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

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Capítulo 3<br />

aggregation; on the other hand, in especially dry years <strong>sur</strong>vival is usually too low for<br />

any aggregation to be observed. Therefore, experim<strong>en</strong>tal <strong>de</strong>signs and statistical<br />

analyses should consi<strong>de</strong>r the above‐<strong>de</strong>scribed spatial and temporal heterog<strong>en</strong>eity<br />

(Leg<strong>en</strong>dre, 1993; Zas, 2006) in or<strong>de</strong>r to accurat<strong>el</strong>y assess the influ<strong>en</strong>ce of some key<br />

factors influ<strong>en</strong>cing early recruitm<strong>en</strong>t stages. Although an increasing number of<br />

spatially explicit experim<strong>en</strong>tal <strong>de</strong>signs is being used to examine aggregation patterns<br />

for recruitm<strong>en</strong>t‐r<strong>el</strong>ated variables (Maestre et al., 2003; García and Houle, 2005; Quero,<br />

2007a), few authors have applied them simultaneously to several philog<strong>en</strong>etically<br />

r<strong>el</strong>ated species.<br />

Moreover, no study appears to have so far be<strong>en</strong> conducted to establish the<br />

aggregation patterns for morphological and growth r<strong>el</strong>ated variables in seedlings (but<br />

see Laliberté et al., 2008), which might have an impact on p<strong>la</strong>nt establishm<strong>en</strong>t.<br />

Seedling growth rates are very oft<strong>en</strong> influ<strong>en</strong>ced by <strong>en</strong>vironm<strong>en</strong>tal factors (Poorter,<br />

2001; Vil<strong>la</strong>r et al., 2008); therefore, changes in such factors along spatial and temporal<br />

gradi<strong>en</strong>ts might lead to the pres<strong>en</strong>ce of areas with bigger or faster growing seedlings.<br />

In addition to <strong>en</strong>vironm<strong>en</strong>tal factors, some intrinsec traits as seed mass <strong>de</strong>termine<br />

early seedling performance (ver capítulo 5). Experim<strong>en</strong>ts that evaluate seedling growth<br />

have be<strong>en</strong> typically carried out un<strong>de</strong>r controlled conditions, and fi<strong>el</strong>d experim<strong>en</strong>ts use<br />

to limit growth mea<strong>sur</strong>es just to seedling height (Beckage and C<strong>la</strong>rck, 2003; Laliberté et<br />

al., 2008). However, it is necessary to contrast the results and conclusions of this kind<br />

of works with more complete fi<strong>el</strong>d studies (Pérez–Ramos et al., 2010) in which more<br />

morphological traits were involved.<br />

The g<strong>en</strong>us <strong>Quercus</strong> is wi<strong>de</strong>ly repres<strong>en</strong>ted in the Mediterranean basin. Evergre<strong>en</strong><br />

species are abundant in the semi‐humid Mediterranean mountains of southern Spain;<br />

by contrast, semi‐<strong>de</strong>ciduous and <strong>de</strong>ciduous species are scantier and occupy microsites<br />

with higher water avai<strong>la</strong>bility owing to their lower drought tolerance (Acheral and<br />

Rambal, 1992; Carrión et al., 2000, Urbieta et al., 2008b). Moreover, <strong>de</strong>ciduous oaks<br />

usually have higher leaf areas and growth rates than evergre<strong>en</strong>s (Ruiz Robleto and<br />

Vil<strong>la</strong>r, 2005; Quero et al., 2006).<br />

77

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