257 research outputs found

    Organic yerba mate : an environmentally, socially and financially suitable agroforestry system

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    Paper presented at the 12th North American Agroforesty Conference, which was held June 4-9, 2011 in Athens, Georgia.In Ashton, S. F., S.W. Workman, W.G. Hubbard and D.J. Moorhead, eds. Agroforestry: A Profitable Land Use. Proceedings, 12th North American Agroforestry Conference, Athens, GA, June 4-9, 2011.Trade in yerba mate (YM) (Ilex paraguariensis) is a lucrative business in Argentina, Paraguay, and Brazil. YM leaves are locally consumed as a tea with a market expanding to the USA, Europe and Asia, as it contains nearly twice the antioxidant levels of green tea and is energizing, making it an alternative to coffee. Approximately 5 percent of Misiones province, Argentina is in YM production. Many small farmers do not reach acceptable production levels due to lack of adequate technology. Organic YM producers can get up to 20 [percent] price surplus and most YM cooperatives have organic YM as one of their products. Typically grown in monocultures, its management can cause erosion and soil exhaustion, however YM naturally grows in subtropical forest and is shade tolerant thus it is adequate for agroforestry systems (AFS). We examined organic AFS of YM with other native trees by conducting semi-structured interviews with farmers in Misiones, including smaller, family-operated farms as well as larger farms, private companies, and private reserves. We recorded a substantial number of individuals of native species. Many farmers have their own nurseries to produce seedlings to use with YM and to sell for additional income. The extra work involved in using the organic practices and planting and tending for the native species is compensated by higher YM prices. YM AFS with native trees improve soil fertility of degraded areas without relying on fertilizers, while providing additional income from the timber of native trees. We conclude that AFS that combine YM with indigenous trees can favor the spread of organic YM production and diversify income in Argentina and elsewhere.Florencia Montagnini (1), Beatriz I. Eibl (2) and Sara R. Barth (2,3) ; 1. Yale University, Forestry and Env. Studies. 2. Facultad Ciencias Forestales, Universidad Nacional de Misiones. 3. Instituto Nacional de Tecnologïżœa Agropecuaria, INTA.Includes bibliographical references

    A Dynamic Approach to the Thermodynamics of Superdiffusion

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    We address the problem of relating thermodynamics to mechanics in the case of microscopic dynamics without a finite time scale. The solution is obtained by expressing the Tsallis entropic index q as a function of the Levy index alpha, and using dynamical rather than probabilistic arguments.Comment: 4 pages, new revised version resubmitted to Phys. Rev. Let

    The Spatial and Temporal Deployment of Voluntary Attention across the Visual Field

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    Several studies have addressed the question of the time it takes for attention to shift from one position in space to another. Here we present a behavioural paradigm which offers a direct access to an estimate of voluntary shift time by comparing, in the same task, a situation in which subjects are required to re-engage their attention at the same spatial location with a situation in which they need to shift their attention to another location, all other sensory, cognitive and motor parameters being equal. We show that spatial attention takes on average 55 ms to voluntarily shift from one hemifield to the other and 38 ms to shift within the same hemifield. In addition, we show that across and within hemifields attentional processes are different. In particular, attentional spotlight division appears to be more difficult to operate within than across hemifields

    Neighbour identity hardly affects litter-mixture effects on decomposition rates of New Zealand forest species.

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    The mass loss of litter mixtures is often different than expected based on the mass loss of the component species. We investigated if the identity of neighbour species affects these litter-mixing effects. To achieve this, we compared decomposition rates in monoculture and in all possible two-species combinations of eight tree species, widely differing in litter chemistry, set out in two contrasting New Zealand forest types. Litter from the mixed-species litter bags was separated into its component species, which allowed us to quantify the importance of litter-mixing effects and neighbour identity, relative to the effects of species identity, litter chemistry and litter incubation environment. Controlling factors on litter decomposition rate decreased in importance in the order: species identity (litter quality) >> forest type >> neighbour species. Species identity had the strongest influence on decomposition rate. Interspecific differences in initial litter lignin concentration explained a large proportion of the interspecific differences in litter decomposition rate. Litter mass loss was higher and litter-mixture effects were stronger on the younger, more fertile alluvial soils than on the older, less-fertile marine terrace soils. Litter-mixture effects only shifted percentage mass loss within the range of 1.5%. There was no evidence that certain litter mixtures consistently showed interactive effects. Contrary to common theory, adding a relatively fast-decomposing species generally slowed down the decomposition of the slower decomposing species in the mixture. This study shows that: (1) species identity, litter chemistry and forest type are quantitatively the most important drivers of litter decomposition in a New Zealand rain forest; (2) litter-mixture effects—although statistically significant—are far less important and hardly depend on the identity and the chemical characteristics of the neighbour species; (3) additive effects predominate in this ecosystem, so that mass dynamics of the mixtures can be predicted from the monocultures

    Litter mixture interactions at the level of plant functional types are additive.

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    It is very difficult to estimate litter decomposition rates in natural ecosystems because litters of many species are mixed and idiosyncratic interactions occur among those litters. A way to tackle this problem is to investigate litter mixing effects not at the species level but at the level of Plant Functional Types (PFTs). We tested the hypothesis that at the PFT level positive and negative interactions balance each other, causing an overall additive effect (no significant interactions among PFTs). Thereto, we used litter of four PFTs from a temperate peatland in which random draws were taken from the litter species pool of each PFT for every combination of 2, 3, and 4 PFTs. Decomposition rates clearly differed among the 4 PFTs (Sphagnum spp. < graminoids = N-fixing tree < forbs) and showed little variation within the PFTs (notably for the Sphagnum mosses and the graminoids). Significant positive interactions (4 out of 11) in the PFT mixtures were only found after 20 weeks and in all these combinations Sphagnum was involved. After 36 and 56 weeks of incubation interactions were not significantly different from zero. However, standard deviations were larger than the means, indicating that positive and negative interactions balanced each other. Thus, when litter mixture interactions are considered at the PFT level the interactions are additive. From this we conclude that for estimating litter decomposition rates at the ecosystem level, it is sufficient to use the weighted (by litter production) average decomposition rates of the contributing PFTs. © 2009 The Author(s)

    Dynamics of tree diversity in undisturbed and logged subtropical rainforest in Australia

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    In subtropical rainforest in eastern Australia, changes in the diversity of trees were compared under natural conditions and eight silvicultural regimes over 35 years. In the treated plots basal area remaining after logging ranged from 12 to 58 m2 per ha. In three control plots richness differed little over this period. In the eight treated plots richness per plot generally declined after intervention and then gradually increased to greater than original diversity. After logging there was a reduction in richness per plot and an increase in species richness per stem in all but the lightest selective treatments. The change in species diversity was related to the intensity of the logging, however the time taken for species richness to return to pre-logging levels was similar in all silvicultural treatments and was not effected by the intensity of treatment. These results suggest that light selective logging in these forests mainly affects dominant species. The return to high diversity after only a short time under all silvicultural regimes suggests that sustainability and the manipulation of species composition for desired management outcomes is possible
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