Habitat selection and activity patterns in Alpine mountain hare (Lepus timidus varronis)

We investigated activity patterns and habitat use of 34 radio-tracked mountain hares (Lepus timidus) in the Italian Alps. We first showed that hares were nocturnal and that activity patterns changed seasonally in parallel with circadian rhythms. We predicted that day home ranges will include suitable resting (shelter) habitats, and night home ranges will primarily include suitable foraging habitats. A hare's night-range was larger than its day-range. On average, night and day ranges overlapped by 36%, suggesting that selective pressures affecting space use were, at least partly, different at night than day. Dwarf mountain-pine was the most preferred habitat in all seasons and was selected both for active behaviour (night) and resting (day) and hares avoided the most open habitats. Exploring the effects of season, time of day (day vs. night) and site, we found that habitat use by mountain hares did not differ between seasons or between the active (night) and resting (day) period of circadian cycle. Also, we found no effects of differences in landscape structure (habitat patchiness and heterogeneity) on the patterns of habitat selection. Hares always preferred the dense, forested habitats, which seemed to provide food resources as well as shelter from predators throughout the year.     

The occurrence and abundance of helminth parasites of the mountain hare Lepus timidus (L.) and the wild rabbit Oryctolagus cuniculus (L.) in Aberdeenshire, Scotland

Mountain hares were collected each month between April 1984 and March 1985 and their intestines examined for helminths. 26 rabbits were also collected between July and December 1984 and examined for gastro-intestinal helminths. Three nematode and two cestode species were found in the hares while only two nematode and one cestode species were found in the rabbits. Trichostrongylus retortaeformis was recorded from 88% of the 193 hares and 92% of the rabbits while comparable figures for Passalurus ambiguus were 0.5% and 54% and for Mosgovoyia pectinata 14% and 81%. Seasonal fluctuations were observed in the T. retortaeformis populations in the hare; numbers tended to be low during the winter months and high throughout the summer. Paranoplocephala wimerosa was reported for the first time from the British Isles and Trichostrongylus axei was recorded for the first time in the mountain hare.     

The diet of the mountain hare (Lepus timidus hibernicus) on coastal grassland

Across most of their range in Europe, mountain hares are usually restricted to upland areas with poor food quality. In these areas they generally feed on browse species such as heather or twigs and barks of trees. On lowland areas in Europe, with better food quality, the mountain hare is replaced by the brown hare ( Lepus europaeus ) which feeds predominantly on greasses. This khas led some authors to conclude that mountain hares are primarily adapted for browsing. In the absence of brown hares in Ireland, mountain hares are found on a wide variety of habitats including grassland. On grassland, their diet consists almost exclusively of grasses, up to 94% of their annual diet, which is more than has been reported for brown hares on similar habitat. Based on this evidence, and other work, it is proposed that the mountain hare in primarily a grazing animal and competitive exclusion by brown hares may underlie much of their present distribution in Europe.     

Spatial patterns of genetic diversity across European subspecies of the mountain hare, Lepus timidus L

Fossil evidence shows that populations of species that currently inhabit arctic and boreal regions were not isolated in refugia during glacial periods, but instead maintained populations across large areas of central Europe. These species commonly display little reduction in genetic diversity in northern areas of their range, in contrast to many temperate species. The mountain hare currently inhabits both temperate and arctic-boreal regions. We used nuclear microsatellite and mtDNA sequence data to examine population structure and alternate phylogeographic hypotheses for the mountain hare, that is, temperate type (lower genetic diversity in northern areas) and arctic-boreal type (high northern genetic diversity). Both data sets revealed concordant patterns. Highest allelic richness, expected heterozygosity and mtDNA haplotype diversity were identified in the most northerly subspecies, indicating that this species more closely maps to phylogeographic patterns observed in arctic-boreal rather than temperate species. With regard to population structure, the Alpine and Fennoscandian subspecies were most genetically similar (F(ST) approximately 0.1). These subspecies also clustered together on the mtDNA tree and were assigned with highest likelihood to a common Bayesian cluster. This is consistent with fossil evidence for intermediate populations in the central European plain, persisting well into the postglacial period. In contrast, the geographically close Scottish and Irish populations occupied separate Bayesian clusters, distinct clades on the mtDNA maximum likelihood tree and were genetically divergent from each other (F(ST) > 0.4) indicating the influence of genetic drift, long isolation (possibly dating from the late glacial era) and/or separate postglacial colonisation routes.     

Contagious mucocutaneous dermatitis of the mountain hare (Lepus timidus): pathology and cause

Contagious mucocutaneous dermatitis is a frequently encountered disease of mountain hares (Lepidus timidus) in Finland. We describe the histopathologic changes and propose an etiologic cause for this disorder. Fifty-three cases collected during 1982-2000 were examined histologically. Transmission electron microscopy was performed in one case. In fully developed lesions, keratinocytes in epidermis and follicular infundibula were swollen and contained large eosinophilic intracytoplasmic inclusion bodies with marked reticular and ballooning degeneration. In later stages, there was marked necrosis and ulceration with severe pyogranulomatous and suppurative inflammation. At this stage, no viral inclusions were detectable, but secondary Staphylococcus warnerii infection was present in most cases. In late lesions, there was dermal fibrosis with epidermal hyperplasia. No spiral-shaped bacteria suggesting treponematosis were detected at any stage. Ultrastructurally, swollen epidermal and follicle infundibular cells contained round intracytoplasmic inclusion bodies with a myriad of virions typical of poxvirus with a biconcave nucleocapsid core, two lateral bodies, and a clearly discernible outer lipoprotein capsule. The findings suggest that contagious mucocutaneous dermatitis in mountain hares is a viral disease caused by a poxvirus. The disease is often complicated by secondary bacterial infection, most commonly S. warneri.     

The 24-hour cycle of the mountain hare Lepus timidus Linnaeus, 1758

The behavioral decisions of wild animals are influenced by the often conflicting needs to both feed efficiently and to avoid predators. Information regarding how lagomorphs such as the mountain hare (Lepus timidus) balance these factors throughout the day-night cycle is largely lacking despite its importance to management.To better understand the type and proportion of various behaviors the mountain hare engages in over the course of a 24-hour period, I monitored the behavior of six mountain hares under controlled conditions from early to mid-winter. The mountain hares spend the majority of their time resting (mean ± standard deviation: 32.4 ± 14.4%) and under canopy (22.4 ± 18.7%), and a smaller proportion of their time feeding (16.2 ± 6.1%). Activity peaks over the course of the 24-hour cycle reflect natural behavior patterns that emphasize the reduction of predation risk. The sunrise phase is characterized by the search for a suitable resting place; the day phase by resting and hiding. The sunset phase is characterized by the search for food, and the night phase by an equal mix of food intake and movement through the home range. These results can help land managers predict how factors such as increasing tourist activity (perceived by the hare as a safety threat) will influence the behavior of free-ranging mountain hares.     

Further observations on a Callunetum intensively grazed by mountain hares (Lepus timidus L.)

Summary

Heavy utilisation by mountain hares checked the growth of Calluna so that mean height was only 12 cm thirty years after the 0.2 ha area was burnt. Cover and biomass increased gradually over the thirteen years studied, from 59 to 85% and 300 to 580 g/m² respectively. Differences in sward height were maintained, the greater utilisation of short heather being offset by greater growth. Compared to ruminant-grazed Calluneta, the hare-grazed sward had a distinctive, compact form, and biomass was great relative to cover and height because of the many shoots. Non-ericoid angiosperms had little cover.     

A single multiplex of twelve microsatellite markers for the simultaneous study of the brown hare (Lepus europaeus) and the mountain hare (Lepus timidus)

The management of hunted species is challenging, as it must conciliate the conservation of species and their sustainable exploitation. Nongenetic tools are widely used in this context but they may present limitations notably when species can hybridize or when large‐scale spatial monitoring is required to establish optimal management actions. This is why genetic tools have been more and more integrated in wildlife management practices. However, the markers proposed are often amplified in small multiplexes when larger ones could allow to better cope with the small quantities of DNA obtained with noninvasive sampling methods. Here, we propose a unique multiplex of 12 autosomal microsatellite markers for the study of two hare species that exist in sympatry in some areas in Europe and are hunted notably in France: the brown hare Lepus europaeus and the mountain hare L. timidus. We tested 17 markers previously used in these two species or other lagomorph species, from which 12 were included in this single multiplex. Diversity was between 4 and 30 alleles per locus totaling 126 alleles, and we showed that these markers possess appropriate genetic resolution for individual and species identification for the populations under study. This multiplex panel represents the largest number of microsatellites amplified in one reaction proposed for these two hare species and provides a cost‐effective and valuable tool for further hybridization studies and the management of hares.     

A preliminary study on the seasonal body temperature rhythms of the captive mountain hare (Lepus timidus)

The mountain hare (Lepus timidus) is a year-round active herbivore adapted to survive the boreal winter. Captive mountain hares (N = 4) were implanted with intraabdominal thermosensitive loggers to record their core body temperature (T_b) for a year and during food deprivation (8–48 h) in summer and winter. The average T_b was 38.7 ± 0.01 °C in summer and 38.3 ± 0.01 °C in winter. The yearly T_b correlated positively with the ambient temperature. The 24-h T_b was the highest from late scotophase to early photophase in summer and winter and the lowest during middle-late photophase in summer or during early-middle scotophase in winter. The range of the 24-h oscillations in T_b increased in three animals in winter. Food deprivation did not induce hypothermia in summer or winter. These preliminary data suggest that the mountain hare can spare a modest amount of energy with the wintertime reduction in T_b.     

The diel activity pattern of mountain hare (Lepus timidus) on managed heather moorland in Scotland

The research presented in this paper provides an insight into the behavioral ecology of mountain hares on heather moorland in the Lammermuir Hills of southeast Scotland. We examine the seasonal and diel activity patterns using camera traps over a period of 12 months. The rate of camera detections was calculated for the different divisions of the 24‐hr cycle (daylight, dusk, night, and dawn). During autumn and winter (October–February), the activity pattern was crepuscular with greater activity at dusk than at dawn. Daylight activity was relatively low, and there was a regular pattern of small peaks of activity during the night. In spring and summer (March–September), peaks of crepuscular activity remained evident but daylight activity was much more prevalent than during autumn and winter, and night activity was lower. We discuss the problematic definition of twilight and present an explanation for seasonal changes in the pattern of diel activity that is linked to the reproductive cycle of the mountain hare.     

Weights and growth rates in the Mountain hare Lepus timidus scoticus

Mountain hares were weighed during live trapping on a study area near Dufftown, Banffshire, from June 1958 to August 1966. Hares shot or killed by other means on the study area and elsewhere were also weighed. Females were heavier than males throughout the year and this difference became apparent in juveniles by August of their year of birth. Male hares lost weight during the breeding season (January to June) but regained it in late summer. Young hares gained weight initially at about 14 g per day, then at about 6 g per day to adult weight. Small juveniles, or those born late in the season, tended to become small adults, large or early juveniles to become large adults. Small hares moulted less completely andjbegan to breed later in the season than large hares. The effects of disease, starvation, severe weather and injury on hare weights were considered. Female weights were greater when the population was small, due to more late pregnancies or more embryos per female. Weight could not be used to distinguish between adult and juvenile hares above 2.1 kg, nor between young and older adults.     

European hare (Lepus europaeus) invasion ecology: implication for the conservation of the endemic Irish hare (Lepus timidus hibernicus)

European hare Lepus europaeus populations have undergone recent declines but the species has successfully naturalised in many countries outside its native range. It was introduced to Ireland during the mid-late nineteenth century for field sport and is now well established in Northern Ireland. The native Irish hare Lepus timidus hibernicus is an endemic subspecies of mountain hare L. timidus and has attracted major conservation concern following a long-term population decline during the twentieth century and is one of the highest priority species for conservation action in Ireland. Little is known about the European hare in Ireland or whether it poses a significant threat to the native mountain hare subspecies by compromising its ecological security or genetic integrity. We review the invasion ecology of the European hare and examine evidence for interspecific competition with the mountain hare for habitat space and food resources, interspecific hybridisation, disease and parasite transmission and possible impacts of climate change. We also examine the impact that introduced hares can have on native non-lagomorph species. We conclude that the European hare is an emerging and significant threat to the conservation status of the native Irish hare. Invasive mammal species have been successfully eradicated from Ireland before and immediate action is often the only opportunity for cost-effective eradication. An urgent call is issued for further research whilst the need for a European hare invasive Species Action Plan (iSAP) and Eradication strategy are discussed.     

Winter diet, habitat selection and fluctuation of a mountain hare Lepus timidus population in Finnish Forest Lapland

Composition of the winter diet, habitat selection and population fluctuations in the mountain hare Lepus timidus were studied in the Värriötunturi fell area, Eastern Finnish Forest Lapland, during the winters 1968/69–1984/85. The three population lows recorded during this 17-year period followed each other at intervals of 4 and 8 years. During the lows the hares occurred only in the most favoured (forest-covered) habitats and in two of them they behaved according to the concept of the refuge theory. The mountain birch Betula pubescens ssp. tortuosa appeared to be the most important, but not the most favoured winter food item. When the population crashed, the proportion of birch in the diet decreased, and was replaced especially by juniper which is one of the secondary food items (and is for this reason often discarded although cut). It is suggested that the quality and/or quantity of the winter food (i.e. winter pastures) are one of the driving forces in the population fluctuation of the mountain hare in this area.     

Invasion from the cold past: extensive introgression of mountain hare (Lepus timidus) mitochondrial DNA into three other hare species in northern Iberia

Mitochondrial DNA introgression from Lepus timidus into Lepus granatensis and Lepus europaeus was recently reported in Iberia, although L. timidus presumably retreated from this region at the end of the last ice age. Here we assess the extent of this ancient mtDNA introgression by RFLP analysis of 695 specimens representing the three hare species present in Iberia. The introgressed L. timidus lineage was found in 23 of the 37 populations sampled. It is almost fixed in L. europaeus across its Iberian range in the Pyrenean foothills, and in L. granatensis, which occupies the rest of the peninsula, it is predominant in the north and gradually disappears further south. We also found it in Lepus castroviejoi, a species endemic to Cantabria. Multiple hybridizations and, potentially, a selective advantage for the L. timidus lineage can explain the remarkable taxonomic and geographical range of this mitochondrial introgression.