. Other major tree species growing at the study site are black alder Alnus glutinosa, grey alder Alnus incana, ash Fraxinus excelsior, aspen Populus tremula, small-leaved lime Tilia cordata, and pedunculate oak Quercus robur. Hazel Corylus avellana, glossy buckthorn Frangula alnus, bird cherry Padus avium, rowan Sorbus aucuparia, and dwarf honeysuckle Lonicera xylosteum are the main shrub species in the understory. Over most of the study site, the forest is of middle age (about 60 to 70 years old). Various forest management operations, including clear felling, are routinely carried out by foresters. In the area of the study site, there are no old trees with natural hollows; the only natural hollows are those made by woodpeckers Dendrocopos spp. These hollows are usually high up in aspen trees without branches, where it would be unsafe for dormice to reach them.
The approval from the Environmental Protection Agency of Lithuania was obtained for the field studies of M. avellanarius at study site.
The indices of nestbox use were calculated for all 272 boxes using data from their controls in 2007 to 2011. Use of nestboxes by dormice in separate years was scored in points: 0 points, no use of the nestbox at all; 1 point, short-term use of the nestbox (a dormouse, its excrement, or food remains found in an empty nestbox); 2 points, long-term use of the nestbox during one activity season (dormouse nest or one dormouse found in a nest); 3 points, more than one individual (but not a litter) found in a nest; 4 points, a female with a litter of juveniles in a nest; and 5 points, a female with a litter of juveniles and one or more other dormice in a nest.
Points from 5 years were totaled for every nestbox, and the sum of the points was used as an index of nestbox use. The index of nestbox use by M. avellanarius was considered to be an indicator of nest site suitability for dormice: the higher the index, the better the quality of nest site for M. avellanarius.
To evaluate vegetation parameters around nest sites of M. avellanarius, 50 of the 272 nestboxes were selected (Figure 1), using the procedure of stratified random sampling according to Krebs ( 1999). After calculating the indices of nestbox use, the sample of 50 nestboxes was allocated to quotas proportional to numbers of nestboxes with the same index among the 272 nestboxes. For example, if 10% nestboxes (n = 27) among all 272 nestboxes had the same index, then 10% of nestboxes (n = 5) with the same index were also chosen among the 50 selected nestboxes. Locations of the particular nestboxes used in the sample were selected randomly. However, nestboxes situated at the forest edge or the edge of clear-felled plots were not included in the analysis, as the vegetation sampling technique described below could not be applied in such cases.
Evaluation of vegetation parameters around nest sites was performed by applying Dueser and Shugart’s ( 1978) detailed sampling technique using plots and transects of various sizes. This method was adopted by other authors for studies of nest site selection and microhabitat use in different dormouse species (Bertolino 2007; Bertolino and Cordero di Montezemolo 2007; Panchetti et al. 2007). Four rectangular transects (each 10 × 25 m) starting at the nestbox tree and representing nest site surroundings were selected. Overlapping areas of transects in close proximity to the nestbox-carrying tree were sampled only once. The total sampled area around each nestbox was 900 m2, and the following groups of vegetation parameters were evaluated: (1) the number of individuals of each species in the overstory (canopy trees and sub-canopy trees separately) and the understory (young trees 1 to 4 m in height and shrubs separately); (2) the number of tree stumps (with a diameter of >10 cm), logs, dead standing trees, and trunks (dead trees taller than 1 m without branches); (3) the number of trees and shrubs with a crown or a trunk connected to the crown of the nestbox tree; (4) the canopy cover of hazel shrubs and mature oak trees (in m2); (5) the cover of raspberries Rubus ideus, stone brambles Rubus saxatilis, and wild strawberries Fragaria vesca in the ground vegetation layer (in %); and (6) areas of glades, forest roads, and rides (in m2).
The number and canopy cover of hazel shrubs were evaluated separately for hazels lower than 4 m and taller than 4 m. The cover of selected plants in the ground vegetation layer was visually estimated at randomly located 10 × 10-m squares in each transect. During the evaluation process, the following canopy-forming tree species were recorded: Norway spruce, silver and downy birches B. pendula and B. pubescens, grey and black alders, pedunculate oak, ash, aspen, willow Salix spp. (mostly Salix caprea, but also Salix cinerea and Salix myrsinifolia), small-leaved lime, Scotch pine Pinus sylvestris, Wych and field elms Ulmus glabra and Ulmus minor, Norway maple Acer platanoides, wild apple Malus sylvestris, common buckthorn Rhamnus cathartica, and common hornbeam Carpinus betulus. Understory species recorded were hazel, glossy buckthorn, bird cherry, rowan, dwarf honeysuckle, European spindle Euonymus europaeus, blackcurrant Ribes nigrum, red elderberry Sambucus racemosa, and mezereon Daphne mezereum.
Overall, 70 variables, including direct field measurements, combinations of them (e.g., total area of glades, forest roads, and rides, total number of overstory trees, etc.), and derived variables (e.g., the density of the shrub layer, Shannon-Wiener index, etc.) were used in the initial data analysis. The inter-correlation of all vegetation parameters was checked using Spearman’s correlation analysis. Highly inter-correlated variables, with r S values of >0.70, were excluded from further analysis, leaving a total of 51 variables. Exclusion was based on a lower correlation with the index of nestbox use and on the possible biological interpretation of results. Spearman’s correlation coefficients between vegetation parameters evaluated in the surroundings of nestboxes and indices of nestbox use were calculated.
Subsequently, the relationship between the dependent variable (index of nestbox use by M. avellanarius) and independent vegetation parameters were explored using general linear model (GLM) procedures in Statistica for Windows vers. 6.0 software (StatSoft 2004). We selected the best multiple linear regression model, using a forward stepwise method (StatSoft 2010). Variables were tested for normality using the Kolmogorov-Smirnov one-sample test; variables failing the test were transformed. Counts were transformed by taking the square root after adding 0.5, percentages were arcsine square root-transformed after adding 0.01, and other variables were log-transformed after adding 0.01 (Zar 1999).
Nest site selection by M. avellanarius was also analyzed using comparisons of different nest site categories. All 50 nest sites investigated were grouped into five categories according to the extent of nestbox use over 5 years (2007 to 2011): (1) nest sites avoided for resting, i.e., nestboxes used for resting in 0 to 1 year; (2) nest sites occasionally used for resting, i.e., nestboxes used for resting in 2 to 3 years; (3) nest sites preferred for resting, i.e., nestboxes used for resting in 4 to 5 years; (4) nest sites used for breeding once, i.e., nestboxes used for breeding in 1 year (irrespective of the use for resting); and (5) nest sites preferred for breeding, i.e., nestboxes used for breeding in 2 to 4 years (irrespective of the use for resting). No nestbox was used for breeding in all 5 years.
A Kruskal-Wallis analysis of variance (ANOVA) was used to compare vegetation parameters among these five nest site categories. To compare characteristics of nest sites used by M. avellanarius for breeding and not used for breeding, categories 4 and 5, and 1 to 3 were pooled and Student’s t test was applied.
Rényi’s diversity numbers (Tóthmérész 1998) were used to test for differences in the diversity of the understory and overstory around nestboxes used by M. avellanarius for breeding (categories 4 and 5) and not used for breeding (categories 1 to 3). The major advantage in applying the Rényi’s diversity numbers is that they display not just a single index but also a family of indices, many of which are currently applied and widely used in ecology and have varying sensitivities to the presence of rare and abundant species (Carranza et al. 2007; Juškaitis et al. 2012; Rudolf et al. 2012).
The scale parameter α = 0 gives a Rényi’s diversity equal to the logarithm of the number of species; α = 1 yields a Rényi’s diversity equal to Shannon’s H; α = 2 is related to Simpson’s index of dominance; while α = 3 and 4 represent a growing emphasis on the dominant species (Tóthmérész 1998; Carranza et al. 2007). Rényi’s diversity curves for the understory and overstory around nestboxes used by M. avellanarius for breeding and not used for breeding were created using the freeware DOSBox vers. 0.74, running the DivOrd program vers. 1.90 (Tóthmérész 1993). If the diversity curves produced by this method do not intersect, the diversity of either the understory or overstory in the areas around nestboxes used for breeding and not used for breeding significantly differs. According to the theory of diversity ordering, one community can be regarded as more diverse than another only if all its Rényi’s diversity numbers are higher (Tóthmérész 1998).
Of the 272 nestboxes in the area of the study site (Figure 1), only ten boxes (3.7%) were not used by M. avellanarius at all in the period 2007 to 2011; 157 (57.7%) were used for resting, but not for breeding; and 105 (38.6%) were used for breeding. Among the 50 nest sites selected for evaluation of vegetation parameters, 3, 26, and 21 nestboxes were in the respective categories.
Significant Spearman’s correlations between indices of nestbox use by Muscardinus avellanarius and vegetation parameters
Coefficient of Spearman’s correlation
Cover of hazel shrubs taller than 4 m
Number of bird cherry trees
Number of Norway spruce trees in canopy
Number of Scotch pine trees in canopy
Number of young Wych elm trees
Number of young black alder trees
Number of European spindle shrubs
Density of young trees, individuals/ha
Connectivity of nestbox tree with its surroundingsa
Shannon-Wiener index of overstory species
Number of woody plant species in understory
Number of shrub species
where Y is the index of nestbox use, X 1 is the number of shrub species, X 2 is the cover of hazel shrubs taller than 4 m, and X 3 is the number of Norway spruce trees in the canopy.
Results of a stepwise multiple regression
Input to adjusted R2
Number of shrub species
Cover of hazel shrubs taller than 4 m
Number of Norway spruce trees in canopy
Comparison of some vegetation parameters around nestboxes used by Muscardinus avellanarius
Nestboxes used for breeding, mean ± SD
Nestboxes not used for breeding, mean ± SD
Cover of pedunculate oaks
56.00 ± 80.77
129.14 ± 174.13
Number of grey alder trees
12.29 ± 22.28
4.45 ± 6.72
Number of Norway spruce trees in canopy
17.95 ± 15.61
33.52 ± 24.12
Number of bird cherry trees
49.86 ± 56.46
22.59 ± 27.11
Number of common hornbeam trees
7.38 ± 23.45
0.48 ± 1.27
Connectivity of nestbox tree with its surroundingsa
6.71 ± 2.53
5.48 ± 2.95
Number of shrub species
5.71 ± 0.90
5.17 ± 1.14
In most cases, nest site selection by mammals has been studied using comparisons of characteristics of nest sites with randomly selected sites or sites not used by the animals (e.g., Bertolino and Cordero di Montezemolo 2007; Gregory et al. 2010; Cudworth and Koprowski 2011). At our study site, only 10 of the 272 nestboxes were not used at all by M. avellanarius in the period 2007 to 2011. Such a small proportion of nestboxes not being used during this 5-year period suggests that the absolute majority of nest sites are more or less suitable as quality nest sites for this species in the area of the study site. For this reason, comparison of dormouse nest sites and randomly selected sites would be incorrect in our case.
Different statistical methods used to analyze vegetation parameters determining nest site selection by M. avellanarius revealed that two groups of variables related to safety and food are important to dormice.
In the stepwise multiple regression analysis, three vegetation parameters, namely the number of shrub species, the cover of hazel shrubs, and the number of Norway spruce trees in the canopy, determined over 85% of the index of nestbox use by M. avellanarius. The number of shrub species in the vicinity of the nest site had the highest impact among these. Hazel (especially hazel shrubs taller than 4 m) and bird cherry were the most important understory species for M. avellanarius. Typically, hazel shrubs have several stems, which grow apart from each other and form a large distaff-shaped shrub. Every stem has several diagonal or nearly horizontal branches which are in contact with branches of other hazel shrubs or other trees. In this way, inter-communicating hazel shrubs form excellent routes for the movement of M. avellanarius in a three-dimensional space. Branchy bird cherry trees can also be used by M. avellanarius in the same way.
Interlocking trunks and branches provide more access routes to and from the nest for tree-climbing rodents. A positive correlation between the index of nestbox use and the number of trees or shrubs which have a crown or a trunk connected to the crown of the nestbox tree proves the importance of safe connectivity of nest sites with its surroundings for M. avellanarius. Connectivity of the nestbox tree with the surroundings was the best in nest sites used by M. avellanarius for breeding and preferred for resting. Nest site connectivity for arboreal travel was also a significant predictor of nest site selection by the western grey squirrel Sciurus griseus (Gregory et al. 2010) and Abert’s squirrel Sciurus aberti (Edelman and Koprowski 2005).
In a similar manner to M. avellanarius, a well-developed and diverse understory was the main habitat component which determined nest site preference of the forest dormouse Dryomys nitedula (Juškaitis et al. 2012). A dense understory protects animals from both areal and tree-climbing predators. All potential predators, including the pine marten Martes martes, would be more easily detected by dormice because of their movements through thick vegetation (Panchetti et al. 2007). For example, in tangles of the bramble Rubus fruticosus, the long twines of these plants work like antenna, signaling to the nest occupier if something is approaching from the outside (Juškaitis and Büchner 2013).
M. avellanarius avoids nest sites with high numbers of Norway spruce trees in the canopy because the understory is shaded, and both the density and diversity of the understory are significantly reduced in such places. Similar results on nest site selection by M. avellanarius were also obtained in a mature 75- to 180-year-old mixed forest where M. avellanarius preferred forest stands with a well-developed understory and avoided nest sites with a high number of coniferous trees forming the canopy (Juškaitis and Šiožinytė 2008).
The forest understory consists of shrubs and young trees, but the importance of these two groups is discrepant for M. avellanarius. Dormice avoided nest sites with the highest density of young trees. Young deciduous trees (e.g., lime or ash trees) grow vertically with few diagonal branches and are much less suitable for movement of M. avellanarius in a three-dimensional space compared to hazel shrubs and bird cherry trees. Although the index of nestbox use was positively related to the number of young black alder trees, the last parameter was positively inter-correlated with the total cover of hazel shrubs.
Except with hazel, no statistically significant positive correlations were found between indices of nestbox use and numbers or cover of plants important as food to M. avellanarius, such as the willow, Norway spruce, pedunculate oak, raspberry, dwarf honeysuckle, or glossy buckthorn. The correlation with the number of Norway spruce trees in the canopy was significantly negative. However, selection of nest sites by M. avellanarius was related to the diversity of understory and overstory species in the vicinity of nestboxes, particularly with the number of shrub species. Because the main food sources and accordingly the food plants of M. avellanarius vary during the active season (Juškaitis and Baltrūnaitė 2013), the diversity of understory and overstory species is related to the continuity of the food supply in areas with diverse woody plant communities.
When possible, tree-climbing rodents combine the safety of nest sites and food availability. For example, Arizona grey squirrels Sciurus arizonensis select nest sites with greater canopy cover which may provide more protection from diurnal birds of prey. However, most nest tree species selected by Arizona grey squirrels also provide potential food resources, possibly minimizing travel distances to food sources (Cudworth and Koprowski 2011). Fat dormice prefer denser forest stands with well-connected tree canopies and higher numbers of oak trees, the acorns of which are an important food source (Eiberle 1977; Schlund et al. 1997; Juškaitis and Šiožinytė 2008).
When selecting nest sites in a typical Lithuanian habitat, M. avellanarius also combines the safety of nest sites and food availability in the vicinity of nest sites. A well-developed and inter-connected understory ensures the safety of nest sites from predators. A diversity of understory and overstory species guarantees continuity of the food supply. Similar results were obtained in Sweden where the number of shrub species and cover of different shrub species were among the main factors that were related to the occurrence of M. avellanarius (Berg and Berg 1998). An unshaded well-developed inter-digitating understory with high species diversity was shown to provide an optimal habitat for M. avellanarius in England (Bright and Morris 1990 1996). Meanwhile in Italy, M. avellanarius preferred nest sites with a more-developed understory, but no correlation was found between dormouse presence and shrub species diversity. Telemetric observations showed that dormice traveled rather long distances to reach food sources (Panchetti et al. 2007).
When selecting nest sites for breeding, females of M. avellanarius seek greater safety and better feeding conditions compared to the remaining nest sites. Nest sites used by M. avellanarius for breeding were distinguished by a better-developed and more diverse understory. Nest sites used for breeding were characterized by a higher number of bird cherry trees in the understory, but a lower number of Norway spruce trees in the canopy and a lower cover of oak trees, both of which reduce understory cover. Around nestboxes used for breeding, the diversity of the overstory was also higher among common tree species, including the willow, Norway spruce, and pedunculate oak, which are important feeding plants for M. avellanarius (Juškaitis and Baltrūnaitė 2013).
In summary, the results of our study showed that (a) when selecting nest sites with a diverse and well-developed inter-connected understory, M. avellanarius combines the presence of food in the surroundings with safety from predators; and (b) nest sites used by M. avellanarius for breeding are distinguished by a better-developed understory and a more diverse understory and overstory compared to the remaining nest sites.
M. avellanarius also lives in similar habitats in the adjacent countries of Latvia and Belarus (Pilāts 1994; Kashtalian 2004). It is expected that the results of our study would characterize the situation with nest site selection by M. avellanarius in rather large areas on the northern periphery of its range.
This research was funded by the European Social Fund under the Global Grant Measure (grant no. VP1-3.1-ŠMM-07-K-01-026). We thank two anonymous reviewers for their helpful comments on an earlier version of the manuscript, G. Vaitonis for his help in preparing the figures, and J. Stratford for revision of the English.
- Amori G, Hutterer R, Kryštufek B, Yigit N, Mitsain G, Meinig H, Juškaitis R: Muscardinus avellanarius, IUCN 2012. IUCN Red list of threatened species. Vers. 2012.2. 2008. Available at . Accessed 06 June 2013 http://www.iucnredlist.org Google Scholar
- Atiénzar F, Antón-Pardo M, Armengol X, Barba E: Distribution of the white-headed duck Oxyura leucocephala is affected by environmental factors in a Mediterranean wetland. Zool Stud 2012, 51: 783–792.Google Scholar
- Berg L, Berg Å: Nest site selection by the dormouse Muscardinus avellanarius in two different landscapes. Ann Zool Fenn 1998, 35: 115–122.Google Scholar
- Bertolino S: Microhabitat use by garden dormice during nocturnal activity. J Zool 2007, 272: 176–182. 10.1111/j.1469-7998.2006.00254.xView ArticleGoogle Scholar
- Bertolino S, Cordero di Montezemolo N: Garden dormouse ( Eliomys quercinus ) nest site selection in an alpine habitat. Ethol Ecol Evol 2007, 19: 51–60. 10.1080/08927014.2007.9522580View ArticleGoogle Scholar
- Bertolino S, Perrone A, Gola L, Viterbi R: Population density and habitat use of the introduced eastern cottontail ( Sylvilagus floridanus ) compared to the native European hare ( Lepus europaeus ). Zool Stud 2011, 50: 315–326.Google Scholar
- Bright PW, Morris PA: Habitat requirements of dormice Muscardinus avellanarius in relation to woodland management in southwest England. Biol Conserv 1990, 54: 307–326. 10.1016/0006-3207(90)90143-DView ArticleGoogle Scholar
- Bright PW, Morris PA: Why are dormice rare? A case study in conservation biology. Mamm Rev 1996, 26: 157–187. 10.1111/j.1365-2907.1996.tb00151.xView ArticleGoogle Scholar
- Bright P, Morris P, Mitchell-Jones T: The dormouse conservation handbook. 2nd edition. Peterborough: English Nature; 2006.Google Scholar
- Capizzi D, Battistini M, Amori G: Analysis of the hazel dormouse, Muscardinus avellanarius , distribution in a Mediterranean fragmented woodland. Ital J Zool 2002, 69: 25–31. 10.1080/11250000209356434View ArticleGoogle Scholar
- Carranza ML, Acosta AC, Ricotta C: Analyzing landscape diversity in time: the use of Rényi’s generalized entropy function. Ecol Indic 2007, 7: 505–510. 10.1016/j.ecolind.2006.05.005View ArticleGoogle Scholar
- Cudworth NL, Koprowski JL: Importance of scale in nest-site selection by Arizona gray squirrels. J Wildl Manage 2011, 75: 1668–1674. 10.1002/jwmg.194View ArticleGoogle Scholar
- Dueser RD, Shugart HH Jr: Microhabitats in a forest floor small mammal fauna. Ecology 1978, 59: 89–98. 10.2307/1936634View ArticleGoogle Scholar
- Edelman AJ, Koprowski JL: Selection of drey sites by Abert’s squirrels in an introduced population. J Mamm 2005, 86: 1220–1226. 10.1644/04-MAMM-A-029R1.1View ArticleGoogle Scholar
- Eiberle K: Zur Populationsdynamik des Siebenschläfers ( Glis glis L.) im Lehrwald der ETHZ. Schweiz. Z Forstw 1977, 128: 630–645.Google Scholar
- Gregory SC, Vander Haegen WM, Chang WY, West SD: Nest site selection by western gray squirrels at their northern range terminus. J Wildl Manage 2010, 74: 18–25. 10.2193/2009-021View ArticleGoogle Scholar
- Juškaitis R: Peculiarities of habitats of the common dormouse, Muscardinus avellanarius , within its distributional range and in Lithuania: a review. Folia Zool 2007, 56: 337–348.Google Scholar
- Juškaitis R: Habitat selection in the common dormouse Muscardinus avellanarius (L.) in Lithuania. Balt For 2007, 13: 89–95.Google Scholar
- Juškaitis R: The common dormouse Muscardinus avellanarius: ecology, population structure and dynamics. Vilnius, Lithuania: Institute of Ecology of Vilnius Univ. Publishers; 2008.Google Scholar
- Juškaitis R, Baltrūnaitė L: Feeding on the edge: diet of the hazel dormouse Muscardinus avellanarius (Linnaeus 1758) on the northern periphery of its distributional range. Mammalia 2013, 77: 149–155.Google Scholar
- Juškaitis R, Büchner S: The hazel dormouse Muscardinus avellanarius. NBB English edition, vol 2. Hohenwarsleben: Westarp Wissenschaften; 2013.Google Scholar
- Juškaitis R, Šiožinytė V: Habitat requirements of the common dormouse ( Muscardinus avellanarius ) and the fat dormouse ( Glis glis ) in mature mixed forest in Lithuania. Ekológia (Bratislava) 2008, 27: 143–151.Google Scholar
- Juškaitis R, Balčiauskas L, Šiožinytė V: Nest site preference of forest dormouse Dryomys nitedula (Pallas) in the north-western corner of the distribution range. Pol J Ecol 2012, 60: 815–826.Google Scholar
- Kashtalian AP: Common dormouse Muscardinus avellanarius (Linnaeus, 1758). In The Red data book of Belarus. Animals. Rare and standing under a threat of extinction species of wild animals. Edited by: Pashkov GP. Minsk (in Russian): “Belaruskaya Encyklapedyya“ imeni Petrusya Brovki; 2004.Google Scholar
- Kopij G: Habitat and drey sites of the red squirrel Sciurus vulgaris Linnaeus 1758 in suburban parks of Wrocław, SW Poland. Acta Zool Cracov 2009, 52A: 107–114.Google Scholar
- Krebs CJ: Ecological methodology. 2nd edition. Menlo Park, NJ: Addison Wesley Longman; 1999.Google Scholar
- Morris PA, Bright PW, Woods D: Use of nestboxes by the dormouse Muscardinus avellanarius . Biol Conserv 1990, 51: 1–13. 10.1016/0006-3207(90)90027-MView ArticleGoogle Scholar
- Panchetti F, Sorace A, Amori G, Carpaneto GM: Nest site preference of common dormouse ( Muscardinus avellanarius ) in two different habitat types of central Italy. Ital J Zool 2007, 74: 363–369. 10.1080/11250000701588224View ArticleGoogle Scholar
- Pilāts V: Dormice - their present status in Latvia. Hystrix 1994, 6: 185–194.Google Scholar
- Rosalino LM, Ferreira D, Leitćo I, Santos-Reis M: Selection of nest sites by wood mice Apodemus sylvaticus in a Mediterranean agro-forest landscape. Ecol Res 2011, 26: 445–452. 10.1007/s11284-010-0797-9View ArticleGoogle Scholar
- Rudolf K, Morschhauser T, Pál-Fám F: Macrofungal diversity in disturbed vegetation types in north-east Hungary. Cent Eur J Biol 2012, 7: 634–647. 10.2478/s11535-012-0050-3Google Scholar
- Schlund W, Scharfe F, Strauss MJ, Burkhardt JF: Habitat fidelity and habitat utilization of an arboreal mammal ( Myoxus glis ) in two different forests. Z Säugetierkd 1997, 62: 158–171.Google Scholar
- Sherman LJ: The effects of patchy food availability on nest-site selection and movement patterns of reproductively active female meadow voles Microtus pennsylvanicus . Holarc Ecol 1984, 7: 294–299.Google Scholar
- Skórka P, Martyka R, Wójcik JD, Lend M: Site parameters’ variance - a missing dimension in the studies of nest-site selection? Pol J Ecol 2011, 59: 423–426.Google Scholar
- StatSoft: STATISTICA (data analysis software system), vers. 6. 2004. Available at . Accessed 06 June 2103 http://www.statsoft.com Google Scholar
- StatSoft: Electronic statistics textbook. Tulsa, OK: StatSoft; 2010. Available at . Accessed 28 Jan 2013 http://www.statsoft.com/textbook/ Google Scholar
- Tóthmérész B: DivOrd 1.50: a program for diversity ordering. Tiscia 1993, 27: 33–44.Google Scholar
- Tóthmérész B: On the characterization of scale-dependent diversity. Abstr Bot 1998, 22: 149–156.Google Scholar
- Wolton R: Hazel dormouse Muscardinus avellanarius (L.) nest site selection in hedgerows. Mammalia 2009, 73: 7–12.View ArticleGoogle Scholar
- Wuttke N, Büchner S, Roth M, Böhme W: Habitat factors influencing the distribution of the hazel dormouse ( Muscardinus avellanarius ) in the Ore Mountains, Saxony, Germany. Peckiana 2012, 8: 11–20.Google Scholar
- Zar JH: Biostatistical analysis. 4th edition. Upper Saddle River, NJ: Prentice-Hall; 1999.Google Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.