Please use this identifier to cite or link to this item: https://hdl.handle.net/11000/39057
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dc.contributor.authorBarbosa, Jomar M.-
dc.contributor.authorSebastián González, Esther-
dc.contributor.authorAsner, Gregory P.-
dc.contributor.authorKnapp, David E.-
dc.contributor.authorAnderson, Christopher-
dc.contributor.authorMartín, Roberta E.-
dc.contributor.authorDirzo, Rodolfo-
dc.contributor.otherDepartamentos de la UMH::Biología Aplicadaes_ES
dc.date.accessioned2026-02-02T07:43:36Z-
dc.date.available2026-02-02T07:43:36Z-
dc.date.created2016-
dc.identifier.citationEcological Applications, 26(1), 2016, pp. 55–66es_ES
dc.identifier.issn1939-5582-
dc.identifier.issn1051-0761-
dc.identifier.urihttps://hdl.handle.net/11000/39057-
dc.description.abstractSpecies interactions are susceptible to anthropogenic changes in ecosystems, but this has been poorly investigated in a spatially explicit manner in the case of plant parasitism, such as the omnipresent hemiparasitic mistletoe–host plant interactions. Analyzing such interactions at a large spatial scale may advance our understanding of parasitism patterns over complex landscapes. Combining high- resolution airborne imaging spectroscopy and Li DAR , we studied hemiparasite incidence within and among tree host stands to examine the prevalence and spatial distribution of hemiparasite load in ecosystems. Specifi - cally, we aimed to assess: (1) detection accuracy of mistletoes on their oak hosts; (2) hemiparasitism prevalence within host tree canopies depending on tree height, and (3) spatial variation in hemiparasitism across fragmented woodlands, in a low- diversity mediterranean oak woodland in California, USA . We identifi ed mistletoe infestations with 55–96% accuracy, and detected signifi cant differences in remote- sensed spectra between oak trees with and without mistletoe infestation. We also found that host canopy height had little infl uence on infestation degree, whereas landscape- level variation showed consistent, nonrandom patterns: isolated host trees had twice the infestation load than did trees located at the core of forest fragments. Overall, we found that canopy exposure (i.e., lower canopy density or proximity to forest edge) is more important than canopy height for mistletoe infestation, and that by changing landscape structure, parasitic prevalence increased with woodland fragmentation. We conclude that reducing fragmentation in oak woodlands will minimize anthropogenic impact on mistletoe infestation at the landscape level. We argue that advanced remote sensing technology can provide baselines to quantitatively analyze and monitor parasite–host trajectories in light of global environmental change, and that this is a promising approach to be further tested in other temperate and tropical forests.es_ES
dc.formatapplication/pdfes_ES
dc.format.extent12es_ES
dc.language.isoenges_ES
dc.publisherEcological Society of Americaes_ES
dc.rightsinfo:eu-repo/semantics/closedAccesses_ES
dc.rightsAttribution-NonCommercial-NoDerivatives 4.0 Internacional*
dc.rights.urihttp://creativecommons.org/licenses/by-nc-nd/4.0/*
dc.subjectdetection of host–parasite interactionses_ES
dc.subjectforest fragmentationes_ES
dc.subjectJasper Ridge Biological Preservees_ES
dc.subjectmistletoeses_ES
dc.subjectoak forestes_ES
dc.subjectCarnegie Airborne Observatoryes_ES
dc.titleHemiparasite–host plant interactions in a fragmented landscapeassessed via imaging spectroscopy and Li DARes_ES
dc.typeinfo:eu-repo/semantics/articlees_ES
dc.relation.publisherversionhttps://doi.org/10.1890/14-2429es_ES
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