Biodiversity and Forests
Biodiversity and Forests
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