1 - Ecologia Mediterranea
1 - Ecologia Mediterranea
1 - Ecologia Mediterranea
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Bergmeier<br />
Fine-scale species composition<br />
The total number of spring-reproducing taxa was<br />
only slightly higher in the grazed microplots - 91 as<br />
against 86 (table 4). The mean number of taxa per<br />
microplot, however, was significantiy higher in the<br />
non-grazed plots (15.3 as against 19.5; t-Test with p <<br />
0.001). The same was true for the total and mean<br />
numbers of reproduction units.<br />
Post-tire Grazed Non-grazed<br />
management (n = 50) (n = 50)<br />
Total number of taxa 91 86<br />
Mean number of taxa<br />
per microp1ot 15.3 19.5<br />
Total number of<br />
reproduction units 5397 6493<br />
Mean number of repr.<br />
units per microplot 107.9 129.9<br />
Table 4. Diversity characteristics of the microplots<br />
The quantitative analysis of the microplots reveals<br />
that certain taxa were promoted by non-grazing, others<br />
were not (figure 2). Particularly Asteraceae such as<br />
Picris altissima, Crepis commutata and Urospermum<br />
picroides were supported by non-grazing; as were<br />
certain legumes (Lotus peregrinus, Lotus edulis) and<br />
grasses (Avena barbata, Bromus intermedius, Hyparrhenia<br />
hirta). Similar results were detected concerning<br />
the reproduction units (table 5). On the other hand, a<br />
small number of taxa was affected by non-grazing.<br />
Valantia hispida and Galium murale displayed lower<br />
constancy as weIl as fewer individuals. Crepis cretica<br />
was also much less abundant in the non-grazed plots<br />
but so far maintained its high constancy. It should be<br />
emphasized that no taxon promoted by non-grazing is<br />
lacking completely on the grazed ground, and so far,<br />
the reverse is also true.<br />
DISCUSSION AND CONCLUSIONS<br />
Pre-tire vs post-tire<br />
In the present case study, fire had only little effects<br />
on the overall diversity of phrygana. AIready in the<br />
first post-fire spring the composition of herbaceous<br />
6<br />
Combined effects offire and grazing on phrygana<br />
taxa was almost identical to that of the pre-fire vegetation.<br />
This is in accordance with Bôhling (1994), but<br />
apparently not with Arianoutsou-Faraggitaki & Margaris<br />
(1981: 187; 1982) who found the ground "carpeted<br />
with annual and perennial herbaceous species<br />
rarely seen in the undisturbed sites". However, noth<br />
ing in detail is said in the latter study about pre-fire<br />
species composition and vegetation structure, so one<br />
might assume a rather dense and species-poor scrub<br />
which supports a floristic post-fire flush (Arianoutsou<br />
& Margaris, 1981; Papavassiliou & Arianoutsou,<br />
1993). In the present study, only Lavatera bryoniifolia,<br />
and to a minor degree Asphodelus ramosus and<br />
Sarcopoterium spinosum, were stimulated after fire.<br />
The coverage of the herbaceous vegetation on the<br />
grazed ground was but slightly higher than before the<br />
fire. The dwarf shrub layer was destroyed completely<br />
and, after two years, the process of regeneration had<br />
only just started. While the unburned phrygana shrubs<br />
provide effective protection against soil erosion (Dieckmann<br />
et al., 1985), the post-fire phrygana is highly<br />
susceptible to erosion as long as the shrub layer did<br />
not regenerate.<br />
The pre-fire dwarf shrub layer was rather homogeneous<br />
with dominant Calicotome vil/osa and Coridothymus<br />
capitatus, and with sparse Sarcopoterium<br />
spinosum. The high proportion of seedlings of the<br />
latter species in the grazed post-fire vegetation (table<br />
3) suggested that the post-fire shrub layer, once reestablished,<br />
might be richer in Sarcopoterium than the<br />
pre-fire vegetation, at least temporarily. This is corroborated<br />
by numerous observations of Sarcopoterium<br />
dominating initial regeneration stages of phrygana<br />
(Raus, 1979; Arianoutsou-Faraggitaki & Margaris,<br />
1982; Arianoutsou-Faraggitaki, 1984; Bohling, 1994;<br />
Bergmeier, 1995). Sarcopoterium spinosum is known<br />
to be fire-promoted (Roy & Arianoutsou-Faraggitaki,<br />
1985), and there is evidence for its representation in<br />
seed banks of <strong>Mediterranea</strong>n dwarf scrub ecosystems<br />
(Litav & Orshan, 1971). Moreover, S. spinosum often<br />
regenerates by both seeding and resprouting, the latter<br />
strategy according to Papanastis (1977) chiefly in<br />
more humid regions.<br />
This flexible response may prove favourable under<br />
variable ecological conditions.<br />
ecologia mediterranea 23 (3/4) - 1997