Selecting species for passive and active riparian restoration in Southern Mexico
Identifiers
Permanent link (URI): http://hdl.handle.net/10017/38510DOI: 10.1111/j.1526-100X.2012.00934.x
ISSN: 1061-2971
Date
2013Academic Departments
Universidad de Alcalá. Departamento de Ciencias de la Vida
Teaching unit
Unidad Docente Ecología
Funders
Ministerio de Ciencia e Innovación
Comunidad de Madrid
Rufford Small Grant for Nature Conservation
Bibliographic citation
Restoration Ecology, 2013, v. 21, n. 2, p. 163-165
Keywords
Indicators
Lacandonia
Natural regeneration
Rainforest
Recovery
Project
info:eu-repo/grantAgreement/The Rufford Foundation//40.11.09/UK
info:eu-repo/grantAgreement/MICINN//CGL2010-18312/ES/Restauración de la biodiversidad y los servicios ecosistémicos en sistemas agrarios. Un enfoque multi-escala
info:eu-repo/grantAgreement/CAM//S2009%2FAMB-1783/ES/Restauración y conservación de los ecosistemas madrileños: respuesta frente al cambio global/
Document type
info:eu-repo/semantics/article
Version
info:eu-repo/semantics/publishedVersion
Rights
Attribution-NonCommercial-NoDerivatives 4.0 International (CC BY-NC-ND 4.0)
© 2013 Society for Ecological Restoration
Access rights
info:eu-repo/semantics/openAccess
Abstract
In revegetation projects, distinguishing species that can be passively restored by natural regeneration from those requiring active restoration is not a trivial decision. We quantified tree species dominance (measured by an importance value index, IVIi) and used abundance&#-size correlations to select those species suitable for passive and/or active restoration of disturbed riparian vegetation in the Lacandonia region, Southern Mexico. We sampled riparian vegetation in a 50&;8201#× 10&#-m transect in each of six reference (RE) and five disturbed (DE) riparian ecosystems. Those species representing more than 50% of total IVI in each ecosystem were selected, and Spearman rank correlation between abundance and diameter classes was calculated. For eight species, it was determined that passive restoration could be sufficient for their establishment. Another eight species could be transplanted by means of active restoration. Five species regenerate well in only one ecosystem type, suggesting that both restoration strategies could be used depending on the degree of degradation. Finally, two species were determined to not be suitable for restoration in the RE (based on the above selection criteria) and were not selected during this initial stage of our restoration project. The high number of tree species found in the RE suggests that the species pool for ecological restoration is large. However, sampling in both ecosystem types helped us reduce the number of species that requires active restoration. Restoration objectives must guide the selection of which methods to implement; in different conditions, other criteria such as dispersal syndrome or social value could be considered in the species selection.
Files in this item
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| selecting_meli_RE_2013.pdf | 603.0Kb |
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| selecting_meli_RE_2013.pdf | 603.0Kb |
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