Overview
Brief Summary
Biology
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Comprehensive Description
Description
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Distribution
Range Description
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Geographic Range
Rhinolophus ferrumequinum are found in northern India, south to northwestern Africa and throughout temperate Eurasia including Great Britain and Japan
(Koopman, 1994). They are also found throughout Turkey, Israel and Jordan (DeBlase, 1980)
Biogeographic Regions: palearctic (Native )
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Range
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Physical Description
Morphology
Physical Description
Rhinolophus ferrumequinum is the largest horseshoe bat in Europe (Schober and Grimmberger, 1997). Its most distinctive feature is the upper saddle process or noseleaf, the upper part of which is pointed while the lower part is horseshoe shaped (Nowak, 1994). Tooth and bone structures distinguish R. ferrumequinum from other rhinolophids. The first premolar on the upper jaw protrudes from the row of teeth. Often this premolar is very small or non-existent. The third and fourth metacarpal bones in the wings are shorter than those of its relatives (Koopman, 1994). The tragus is absent (Simmons and Conway, 1997). The length of the head and body ranges from 57 to 71mm, the tail length ranges from 35 to 43 mm and the forearm from 54 to 61 mm. The wing span ranges from 350 to 400 mm, and the weight from 17 to 34 grams. The Greater horseshoe bat can also be identified by its color. The back is brownish gray with a slight tint of red, while the underside is a lighter gray color. The membrane that connects the forearm and tail is brownish gray. Young R. ferrumequinum are uniformly gray. (Schober and Grimmberger, 1997)
Range mass: 17 to 34 g.
Range length: 57 to 71 mm.
Range wingspan: 350 to 400 mm.
Other Physical Features: endothermic ; bilateral symmetry
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Ecology
Habitat
Habitat and Ecology
In South Asia, this species is found in montane forests among the mountains and valleys of the Himalaya. It is gregarious and roosts in caves, old temples, old and ruined buildings in tight clusters. It has a slow and fluttering flight and feeds on small insects, lacewings, small moths, spiders and grasshoppers. A single young is born after a gestion period of 72 days (Bates and Harrison, 1997).
Systems
- Terrestrial
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Habitat
Rhinolophus ferrumequinum prefer to dwell in karst caves and cave-like spaces under boulders year-round (DeBlase, 1980). In the winter, R. ferrumequinum roost in caves warmer then 7-10 degrees Celsius. This species prefers warmer regions, which have water, shrubs and trees (Schober and Grimmberger, 1997).
Habitat Regions: temperate ; terrestrial
Terrestrial Biomes: forest
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Habitat
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Trophic Strategy
Food Habits
Rhinolophus ferrumequinum hunt at nightfall. This species is an insectivore and preys primarily on larger insects such as Lepidoptera (butterflies and moths) and Coleoptera (beetles) (Jones, 1990). In order to obtain their prey, hunting bats fly close to the ground surface (Schober and Grimmberger, 1997). Rhinolophus ferrumequinum does not hunt in the winter unless the air temperature is warm enough for insect flight, and as a result they hunt less during colder and inclement weather (Racey, 1982). Like other microchiropteran bat species, R. ferrumequinum use echolocation to locate their prey. This species emits a call consisting of short blasts at a low frequency (77-81 kHz) (Schober and Grimmberger, 1997). The call is emitted from the nose, not the mouth (Nowak, 1994).
Animal Foods: insects
Primary Diet: carnivore (Insectivore )
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Associations
Known prey organisms
Insecta
This list may not be complete but is based on published studies.
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Associations
Basilia nana ectoparasitises Rhinolophus ferrumequinum
Other: minor host/prey
In Great Britain and/or Ireland:
Animal / parasite / ectoparasite
Phthiridium biarticulata ectoparasitises Rhinolophus ferrumequinum
Other: major host/prey
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Life History and Behavior
Life Expectancy
Lifespan/Longevity
Lifespan/ Longevity: The oldest recorded age of an R. ferrumequinum is 30 years (Schober and Grimmberger, 1997)
Range lifespan
Status: wild: 30 (high) years.
Average lifespan
Status: wild: 30.0 years.
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Lifespan, longevity, and ageing
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Reproduction
Reproduction
Females are not sexually mature until their third year, while males are sexually reproductive at age two. Females often do not have young until their fifth year (Racey,1982). Mating usually occurs in the fall but can also occur in the spring (Rossiter et al. 2000). Fertilization does not take place until later and is controlled by the females (Schober and Grimmberger, 1997). After mating, the vagina of Rhinolophus ferrumequinum females is closed by a vaginal plug secreted by the male. It is speculated that the plug is used to keep unwanted sperm out, as a method of mate selection (Fenton, 1984) or to hold the sperm until fertilization in the spring (Rossiter et al., 2000). Female R. ferrumequinum return to the same roosting area year after year to give birth and care for their young.
Average number of offspring: 1.
Average weaning age: 8 weeks.
Range age at sexual or reproductive maturity (female): 2 to 5 years.
Average age at sexual or reproductive maturity (female): 3 years.
Range age at sexual or reproductive maturity (male): 2 to 5 years.
Average age at sexual or reproductive maturity (male): 3 years.
Key Reproductive Features: seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (Internal ); sperm-storing ; delayed fertilization
Average birth mass: 5.8 g.
Average gestation period: 80 days.
Average number of offspring: 1.
A female produces one baby which is typically born during June or July (Schober and Grimmberger, 1997). Young open their eyes at 7 day and can fly during the third to fourth week. After seven to eight weeks, young are ready to leave the roost. Females form maternity roosts in warmer places such as attics to care for the young (Schober and Grimmberger, 1997). Greater horseshoe bats lose their milk teeth before birth (Nowak, 1994).
Parental Investment: altricial ; female parental care
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Molecular Biology and Genetics
Molecular Biology
Statistics of barcoding coverage: Rhinolophus ferrumequinum
Public Records: 0
Species: 9
Species With Barcodes: 1
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Conservation
Conservation Status
IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
Assessor/s
Reviewer/s
Justification
History
- 2000Lower Risk/near threatened
- 1996Lower Risk/conservation dependent
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Conservation Status
Rhinolophus ferrumequinum are threatened in western Germany and Austria. Because R. ferrumequinum are sensitive to human disturbances, a special effort has to be made to protect the roosts and to lower the amount of insecticides used on crops in western Germany and Austria. The insecticides kill R. ferrumequinum prey, thus destroying their only food source (Nowak, 1994), as well as harming the bats themselves
US Migratory Bird Act: no special status
US Federal List: no special status
CITES: appendix iii
IUCN Red List of Threatened Species: least concern
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Status
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Trends
Population
In Europe, the two most widespread Rhinolophus species, R. ferrumequinum and R. hipposideros, are of particular conservation concern and are the subject of considerable research and monitoring. R. ferrumequinum has shown marked declines in range in northwest Europe within the last 100 years (e.g. United Kingdom, Germany, Austria), and has gone extinct in some countries (eg. Belgium, Netherlands). However, there are signs of stabilisation and/or recovery in some northwest European countries (Hutson et al 2001). For example, in the UK the species declined massively in the past but it is now stable at a low population level (around 5,000 individuals) (Ransome and Hutson 2000). However, in Austria declines continue, with population reductions of 70% in the last 10 years (from 100 to 30 breeding individuals: Spitzenberger 2002, F. Spitzenberger pers. comm. 2006). In other parts of Europe, trends vary and are generally less well known: in Malta the species has gone extinct, in Portugal and Spain the trend is not known (although some colonies have disappeared in Spain) (Palomo and Gisbert 2002, Cabral et al. 2005), in Croatia the population is thought to be stable (N. Tvrtkovic pers. comm.), and in Romania the population has been slowly increasing since 1989 due to reduced use of pesticides and a return to traditional agriculture with colonies of up to 800 individuals. In Switzerland the species is very rare (3 maternity roosts with some 200 individuals), but the population trend appears stable (H. Kraettli pers. comm. 2006).
In its north African and south Asian range the population size and trends are unknown.
Population Trend
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Threats
Threats
In South Asia, this species is threatened by deforestation, generally resulting from logging operations and the conversion of land for agricultural and other uses. Disturbance to roosting sites is likely to be a potential threat to the populations of this species (Molur et al. 2002).
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Threats
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Management
Conservation Actions
It is protected by national legislation in some range states. There are international legal obligations for its protection through the Bonn Convention (Eurobats) and Bern Convention in parts of its range where these apply. It is included in Annex II (and IV) of the European Union Habitats Directive, and hence requires special measures for conservation including designation of Special Areas for Conservation. There is some habitat protection through Natura 2000 (some roosts are already protected by national legislation).
There are no specific conservation measures in place for the species in North Africa or South Asia. Populations should
be monitored to record changes in abundance and distribution (Molur et al. 2002).
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Conservation
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Relevance to Humans and Ecosystems
Benefits
Economic Importance for Humans: Positive
Positive Impacts: controls pest population
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Wikipedia
Greater Horseshoe Bat
The Greater Horseshoe Bat (Rhinolophus ferrumequinum) is a European bat of the Rhinolophus genus. Its distribution covers Europe, Africa, South Asia and Australia.[2] It is the largest of the European Horseshoe Bats and is thus easily distinguished from other species. The species is sedentary, travelling between 20 and 30 km between the winter and summer roosts, with the longest recorded movement being 180 km. The species is notable as having the oldest recorded age for any European bat, with a bat living for over 30 years. The frequencies used by this bat species for echolocation lie between 69–83 kHz, have most energy at 81 kHz and have an average duration of 37.4 ms.[3][4]
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Physical description
Its distinctive horseshoe noseleaf helps to focus the ultrasound it uses to 'see'.
The Greater Horseshoe Bat is on average between 57 and 71 mm long, with a 35–43 mm tail and a 350–400 mm wingspan. The fur of the species is soft and fluffy, with the base of hairs being light grey, the dorsal side hair grey brown and the ventral side grey-white, with juvenile bats having more of an ash-grey tint to their fur. Wing membranes and ears are light grey-brown. It weighs up to 30 grams.[5] During the winter the bats hibernate in caves, abandoned mines or other underground places.
Habitat
The Greater Horseshoe Bat lives in warmer regions of areas of open trees and scrub, near areas of standing water (e.g., ponds), areas of limestone and human settlement. The species is mainly house-dwelling in the north and cave-dwelling in the south. In the mountains nests are normally at below 800 metres above sea level. They are faithful to their summer and winter roosts, returning to the same sites each year.
Other favoured habitat include woodland with grassy rides and glades, old orchards, old 'veteran' trees with holes, permanent pasture, hedgerows linking the different features together.
Mating
Females normally produce their young when around 4 years old in England and 3 years old in the south of Europe, with males becoming mature around the end of their second year. Mating season is from autumn to spring, with nurseries of up to 200 females clustered together with their young. The maternity roosts are usually found in old buildings, occasionally caves or abandoned mines.
The babies are born in June or July. Each bat only has one baby. Young Greater Horseshoe Bats open their eyes at about 4 days, are able to fly after three weeks and become independent at 7–8 weeks, during August. The false nipples of female bats, which newborn bats cling to after birth, are not fully developed until after the first birth.
Diet and hunting
The species feeds preferentially on lepidoptera (moths), making up around 41% of the diet by volume.[6] - in particular the noctuidae species [7], Coleoptera (beetles) constitute around 33% of the diet[6], of which dung beetles are often taken Aphodius rufipes is one such dung beetle forming an especially important part of its diet. Cow pats are part of its life cycle, acting as food source and habitat for the larvae. Up to 100 larvae can be found in a single cow pat. The beetle is most abundant in August when the young bats begin their first feeeding flights).[8] The remainder of the diet being hymenoptera and diptera.[6] Cockchafers also form an important part of its diet.
The feeding area from the maternity roost is typically of radius 4 km, as neither the lactating females or young can travel far. In late August and September the bats feed on cranefly, to fatten up before hibernation. Breeding females depend on beetles from April until June, and moths from June to August.
The Greater Horseshoe Bat leaves its roost at dusk, and its flying is made up of slow, fluttering travel with short glides, normally between 0.3 and 6 metres above the ground, with little hunting during wet and windy weather. It hunts in terrain with poor tree cover such as hillsides, cliff faces and in gardens, locating insects from its resting place and then intercepting them. The species has the ability to pick food up off the ground while still in flight, and indeed drinks during low-level flight or while hovering. The feeding range of colonies in England is between 8 and 16 kilometres.
Status in Britain
The species is rare in Britain, confined to just a small number of sites. Its distribution can be found on the National Biodivesity website here. Its breeding sites include Brockley Hall Stables near Bristol, Iford Manor near Bath, and Littledean Hall in the Forest of Dean. Its winter hibernation sites include Banwell Caves and Compton Martin Ochre Mine in the Mendip Hills, Chilmark Quarries in Wiltshire, and Combe Down and Bathampton Down Mines near Bath. In Dorset, the species roosts at Bryanston, Creech Grange and in Belle Vue Quarry. The species also occurs at Berry Head in Devon and has a monitored roost site at Woodchester Mansion in Stroud.
The species has disappeared from over half of its former range within the United Kingdom, with about 1% of the population surviving. Like all horseshoe bats it is sensitive to disturbance, and is threatened by the use of insecticides and the elimination of beetles by the changing agricultural practices.
There are seventeen recorded species of bat in Britain as of recent survey results.The greater horseshoe bat is one of the rarest. There are currently 35 recognised maternity and all-year roosts and 369 hibernation sites. Current estimates range between 4000 and 6600 individuals. Greater Horseshoes have declined for numerous reasons ranging from the use of agrichemicals (Ivermectin in particular) to loss of habitat and redundancy of farming methods. Avermectin kills off insect larvae and thus a decrease in the abundance of food for the Horseshoes, causing them to travel further and face increased dangers. Habitat loss is primarily the lack of established hedgerows and deciduous woodland-pasture ecotones. Modern farming methods have seen the reduction of cattle-grazing and this has impacted the Horseshoes who previously found that dung attracted insects and sustained entomogenous populations, giving their prey a stable population.
Gallery
Greater horseshoe bat (Rhinolophus ferrumequinum)
References
- ^ Chiroptera Specialist Group (2000). "Rhinolophus ferrumequinum". IUCN Red List of Threatened Species. Version 2.3. International Union for Conservation of Nature. http://www.iucnredlist.org/apps/redlist/details/19517. Retrieved 11 May 2006.
- ^ Maurice Burton, Robert Burton The international wildlife encyclopedia, Volume 9 Marshall Cavendish, 2002, ISBN 0-7614-7266-5
- ^ Parsons, S. and Jones, G. (2000) 'Acoustic identification of twelve species of echolocating bat by discriminant function analysis and artificial neural networks.' J Exp Biol., 203: 2641–2656.
- ^ Obrist, M.K., Boesch, R. and Flückiger, P.F. (2004) 'Variability in echolocation call design of 26 Swiss bat species: Consequences, limits and options for automated field identification with a synergic pattern recognition approach.' Mammalia., 68 (4): 307–32.
- ^ Nature, English (1998). Managing Landscapes For The Greater Horseshoe Bat. Ruddocks (Lincoln) Ltd. ISBN 1-85716-416-4.
- ^ a b c Jones, G. (1990), "Prey selection by the greater horsehoe bat (Rhinolophus ferrumequinum): Optimal foraging by echolocation?", Journal of Animal Ecology, 59: 587–602.
- ^ Bat Conservation Trust Greater Horseshoe bat Species information leaflet
- ^ Wild Devon The Magazine of the Devon Wildlife Trust, page 14, Winter 2009 edition
Further reading
- Schober, Wilfried; Eckard Grimmberger (1989). Dr. Robert E. Stebbings. ed. A Guide to Bats of Britain and Europe (1st ed.). UK: Hamlyn Publishing Group. ISBN 0-600-56424-X.
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