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dc.creatorSouza, Cléber R.-
dc.creatorMaia, Vinicius A.-
dc.creatorAguiar-Campos, Natália de-
dc.creatorSantos, Alisson B. M.-
dc.creatorRodrigues, André Ferreira-
dc.creatorFarrapo, Camila L.-
dc.creatorGianasi, Fernanda M.-
dc.creatorPaula, Gabriela G. P. de-
dc.creatorFagundes, Nathalle C. A.-
dc.creatorSilva, Wilder B.-
dc.creatorSantos, Rubens M.-
dc.date.accessioned2022-01-27T18:53:28Z-
dc.date.available2022-01-27T18:53:28Z-
dc.date.issued2021-06-01-
dc.identifier.citationSOUZA, C. R. et al. Long-term ecological trends of small secondary forests of the atlantic forest hotspot: A 30-year study case. Forest Ecology and Management, Amsterdam, v. 489, 119043, 1 June 2021. DOI: 10.1016/j.foreco.2021.119043.pt_BR
dc.identifier.urihttps://doi.org/10.1016/j.foreco.2021.119043pt_BR
dc.identifier.urihttp://repositorio.ufla.br/jspui/handle/1/49050-
dc.description.abstractForest dynamics are driven by a myriad of factors and link directly to ecosystem services. The dynamics of the highly degraded Brazilian Atlantic Forest (AF) hotspot is mostly driven by its anthropogenic context. Currently, most of the AF region is composed of small disturbed secondary forest fragments that have received partial or full environmental protection with recent environmental norms. Such protection prevents further disturbances and consequently shifts the course of forest dynamics and ecosystem services in AF. Here, we assess long-term forest dynamics trends of a small secondary AF fragment to test the hypothesis that disturbed AF fragments are reaching advanced successional stages. We used a unique dataset of 126 permanent subplots (totaling 5.04 ha) monitored for 30 years (8 inventories between 1987 and 2017) of a disturbed secondary AF fragment (6.35 ha) that has been fully protected since 1986. In each inventory, we measured all living trees with a diameter at breast height (DBH) ≥ 5 cm and counted survivors, recruits and dead individuals between intervals. We monitored the temporal trends of (i) structural variables (biomass, tree density and species richness), (ii) functional composition (wood density and maximum potential size), (iii) and species dominance. Our results indicate that, now under full protection, the fragment is shifting towards a late successional stage: we observed increasing biomass, decreasing tree density (self-thinning) and increasing abundance of late-successional species with conservative strategies. Species richness and dominant species composition were stable throughout the monitoring period, suggesting an absence of substantial changes in community assembly. These results underscore the role played by small secondary AF fragments in ecosystem service provision (e.g., carbon uptake and shelter for biodiversity) and point to their forest dynamics trends.pt_BR
dc.languageen_USpt_BR
dc.publisherElsevierpt_BR
dc.rightsrestrictAccesspt_BR
dc.sourceForest Ecology and Managementpt_BR
dc.subjectSemideciduous forestspt_BR
dc.subjectFunctional compositionpt_BR
dc.subjectFragmentationpt_BR
dc.subjectForest dynamicspt_BR
dc.subjectFlorestas semidecíduaspt_BR
dc.subjectComposição funcionalpt_BR
dc.subjectFragmentaçãopt_BR
dc.subjectDinâmica florestalpt_BR
dc.titleLong-term ecological trends of small secondary forests of the atlantic forest hotspot: A 30-year study casept_BR
dc.typeArtigopt_BR
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