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Plant Biosystems - An International Journal Dealing
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Gap analysis revealed a low efficiency of Natura 2000
network for the conservation of endemic species in
Mediterranean temporary freshwater habitats
S. Bagellaa, M.C. Cariaa & R. Filigheddua
a Dipartimento di Scienza della Natura e del Territorio, University of Sassari, I-07100,
Sassari, Italy
Accepted author version posted online: 28 Oct 2013.Published online: 21 Nov 2013.
To cite this article: S. Bagella, M.C. Caria & R. Filigheddu , Plant Biosystems - An International Journal Dealing with all
Aspects of Plant Biology (2013): Gap analysis revealed a low efficiency of Natura 2000 network for the conservation of
endemic species in Mediterranean temporary freshwater habitats, Plant Biosystems - An International Journal Dealing with all
Aspects of Plant Biology: Official Journal of the Societa Botanica Italiana, DOI: 10.1080/11263504.2013.860055
To link to this article: http://dx.doi.org/10.1080/11263504.2013.860055
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Plant Biosystems, 2014
http://dx.doi.org/10.1080/11263504.2013.860055
Gap analysis revealed a low efficiency of Natura 2000 network for the
conservation of endemic species in Mediterranean temporary fresh-
water habitats
S. BAGELLA, M.C. CARIA, & R. FILIGHEDDU
Dipartimento di Scienza della Natura e del Territorio, University of Sassari, I-07100 Sassari, Italy
Abstract
Listed and rare species are abundant in temporary freshwater habitats. Among them, the endemic contingent represents a
crucial conservation target particularly in the areas characterized by abundant endemic flora for which the local
administrations have a high level of responsibility. The aim of this research was to test how the endemic plants found in
Mediterranean temporary ponds were represented in Natura 2000 network in a biodiversity hotspot of the Mediterranean
region. The results of our research at regional scale pointed out that the existing Nature 2000 sites provide a limited degree of
protection and that the gap analysis should be taken into account when conservation priorities are set.
Keywords: Habitat Directive, responsibility, temporary ponds, threatened species, wet habitats
Introduction
Freshwater habitats represent one of the main target
of the conservation policies at global scale because the
great variety of rare species (Ernandes & Marchiori
2012; Minggagud & Yang 2012) and vegetation types
(Asensi & Dı
´ez-Garretas 2011; Costa et al. 2011;
Lumbreras et al. 2011; Sburlino et al. 2011; Nucci
et al. 2012) they host were dramatically reduced in the
last decades (Iberite et al. 2011; Zuccarini & Kampus
ˇ
2011; Buffa & Villani 2012; Croce et al. 2012;
Manolaki & Papastergiadou 2012).
In recent years, a growing attention was given to
the temporary freshwater habitats and their strategic
role for the conservation of the overall freshwater
biodiversity was stressed (Williams et al. 2004)
because they harbor not only species specialized to
live in temporary waters but also generalist of
freshwater habitats or terrestrial species (Caria
et al. in press) for which they could represent a
refuge (Rhazi et al. 2006). Listed and rare species are
abundant in these habitats (Rhazi & Grillas 2010),
and among them, the endemic contingent represent a
crucial conservation target particularly in the areas
characterized by abundant endemic flora for which
the local administrations have an high level of
responsibility (Bacchetta et al. 2011).
Despite the European Community (Council of
Europe 1992) listed temporary freshwater habitats
in the Habitat Directive (codex 3120, 3130, and
3170*), they are often poorly identified and their
importance is largely unappreciated, leaving them
vulnerable also to unintentional destruction
(Grillas et al. 2004).
The aim of this research was to test how the
endemic plants found in Mediterranean temporary
ponds were represented in Natura 2000 network in a
biodiversity hotspot of the Mediterranean region.
Material and methods
Study area
The study was carried out in the island of Sardinia,
Western Mediterranean biogeographic subregion
(Blasi & Frondoni 2011), which is included in the
biodiversity hotspot of the Thyrrenian islands
(Grillas et al. 2004). In the island, 122 Natura
2000 sites were designated (http://www.
minambiente.it).
Correspondence: S. Bagella, Dipartimento di Scienze della Natura e del Territorio, University of Sassari, Via Piandanna 4, I-07100 Sassari, Italy. Tel: þ39 079
228641. Fax: þ39 079 233600. Email: sbagella@uniss.it
q 2013 Societa
` Botanica Italiana
Downloaded by [University Di Sassari] at 07:33 25 November 2013
2 S. Bagella et al.
Table I. List of the endemic plants found in Sardinian
Mediterranean temporary ponds and relative percentage of the
point of presence outside Natura 2000 sites.
% points
of presence
outside Natura
2000 sites
Bellium bellidioides L. 45
Carex caryophyllea Latourr. ssp. insularis
(Christ ex Barbey) Arrigoni 38
Cerastium palustre Moris 81
Colchicum verlaqueae Fridl. 0
Crocus minimus DC. in Re
`doute
´ 48
Festuca morisiana Parl. 21
Festuca sardoa (Haeckel in Barbey) Richter 0
Leucojum roseum Martin 50
Mentha requienii Benth. ssp. requienii 20
Morisia monanthos (Viv.) Asch. ex Barbey 80
Myosotis soleirolii Godr. in Gren. et Godr. 25
Nananthea perpusilla (Loisel.) DC. 11
Oenanthe lisae Moris 66
Ornithogalum corsicum Jord. et Fourr. 64
Ranunculus cordiger Viv. ssp. cordiger 17
Ranunculus cordiger Viv. ssp. diffusus
(Moris) Arrigoni 51
Ranunculus cymbalarifolius Balbis et Moris 56
Ranunculus revelieri Boreau subsp. revelieri 36
Romulea bocchierii Frignani & Iiriti 0
Romulea requienii Parl. 42
Romulea revelieri Jord. et Fourr. 14
In Sardinian Mediterranean temporary ponds,
186 plant species/subspecies were found (Bagella &
Caria 2012), of which 21 were listed as endemic
(Table I) (Arrigoni et al. 1977 –1991; Frignani &
Iiriti 2008; Fridlender 2009). The distribution data
(i.e. the points of presence) of these entities were
available in a Geographic Information System
(Mestroni 2012).
Gap analysis
In order to test how the endemic plants growing in
Mediterranean temporary ponds were represented in
Natura 2000 network, we applied the gap analysis
(Rosati et al. 2008). First, we overlapped the
shapefile of the distribution data of each entity to
the shapefile of the Natura 2000 network (www.
minambiente.it) using ArcGIS 10.1 Second, we
evaluated for each entity the percentage of sites
outside Natura 2000 sites.
Results
The 21 entities were located in 40 Natura 2000 sites.
Against 716 points analyzed, about half were located
outside Natura 2000 network. The species with the
higher percentage of points outside Natura 2000
network (around 80%) were Cerastium palustre and
Morisia monanthos, while Festuca sardoa and Romulea
bocchieri did not have any point outside the network
(Table I).
Discussion and conclusions
Capotorti et al. (2012) emphasized the essential role
of National Park network for biodiversity conserva-
tion in Italy encouraging a deeper level study
throughout the system of national protected areas
to provide more detailed information. The results of
our research at regional scale on a selected group of
species pointed out that the existing Nature 2000
sites provide a limited degree of protection. This
finding is in agreement with other studies evaluating
the effectiveness of the Natura 2000 system (Arau
´jo
2004; Maiorano et al. 2006; Jantke et al. 2011). New
opportunities for the conservation of habitat and
species were nevertheless recently offered by the IPA
project which was effective in filling some gaps in the
system of the protected areas (Blasi et al. 2011).
The conservation of the studied species, which
are not listed anywhere as policy species and then are
not protected under the legislative point of view,
could go through the conservation of the habitats
listed in the Annex 1 of the Habitat Directive
(Council of Europe 1992). The three habitat types
related to temporary waters (3120, 3130, and 3170*)
in which they grow could act as umbrella for them
but unfortunately these habitats are in turn not well
represented in the Natura 2000 network (Bagella
et al. 2009, 2010; Bagella & Caria 2013).
Our results suggest that in setting conservation
priorities on the basis of regional responsibility, it is
advantageous taking into account how the species are
represented in the Habitat 2000 sites. Indeed,
following (Bacchetta et al. 2011) Cerastium palustre,
endemic to Sardinia subprovince, deserves particular
attention as this species is listed in a high threat
category. Morisia monanthos, endemic to Sardinian –
Corsican Province and listed by the same authors in a
low threat category, probably would be worth
considering if the gaps in the Natura 2000 network
were included in the evaluation. On the other hand,
for the two species represented 100% inside the
Natura 2000 network, i.e. Romula bocchieri and
Festuca sardoa, this type of information could be
unfavorable if not taken into account the point
distribution areal: Romula bocchieri is endemic to the
Sardinian sub-province and was found just in one site
(Frignani & Iiriti 2008)while Fes tuca sard oa is endemic
to Sardinian–Corsican Province but, in Sardinia, they
grow just in one site (Arrigoni et al. 1977– 1991).
Besides the implementation of priority list at
regional scale, the data collected could be a source of
information for national databases (Landucci et al.
Downloaded by [University Di Sassari] at 07:33 25 November 2013
3
2012), systematic spatial decision support systems
(Guillet et al. 2012) and media application (Nimis
et al. 2012). The latter could be an opportunity to
increase public awareness to neglected habitats, such
as temporary wetlands.
Acknowledgements
This research was funded by the PAULIS project
(Regione Sardegna, CRP-24943).
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