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Oliveira-Neto NE, Nascimento DR, Carvalho FA (2017). Biodiversity

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Oliveira-Neto NE, Nascimento DR, Carvalho FA (2017). Biodiversity Short Communication ii FF o o r r e e s s t t doi: 10.3832/ifor1901-009 Biogeosciences and Forestry vol. 10, pp. 303-308 Biodiversity inventory of trees in a neotropical secondary forest after abandonment of shaded coffee plantation Norberto Emídio Oliveira-Neto (1), Tree structure and diversity of a secondary Atlantic Forest resulting from the Diego Raymundo Nascimento (1), abandonment (ca. 70 years) of a shaded coffee (Coffea arabica) plantation Fabrício Alvim Carvalho (2) was studied in southeastern Brazil. All trees with DBH ≥ 5 cm (alive and dead) were measured in 25 plots of 20 × 20 m. Out of the 1926 sampled trees, 1837 were living trees belonging to 116 species. The most important species (impor- tance value – IV) in the community were Euterpe edulis (22.9% - present in all plots) and Piptadenia gonoacantha (16.5%). Euterpe edulis is a typical palm tree of high importance value in mature forests, comprising 41.2% of individu- als. The results show a more mature tree community in relation to other sec- ondary forests with the same abandonment period in the region, with high richness and diversity of species, high basal area, and low dead tree density. In addition, several endangered species were recorded with high conservation value for the regional flora. The results also showed many typical characteris- tics of “novel ecosystems” discussed here in order to value these environ- ments, still neglected due to strong environmental human alterations. Keywords: Brazilian Atlantic Forest, Forest Succession, Novel Ecosystem, Agro- forestry Introduction tential to remain ecologically untapped study area. Chazdon et al. (2009) claim that The development of agriculture in Brazil due to their rapid growth characteristics the management of secondary formations has led to a high degree of fragmentation (Guariguata & Ostertag 2001). Its vast ex- is one of the greatest potential solutions to of the Atlantic Forest, with the formation tension in humid tropics and its predomi- increasing biodiversity conservation of tro- of landscape mosaics between secondary nance in biomes such as the Brazilian At- pical forests, including Brazilian forests. and mature forests, and the subsequent lantic Forest, calls for an increased under- This study focused on a secondary At- extinction of several species belonging to standing and appreciation of the environ- lantic Forest formerly used as a shaded cof- the native flora (Fonseca 1985). The areas mental services provided by these forests fee plantation (Coffea arabica), that has with the highest levels of degradation coin- by addressing the existing research gaps been naturally regenerating in the last 70 cide with the main areas of economic and providing the scientific basis of refor- years after abandonment. The main goal development in the country (Ayres et al. estation and restoration methods (Chaz- was to evaluate the structure and species 2005). Based on current cover rates of the don et al. 2009). diversity of its tree regenerating commu- tropical forest vegetation, it is clear that Phytosociological studies conducted in nity. We tested the hypothesis that the for- the few existing mature forests will even- forest fragments in southeastern Brazil est would present distinct successional tually disappear. These ecosystems are provided important advances to the knowl- tree community indicators (structural and being more and more replaced by a com- edge of forest succession under anthropo- diversity parameters) in comparison with plex mosaic of small forest fragments at genic influence (Valente et al. 2011, Fonseca secondary forests studied to date, with the different successional stages, in most cases & Carvalho 2012, Moreira & Carvalho 2013, same abandonment time in the region, due separating agricultural crops from urban Brito & Carvalho 2014, Carvalho et al. 2014, to its history of regeneration from shaded areas (Ribeiro et al. 2009). Moreira 2014). Such information may help plantations. Mature forests of neotropical regions are planning of appropriate management prac- currently subject to a great human pres- tices, particularly where species with viable Materials and methods sure, while secondary forests have the po- economic production are present in the The study area was located in an Atlantic Forest fragment that belongs to the Fed- (1) Programa de Pós-graduação em Ecologia, Instituto de Ciências Biológicas, Universidade eral University of Juiz de Fora Botanical Federal de Juiz de Fora, Campus Universitário, no number, São Pedro, 36036-900, Juiz de Garden (JB-UFJF) in the city of Juiz de Fora, Fora-MG (Brazil); (2) Departamento de Bot’nica, Universidade Federal de Juiz de Fora, Cam- Minas Gerais, southeastern Brazil (Fig. 1). pus Universitário, no number, São Pedro. 36036-900, Juiz de Fora-MG (Brazil) The JB-UFJF covers about 80 ha and is con- tiguous to the Environmental Protection @ Norberto Emídio Oliveira-Neto ([email protected]) Area of “Mata do Krambeck” forest, form- ing an extensive urban forest remnant with Received: Oct 20, 2015 - Accepted: Sep 14, 2016 a total area of approx. 370 ha. According to Köppen, the climate is humid subtropical Citation: Oliveira-Neto NE, Nascimento DR, Carvalho FA (2017). Biodiversity inventory of (Cwa) with two distinct seasons: summer- trees in a neotropical secondary forest after abandonment of shaded coffee plantation. spring, with higher temperatures and rain- iForest 10: 303-308. – doi: 10.3832/ifor1901-009 [online 2017-02-23] fall (October to April); and autumn-winter, which is colder and drier (May to Septem- Communicated by: Raffaele Lafortezza ber – Fonseca & Carvalho 2012). The annual rainfall average is close to 1500 mm, with © SISEF http://www.sisef.it/iforest/ 303 iForest 10: 303-308 Oliveira-Neto NE et al. - iForest 10: 303-308 y r Results t s We sampled a total of 1927 individual e r trees, of which 1837 were living trees. We o found 117 species belonging to 84 genera F and 33 families (Tab. 1). The five families d n with the highest species richness were a Fabaceae (17 species; 14.6% of the total), s e Myrtaceae (10; 11.6%), Moraceae (9; 7.8%), c n Lauraceae (8; 6.9%), and Annonaceae (7; e i 6.0%), which together accounted for 46.2% c s of the total number of sampled species. o Among the most abundant families in the e g area, five had the highest density of indi- o i viduals: Arecaceae (824 individuals; 44.9% B of the total), Fabaceae (234; 12.7%), Anno- – naceae (186; 10.1%), Rubiaceae (66; 3.6%), t s and Sapindaceae (65; 3.5%), which together e r accounted for 74.8% of the total number of o F sampled individuals. i We also sampled 89 standing dead trees, representing 4.6% of all sampled trees. The community had a total basal area of 43.61 m2 ha-1, and a strong dominance of few species. The five species with the highest importance value (IV) in the community Fig. 1 - Geographical location of the study area, a secondary forest regenerating after were Euterpe edulis (22.9%), Piptadenia the abandonment of a shaded coffee plantation (Coffea arabica) in the Botanical Gar- gonoacantha (16.5%), Xylopia sericea (5.7%), den of the Federal University of Juiz de Fora, Juiz de Fora, Minas Gerais, Southeastern Annona cacans (3.5%), and Syagrus roman- Brazil. zoffiana (3.3%), which together amounted to 51.9% of the total IV. Euterpe edulis had the highest rates in January (ca. 300 mm), Twenty-five permanent plots of 20×20 m the highest abundance (759 ind ha-1), repre- while the annual temperature average is (400 m2) were established in the surveyed sented 41.2% of the total, and was present around 18.9 °C (Fonseca & Carvalho 2012). area, with a total sampled area of 1 ha in all plots. Not surprisingly, the species The relief is formed by very old rocks, basi- (Felfili et al. 2005). We measured the diam- with the highest basal area was P. gonoa- cally gneiss and granite, with predominant eter of all living and standing dead individ- cantha (16.60 m² ha-1), representing 38.2% soils classified as Dystrophic Yellow Oxi- ual trees with a DBH ≥ 5 cm (diameter at of the total. soils (Oliveira-Neto 2014). The forest vege- breast height at 1.3 m from the soil). The The value of Shannon’s diversity species tation is classified as mountainous semi- botanical material collected was identified index for the whole community was H' = deciduous (seasonally) forest according to using the CESJ herbarium collection from 2.92, while that of the Pielou evenness the Brazilian Vegetation System (IBGE UFJF and the collection of Plant Ecology index was J = 0.61. Excluding the high-den- 2012). Laboratory (UFJF). The specific nomencla- sity species E. edulis from the analyses, the The entire area corresponding to the JB- ture and the abbreviations of the names of highest values were H' = 3.83 and J = 0.80. UFJF was formerly a coffee crop plantation authorities follow the Species List of Brazil- With 117 species in a standard 1-ha sam- (Coffea arabica L.) cultivated both in full ian Flora (http://floradobrasil.jbrj.gov.br/). pled area, we found the highest species sun and under the canopy of native forest The classification of botanical families fol- richness compared to secondary patches species, especially Pau-jacaré (Piptadenia lowed the APG III system (APG 2009). with the same vegetation type in the gonoacantha [Mart.] J.F.Macbr.), a large The characterization of the tree commu- region, which registered 105 (Brito & Car- size, long-lived pioneer tree species native nity was carried out by calculating follow- valho 2014), 78 (Fonseca & Carvalho 2012) to Brazilian seasonal forests and exploited ing phytosociological parameters for each and 48 species (Moreira 2014), respec- for tannins (Carvalho 2003). The current species: species richness (S), absolute den- tively.
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