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dc.contributor.authorSosa, Beatriz
dc.contributor.authorRomero-Pacheco, David 
dc.contributor.authorFernández, Gabriela
dc.contributor.authorAchkar, Marcel
dc.date.accessioned2025-01-27T11:02:17Z
dc.date.available2025-01-27T11:02:17Z
dc.date.issued2018-01
dc.identifier.citationSosa B, Romero D, Fernández G, Achkar M (2018) Spatial analysis to identify invasion colonization strategies and management priorities in riparian ecosystems, Forest Ecology and Management, Volume 411, 2018, Pages 195-202.es_ES
dc.identifier.urihttps://hdl.handle.net/10630/37061
dc.description.abstractExotic species have different strategies to invade a new area. Invasive species limited by establishment have a wide dispersion range and high seedling mortality rate. Riparian forests are harsh environments for the establishment of plants. In this sense, we tested the hypothesis that the invasive process of G. triacanthos is limited by establishment in a riparian forest of the Uruguay River and that it begins in the fluvial bank at the transition zone between forest and grassland and moves towards the shore border. We expected that: (1) the distribution pattern of adults of G. triacanthos would be decoupled from the distribution pattern of seedlings and saplings (prereproductive stages); (2) the population would have a cluster distribution pattern related to the occurrence of punctual events that favoured the development to adult stages; and (3) the abundance of seedlings, saplings and adults would be higher in the transition zone (between forest and grassland) than in the shore border of the fluvial bank. The spatial pattern of G. triacanthos along the Uruguay River was analyzed using spatial point pattern analysis: autocorrelation indexes, hot spots and wavelet analysis. The effect of the fluvial bank position on the abundance of G. triacanthos was evaluated using non-metric multidimensional scaling (NMDS). This methodology allowed us to detect a primary invasion area, an invasion focus and the dispersal area. This pattern corresponded to an infiltration invasion pattern limited by establishment. It did not seem to be affected by position in the fluvial bank. This information could be relevant to establish correct decision-making in the control of an invasive process and provide an applicable methodology for any other invasion process, especially in riparian ecosystems.es_ES
dc.description.sponsorshipThis study was supported by a research grant of the Comisión Sectorial de Investigación Científica (CSIC) of the Universidad de la República Uruguay. Beatriz Sosa was supported by a PhD grant of the Comisión Sectorial de Investigación Científica (CSIC) of the Universidad de la República Uruguay. and a PhD grant of Dr. David Romero was supported by the National Agency for Research and Innovation (acronym from Spanish, ANII): PD_NAC_2015_1_108393.es_ES
dc.language.isoenges_ES
dc.publisherElsevieres_ES
dc.rightsAttribution-NonCommercial-NoDerivatives 4.0 Internacional*
dc.rights.urihttp://creativecommons.org/licenses/by-nc-nd/4.0/*
dc.subjectEspecies exóticas invasorases_ES
dc.subject.otherBiological invasiones_ES
dc.subject.otherControl strategieses_ES
dc.subject.otherGleditsia triacanthoses_ES
dc.subject.otherFluvial bankes_ES
dc.subject.otherInvasive frontes_ES
dc.subject.otherSpatial analysises_ES
dc.titleSpatial analysis to identify invasion colonization strategies and management priorities in riparian ecosystemses_ES
dc.typejournal articlees_ES
dc.identifier.doidoi.org/10.1016/j.foreco.2018.01.039
dc.type.hasVersionAMes_ES
dc.departamentoBiología Animal
dc.rights.accessRightsopen accesses_ES


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