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Establecimiento de cuatro especies de Quercus en el sur de la ...

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Spatial and temporal heterog<strong>en</strong>eity effects on seedling growth and establishm<strong>en</strong>t in four <strong>Quercus</strong> species<br />

INTRODUCTION<br />

Natural reg<strong>en</strong>eration in Mediterranean vegetation is strongly limited at all stages<br />

(Jordano et al., 2008), but particu<strong>la</strong>rly in seedlings, which are highly s<strong>en</strong>sitive to their<br />

micro<strong>en</strong>vironm<strong>en</strong>tal conditions (Grubb, 1977; González‐Rodríguez et al., 2008a;<br />

Urbieta et al., 2008a). The avai<strong>la</strong>bility of major resources including light, water and<br />

nutri<strong>en</strong>ts for p<strong>la</strong>nts can change within a few metres (Gal<strong>la</strong>rdo, 2003; Gómez et al.,<br />

2004; Quero, 2006). Also, these <strong>en</strong>vironm<strong>en</strong>tal factors exhibit complex mutual<br />

r<strong>el</strong>ationships (Sack and Grubb, 2001; Gal<strong>la</strong>rdo, 2003; Marañón et al., 2004) and can<br />

vary wi<strong>de</strong>ly in space and time, affecting ecosystem structure and composition<br />

(Terradas, 2001; Maestre, 2006). Thus, op<strong>en</strong> forest areas possess a light avai<strong>la</strong>bility<br />

that influ<strong>en</strong>ces not only abiotic resources such as nutri<strong>en</strong>ts or soil moisture (D<strong>en</strong>slow<br />

et al., 1998), but also the structure and composition of the herbaceous <strong>la</strong>yer (Milton,<br />

1995). Herb abundance can either diminish seedling <strong>sur</strong>vival through competition for<br />

water (Rey B<strong>en</strong>ayas et al., 2005) or increase it by reducing evaporation and alleviating<br />

the effects of high temperatures (Thomas and Davis, 1989; Gómez‐Aparicio et al.,<br />

2005). In addition, the spatial structure of seedling recruitm<strong>en</strong>t may be governed not<br />

only by resources avai<strong>la</strong>bility, but also by factors involved in the earliest reg<strong>en</strong>eration<br />

stages such as seed rain and dispersal (Gómez et al., 2004; García and Houle, 2005).<br />

Therefore, the distribution of <strong>en</strong>vironm<strong>en</strong>tal variables, which usually take the<br />

form of gradi<strong>en</strong>ts or patches, are usually of a non‐random nature and promote the<br />

formation of heterog<strong>en</strong>eous microsites to which p<strong>la</strong>nts respond differ<strong>en</strong>tly (Jur<strong>en</strong>a and<br />

Archer, 2003), thereby facilitating coexist<strong>en</strong>ce betwe<strong>en</strong> species (Beckage and C<strong>la</strong>rk,<br />

2003).<br />

The spatial structure of <strong>en</strong>vironm<strong>en</strong>tal variables is also time‐<strong>de</strong>p<strong>en</strong><strong>de</strong>nt. The<br />

significance of temporal variability in the resources for establishm<strong>en</strong>t success has be<strong>en</strong><br />

the subject of many studies (Paynter et al., 1998; Castro et al., 2004; Gómez‐Aparicio<br />

et al., 2005), especially un<strong>de</strong>r Mediterranean and semi‐arid climates, where water is a<br />

highly restrictive resource (Milton, 1995; Ve<strong>en</strong><strong>en</strong>daal et al., 1996). Thus, Herrero et al.<br />

(2008) found the spatial structure of p<strong>la</strong>nt <strong>sur</strong>vival to vary betwe<strong>en</strong> years with<br />

differ<strong>en</strong>t precipitation. In very wet years, <strong>sur</strong>vival can be high <strong>en</strong>ough to prev<strong>en</strong>t<br />

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