1000 resultados para Floresta Tropical Seca


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As ilhas de Cabo Verde elevam-se de um soco submarino, em forma de ferradura, situado a uma profundidade da ordem de 3.000 metros. Deste soco emergem três pedestais bem distintos1. A Norte, compreendendo as ilhas de St° Antão, S. Vicente, St.ª Luzia e S. Nicolau e os ilhéus Boi, Pássaros, Branco e Raso. A Leste e a Sul, com as ilhas do Sal, Boa Vista, Maio e Santiago e os ilhéus Rabo de Junco, Curral de Dadó, Fragata, Chano, Baluarte e de Santa Maria. A Oeste, compreendendo as ilhas do Fogo e da Brava e os ilhéus Grande, Luís Carneiro e de Cima (Fig. 1 - Mapa de Cabo Verde e distribuição das ilhas nos três pedestais). A formação das ilhas teria sido iniciada por uma actividade vulcânica submarina central, mais tarde completada por uma rede físsural manifestada nos afloramentos. A maior parte das ilhas é dominada por emissões de escoadas lávicas e de materiais piroclásticos (escórias, bagacinas ou "lapilli" e cinzas) subaéreos, predominantemente basálticas. O Arquipélago de Cabo Verde fica localizado na margem Oriental do Atlântico Norte, a cerca de 450 Km da Costa Ocidental da África e a cerca de 1.400 Km a SSW das Canárias, limitado pelos paralelos 17° 13' (Ponta Cais dos Fortes, Ilha de St° Antão) e 14º 48' (Ponta de Nho Martinho, Ilha Brava), de latitude Norte e pelos meridianos de 22° 42' (ilhéu Baluarte, Ilha da Boa Vista) e 25° 22' (Ponta Chã de Mangrado, Ilha de St° Antão) de longitude Oeste de Greenwich. O Arquipélago de Cabo Verde fica situado a cerca de 2.000 Km a Leste do actual "rift" da "Crista Média Atlântica" e a Oeste da zona de quietude magnética ("quite zone"), entre as isócronas dos 120 e 140 M.A., segundo Vacquier (1972), e a dos 107 e 153 M.A., segundo Haynes & Rabinowitz (1975), argumentos invocados para se considerar que as ilhas teriam sido geradas em ambiente oceânico. O Arquipélago de Cabo Verde fica situado numa região elevada do actual fundo oceânico, que faz parte da "Crista de Cabo Verde" (" Cape Verde Rise"), e que na vizinhança das ilhas corresponde a um domo com cerca de 400 Km de largura (Lancelot et al., 1977). Presume-se que um domo daquelas dimensões representa um fenómeno importante, possivelmente relacionado com descompressão e fusão parcial (Le Bas, 1980) que forneceria a fonte dos magmas que originaram as ilhas (Stillman et al., 1982). As ilhas se teriam implantado por um mecanismo do tipo "hot-spot", de acordo com alguns autores.

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Cabo Verde é um País insular, situado à 500kms da costa Ocidental Africana. Composto por 10 ilhas de origem vulcânicas, pertencentes a zona climática Saheliana árida, onde a precipitação anual é muito limitada e a estação das chuvas vai de Agosto a Outubro. A área do estudo é a bacia hidrográfica de Ribeira Seca, situada na parte nordeste da ilha de Santiago. De acordo com o Censo 2000, a população da bacia é estimada em 14.343 habitantes. Apesar de ser uma das bacias mais exploradas de Santiago, do ponto de vista da extracção da água, não existe um único piezométro. A obtenção de valores do volume explorado na bacia é uma tarefa bastante difícil, uma vez que a grande maioria dos poços e nascentes não é licenciado. Um conjunto de pontos de observação, onde periodicamente se efectua as medições do nível da água e o caudal das nascentes, constitui a rede de quantidade de água que compreende a rede piezométrica e a de caudais das nascentes. Este trabalho pretende elaborar uma rede de referência de quantidade de água que visa essencialmente a caracterização do recurso e o acompanhamento da sua evolução espaço-temporal para uma adequada gestão do mesmo.

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Severe land degradation has strongly affected both people’s livelihood and the environment in Cape Verde (Cabo Verde in Portuguese), a natural resource poor country. Despite the enormous investment in soil and water conservation measures (SWC or SLM), which are visible throughout the landscape, and the recognition of their benefits, their biophysical and socioeconomic impacts have been poorly assessed and scientifically documented. This paper contributes to filling this gap, by bringing together insights from literature and policy review, field survey and participatory assessment in the Ribeira Seca Watershed through a concerted approach devised by the DESIRE project (the “Desire approach”). Specifically, we analyze government strategies towards building resilience against the harsh conditions, analyze the state of land degradation and its drivers, survey and map the existing SWC measures, and assess their effectiveness against land degradation, on crop yield and people’s livelihood. We infer that the relative success of Cape Verde in tackling desertification and rural poverty owes to an integrated governance strategy that comprises raising awareness, institutional framework development, financial resource allocation, capacity building, and active participation of rural communities. We recommend that specific, scientific-based monitoring and assessment studies be carried out on the biophysical and socioeconomic impact of SLM and that the “Desire approach” be scaled-up to other watersheds in the country.

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Dans cet article, l´auteur caractérise l´eau et l´agriculture des îles du Cap Vert et analyse les défis de l´eau après la construction du barrage de Poilao dans la Vallée de Ribeira Seca, sur l´île de Santiago, en se servant de l´approche GIRE (Gestion Intégrée des Ressources en Eau). Au niveau de la législation, il s´avère nécessaire de proposer de nouvelles lois, décrets et règlements qui soient en accord avec notre réalité, en opposition à un important lot d´instruments juridiques inapplicables, obsolètes et de compréhension difficile. La construction du barrage de Poilão a produit des impacts environnementaux, socio-économiques et sur l´irrigation. Il s´agit de trouver un modèle de gestion qui s´adapte à la réalité du Cap Vert et de l´île de Santiago, regroupant tous les partenaires pour une gestion durable de la vallée de Ribeira Seca et qui puisse servir d´exemple aux futurs barrages à construire.

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The synanthropic index and other ecological aspects of the Muscidae family were evaluated through simultaneous monthly sampling in three different environments (urban, rural and forest) using van Someren-Rydon traps baited with human faeces, chicken viscera and decomposing fish and onion. Four traps were set up in each environment (one per bait item) for 48 hours per month, with samples taken every 12 hours. A total of 5726 specimens were collected, belonging to 19 species and 13 genera. Brontaea normata (+99,9), Brontaea quadristigma (+96,9), Synthesiomyia nudiseta (+96,5), Ophyra aenescens (+96,2), Musca domestica (+95,7) and Atherigona orientalis (+93,8) had the highest synanthropic indices, showing a marked preference for human environments. The most abundant species were B. normata (24,31%), Biopyrellia bipuncta (20,60%) and Pseudoptilolepis nigripoda (15,82%), the latter two showed a preference for uninhabited areas. A total of 11 new records for Colombia were found: Ophyra aenescens, Cyrtoneuropsis pararescita, Morellia basalis, Neomuscina dorsipuncta, Biopyrellia bipuncta, Pseudoptilolepis nigripoda, Neomuscina instabilis, Neomuscina currani, Polietina orbitalis, Neomuscina pictipennis and Cyrtoneuropsis maculipennis. Except for the first four species, the remainder presented negative synantrophy indexes (from minor to major), which would allow to use them as ecological indicators of the disturbance degree of dry forests in Colombia.

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Diversity of gall-inducing insects in the tropical dry forest (caatinga) of Pernambuco. We report on the richness of galling insects in the vegetation of caatinga of Pernambuco state, Brazil. We recorded 64 different types of galls collected primarily from leaves and stems of 48 species of host plants belonging to 17 families and 31 genera. The most common gall morphological types were spheroid and discoid, glabrous, predominantly green and with one chamber. The main gall inducing taxon was the Cecidomyiidae (Diptera). The results of this study contribute to existing knowledge of galling insect and host-plant diversity in caatinga.

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Influence of different tropical fruits on biological and behavioral aspects of the Mediterranean fruit fly Ceratitis capitata (Wiedemann) (Diptera, Tephritidae). Studies on Ceratitis capitata, a world fruit pest, can aid the implementation of control programs by determining the plants with higher vulnerability to attacks and plants able to sustain their population in areas of fly distribution. The objective of the present study was to evaluate the influence of eight tropical fruits on the following biological and behavioral parameters of C. capitata: emergence percentage, life cycle duration, adult size, egg production, longevity, fecundity, egg viability, and oviposition acceptance. The fruits tested were: acerola (Malpighia glabra L.), cashew (Anacardium occidentale L.), star fruit (Averrhoa carambola L.), guava (Psidium guajava L.), soursop (Annona muricata L.), yellow mombin (Spondias mombin L.), Malay apple (Syzygium malaccense L.), and umbu (Spondias tuberosa L.). The biological parameters were obtained by rearing the recently hatched larvae on each of the fruit kinds. Acceptance of fruits for oviposition experiment was assessed using no-choice tests, as couples were exposed to two pieces of the same fruit. The best performances were obtained with guava, soursop, and star fruit. Larvae reared on cashew and acerola fruits had regular performances. No adults emerged from yellow mombin, Malay apple, or umbu. Fruit species did not affect adult longevity, female fecundity, or egg viability. Guava, soursop, and acerola were preferred for oviposition, followed by star fruit, Malay apple, cashew, and yellow mombin. Oviposition did not occur on umbu. In general, fruits with better larval development were also more accepted for oviposition.

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A República de Cabo Verde é uma nação insular, situada à 500km da costa Ocidental da África. Composta por 10 ilhas de origem vulcânicas, pertencentes a zona climática Saheliana árida, onde a precipitação anual é muito limitada e a estação das chuvas vai de Agosto a Outubro. Os aquíferos costeiros constituem um recurso importante de água doce cuja qualidade tem vindo a deteriorar devido ao incremento das necessidades de água, consequência directa do aumento demográfico, industrial e agrícola que se verifica nas zonas litorais. A exploração intensiva e prolongada em captações muito próximas do mar, onde não existe uma fonte de compensação destas extracções por recarga natural ou artificial do aquífero, pode provocar o avanço da interface água doce – água salgada no sentido dos furos e a sua posterior contaminação. O aumento de volume de água doce nos aquíferos consegue-se adoptando regras que controlem a extracção, planeando correctamente os locais de descarga dos sistemas de drenagens e tratamento de águas pluviais e residuais, promovendo políticas para a utilização racional da água, incrementando a recarga com água de superfície e implementando medidas que façam diminuir o volume de água salgada/salobra no aquífero. A área do estudo é a parte jusante da bacia hidrográfica de Ribeira Seca, situada na parte nordeste da ilha de Santiago (maior ilha da nação). De acordo com o Censo 2000, a população da bacia é estimada em 14.343 habitantes e está dividida em três sub-bacias Ribeira de Montanha, Ribeira de Mendes Faleiro Cabral e Ribeira Seca, perfazendo uma superfície total de 71,5Km2. Este trabalho pretende identificar o problema da sobre exploração de aquíferos costeiros, da contaminação das águas subterrâneas e propor estratégias de forma integrada visando a prevenção e controlo da poluição salina, problema que afecta principalmente a parte jusante da bacia devido principalmente a exploração dos aquíferos em quantidades superiores a recarga.

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This paper presents the assessment and mapping of the Ribeira Seca catchment, an insular Sahelian mountain region sensitive to desertification, located on the island of Santiago, Cabo Verde. Desertification is a threat to the global environment, representing a serious ecological problemin Cabo Verde. To successfully combat desertification, an evaluation of desertification consequences is required and the building of cartography of the sensitivity for arid and semi-arid ecosystems is required as a first step. The MEDALUS model was the basis for this study in which six quality indicators were used: climate, soil, vegetation, land management, erosion and social factors. Several parameters were defined for each indicator with weights varying between 1 (very low) and 2 (very high). The geometric mean of each of the six quality indicators was employed to produce a map of areas sensitive to desertification. The results of this study show that more than 50% of the watershed show clear evidence of becoming a desertified area.

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Ant species (Hymenoptera, Formicidae) from the seasonally dry tropical forest of northeastern Brazil: a compilation from field surveys in Bahia and literature records. The Caatingas occur predominantly in northeastern Brazil and comparatively it is the biome that received less attention than any other ecosystem in Brazil, representing the region where invertebrate groups are less known. We present here the first list of ant species of the Caatingas, compiling information from the literature, from a study of samples preserved in alcohol in the Laboratory of Entomology (Universidade Estadual de Feira de Santana), and from a field survey conducted in Milagres, Bahia, submitting standardized 1-m² samples of the leaf-litter to Winkler extractors. Summing all information, 11 subfamilies, 61 genera and 173 species (plus one subspecies) of ants are recognized in the biome. This species number does not consider morphospecies that could not be named due to the lack of reliable recent taxonomic information for some Neotropical ant genera. The list presented here for ant species of the Caatingas is therefore underestimated, but it is relevant because it allows the identification of areas to be sampled in order to improve our knowledge of the diversity of ants in this biome.

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We conducted a survey of insects and pest management practices on 34 farms growing ornamental tropical foliage plants in the central coffee region of Colombia over two years. Tropical foliage provided habitat for a diverse range of insects. In total, phytophagous or detritivorous insects from six orders, 40 families and 62 genera were collected. The most common were Hemiptera (29 genera from 16 families), followed by Coleoptera (17 genera from 4 families), Diptera (5 genera from 5 families), Lepidoptera (5 genera from 4 families), Hymenoptera (3 genera from 2 families) and Orthoptera (2 genera from 2 families). The most common phytophagous species were leaf cutting ants (Atta and Acromyrmex spp.), leaf beetles (Chrysomelidae), leafhoppers (Cicadellidae), stinkbugs (Pentatomidae), squash bugs (Coreidae), tree hoppers (Membracidae) and plant hoppers (Fulgoridae). Beneficial insects identified from tropical foliage included predators and parasitoids amongst 5 orders, 12 families and 22 genera. The most abundant were predators among the Coccinellidae, Chrysopidae, Reduviidae, Lycidae and Formicidae but only low numbers of parasitoids (Ichneumonidae, Braconidae and Tachinidae) were collected. A pest management questionnaire given to growers revealed a preponderance of reliance on broad spectrum insecticides with a smaller number of growers (approximately one third) also using some biological control methods. Our survey contributes basic information regarding diversity of Neotropical insects associated with ornamental foliage plants.

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Em casa de vegetação da Escola Superior de Agricultura "Luiz de Queiroz", em Piracicaba (SP), no período de janeiro a agosto de 1992, foi desenvolvido um experimento com amostra superficial de um latossolo vermelho-amarelo textura argilosa. Utilizou-se um esquema fatorial 4 x 3 x 4, com doses de calcário (0; 380; 760 e 1.140 mg kg-1 de terra), doses de potássio (0; 40 e 120 mg kg-1 de terra) e quatro cultivares de alfafa (Crioula, Moapa, Florida 77 e CUF 101). O delineamento experimental foi o de blocos ao acaso, com quatro repetições. Efetuou-se o primeiro corte 70 dias após a semeadura, enquanto o segundo corte foi realizado entre 34 e 41 dias após o primeiro. Os cultivares de maior rendimento de matéria seca no primeiro corte foram Florida 77 e CUF 101, que se igualaram aos cultivares Crioula e Moapa no segundo corte. As máximas produções de matéria seca e quantidades totais de nitrogênio estimadas corresponderam às doses de calcário dolomítico entre 886 e 1.095 mg kg-1, que elevaram a saturação por bases do solo para 64,8 a 68,6%, enquanto, para o potássio, esses pontos de máximo foram estimados para doses entre 44,7 e 74,2 mg kg-1. Sintomas visuais de deficiência de potássio foram observados na alfafa, nos tratamentos sem adubação potássica.

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The precise sampling of soil, biological or micro climatic attributes in tropical forests, which are characterized by a high diversity of species and complex spatial variability, is a difficult task. We found few basic studies to guide sampling procedures. The objective of this study was to define a sampling strategy and data analysis for some parameters frequently used in nutrient cycling studies, i. e., litter amount, total nutrient amounts in litter and its composition (Ca, Mg, Κ, Ν and P), and soil attributes at three depths (organic matter, Ρ content, cation exchange capacity and base saturation). A natural remnant forest in the West of São Paulo State (Brazil) was selected as study area and samples were collected in July, 1989. The total amount of litter and its total nutrient amounts had a high spatial independent variance. Conversely, the variance of litter composition was lower and the spatial dependency was peculiar to each nutrient. The sampling strategy for the estimation of litter amounts and the amount of nutrient in litter should be different than the sampling strategy for nutrient composition. For the estimation of litter amounts and the amount of nutrients in litter (related to quantity) a large number of randomly distributed determinations are needed. Otherwise, for the estimation of litter nutrient composition (related to quality) a smaller amount of spatially located samples should be analyzed. The determination of sampling for soil attributes differed according to the depth. Overall, surface samples (0-5 cm) showed high short distance spatial dependent variance, whereas, subsurface samples exhibited spatial dependency in longer distances. Short transects with sampling interval of 5-10 m are recommended for surface sampling. Subsurface samples must also be spatially located, but with transects or grids with longer distances between sampling points over the entire area. Composite soil samples would not provide a complete understanding of the relation between soil properties and surface dynamic processes or landscape aspects. Precise distribution of Ρ was difficult to estimate.