Abstract:Federal de Vic ßosa, Vic ßosa, Minas Gerais, Brasil Summary 1. Fragmentation of tropical forests is one of the greatest threats to global biodiversity. Understanding how biological and functional attributes of communities respond to fragmentation and, in turn, whether ecosystem functioning is impacted upon are critical steps for assessing the long-term effects and conservation values of forest fragments. Ecosystem functioning can be inferred through functional diversity metrics, including functional richness, … Show more
“…We used the metrics proposed by Villéger et al [27], because they are independent from each other (Pearson r ¼ 20.02, p ¼ 0.89), are easy to calculate [42] and are often used in the literature (e.g. [7,8,11]), which makes our results more comparable to other studies. Higher values for these metrics correspond to higher functional trait diversity.…”
Section: (E) Functional Trait Diversitymentioning
confidence: 89%
“…Current knowledge, however, does not point to a simple pattern, as some studies have found that functional diversity remained unchanged or was even positively affected (e.g. [5,[8][9][10][11]). Existing evidence thus suggests that the consequences of environmental changes for ecological functions are complex and far from being well understood.…”
Habitat loss often reduces the number of species as well as functional diversity. Dramatic effects to species composition have also been shown, but changes to functional composition have so far been poorly documented, partly owing to a lack of appropriate indices. We here develop three new community indices (i.e. functional integrity, community integrity of ecological groups and community specialization) to investigate how habitat loss affects the diversity and composition of functional traits and species. We used data from more than 5000 individuals of 137 bird species captured in 57 sites in the Brazilian Atlantic Forest, a highly endangered biodiversity hotspot. Results indicate that habitat loss leads to a decrease in functional integrity while measures of functional diversity remain unchanged or are even positively affected. Changes to functional integrity were caused by (i) a decrease in the provisioning of some functions, and an increase in others; (ii) strong within-guild species turnover; and (iii) a replacement of specialists by generalists. Hence, communities from more deforested sites seem to provide different but not fewer functions. We show the importance of investigating changes to both diversity and composition of functional traits and species, as the effects of habitat loss on ecosystem functioning may be more complex than previously thought. Crucially, when only functional diversity is assessed, important changes to ecological functions may remain undetected and negative effects of habitat loss underestimated, thereby imperiling the application of effective conservation actions.
“…We used the metrics proposed by Villéger et al [27], because they are independent from each other (Pearson r ¼ 20.02, p ¼ 0.89), are easy to calculate [42] and are often used in the literature (e.g. [7,8,11]), which makes our results more comparable to other studies. Higher values for these metrics correspond to higher functional trait diversity.…”
Section: (E) Functional Trait Diversitymentioning
confidence: 89%
“…Current knowledge, however, does not point to a simple pattern, as some studies have found that functional diversity remained unchanged or was even positively affected (e.g. [5,[8][9][10][11]). Existing evidence thus suggests that the consequences of environmental changes for ecological functions are complex and far from being well understood.…”
Habitat loss often reduces the number of species as well as functional diversity. Dramatic effects to species composition have also been shown, but changes to functional composition have so far been poorly documented, partly owing to a lack of appropriate indices. We here develop three new community indices (i.e. functional integrity, community integrity of ecological groups and community specialization) to investigate how habitat loss affects the diversity and composition of functional traits and species. We used data from more than 5000 individuals of 137 bird species captured in 57 sites in the Brazilian Atlantic Forest, a highly endangered biodiversity hotspot. Results indicate that habitat loss leads to a decrease in functional integrity while measures of functional diversity remain unchanged or are even positively affected. Changes to functional integrity were caused by (i) a decrease in the provisioning of some functions, and an increase in others; (ii) strong within-guild species turnover; and (iii) a replacement of specialists by generalists. Hence, communities from more deforested sites seem to provide different but not fewer functions. We show the importance of investigating changes to both diversity and composition of functional traits and species, as the effects of habitat loss on ecosystem functioning may be more complex than previously thought. Crucially, when only functional diversity is assessed, important changes to ecological functions may remain undetected and negative effects of habitat loss underestimated, thereby imperiling the application of effective conservation actions.
“…Inhibited regeneration may have consequences for the future of altered riparian zones, but it remains to be seen if reductions in seedling and sapling abundance will propagate to larger size classes of trees. Because tree longevity in tropical forests is high, reduced seedling and sapling abundance suggests the possibility of an extinction debt, or inevitable future extinctions caused by past events (Magnago et al 2013).…”
Abstract. Deforestation and fragmentation influence the microclimate, vegetation structure, and composition of remaining patches of tropical forest. In the southern Amazon, at the frontier of cropland expansion, forests are converted and fragmented in a pattern that leaves standing riparian forests whose dimensions are mandated by the Brazilian National Forest Code. These altered riparian forests share many characteristics of well-studied upland forest fragments, but differ because they remain connected to larger areas of forest downstream, and because they may experience wetter soil conditions because reduction of forest cover in the surrounding watershed raises groundwater levels and increases stream runoff. We compared forest regeneration, structure, composition, and diversity in four areas of intact riparian forest and four areas each of narrow, medium, and wide altered riparian forests that have been surrounded by agriculture since the early 1980s. We found that seedling abundance was reduced by as much as 64% and sapling abundance was reduced by as much as 67% in altered compared to intact riparian forests. The most pronounced differences between altered and intact forest occurred near forest edges and within the narrowest sections of altered riparian forests. Woody plant species composition differed and diversity was reduced in altered forests compared to intact riparian forests. However, despite being fragmented for several decades, large woody plant biomass and carbon storage, the number of live or dead large woody plants, mortality rates, and the size distribution of woody plants did not differ significantly between altered and intact riparian forests. Thus, even in these relatively narrow forests with high edge : area ratios, we saw no evidence of the increases in mortality and declines in biomass that have been found in other tropical forest fragment studies. However, because of the changes in both species community and reduced regeneration, it is unclear how long this relative lack of change will be sustained. Additionally, Brazil recently passed a law in their National Forest Code allowing narrower riparian buffers than those studied here in restored areas, which could affect their long-term sustainability.
“…Devido à influência desses mapas sobre a organização de iniciativas oficiais de conservação e pesquisa da biodiversidade, desde então muitos estudos ecológicos têm optado por retratar a Floresta de Linhares como uma "floresta ombrófila densa" ou dense rain forest (por exemplo, Oliveira- Magnago et al 2014). Todavia, na contramão dessa tendência, alguns estudos têm considerado observações de campo ou análises do clima local para adotar o termo "floresta estacional semidecidual" (por exemplo, Rolim & Nascimento 1997;Rolim et al 1999;Kindel & Garay 2002;Saiter et al 2015), uma denominação disponível no sistema de Veloso et al (1991).…”
Section: A Semideciduidade Ou a Perenidade Da Floresta De Linharesunclassified
ResumoApresentamos uma revisão das visões controversas acerca da classificação fisionômica da Floresta de Linhares, aqui definida como a floresta sobre tabuleiros costeiros que ocorre entre os rios Doce e Barra Seca, no norte do Espírito Santo. Compilamos informações sobre o clima estacional dessa região e analisamos a inter-relação das variações interanuais e da dinâmica sazonal da precipitação com atributos ecológicos da floresta. Nossas interpretações revelaram que dados mensais médios de precipitação não exprimem a realidade dos períodos biologicamente secos ano a ano e suas consequências sobre a fisionomia da vegetação. Percebemos que a Floresta de Linhares pode se manifestar como semidecídua ou perenifólia, a depender da severidade da seca em um dado período. Então, propomos que a flexibilidade do regime de renovação foliar da Floresta de Linhares deve ser considerada em sua classificação. Sugerimos classificar a floresta duplamente como estacional semidecidual nos períodos anuais ou supra-anuais caracterizados por deficit hídrico pronunciado, e como floresta estacional perenifólia nos períodos anuais ou supra-anuais sem deficit hídrico significativo. Palavras-chave: deficit hídrico, floresta de tabuleiro, floresta estacional semidecidual, floresta estacional perenifólia, sazonalidade de precipitação.
AbstractWe present a review of the controversial points of view concerning the physiognomic classification of Linhares Forest, which is defined here as the forest over coastal tablelands that is found between the Rio Doce and the Rio Barra Seca, in the north of Espírito Santo. We compiled information about the seasonal climate of such region and analyzed the relationship of both the interannual variation and the seasonality of the rainfall with the ecological attributes of the forest. Our interpretations unveiled that the average monthly rainfall does not express the reality of the biologically dry periods year after year nor does it express the consequences on the vegetation physiognomy. We perceived that Linhares Forest may manifest itself as semideciduous or evergreen, depending on the drought severity within a given period. Thus, we propose that the flexibility of Linhares Forest leaf flush regime must be considered in its classification. We suggest a double classification for the forest: one as a seasonal semideciduous forest during annual or supra-annual periods that are characterized by pronounced water deficit and the other as a seasonal evergreen forest during annual or supra-annual periods with no significant water deficit.
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