1000 resultados para Carta de ocupação do solo
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Como o objeto específico de nossa atenção é a Região Metropolitana de São Paulo, Metrópole Nacional e o maior polo de desenvolvimento da América Latina, pretendemos ao final deste trabalho analisar e discutir as medidas de planejamento urbano adotadas para o controle e administração do seu crescimento e de sua problemática. Para isto tomaremos por base as normas institucionais do uso e da ocupação do solo urbano na região já existentes. Para que se possa avaliar essas medidas é necessário que se conheçam as disposições constitucionais que regem o assunto, no que tange às competências específicas da União, do Estado e do Município para legislar em assuntos urbanos.
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Impactos ambientais causados pelas atividades agropecuárias sobre o meio rural podem ser constatados quando são analisadas as paisagens da região. Vários estudos demonstraram que informações da paisagem obtidas a partir de imagens fotográficas são indispensáveis para o diagnóstico do processo erosivo do solo, aspecto indispensável no planejamento conservacionista. Neste trabalho, utilizando-se de técnicas de fotointerpretação, foi realizada a quantificação das classes de erosão acelerada no município de Franca - SP, relacionando-as com os tipos de cobertura vegetal. A coleção de fotografias aéreas empregadas foi produzida pela Base Aerofotogrametria e Projetos S.A., com escala aproximada 1:35.000, em outubro de 1990. Elaboraram-se cartas temáticas do uso/ocupação do solo e dos estados erosivos presentes em cada tipo de cobertura vegetal do solo, estabelecendo-se, em seguida, as relações entre a erosão acelerada e os tipos de comunidades vegetais do município de Franca. Os resultados obtidos mostraram que, nesse município, o solo agrícola encontra-se relativamente conservado, apresentando 74,23% da área com erosão laminar ligeira/moderada. Os diferentes usos/ocupações do solo influenciaram de modos distintos na manifestação do processo erosivo.
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The accelerated pressure of use and occupation of Rio Grande do Norte coastline in the last two decades presented the tourism as its main vector, having as a consequence a strong, articulated and growing real estate speculation of this area. In the Natal County there is a Zona Especial de Interesse Turistico II (Special Zone of Tourism Interest II) (ZET-II), consisted of urban beaches with approximately 8.5 km that is an important seashore of the city. The purpose of this research was identification, characterization and assessment of the process of use and occupation of dunes fields emphasizing the role of ZET-II, whereas the specific goals was the analysis of weather, geology and geomorphology, characterization of use and occupation of soil, and elaboration of an environmental diagnosis with identification and description of its mains consequences. The result of this work was the delineation of geologic-geomorphological map of the area with identification of principals units, determining its use and occupation, the measurement of the area already occupied by equipments, besides the description of the environmental impacts on dune fields: devastation, coastline erosion, ocean pollution by sewer and pluvial waters, contamination of groundwater, distribution inadequate of solid residues, landscape degradation, and occupation of seashore through the privatization of public areas. Concluding that the degrading changes occurred in this areas are resulting from the nature of use and urban seashore regulations, which have been diminishing the natural aspect, altering the landscape definitely, compromising the quality of hydro resources and altering its use, privatizing the areas between tides, complicating the population access and obstructing the scenery visualization of dunes and ocean. There is an urgent necessity of improvement of public politics in order to improve the strategies and organization of use and occupation of space urban-coastline
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One of the most important natural resources for sustaining human life, water, has been losing the basic requirements of quality and quantity sufficient enough to attend the population due to water contamination'problems, often caused by human beings themselves. Because of this, the sources of this resource are often located in remote places of the natural environment to ensure the quality of the water. However, when urban expansion began to occupy these areas, which were once regarded as distant, environmental pollution problems began to occur due to occupation of the land without planning. Based on this occurrence, this study aims to propose environmental zoning for the Maxaranguape river watershed in order to protect its water resources. This is important because this river can serve as a source of supply for the metropolitan area of Natal, the capital of Rio Grande do Norte. In accordance to this proposition, the model of natural soil loss vulnerability (CREPANI et al., 2001), the model of aquifer pollution vulnerability (FOSTER et al., 2006), and the legal incompatibility map (CREPANI et al., 2001) were used to delimit the zones. All this was done with Geographic Information System (GIS) and also created a geographic database update of the basin. The results of the first model mentioned indicated that 63.67% of the basin was classified as moderately stable / vulnerable, 35.66% as moderately vulnerable, and 0.67% as vulnerable. The areas with high vulnerability degree correspond with sand dunes and river channels areas. The second model indicated that 2.84% of the basin has low vulnerability, 70.27%) has median vulnerability, and 26.76% and 0.13% has high vulnerability and extreme vulnerability, respectively. The areas with the highest vulnerability values also refer to part of the sand dunes and river channels besides other areas such as Pureza urban area. The legal incompatibility map indicated that the basin has 85.02 km2 of Permanent Protection Area (PPA) and 14.62% of this area has some incongruity of use. Based on these results it was possible to draw three main zones: Protection and Sustainable Use Zone (PSUZ), Protection and Environmental Restoration Zone (PERZ) and Environmental Control Zone, which are divided into A, B and C. The PSUZ refer to the coastal areas of the basin, where the sand dunes are located. These sites should be areas of environmental protection and of sustainable urban expansion. The ZPRA refer to river channels, which are in high need of rehabilitation. The third zone corresponds to the rest of the basin which should have, in general, the mapping of possible sources of contamination for further control on the use and occupation of the river
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Pós-graduação em Agronomia (Energia na Agricultura) - FCA
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Pós-graduação em Geociências e Meio Ambiente - IGCE
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Pós-graduação em Geociências e Meio Ambiente - IGCE
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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
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Pós-graduação em Engenharia Civil - FEIS
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Pós-graduação em Agronomia (Energia na Agricultura) - FCA
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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Pós-graduação em Agronomia (Irrigação e Drenagem) - FCA