Resumo A Serra Negra, no município de Rio Preto (MG), estende-se por uma região com fisionomias florestais serranas da Mantiqueira e campos altimontanos, entre as elevações do maciço do Itatiaia (RJ, SP e MG) e da Serra do Ibitipoca (MG). Com o objetivo de investigar o comportamento das variáveis comunitárias da flora arbórea em condições diferentes de altitude e alagamento, determinou-se a composição florística, estrutura e similaridade entre três fragmentos de floresta (aluvial, montana e nebular) e a suas relações florísticas com estudos da região. Foram amostrados 2.572 indivíduos, identificados em 194 espécies, distribuídas em 59 famílias e 118 gêneros. As famílias com maior riqueza foram Myrtaceae (30 espécies), Lauraceae (20), Melastomataceae (17) e Fabaceae (13). Os três tipos de vegetação estudados, associados a diferentes condições ambientais, diferem entre si em sua composição e estrutura. A floresta aluvial revelou-se com reduzida diversidade, baixa estatura e alta dominância ecológica. A floresta nebular destacou-se por apresentar elementos típicos de altitude em detrimento de espécies freqüentes na região abaixo da escarpa da serra, onde a diversidade foi maior. A flora arbórea da Serra Negra, formada pelo conjunto das áreas estudadas, apresenta um conjunto considerável de elementos com distribuição característica de ambientes montanhosos do Sudeste do Brasil.

We analyzed the community structure of an upper montane cloud forest (elevation, 1900 m) in the Serra da Mantiqueira Mountain Range, in the state of Minas Gerais, Brazil. Our objective was to determine the comparative tree species richness and floristic diversity within this forest, which is at one of the higher elevations in the range, in relation to surrounding forests that are at lower elevations, adjusting for elevational gradients. Within 15 permanent plots (40 × 10 m each), we tagged all tree individuals with a diameter at breast height ≥ 5 cm, registering their height and diameter. To compare the study area with neighboring cloud forests, we used the Sørensen similarity coefficient and phytosociological parameters. We sampled 1250 individuals distributed among 89 species, 55 genera, and 34 families. Canonical correspondence analysis revealed no gradients related to the vegetation or soil. We found that tree species richness and diversity were high in the study area. There was structural and floristic heterogeneity among the communities evaluated, underscoring the importance of conservation of these high-elevation ecosystems, which are so unique and irreplaceable.

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1. Large-scale data compilation is increasing steadily in tropical forest research, but the lack of standardized methods for data collection limits drawing inference from large datasets and cross-biome analyses. Different inclusion methods and minimum tree diameter threshold are among these varying factors. To tackle this issue, we evaluated how different approaches for tree sampling affects our understanding of diversity and functioning in different tropical vegetation types.2. We used a unique dataset of 44 inventory plots (43.54 ha) encompassing an aridity gradient: evergreen moist forests, semideciduous and deciduous tropical forests.Data were collected using the by-tree inclusion method, in which, all stems are measured if the equivalent diameter of the tree reaches the minimum threshold.We simulated the impact of adopting different inclusion methods (by-stem and by-tree) and different minimum diameter thresholds on the estimation of number of trees and stems, biomass and species richness. We used linear and nonlinear mixed models to investigate the effect of minimum diameter threshold and inclusion method on our different response variables. We also evaluated species chance to be sampled under different minimum inclusion criteria.3. Inclusion method and minimum diameter threshold mainly affect the estimation of number of trees and stems and species richness, especially in deciduous and semideciduous forests, where resprouting is a prevalent strategy. In these forests, many trees that have several stems do not reach the minimum size individually when adopting the by-stem method, yet they do reach the minimum size threshold when all stems are considered together. For these environments under water stress, our analysis showed that using large minimum sizes, such as the 10 cm typically used in rainforests, implies large sampling losses, especially when used jointly with the by-stem inclusion method.4. The by-tree inclusion method represents an alternative approach that offers a more reliable sampling in different vegetation types, particularly in those habitats where resprouting is a widely encountered strategy along all age classes. 2018 | Methods in Ecology and Evoluঞon de SOUZA et Al.