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Ecologia Mediterranea

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tidissima, and J. excelsa) and the low dominance<br />

of juveniles of these tree species in<br />

Michmich reflect the impact of grazing and<br />

other natural resource harvesting practices<br />

that local communities undertake. Q. calliprinos<br />

was observed with a high dominance<br />

of juvenile and juvenile trees, which reveals<br />

anthropogenic activities such as lumbering for<br />

either household use or charcoal production<br />

(Figure 3d).<br />

The Qammoua forest comprises different<br />

types of tree communities. The P. brutia population<br />

comprises different age categories.<br />

Tree communities of C. libani and A. cilicica<br />

ecologia mediterranea – Vol. 38 (2) – 2012<br />

Towards the establishment of a natural park in Eastern <strong>Mediterranea</strong>n forests in Mount Makmel:<br />

Botanical assessment and communities participation practices<br />

a) Hrar b) Jayroun<br />

c) Qemmamine d) Michmich<br />

Figure 3 – Age structure of the tree populations found in the different regions.<br />

presented diversity in the demographic structure<br />

(Figure 3e). High frequency of the candle-shaped<br />

C. libani trees reveal ancient lumbering<br />

practices, which reflect the innate<br />

sense of local communities for sustainability.<br />

At the lower altitude, Q. cerris demonstrated<br />

a homogenous demographic structure, recording<br />

high dominance of juvenile and mature<br />

trees. The low coverage of juvenile trees calls<br />

for the strict conservation of these remnant<br />

stands, and suggests the need to consider the<br />

seedlings recruitment in future monitoring<br />

program (Figure 3f).<br />

e) Qammoua f) Qammoua Q. cerris stand<br />

89

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