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opennotspecifiedAug 2003View details →

Fig. 2 in A soil population of Lithobius tricuspis Meinert in a Mediterranean forest (Chilopoda, Lithobiomorpha: Lithobiidae)

Fig. 2. Average monthly densities of males, females, larvae and total number of Lithobius tricuspis specimens captured in each level.

opennotspecifiedAug 2003View details →

Fig. 3 in A soil population of Lithobius tricuspis Meinert in a Mediterranean forest (Chilopoda, Lithobiomorpha: Lithobiidae)

Fig. 3. Average monthly densities of LI, LII, LIII and LIV larval stages of Lithobius tricuspis captured in each edaphic horizon.

opennotspecifiedAug 2003View details →

Fig. 4 in A soil population of Lithobius tricuspis Meinert in a Mediterranean forest (Chilopoda, Lithobiomorpha: Lithobiidae)

Fig. 4. Monthly Usher index values (depth error) of males, females, larvae and total specimens of Lithobius tricuspis.

opencc-by-4.0Feb 2024View details →

Plant-herbivorous-insect-incidence-matrix Mediterranean Mixed Forest

Datasets for the presence/absence of sucking and chewing insects associated to dominant woody species from the Medirranean mixed forest.

opennotspecifiedJul 2018View details →

Distribution. Most of Europe, from the British Is and NW France E to W Siberia as far E as Irtysh and Ob rivers, and from S Sweden, S Finland, and S Karelia (Russia) S to N Italy and N Balkans; marginally present also in NW Kazakhstan. In E Europe and in Asia the border roughly follows the extreme extension of the taiga in the N (northernmost record is from Pechora River close to 68°N) and the steppe-forest—steppe transition in the S. Present on some Is in the Baltic Sea and around Denmark (Oland, Funen, Zeeland, Bjgrng, Tasinge, Tung, Langeland, Riigen, Usedom, and Wollin), around Great Britain (Sky, Mull, Anglesey, Wight, and Jersey), offshore W coast of France (Ouessant and Ré), and on Cres (Croatia) as the only Mediterranean I. in Talpidae

Distribution. Most of Europe, from the British Is and NW France E to W Siberia as far E as Irtysh and Ob rivers, and from S Sweden, S Finland, and S Karelia (Russia) S to N Italy and N Balkans; marginally present also in NW Kazakhstan. In E Europe and in Asia the border roughly follows the extreme extension of the taiga in the N (northernmost record is from Pechora River close to 68°N) and the steppe-forest—steppe transition in the S. Present on some Is in the Baltic Sea and around Denmark (Oland, Funen, Zeeland, Bjgrng, Tasinge, Tung, Langeland, Riigen, Usedom, and Wollin), around Great Britain (Sky, Mull, Anglesey, Wight, and Jersey), offshore W coast of France (Ouessant and Ré), and on Cres (Croatia) as the only Mediterranean I.

FIGURES 7–13. FIGURES 7–10 in New species of Pseudoscorpiones (Arachnida) from tree hollows in a Mediterranean oak forest in Spain

FIGURES 7–13. FIGURES 7–10. Neobisium (N.) maroccanum Beier, 1930. 7, distal end of movable finger of left chelicera of paratype female from Korifla; 9, anterior and medial processes of right coxa I, idem; 8, distal end of movable finger of right chelicera, female from Xauen; 10, anterior and medial processes of left coxa I, idem. FIGURES 11–13. Neobisium (N.) hispanicum n. sp., male holotype. 11, left chelicera; 12, distal end of movable finger of left chelicera; 13, anterior and medial processes of left coxa I.

FIGURES 2–6 in New species of Pseudoscorpiones (Arachnida) from tree hollows in a Mediterranean oak forest in Spain

FIGURES 2–6. Habitus of species from Salamanca province. 2. Neobisium hispanicum n. sp.; 3. Amblyolpium dollfusi Simon, 1898; 4. Beierochelifer peloponnesiacus (Beier, 1929); 5. Rhacochelifer gaeli n. sp.; 6, Rhacochelifer nonidezi n. sp.

FIGURE 1 in New species of Pseudoscorpiones (Arachnida) from tree hollows in a Mediterranean oak forest in Spain

FIGURE 1. Sampling areas in Salamanca province, Castilla y León autonomous region, Spain. Area 1, El Rebollar Nature Reserve; area 2, Sierra de las Quilamas Nature Reserve.

FIGURES 26–33. Rhacochelifer gaeli n in New species of Pseudoscorpiones (Arachnida) from tree hollows in a Mediterranean oak forest in Spain

FIGURES 26–33. Rhacochelifer gaeli n. sp., male holotype. 26, right chelicera; 27, right posterolateral corners of carapace and tergites I–IV; 28, right pedipalp, minus chela, dorsal view; 29, right chela, dorsal view; 30, right chelal fingers, antiaxial view (teeth omitted); 31, apex of fixed finger of right chela; 32, basal dentition of right chela; 33, tibia and tarsus of right leg I, antiaxial view. Abbreviations: gp, glandular pore; lms, lateromedial seta.

FIGURES 34–40. Rhacochelifer nonidezi n in New species of Pseudoscorpiones (Arachnida) from tree hollows in a Mediterranean oak forest in Spain

FIGURES 34–40. Rhacochelifer nonidezi n. sp., male holotype. 34, left chelicera; 35, galea of movable cheliceral finger of right chelicera, antiaxial view; 36, left hemitergites VI, with detail of seta ls; 37, left pedipalp, minus chela, dorsal view, with details of setae; 38, left chela, dorsal view; 39, fingers of left chela, antiaxial view; 40, tibia and tarsus of right leg I, antiaxial view. Abbreviations: ds, discal seta; gp, glandular pore; ls, lateral seta; ms, medial seta.

FIGURE 41. Rhacochelifer nonidezi n in New species of Pseudoscorpiones (Arachnida) from tree hollows in a Mediterranean oak forest in Spain

FIGURE 41. Rhacochelifer nonidezi n. sp., male holotype, genital area, ventral view. Abbreviations: fs, forked seta; is, internal seta; sc, statumen convolutum.

opencc-by-nc-4.0Jul 2017View details →

Geographic distribution of 24 Mediterranean and European forest tree species

The 24 distribution maps are a contribution to the regional project "Maximize the production of goods and services of Mediterranean forest ecosystems in the context of global changes" funded by the French Global Environmental Facility (FGEF) and coordinated by FAO-Silva Mediterranea and Plan Bleu. The maps are part of the activities of component 1 "Production of data and development of tools to support decision and management of vulnerable Mediterranean forest ecosystems affected by climate change and the ability of these forest ecosystems to adapt to global change". A total of 24 key forest tree species have been selected by the project partners for their importance for the biodiversity of the Mediterranean basin and for delivering ecosystem services to the Mediterranean forestry community. Data on the geographic distribution of the 24 species were compiled from different sources and make a distinction between locations of known distribution, presumed area of native distribution, and countries (or region within countries) of native distribution. Details on how the maps were produced are given in a published report: N. Wazen, B. Fady (2016) Geographic distribution of 24 major tree species in the Mediterranean and their genetic resources, FAO and Plan Bleu, ISBN 978-92-5-109469-3, http://www.fao.org/3/a-i6338e.pdf The 24 tree species are: <ul> <li>Acer hyrcanum subsp. tauricolum (Boiss. & Balansa) Yalt</li> <li>Arbutus unedo L</li> <li>Cedrus atlantica (Endl.) Manetti ex Carriere</li> <li>Cedrus libani A. Rich</li> <li>Chamaerops humilis L.</li> <li>Ilex aquifolium L.</li> <li>Juniperus drupacea Labill.</li> <li>Juniperus excelsa M. Bieb.</li> <li>Juniperus oxycedrus L.</li> <li>Juniperus phoenicea L.</li> <li>Laurus nobilis L.</li> <li>Pinus brutia Ten.</li> <li>Pinus halepensis Mill.</li> <li>Pinus nigra J.F. Arnold</li> <li>Pinus pinea L.</li> <li>Pistacia lentiscus L.</li> <li>Platanus orientalis L.</li> <li>Quercus canariensis Willd.</li> <li>Quercus cerris L.</li> <li>Quercus coccifera L.</li> <li>Quercus ilex L.</li> <li>Quercus suber L.</li> <li>Taxus baccata L.</li> <li>Tetraclinis articulata (Vahl) Mast.</li> </ul> Updates of the maps are published on the FAO GeoNetwork at http://www.fao.org/geonetwork/srv/en/metadata.show?id=56996 Changes in the successive versions Version 5 <ul> <li>A shapefile was added showing a single distribution area for each species. This distribution area was obtained by merging the different distributions areas available from the different sources. Known distribution localities were converted into a distribution area using alpha-shapes and this area was merged with the others.</li> </ul> Version 4 <ul> <li>Quercus suber, map in Bohbot et al. (2005): the polygon corresponding to the Venetian Lagoon was removed.</li> </ul> Version 3 <ul> <li>Pinus nigra, map of Bolos & Vigo (1984): polygons indicating presence in the eastern part of Corsica and the Balearic Islands were removed. Polygons indicating presence in the coastal zone of Croatia and some Greek islands were added.</li> <li>Quercus cerris, map of the Atlas Florae Europeae: points of occurrence corresponding to coastal tiles with a center that falls in the sea were displaced to the closest land locations.</li> <li>Arbutus unedo, map 39 in Quézel & Santa (1962): three small polygons corresponding to the southernmost part of the distribution were added. </li> <li>Pinus halepensis, map 2 in Quézel & Santa (1962): the polygon corresponding to the zone K2 of the map was added.</li> <li>Pinus halepensis, map 3 in Quézel & Santa (1962): the polygons corresponding to the former georeferencing were removed. A small polygon in the southern and westernmost part of the distribution was added.</li> </ul> Version 2 <ul> <li>The “Source_Dat” field was harmonized using the “author_date_title” format for published references.</li> <li>All polygons were snapped together vertices within a small distance threshold to fix small coordinate misalignment in adjacent polygons. In addition, polygons were clipped with sea and administrative boundaries. </li> <li>Pinus halepensis, map 3 in Quézel & Santa (1962): a new georeferencing using the Algerian chotts as additional georeferencing points was made. However, by mistake, the polygons from the old referencing were kept in the shapefile. This mistake was corrected in the subsequent version.</li> </ul>

Figure 1 in Comparison of reptile communities in three types of thermophilous Mediterranean forest in southern Greece

Figure 1. Map showing the location of the study area and the forest types at Srofylia, western Peloponnisos. Black represents Quercus aegilops, horizontal lines Pinus pinea and vertical lines Pinus halepensis.

Figure 2 in Comparison of reptile communities in three types of thermophilous Mediterranean forest in southern Greece

Figure 2. Cluster analysis dendrogram of Euclidean distances between the three forest habitats and their transition zones. The abbreviations used follow the habitat codes displayed in Table 1.

Figure 2 in The role of hatching asynchrony in brood size reduction of the great tit Parus major in a Mediterranean pine forest

Figure 2. Distribution of estimated age at time of death of nestlings in synchronous (asynchrony of 0 or 1 days, white bars) and asynchronous (asynchrony of 2 or more days, black bars) broods.

Figure 1 in The role of hatching asynchrony in brood size reduction of the great tit Parus major in a Mediterranean pine forest

Figure 1. Mean hatching asynchrony by five-day periods against laying date (vertical lines indicate range of values).