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European Atlas of Forest Tree Species | Tree species
60
< 25%
25% - 50%
50% - 75%
> 75%
Native
Chorology
Frequency
Ailanthus altissimaAesculus hippocastanum
C. Ravazzi, G. Caudullo
Aesculus hippocastanum L., the European horse-chestnut, is a mesophytic broad-leaved tree native to a few mountain
ranges in the Balkan Peninsula, but widespread in the urban landscape of moist, warm-temperate Europe. The morphology
and ecology of its large seeds are very distinctive, and they are also known for their medicinal properties. Natural populations
are reduced and declining after strong insect infections, pollution, wood extraction and forest fires. For this reason it
recently received the status of near-threatened species.
Description
European horse-chestnut (Aesculus hippocastanum L.) is the
only European native species belonging to the Aesculus genus,
which counts 13 tree and shrub species living in temperate
deciduous forests1. It is a large and tall tree growing up to 39 m
and potentially very long-living2. It develops an oval crown, bearing
large shade-giving leaves composed by 5-7 palmate leaflets.
Numerous white hermaphrodite flowers are born in a pyramidal
inflorescence. The petals are yellow at the base, as are their major
veins at pollination maturity, while later turning deep orange and
thus afterwards rejected by bumblebees and honeybees3. Pollen is
very distinctive, with coarse spines4. Only 2-5 (8) flowers from the
base of each inflorescence develop the subglobose fruit, provided
with sharp spines and containing one to three seeds. The ripe seed
recalls the chestnut fruit in its dark brown colour and is used for
horse feeding, justifying the origin of the common name5. The
surface of the seed also bears a large whitish scar-like mark, which
is the hilum, attaching them to the ovary6.
Distribution
The European horse-chestnut is endemic for two relict main
ranges, each containing small isolated populations respectively in
mountains of Greece, Albania and the former Yugoslav Republic
of Macedonia7, 8 and in the Preslavski Balkan, Bulgaria9 , 10. It
is a relic species from the Early Pleistocene, about 1 million
years ago. At that time it was still widespread in Europe11, 12 .
Its subsequent decline may be related to the extinction of large
mammals acting as dispersers of its large seeds13 and to low
tolerant seed physiology to desiccation14. In 1557 AD seeds of
uncertain provenance were imported from Turkey to Prague,
beginning the tree cultivation in Europe5. Claims of occurrence
in the Bronze Age pile dwellings from North Italy15 turned to be
modern contaminants.
Habitat and Ecology
The European horse-chestnut is a mesophytic tree,
growing in moist deciduous broad-leaved forests under a warm-
temperate climate. It thrives especially at the bottom of shady
ravines on limestone bedrock and on alluvial soils in association
with hornbeam (Carpinus betulus), but also in mountain mixed
forests up to 1600 m altitude16. It is very sensitive to forest fire;
moreover seed are both dormant and recalcitrant; i.e. they do not
tolerate water desiccation even at maturity14. This is why horse-
chestnut seedlings do not establish on open and dry substrates,
limiting species ability to pioneering moist rocky and karstic
sites only and preventing migration after forest withdrawals and
climate worsening16.
Importance and Usage
Horse-chestnuts are favourite trees of gardens, parks and
roadways under moist climates. Numerous horticultural varieties
have been described. The seeds have traditionally been used as
a therapy for chronic venous inefficiency17 and are processed by
the pharmaceutical industry. It has been shown that they contain
escin, preventing accumulation of white blood cells responsible for
poor blood flow in the legs, common with ageing18. Unprocessed
seeds are poisonous, but a decoction of the bark and leaves is
also used in folk medicine of Albania, Kosovo and Central Italy to
treat circulatory and rheumatic problems19, 20 .
Threats and Diseases
Total population in the native habitat is reduced to less
than 2 500 mature individuals21, with declining subpopulations
due to strong infections by Cameraria ochridella (nocturnal
moth, Lepidoptera), which feeds on the leaves, causing mid-
summer defoliation and exhaustion of the trees and may reduce
reproduction in natural populations22-24 . Horse-chestnuts are
highly vulnerable25 to the Asian longhorn beetle (Anoplophora
glabripennis) which is a large wood-boring beetle native of
Asian countries, such as Japan, Korea and China. Other threats
are road construction, local tourism, wood extraction, pollution,
and forest fires in the residual native areas. European horse-
chestnut is assessed as vulnerable in Greece and Bulgaria and
near-threatened at European scale21.
Aesculus hippocastanum in Europe: distribution, habitat, usage and threats
This is an extended summary of the chapter. The full version of
this chapter (revised and peer-reviewed) will be published online at
https://w3id.org/mtv/FISE-Comm/v01/e017fc3. The purpose of this
summary is to provide an accessible dissemination of the related
main topics.
This QR code points to the full online version, where the most
updated content may be freely accessed.
Please, cite as:
Ravazzi, C., Caudullo, G., 2016. Aesculus hippocastanum in
Europe: distribution, habitat, usage and threats. In: San-Miguel-
Ayanz, J., de Rigo, D., Caudullo, G., Houston Durrant, T., Mauri, A. (Eds.),
European Atlas of Forest Tree Species. Publ. Off. EU, Luxembourg,
pp. e017fc3+
References
[1] J. W. Hardin, Brittonia 12 (1960).
[2] O. Johnson, D. More, Collins tree guide
(Collins, 2006).
[3] M. C. F. Proctor, P. Yeo, A. Lack, The natural
history of pollination (Timber Press, 1996).
[4] A. E. Pozhidaev, Grana 34, 10 (1995).
[5] H. W. Lack, Arnoldia 61, 15 (2002).
[6] A. Cronquist, An Integrated System
of Classification of Flowering Plants
(Columbia University Press, New York,
1981).
[7] P. Fukarek, Problems of Balkan flora
and vegetation: proceedings of the first
International Symposium on Balkan Flora
and Vegetation, Varna, June 7-14, 1973,
D. Jordanov, ed. (Bulgarian Academy of
Sciences, Sofia, 1975), pp. 146–161.
[8] N. Avtzis, D. Avtzis, S. Vergos, S. Diamantis,
Phytologia Balcanica 13, 11 (2007).
[9] M. Anchev, et al., Phytologia Balcanica 15,
63 (2009).
[10] L. Evstatieva, Red Data Book of the
Republic of Bulgaria, Volume 1 - Plants
& Fungi, D. Peev, V. Vladimirov, eds.
(Bulgarian Academy of Sciences and
Ministry of Environment and Water, Sofia,
Bulgaria, 2011).
[11] C. Ravazzi, Giornale botanico italiano 128,
751 (1994).
[12] J. M. Postigo Mijarra, F. Gómez
Manzaneque, C. Morla, Vegetation History
and Archaeobotany 17, 351 (2008).
[13] L. van der Pijl, Principles of Dispersal in
Higher Plants (Springer Berlin Heidelberg,
Berlin, Heidelberg, 1982).
[14] P. B. Tompsett, H. W. Pritchard, Annals of
Botany 71, 107 (1993).
[15] R. Battaglia, La palafitta del lago
di Ledro nel Trentino : gli scavi e la
stratigrafia, il contenuto del deposito
antropozoico, la metallurgia e la
cronologiadell’abitato palafitticolo, vol.
7 of Memorie Museo Storia Naturale
Venezia Tridentina (Tipografia editrice
mutilati e invalidi, 1943).
[16] I. Horvat, V. Glavač, H. H. Ellenberg,
Vegetation Südosteuropas, vol. 4 of
Geobotanica selecta (Gustav Fischer
Verlag, Jena, 1974).
[17] E. Bombardelli, P. Morazzoni, A. Griffini,
Fitoterapia 67, 483 (1996).
[18] M. H. Pittler, E. Ernst, Cochrane Database
of Systematic Reviews (John Wiley &
Sons, Ltd, Chichester, UK, 2006).
[19] A. Pieroni, et al., Journal of
Ethnopharmacology 91, 331 (2004).
[20] B. Mustafa, et al., Journal of Ethnobiology
and Ethnomedicine 8, 6+ (2012).
[21] S. Khela, The IUCN Red List of Threatened
Species (2013), pp. 202914/0+.
[22] C. Thalmann, J. Freise, W. Heitland, S.
Bacher, Trees 17, 383 (2003)
[23] J. I. Barredo, et al., EPPO Bulletin 45, 273
(2015).
[24] CABI, Cameraria ohridella (horsechestnut
leafminer) (2015). Invasive Species
Compendium. http://www.cabi.org
[25] D. de Rigo, et al., Scientific Topics Focus 2,
mri10a15+ (2016).
[26] J. Acevski, B. Simovski, Proceedings of
the International conference Integrated
management of environmental resources:
Suceava, November 4-6th, 2011, S.-A.
Horodnic, M.-L. Duduman, C. Palaghianu,
eds. (Editura Universităţii "Ştefan cel
Mare", Suceava, Romania, 2012).
[27] R. D. Smith, K. A. Smith, eds., Country
Study for Biodiversity of the Republic
of Macedonia - First National Report
(Ministry of Environment and Physical
Planning, Skopje, Macedonia, 2003).
[28] D. H. Peçi, A. Mullaj, A. Dervishi, Journal of
Institute Alb-Shkenca 5, 153 (2012).
The large brown seeds are also known as conkers.
(Copyright Free Photos, www.flickr.com: CC-BY)
The distinctive flowers appear in spring and are pollinated by bees.
(Copyright Free Photos, www.flickr.com: CC-BY)
Isolated large European horse chestnut in a garden park.
(Copyright Nacho, www.flickr.com: CC-BY)
The large leaves are composed of 5-7 palmate leaflets.
(Copyright Free Photos, www.flickr.com: CC-BY)
Map 1: Plot distribution and simplified chorology map for Aesculus hippocastanum.
Frequency of Aesculus hippocastanum occurrences within the field observations
as reported by the National Forest Inventories. The chorology of the native
spatial range for A. hippocastanum is derived after several sources8, 10, 26-28 .
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