RESUMEN
Enrichment plantings into secondary forest are an important option in restoring species diversity and ecosystem services. However, little attention has been given to environmental requirements for species performance. This study evaluated the effects of lightgaps and topographic position on the growth and survival of four native tree species (Pouteria caimito, Garcinia macrophylla, Dipteryx odorata and Cynometra bauhiniaefolia) planted into a 26-year old secondary forest originating from abandoned pastures in the central Amazon Basin. Artificial lightgaps and control plots under closed canopy were uniformly distributed on plateaus and bottomlands near water bodies. Seedlings were planted randomly into the plots and monitored for 28 months. Seedling survival rate was high (93%) and did not differ among species. Overall, lightgaps produced a 38% increase in seedling height relative to the controls. Although the four species naturally occur in mature forest, two of the four grew significantly more in lightgaps than in closed canopy secondary forest. Overall, bottomlands facilitated greater seedling growth in height (38%) relative to plateaus, but only one species exhibited a significant increase. This study shows the importance of the environmental variability generated with canopy openings along the topographic gradient, suggesting that both the selection of species and microsite conditions of planting sites have to be considered important criteria in the recovery of degraded areas. (AU)
Asunto(s)
Producción de Cultivos , Pastizales , Ecosistema Amazónico , Restauración y Remediación AmbientalRESUMEN
A multilocus mixed-mating model was used to evaluate the mating system of a population of Couratari multiflora, an emergent tree species found in low densities (1 individual/10 ha) in lowland forests of central Amazonia. We surveyed and observed phenologically 41 trees in an area of 400 ha. From these, only four mother trees were analyzed here because few of them set fruits, which also suffered high predation. No difference was observed between the population multilocus outcrossing rate (t mp = 0.953 ± 0.040) and the average single locus rate (t sp = 0.968 ± 0.132). The four mother trees were highly outcrossed (t m ~ 1). Two out of five loci showed departures from the Hardy-Weinberg Equilibrium (HWE) expectations, and the same results occurred with the mixed-mating model. Besides the low number of trees analyzed, the proportion of loci in HWE suggests random mating in the population. However, the pollen pool was heterogeneous among families, probably due to both the small sample number and the flowering of trees at different times of the flowering season. Reproductive phenology of the population and the results presented here suggest, at least for part of the population, a long-distance pollen movement, around 1,000 m.
Foi utilizado um modelo de cruzamento misto multilocos para analisar o sistema de cruzamento de uma população de Couratari multiflora, espécie arbórea emergente encontrada em baixas densidades (1 indivíduo/10 ha) nas florestas de "terra firme" da Amazônia central. Inventariamos e observamos fenologicamente 41 árvores em uma área de 400 ha. Dessas, somente quatro árvores-mãe foram analisadas, pois poucas árvores produziram frutos, os quais também sofreram alta predação. Não foi observada diferença entre a taxa de cruzamento multilocos (t mp = 0,953 ± 0,040) e a taxa média de loco único (t sp = 0,968 ± 0,132). As quatro árvores-mãe apresentaram alta taxa de cruzamento (t m ~ 1). Dois dos cinco locos analisados mostraram desvios das expectativas do Equilíbrio de Hardy-Weinberg (EHW), e os mesmos resultados ocorreram para o modelo misto de cruzamento. Apesar do baixo número de árvores analisadas, a alta proporção de locos em EHW sugere que a população tenha um sistema de cruzamento aleatório. Entretanto, o conjunto polínico foi heterogêneo entre famílias, provavelmente pelo pequeno número e florescimento das árvores analisadas em diferentes fases da estação de florescimento. A fenologia reprodutiva da população e os resultados apresentados neste estudo sugerem que ao menos parte da população cruza via movimento de pólen de longa distância, em torno de 1.000 m.
Asunto(s)
Ecosistema Amazónico , FitomejoramientoRESUMEN
As estimativas de densidade e biomassa de árvores vivas com DAP > 10 cm e arvoretas 1-9,9 cm de DAP, liteira lenhosa grossa caída (LCG diâmetro > 10 cm), árvores mortas em pé (> 10 de DAP) e liteira lenhosa fina caída (LCF - 2,5 9,9 cm de diâmetro) foram quantificadas em 56 parcelas permanentes de 1 ha, distribuídas em quatro categorias de tamanho de fragmento - fragmentos de 1 ha (4 parcelas), fragmentos de 10 ha (12 parcelas) e fragmentos de 100 ha (14 parcelas) e floresta contínua (19 parcelas) e em duas classes de distância da borda - < 300 m de distância da borda (29 parcelas) e > 300 m (21 parcelas). A densidade e a biomassa de árvores e arvoretas de espécies de estágios sucessionais mais avançados não diferiram significativamente entre as diferentes categorias de tamanho e entre as duas distâncias da borda. Por outro lado, fragmentos florestais e locais < 300 m de distâcia da borda tiveram maior biomassa e densidade de árvores e arvoretas de espécies pioneiras do que floresta contínua e locais > 300 m da borda, respectivamente. Fragmentos florestais apresentaram maior quantidade de LCG e LCF do que a floresta contínua. Houve também diferenças significativas entre ambas as distâncias da borda para a quantidade de LCG e LCF e necromassa total. Uma análise de covariância mostrou que não houve efeito de tamanho do fragmento, mas a distância da borda teve um efeito significativo sobre a quantidade de LCG e LCF. A quantidade de LCG e LCF foi correlacionada negativamente com a distância da borda - locais mais próximos à borda tiveram cerca de 40 por cento e 60 por cento mais LCG do que locais mais distantes.
Density and biomass of live trees >10 cm DBH and saplings 1-9.9 cm DBH, coarse woody debris (LCG diameter > 10 cm), fine woody debris (LCF diameter 2.5-9.9 cm), and standing dead trees (> 10 cm DBH) were quantified in 56 permanent, 1-ha sample plots. These plots are located in four 1- (4 plots), three 10- (12 plots) and two 100- (14 plots) forest fragments in size and nearby continuous forests (19 plots) as well as in two classes of distance from the edges - < 300 m (29 plots) and > 300 m (21 plots). Density and biomass of primary species did not differ significantly among the four size categories and the two edge distance classes. However, forest fragments and distance < 300 m from the edges had more biomass and density of pioneer trees and saplings than did continuous forest and distance > 300 m from the edge, respectively. There were no significant differences among the size categories for standing dead trees. Forest fragments, however, had more quantity of LCG and LCF than did continuous forests. Moreover, distances < 300 m from the edges had higher quantity of LCG and LCF and total necromass than did distances > 300 m. We performed an ANCOVA to assess whether differences in LCG and LCF in fragments were due to proximity of forest borders. An ANCOVA showed that there was no significant effect of fragment size on necromass, but a significant effect of edge distance on both LCG and LCF. The quantity of LCG and LCF was correlated negatively with edge distance sites close to the edge presented over 40-60 percent more LCG than sites far from the edges in both forest fragments and continuous forests.