81 resultados para understorey


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Climate-driven change represents the cumulative effect of global through local-scale conditions, and understanding their manifestation at local scales can empower local management. Change in the dominance of habitats is often the product of local nutrient pollution that occurs at relatively local scales (i.e. catchment scale), a critical scale of management at which global impacts will manifest. We tested whether forecasted global-scale change [elevated carbon dioxide (CO2) and subsequent ocean acidification] and local stressors (elevated nutrients) can combine to accelerate the expansion of filamentous turfs at the expense of calcifying algae (kelp understorey). Our results not only support this model of future change, but also highlight the synergistic effects of future CO2 and nutrient concentrations on the abundance of turfs. These results suggest that global and local stressors need to be assessed in meaningful combinations so that the anticipated effects of climate change do not create the false impression that, however complex, climate change will produce smaller effects than reality. These findings empower local managers because they show that policies of reducing local stressors (e.g. nutrient pollution) can reduce the effects of global stressors not under their governance (e.g. ocean acidification). The connection between research and government policy provides an example whereby knowledge (and decision making) across local through global scales provides solutions to some of the most vexing challenges for attaining social goals of sustainability, biological conservation and economic development.

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Land-use change can have a major influence on soil organic carbon (SOC) and above-ground C pools. We assessed a change from native vegetation to introduced Pinus species plantations on C pools using eight paired sites. At each site we determined the impacts on 0–50 cm below-ground (SOC, charcoal C, organic matter C, particulate organic C, humic organic C, resistant organic C) and above-ground (litter, coarse woody debris, standing trees and woody understorey plants) C pools. In an analysis across the different study sites there was no significant difference (P > 0.05) in SOC or above-ground tree C stocks between paired native vegetation and pine plantations, although significant differences did exist at specific sites. SOC (calculated based on an equivalent soil mass basis) was higher in the pine plantations at two sites, higher in the native vegetation at two sites and did not differ for the other four sites. The site to site variation in SOC across the landscape was far greater than the variation observed with a change from native vegetation to introduced Pinus plantation. Differences between sites were not explained by soil type, although tree basal area was positively correlated with 0–50 cm SOC. In fact, in the native vegetation there was a significant linear relationship between above-ground biomass and SOC that explained 88.8% of the variation in the data. Fine litter C (0–25 mm diameter) tended to be higher in the pine forest than in the adjacent native vegetation and was significantly higher in the pine forest at five of the eight paired sites. Total litter C (0–100 mm diameter) increased significantly with plantation age (R2 = 0.64). Carbon stored in understorey woody plants (2.5–10 cm DBH) was higher in the native vegetation than in the adjacent pine forest. Total site C varied greatly across the study area from 58.8 Mg ha−1 at a native heathland site to 497.8 Mg ha−1 at a native eucalypt forest site. Our findings suggest that the effects of change from native vegetation to introduced Pinus sp. forest are highly site-specific and may be positive, negative, or have no influence on various C pools, depending on local site characteristics (e.g. plantation age and type of native vegetation).

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O estudo da estrutura e dinâmica da regeneração natural em sub-bosque de plantios com espécies exóticas, como as do gênero Pinus , possibilita dar informações para manejo, conservação e reestabelecimento das espécies nativas de uma comunidade vegetal. O objetivo deste trabalho foi identificar e quantificar a dinâmica da regeneração natural das espécies arbustivo-arbóreas ocorrentes no sub-bosque do povoamento de Pinus caribaea , na Rebio de Saltinho, em Pernambuco. Foram medidas as espécies regenerantes de 10 parcelas permanentes, de 1 x 50 m, e incluídos os indivíduos com circunferência na base a 30 cm do solo (CAB 0,30m) ≤ 15 cm e altura superior a um metro. A altura foi classificada em: Classe 1, indivíduos arbustivoarbóreos, com altura 1 ≤ H ≤ 2; Classe 2 com altura 2 < H ≤ 3; e Classe 3, com altura > 3 m e CAP ≤ 15 cm. Calcularam-se os parâmetros fitossociológicos, a dinâmica da regeneração e os índices de Shannon (H’) e a equabilidade (J’) por Pielou. Protium heptaphyllum teve maior número de indivíduos e valor de importância (VI), e Miconia prasina a melhor frequência nos dois levantamentos. Quanto ao índice H’ de 3,32 nats.ind-1 (2007) passou a 3,07 nats.ind-1 (2012), e a equabilidade de J’ de 0,85 a 0,62, havendo decréscimo tanto para a diversidade, quanto para a distribuição. O levantamento de 2012 registrou aumento de 12,5% do número de indivíduos, e os regenerantes de 2007 tiveram 48,31% de mortalidade. Com relação ao número de indivíduos e área basal, os percentuais de ganhos foram superiores ao das perdas. Conclui-se que a sucessão ecológica da regeneração do sub-bosque do povoamento estudado, encontra-se em modificação positiva, e o povoamento de Pinus caribaea, não está impedindo o surgimento de novos indivíduos e espécies.

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Doutoramento em Engenharia Florestal e dos Recursos Naturais - Instituto Superior de Agronomia - UL

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Faculdade de Engenharia de Recursos Naturais, Univ. do Algarve, 2001

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Regeneration of tree species in felling gaps were studied during the first two years following harvesting in a tropical forest in Acre state, Brazil. Felling gaps averaged 340 m2 in size, while canopy openings averaged 17%. Seedling mortality in adjacent undisturbed forest was 4.6% yr', and 59.6% yr·1 and 100% yr' in the crown and trunk zones respectively, two years after logging. Recruitment of new seedlings inthe undisturbed forest understorey averaged 462 plants ha' yr', two years after gap creation. Inthe crown zones of the gaps, recruitment of seedlings averaged 1350 ha' yr', and in the trunk zones 1392 ha' yr'. The entire seedling community in trunk zones after logging was composed of new recruits. lhere was a tendency for seedling growth rates to increase from the natural forest (0,21cm yr-1) to the crown zone (0.40cm yr'), Before gap creation, species richness and diversity and seedling density were quite similar. After gap creation a sharp decrease could be verified in the gap.zones, however the differences between gap and undisturbed forest decreased rapidly in the second year after gap creation. lhe regeneration of commercial species was not affected by gap creation apart from the increase in growth rates.