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Biodiversity and Forests

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Since the preparation of the <strong>Biodiversity</strong> Country<br />

Study (MOA/UNEP/GEF, 1996), urbanisation<br />

appears to be the main driving force to habitat<br />

loss or change in all areas of Lebanon except<br />

in pine forest communities where recent fires<br />

(natural <strong>and</strong> man-induced) are the main cause<br />

of degradation. Juniper <strong>and</strong> several oak species<br />

are preferentially felled for the production of<br />

charcoal. Overgrazing is further threatening<br />

dwindling juniper forests <strong>and</strong> compromising<br />

or inhibiting regeneration. The stone pine<br />

(umbrella pine) is primarily threatened by urban<br />

development <strong>and</strong> forest fires. The severity of<br />

threats by forest type is presented in Figure 5.3.<br />

Quarries <strong>and</strong> stone crushers, agricultural<br />

expansion into forested areas, climate change,<br />

limited public awareness of conservation issues,<br />

<strong>and</strong> political tensions have a compounding<br />

effect on natural resources including biodiversity<br />

<strong>and</strong> forests.<br />

In rangel<strong>and</strong>s, the main driving force is<br />

urbanisation but followed by overgrazing.<br />

In fact, large swaths of l<strong>and</strong> constitute graze<br />

l<strong>and</strong>s for agro-pastoral ruminant production.<br />

Some of these l<strong>and</strong>s were degraded from<br />

maquis to garrigue <strong>and</strong> then to batha. If these<br />

areas degrade further due to unsustainable<br />

grazing activities <strong>and</strong> intensity, they will no<br />

longer support the biodiversity they originally<br />

sustained. Graze l<strong>and</strong>s cover much greater areas<br />

than areas under conservation management;<br />

the sustainable management of graze l<strong>and</strong>s<br />

therefore will contribute to improving<br />

biodiversity management (MOE/UNDP, FNR-<br />

CBD, 2009). In short, Figure 5.4 illustrates the<br />

impact of each source of pressure on habitat<br />

loss <strong>and</strong>/or forest degradation.<br />

Forest fires, especially fires recorded in 2007 <strong>and</strong><br />

2008, have destroyed in a relatively short time<br />

span 4,200 ha of Lebanon’s vegetation cover.<br />

During a single day in October 2007, the total<br />

burned area was equivalent to three times the<br />

area reforested during 17 years (AFDC, 2007).<br />

The devastating fires <strong>and</strong> their impact on forest<br />

cover raised national concern <strong>and</strong> fears that<br />

Lebanon’s forest cover would disappear unless<br />

radical steps were taken to address <strong>and</strong> prevent<br />

fires (Mitri, 2009). These fires have caused forest<br />

fragmentation <strong>and</strong> loss of associated ecosystem<br />

services. This, in turn, is affecting the livelihoods<br />

of local communities. Figure 5.5 shows the<br />

extent of reported forest fires in Lebanon; these<br />

data were consolidated by the MOE based on<br />

the records of the Internal Security Forces (ISF).<br />

Figure 5.3 Threat intensity based on nine forest species<br />

Source: Adapted from MOA/UNEP/GEF, 1996 by G. Ramadan Jaradi (unpublished)<br />

Figure 5.4 The impact of driving forces on ecosystem change in Lebanon<br />

Tree felling in Sir El Dinnieh<br />

Note: The size of the driving force is proportional to its influence. The influence of<br />

climate change on ecosystems is misevaluated due to lack of data.<br />

Source: G. Ramadan Jaradi (unpubl.)<br />

Chapter 5: <strong>Biodiversity</strong> <strong>and</strong> <strong>Forests</strong> 151

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