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A checklist of pioneer plant regeneration on natural and ...

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Ecuador is a Megadiverse country with 17058 <str<strong>on</strong>g>plant</str<strong>on</strong>g> species Ulloa Ulloa & Neill (1999 -2004). About 4011<br />

<str<strong>on</strong>g>plant</str<strong>on</strong>g> species (26 % <str<strong>on</strong>g>of</str<strong>on</strong>g> the native flora) are regarded as endemic (Valencia et al. 2000). Podocarpus Nati<strong>on</strong>al<br />

Park (PNP) is located in the southwestern part <str<strong>on</strong>g>of</str<strong>on</strong>g> Ecuador between Loja <strong>and</strong> Zamora provinces. Madsen &<br />

øllgard (1994) estimated an number <str<strong>on</strong>g>of</str<strong>on</strong>g> 4000 <str<strong>on</strong>g>plant</str<strong>on</strong>g> species for Podocarpus park, <str<strong>on</strong>g>of</str<strong>on</strong>g> which at least 99 species<br />

are endemic (Lozano et al. 2003). This is the highest degree <str<strong>on</strong>g>of</str<strong>on</strong>g> endemism in any protected area <str<strong>on</strong>g>of</str<strong>on</strong>g> Ecuador.<br />

On the other h<strong>and</strong> this area has a high record <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>natural</strong> as well as anthropogenic l<strong>and</strong>slides (Ohl & Bussmann,<br />

2004). The locati<strong>on</strong> al<strong>on</strong>g the cordillera oriental, with steep slopes, little organic matter in the soil, high<br />

rainfall from 4000 to 6000 mm, <strong>and</strong> human activities like grazing, logging <strong>and</strong> road c<strong>on</strong>structi<strong>on</strong> lead to a<br />

high number <str<strong>on</strong>g>of</str<strong>on</strong>g> both <strong>natural</strong> <strong>and</strong> anthropogenic l<strong>and</strong>slides. The present overview provides a first <str<strong>on</strong>g>checklist</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>pi<strong>on</strong>eer</str<strong>on</strong>g> <str<strong>on</strong>g>plant</str<strong>on</strong>g>s collected as part <str<strong>on</strong>g>of</str<strong>on</strong>g> ecological studies al<strong>on</strong>g altitudinal gradients in both type <str<strong>on</strong>g>of</str<strong>on</strong>g> “gaps” in this<br />

ecosystem.<br />

<br />

Figure 1: A. Road Loja to Zamora, northern part <str<strong>on</strong>g>of</str<strong>on</strong>g> the buffer z<strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> Podocarpus Park; B. A <strong>natural</strong> l<strong>and</strong>slide<br />

170 vegetati<strong>on</strong> plots distributed al<strong>on</strong>g the altitudinal gradient (2100-3000 m.a.s.l.) were established to identify<br />

vegetati<strong>on</strong> changes <strong>on</strong> <strong>natural</strong> l<strong>and</strong>slides. To investigate <str<strong>on</strong>g>pi<strong>on</strong>eer</str<strong>on</strong>g> species <strong>and</strong> floristic changes caused by<br />

human impact due to road-c<strong>on</strong>structi<strong>on</strong> al<strong>on</strong>g the buffer z<strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> PNP 104 vegetati<strong>on</strong> plots al<strong>on</strong>g the<br />

altitudinal gradient (1900–2800 m.a.s.l.) were sampled in additi<strong>on</strong>. The relevés were sampled following the<br />

Braun-Blanquet method (1964). The plot surface was 1x5 m, the floristic inventory <str<strong>on</strong>g>of</str<strong>on</strong>g> each plot was based <strong>on</strong><br />

species presence/absence <strong>and</strong> percentage <str<strong>on</strong>g>of</str<strong>on</strong>g> herbs. Vouchers <str<strong>on</strong>g>of</str<strong>on</strong>g> all species were collected in each plot (series<br />

Lozano & Bussmann). The <str<strong>on</strong>g>plant</str<strong>on</strong>g> material was pressed, dried <strong>and</strong> identified at LOJA herbarium (Universidad<br />

Naci<strong>on</strong>al de Loja).<br />

<br />

Natural l<strong>and</strong>slides c<strong>on</strong>tained 218 <str<strong>on</strong>g>plant</str<strong>on</strong>g> species in 180 genera <strong>and</strong> 51 families, while antropogenic l<strong>and</strong>slides<br />

(al<strong>on</strong>g roads) harbored 312 species in 152 genera <strong>and</strong> 69 families. The presented <str<strong>on</strong>g>checklist</str<strong>on</strong>g> includes four<br />

hundred <str<strong>on</strong>g>plant</str<strong>on</strong>g> species in 186 genera <strong>and</strong> 73 families (Appendix 1). Pteridophytes (14 families, 30 genera <strong>and</strong><br />

69 species) Angiosperms (59 families, 156 genera <strong>and</strong> 331 species). The main p lant families dominating<br />

<strong>natural</strong> l<strong>and</strong>slides included Asteraceae with 52 species; Poacaeae with 32 species; Orchidaceae with 31<br />

species; Ericaceae with 26 species; <strong>and</strong> Melastomataceae with 23 species; other families as Bromeliaceae,<br />

Cunn<strong>on</strong>iaceae, Lycopodiaceae, Rubiaceae <strong>and</strong> Pteridaceae had 10 to 12 species, with the remaining 61<br />

families, having less than 10 species each.

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