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with higher humidity, while the second group has retreated to the same places (Гонча-

ров, 1944). Today these populations are highly influenced by the economic activities of

Man mainly by ploughing the soils and their utilization as arable land. These relict

species form open and genetically unstable populations with restricted capabilities for

distribution. Unfortunately measures for their protection are not undertaken.

Some

Astragalus

species have secondary enlarged their distribution area as a

consequence o f the deforestation in the Danube Plain and the Ludogorie region. These

species have crossed the range of the Stara Planina Mts., most probably in its eastern

lower part, and were preserved on calcareous, rocky and sandy terrains in the Znepole

region, the Thracian Plain, the Tuudza Hilly Plain (Fig. 2). In Southern Bulgaria this

group includes

Astragalus pubijlorus

, /1.

dasyanthus

,

A. asper

,

A. pouficus

and

A. vest-

carius

with small in size populations.

The same migration direction is observed for the widely distributed species

A.

onobrychis.

This Euro-Siberian steppe element is rather polymorphic and possesses a

high ecological plasticity (P av lova , 2003). That’s why it has succeeded to pass the

forest-steppe zone and

irradiate

in Bulgaria and

in

Central Europe.

On such secondary steppe terrains are found the Balkan endemics /1.

wilmottianus

Stoj. and

A. spntnen,

showing the closest morphological similarity with the primitive

syndrome of the middle Asiatic species

A. manspessulamis

L.. This group of relatively

young species has originated in the mountainous and semi-mountainous areas of the

Balkan Peninsula.

Other

Astragalus

species reached Bulgaria migrating along the classical south -

politic route, They demonstrate the connections of our flora with the steppe areas in

Eastern Thracia, a continuation of the steppes in Asia Minor. An example is the species

A. gladiatlms

which is a macedonian-thracian-anatolian geoelement, Quite possibly its

area in former times was larger in southeastern direction, covering pail of the territory of

Turkey. This supposition is based on its close morphological similarity with the endemic

turkish species

A. aucheri

Boi s s . The possibility for the past existence of other closely

related species distributed in the Iran-Turanian area, unknown or extinct, should not be

excluded.

The species of genus

Astragalus,

which have reached the highest level in the

evolutionary process towards xeropbytizatiou, are of special interest. The analysis o f the

distribution patterns and the endemic processes in the group of the spiny representatives

of

Astragalus

reveals their most probable origin in the Pamir-Himaiayan center, They

show considerable migrations to the east and the west. Their migration capabilities are

comparatively weaker as typical xerophytes, so that relict types from the ancient

Mediterranean basin are rarely observed. A representative of this group in the Bulgarian

flora is

A. augustifoftus

Lam. bound to the ecological requirements of calcareous

terrains. Most of its communities are secondary in origin (Велчев. Василев, 1984) on

the place of the former tree vegetation destroyed by the humans. The considerable

displacement in the vertical distribution

oiAstragalus

on the Balkan peninsula up to 2100

m linked with its infraspecific variation are a result of acive specialion processes during

the interstadial migrations and tendency for polyploidization (Pavl ova, 2003).

Similar migration and evolutionary processes have taken place in subgen.

Tragacantha

Bunge (Pod l ech, 1986). This subgenus is poorly represented in the

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