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isolated to harbour high percentage of<br />

endemism despite their mountain affinities<br />

(30% of orophytes or Mediterranean mountain<br />

plants).<br />

Genista lobelii is found along a wide altitudinal<br />

range i.e., from dry coastline mountains<br />

chains at 320 m to colder and relatively humid<br />

situation at more 1110 m. As for A. provincialis,<br />

another endemic of Basse Provence<br />

(Véla et al. 2008; Baumel et al. 2009), the<br />

vegetation associated to G. lobelii is not<br />

homogeneous as reflected by the multivariate<br />

analysis (Figure 4) and floristic composition<br />

(Table 1 and Appendix 2). This heterogeneity<br />

reflects the existence of different habitats<br />

within the distribution of G. lobelii with possible<br />

effects on population sizes. At 800 m<br />

(a.s.l.), on the summital crest of Sainte-<br />

Baume, Sainte-Victoire and Trets (cluster<br />

no 1), G. lobelii shows its ecological optimum<br />

characterized with numerous and large populations.<br />

At the opposite, on coastline mountain<br />

chains (cluster no 3) and at 300-500 m (a.s.l.),<br />

G. lobelii has smaller populations, less than 10<br />

individuals occurring on 10 m2 , similar to<br />

observation made on Cap Canaille stations.<br />

ecologia mediterranea – Vol. 36 (1) – 2010<br />

Distribution, habitat and population size variation of Genista lobelii (Fabaceae)<br />

from the calcareous mountains of Basse Provence (S-E France)<br />

Indeed, in this cluster (n o 3), Mediterranean<br />

mountains plant species are less frequent than<br />

thermophilous Mediterranean species such as<br />

Pistacia lentiscus. Populations of G. lobelii<br />

located at 500 to 800 m are mostly grouped<br />

together (cluster n o 2). In majority, they are<br />

isolated, reduced, under or beside an open formation<br />

dominated by Quercus coccifera<br />

and/or Quercus ilex. The expansion of this<br />

vegetation type is promoted by land-use<br />

changes i.e. pasture abandonment and recurring<br />

fire (Tatoni et al. 2004). From these facts,<br />

it could be hypothesized that G. lobelii probably<br />

occupied larger areas at lowland position<br />

or along mountain slopes during the last centuries<br />

and is now threatened by forest succession.<br />

For example, on Bessillon site (BSS), G.<br />

lobelii forms a small population, only 10 individuals,<br />

and is distant from the nearest population<br />

by 17.95 km. Another good example<br />

concerns the small population of the BMH1<br />

station (cluster n o 2) near the “Hotellerie de la<br />

Sainte-Baume”, found on grassland vegetation<br />

type and threatened by colonisation of Quercus<br />

pubescens Willd. It appears that distribution<br />

of G. lobelii, like numerous open habitat<br />

Appendix 2.2 – Cluster no 2<br />

Species Frequence Family Biological Seeds Biological Demographic Biogeography<br />

(%) cycle dispersal traits stratigies<br />

Thymus vulgaris subsp. vulgaris 97 Lamiaceae Perennial Zele Ch S Steno-W-Medit.<br />

Fumana ericoides subsp. montana 92 Cistaceae Perennial Apro Ch SR Steno-Medit.<br />

Amelanchier ovalis (s.l.) 82 Rosaceae Perennial Zend P CS Medit.-Mont.<br />

Helichrysum stoechas 79 Asteraceae Perennial Apro Ch S Steno-W-Medit.<br />

Rosmarinus officinalis 79 Lamiaceae Perennial Zele NP CSR Steno-Medit.<br />

Aphyllanthes monspeliensis 74 Aphyllanthaceae Perennial Apro H S Steno-W-Medit.<br />

Sesleria caerulea (s.l.) 64 Poaceae Perennial Apro H CS Oroph. C-Europ.<br />

Anthyllis vulneraria (s.l.) 62 Fabaceae Annual, Perennial Alou Th, H SR Eurasiatic<br />

Koeleria vallesiana subsp. vallesiana 62 Poaceae Perennial Apro H S Euri-Medit.<br />

Brachypodium retusum 59 Poaceae Perennial Zepi Ch CS Steno-W-Medit.<br />

Helianthemum oelandicum subsp. italicum 59 Cistaceae Perennial Apro Ch SR Euri-N-Medit.<br />

Ononis minutissima 59 Fabaceae Perennial AuM Ch S Steno-W-Medit.<br />

Echinops ritro 56 Asteraceae Perennial Alou H SR Steno-Medit.<br />

Galium corrudifolium 56 Rubiaceae Perennial Zepi H S Steno-Medit.<br />

Cerastium arvense subsp. suffruticosum 51 Caryophyllaceae Perennial Apro Ch S Oroph. S-Europ.<br />

Teucrium polium subsp. polium 51 Lamiaceae Perennial Zele Ch S Steno-Medit.<br />

Avenula bromoides (s.l.) 49 Poaceae Perennial Zepi H S Steno-W-Medit.<br />

Helianthemum oelandicum subsp. incanum 49 Cistaceae Perennial Apro Ch SR Oroph. S-Europ.<br />

Teucrium chamaedrys (s.l.) 49 Lamiaceae Perennial Baro Ch CS Euri-Medit.<br />

Festuca marginata subsp. marginata 46 Poaceae Perennial Zepi H S Endem. W-Alpica<br />

Genista hispanica subsp. hispanica 44 Fabaceae Perennial AuM Ch S W-Medit.-Mont.<br />

Juniperus phoenicea subsp. phoenicea 44 Pinaceae Perennial Zend P CS Euri-Medit.<br />

Quercus ilex (s.l.) 44 Fagaceae Perennial Zdys p CS Steno-Medit.<br />

Seseli galloprovinciale 44 Apiaceae Perennial Baro H S Subendem.<br />

Quercus coccifera 41 Fagaceae Perennial Zdys P CS Steno-W-Medit.<br />

Juniperus oxycedrus subsp. oxycedrus 38 Pinaceae Perennial Zend p CS Euri-Medit.<br />

Arenaria aggregata 36 Caryophyllaceae Perennial Apro Ch S NW-Medit.-Mont.<br />

Odontites luteus subsp. luteus 36 Scrophulariaceae Annual Apro Th SR Euri-Medit.<br />

Crepis albida 33 Asteraceae Perennial Aleg H S Oroph. SW-Europ.<br />

Iberis stricta subsp. leptophylla 33 Brassicaceae Biennial Baro Th, Ch SR Subendem.<br />

73

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