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ŠUMARSKI LIST 13/2005 str. 105     <-- 105 -->        PDF

V. Ivančević: BIOLOGICAL AND TECHNICAL REGULATION OF THE SENJ TORRENT "TORRF.NTF." Šumarski list - SUPLEMF.NT (2005), 91-109
ly. At such a rate, the quantity of the eroded material is
always lower than the quantity of the formed material.


The geological substrate, the vegetation and other
external impacts determine the development of varied
soil types. Senjska Draga is dominated by shallow and
skeletoidal brown sub-Mediterranean soils, while rendzinas,
red soils, brown eutrophic soils, acid brown
soils, humus - silicate soils and other soil types alternate
sporadically in a mosaic-like pattern.


Climate


According to Köppen´s classification, Senjska Draga
belongs to the continental variety of the Mediterranean
climate (Cfsax"). According to Thörnthwait´s index,
it belongs to the zone of humid climate. The mean
annual temperature of 9.1 °C and the annual precipitation
average of 1.700 mm is characterised by a pronounced
autumn maximum and summer minimum.
This area suffers sudden weather changes, particularly
when large quantities of air mass are on the move. These
changes are responsible for strong winds (bura/northcrly
and y «go/southerly), which have a negative impact
on the development of vegetation and soil.


Vegetation


According to the phytogeographic classification,
the forest vegetation of Senjska Draga belongs to the
sub-Mediterranean vegetational zone and the Mediterranean
- montane vegetation belt of the Adriatic province
of the Mediterranean region. To a lesser degree it
also belongs to the Illyrian province of the North-American
forest region. The first zone, containing forests
and thickets of oriental and hop hornbeam of the alliance
Ostryo-Carpinion orientalis Ht. in two altitudinal
belts, extends from the sea to 700 m above the sea towards
the hinterland (Pelccr, 1972). The first belt
from 0-300 m is covered with forests of pubescent oak
and oriental hornbeam (Querco-Carpinetum orientalis
H-ić 1939) and degraded communities of ornamental
grass and sage (Stipo-Salvietum officinalis H-ić). Ori


ental hornbeam is only partially represented, while hop
hornbeam extends as far as the sea. The second belt
from 300-700 m is inhabited by forests of pubescent
oak and hop hornbeam (Ostryo-Quercetum pubescentis
Ht. 1938), mostly in the form of degraded thickets
in varying stages of the secondary phytocoenosis Seslerio-
Ostryetum. Within the forest of pubescent oak
and hop hornbeam there are several subassociations
and wasteland communities, including sedge and
knapweed {Carici-Centauretum rupestris Ht.), savory
and campanula {Satureio-Edraeaenthetum Ht.) and several
extra-zonal communities. As a final degradation
stage in the forest there are thickets of common juniper
(./. communis) and prickly juniper (J. oxycedrus). The
largest areas of Senjska Draga are covered with forests
and degraded stages of the second belt. Apart from the
zonal, there are also several extra-zonal communities.
These include autochthonous forests of black pine with
cotoneaster {Cotonaestro-Pinetum nigrae Ht. 1938),
forests of sessile oak with woodrash (Luzulo-Quercetum
petraeae I Hill. 1983 / Pass. 1963), forests of sessile
oak with brooms (Luzulo-Quercetum petraeae genistetosum
prov. Pelc.) and forests of beech with woodrushes
(Luzulo-Fagetum Wrab.).


The second vegetation zone towards the continental
hinterland from 700 m upwards contains beech forests
with autumn moor grass (Seslerio-Fagetum sylvaticae
/Ht. 1950/ M. Wraber 1960) extending up to the sub-
mountainous beech forests {Fagetum illyricum subalpinum
Ht.). The elements of xerothermal sub-Mediterranean
forests and mesophytic beech forests are represented
in the prevailing beech forests with autumn
moor grass. Apart from the mentioned forest communities
and their degraded forms, there are also 22 artificially
established cultures - enclosures of black pine
covering 320 ha and distributed in a mosaic-like pattern
across Senjska Draga. Not only do these cultures enclosures
have a predominantly protective role, but
they also play a key role in the successful regeneration
of autochthonous vegetation (Figure 1).


A HISTORICAL SURVEY OF FORESTS IN SENJSKA DRAGA


From preserved forests to their disappearance


According to research by Magdić (1877), at the
turn of the 16lh and the 17th century the surroundings of
Senj, including Senjska Draga, were covered with dense
forests of oak and fir! (it was most probably black
pine, not fir). In the early 17th century mention was made
of the preserved forests of Senjska Draga in connection
with the resettlement of the uskoci (rebel fighters
against the invaders) from Senj into the interior of the
country. Profits from the sale of these forests were to
be used by Venice to cover the costs of their resettlement.
Bishop De Dominis of Senj was to receive a


commission as the middleman in this transaction. However,
the violent death of Rabata, the military commander
of Senj, and the opposition staged by the Viennese
court undermined the realisation of this plan (Sever
in ski, 1967). The forests of Senj must have disappeared
in the first half of the 17th century, since a
highly destructive torrent in 1647 inflicted enormous
damage to the Town of Senj, destroying a part of the
town walls and 50 houses within the town (Vi tezo vic,
1696). Clearly, the torrent caused such devastating
damage because the forests in Senjska Draga had
already completely disappeared. At that time, the Senj