Made available in DSpace on 2015-05-07T14:49:40Z (GMT). No. of bitstreams: 1 arquivototal.pdf: 2083617 bytes, checksum: 24186308fe83b01622c4132a3474af60 (MD5) Previous issue date: 2011-02-28 / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - CAPES / The aim of this study was to determine if the soil losses by erosion in Alto Paraíba basin soils are below the maximum tolerance determined by the Soils Department and Rural Engineering of Paraíba Federal University, campus of Areia/PB. by the Soils Department and Rural Engineering of Paraíba Federal University, campus of Areia/PB. This analysis was based on the Universal Soil Loss Equation mathematic model. Operational procedures were carried out with satellite images and GIS/SPRING. The comparative map obtained between the Losses of Soil Map and Losses of Soil Tolerance Map, was the result of a vectorial combination between these maps. About 61% of the area is under acceptable conditions of soil losses, into the expected studies developed by UFPB/AREIA, and approximated 38% with override values of non acceptable soil losses. This tolerance depends essentially of the soil characteristics, of its depth and topography, and constitutes, this way, important information that allows to the land owner or planner, to know what the best way of soil usage is, and avoiding its degradation and exploitation it with high productivity level allowing the sustainable development of the land. The values of lower erosivity occurred in minor steepest area and open vegetal cover and dense caatinga (a xeric shrubland). It was obtained through data analyses, the tax of 76% representing open and sparse vegetal cover or exposed soil and little crops, that corroborates to erosive process. The largest values of erodibility are associated to planosols. Calculating the soil losses of that basin, with the usage of Universal Soil Loss Equation by laminar erosion, it was considered the intervals for theses losses as being: null or light, to values minor than 2 t ha-1 year-1 (76,13 %); moderate soil losses among 2 and 4 t ha-1 year-1 (9,77 %); high soil losses, among 4 and 6 t ha-1 year-1 (4,79 %) and very high soil losses, over 6 t ha-1 year-1 (9,31 %). / O objetivo deste trabalho é o de determinar se a perda de solo por erosão para os solos existentes na Bacia Hidrográfica do Alto-Paraíba estão compatíveis com as tolerâncias máximas já determinadas para os solos do Estado da Paraíba, em estudo realizado pelo Departamento de Solos e Engenharia Rural da UFPB, campus Areia/PB. No presente trabalho, realizou-se o estudo sobre a vulnerabilidade à erosão, avaliando-se a adequação das atuais formas de uso e ocupação do solo frente a esta vulnerabilidade. Esta análise foi feita com base na aplicação do modelo matemático representado pela Equação Universal de Perda de Solo - USLE. Os procedimentos operacionais foram feitos com o apoio de imagens de satélite, e com SIGs e utilização do software SPRING. O mapa comparativo entre as Perdas de Solo e as Tolerâncias de Perdas de Solo foi resultado de uma combinação vetorial entre estes mapas temáticos. Cerca de 61 % da área encontra-se sob condição aceitável de perda de solos, ou seja, os valores estão dentro do esperado pelos estudos efetuados pela UFPB / Campus Areia, e cerca de 38 % ficaram com valores acima do previsto, ou seja, perdas de solo não aceitáveis. Esta tolerância depende essencialmente das características dos solos, da profundidade e da topografia, e, constitui-se, dessa forma, em informação de significativa importância, visto que permite ao planejador ou proprietário de terra, saber que tipo de uso pode fazer para que não haja degradação dos solos e estes possam ser explorados com elevados níveis de produtividade, permitindo o desenvolvimento sustentável da terra. Os valores de erosividade mais baixos ocorreram na área de menor declividade e cobertura vegetal do tipo caatinga aberta e densa. Obtivemos através da análise dos dados, o percentual de 76% representando cobertura vegetal aberta, rala, solo exposto e pequenas culturas de subsistência, o que corroboram para a existência de processos erosivos. Os maiores valores de erodibilidade estão associados, à classe de solo Planossolo. Ao calcular as perdas de solo dessa bacia hidrográfica, com a utilização da Equação Universal de Perdas de Solo por erosão laminar, considerou-se os intervalos para essas perdas sendo: nula ou ligeira, para valores inferiores a 2 t ha-1 ano-1 (76,13 %); perda de solo moderada, entre 2 e 4 t ha-1 ano-1 (9,77 %); perda de solo alta, entre 4 e 6 t ha-1 ano-1 (4,79%) e perda de solo muito alta, para valores superiores a 6 t ha-1 ano-1 (9,31 %).

Orientador: Isabel Cristina Moroz-Caccia Gouveia / Resumo: O presente trabalho tem como objetivo principal analisar a suscetibilidade aos processos erosivos laminares e lineares, identificando áreas mais críticas e seus impactos sobre os recursos hídricos na Unidade de Gerenciamento de Recursos Hídricos da Bacia Hidrográfica do Rio Aguapeí (UGRHI-20), localizada no oeste do Estado de São Paulo. Para determinar a suscetibilidade à erosão laminar utilizou-se a Equação Universal de Perda de Solo (EUPS), desenvolvida por Wischmeier e Smith (1976). Para a suscetibilidade à erosão linear utilizou-se a metodologia de Fragilidade Ambiental proposta por Ross (1994). Os resultados mostraram que na UGRHI-20, as estimativas de perda de solo por erosão laminar estão muito acima do recomendado pela FAO (1965) e por Wischmeier & Smith (1978), pois 73% da área se enquadra na classe indicativa “Alta” com valores entre 50 – 200 t.ha-1 ano -1. Em relação à erosão linear, a condição da UGRHI-20 é considerada crítica, pois apresenta 57% de sua área nível de fragilidade emergente forte. Diante de tais resultados, espera-se que esse trabalho possa subsidiar o planejamento ambiental desta bacia hidrográfica pelo poder público e principalmente por órgãos gestores. Para isso, serão entregues exemplares desse trabalho em meio digital para o Comitê de Bacias Hidrográficas dos Rios Aguapeí e Peixe (CBH-AP). / Abstract: The present work has as main objective to analyze the susceptibility to laminar and linear erosive processes, identifying the most critical areas and their impacts on water resources at the Aguapeí River Basin Water Resources Management Unit (UGRHI 20), located in the west of São Paulo. To determine susceptibility to laminar erosion, The Universal Soil Loss Equation (USLE) developed by Wischmeier and Smith (1976) was used. For susceptibility to linear erosion, the Environmental Fragility methodology proposed by Ross (1994) was used. The results showed that in the UGRHI-20 laminar erosion soil loss estimates are far above those recommended by FAO (1965) and Wischmeier & Smith (1978), as 73% of the area falls under the “High” indicative class with values between 50 – 200 t.ha-1year-1. Regarding linear erosion, the condition of UGRHI-20 is considered critical, as it presents 57% of its area strong emerging fragility level. Given these results, it is hoped that this work can subsidize the environmental planning of this watershed by the government and especially by management agencies. To this end, copies of this work will be delivered digitally to the Aguapeí and Peixe River Watershed Committee (CBH-AP). / Mestre

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Submitted by CARLA MARIA GOULART DE MORAES (carlagm) on 2015-04-23T20:17:19Z No. of bitstreams: 1 MarciaGomesGeologia.pdf: 3212123 bytes, checksum: 2a235d35b0c87594b8e37e68a2ffd53b (MD5) / Made available in DSpace on 2015-04-23T20:17:19Z (GMT). No. of bitstreams: 1 MarciaGomesGeologia.pdf: 3212123 bytes, checksum: 2a235d35b0c87594b8e37e68a2ffd53b (MD5) Previous issue date: 2009-09-15 / Nenhuma / A degradação dos solos é um dos principais problemas relacionados ao desenvolvimento sustentável, e um dos grandes desafios a serem enfrentados já neste século. A ação do homem no planejamento e desenvolvimento da ocupação do espaço na Terra requer cada vez mais uma visão ampla sobre as necessidades da população, os recursos terrestres e aquáticos disponíveis e o conhecimento sobre o comportamento dos processos naturais, para racionalmente compatibilizar necessidades crescentes com recursos limitados. A crescente degradação do solo sob exploração agrícola em todo o mundo despertou nos últimos anos uma preocupação com a qualidade do solo e a sustentabilidade da produção agrícola. A matéria orgânica do solo é um fator relevante na qualidade deste, sendo uma fonte de energia, de carbono e doadora de elétrons da grande maioria dos organismos, o que evidencia sua importância para a biota desempenhar suas funções no sentido de promover as propriedades do solo. O objetivo deste trabalho é avaliar a degradação do solo na microbacia do arroio Morungava, com uso da Equação Universal de Perda de Solo (EUPS), através de análise da variação temporal da matéria orgânica nos horizontes superficiais, em solos Hidromórficos e Argissolos, sob práticas de cultivo em diferentes períodos de uso (18 meses de cultivo; 10 anos de cultivo; 15 anos de cultivo e mais de 30 anos de cultivo), utilizando áreas de mata nativa como referência. Em condições naturais os argissolos mostram um aumento de matéria orgânica (MO) com a profundidade. Nos horizontes superficiais dos solos cultivados analisados observa-se perda de MO por erosão e oxidação superficial, com pouca translocação vertical. Neste caso, a erosão superficial acelerada antropicamente, faz com que o Horizonte B dos argissolos fique próximo a superfície, eventualmente exposto, com o passar do tempo. Já os solos hidromórficos verificam-se grandes perdas iniciais com a retirada de matas nativas, o que pode ser em parte atribuído à oxidação acelerada da MO, devido às mudanças ambientais. Para os solos hidromórficos com mais de 15 anos de uso, verifica-se um comportamento inverso, ocorrendo um significativo aumento superficial da MO, o que pode ser devido ao aporte de MO originado dos argissolos adjacentes. Assim, as planícies aluvionares, para tempos de uso superiores há 15 anos, devem provavelmente atuar como zonas de acumulação de MO na bacia hidrográfica. Há um provável processo menos intenso de translocação vertical, o qual é observado nos primeiros 10 anos de uso dos hidromórficos. Quanto à avaliação espacial de perda de MO observa-se taxas com variação de 0 até 239,15 t ha¯¹ ano¯¹ com o uso do solo atual. Assim, 54,12 % da área apresentam taxas de perda de MO entre 0 a 0,5 t ha¯¹ ano¯¹ 42,21 % variam de 0,5 a 5 t ha¯¹ ano¯¹e os demais 3,67 % de área apresentam perdas de MO acima de 5 t ha¯¹ ano¯¹. Em um cenário onde a legislação ambiental (Código Florestal Federal - Lei 4.771 de 1965 e Código Florestal Estadual - Lei 9.519 de 1992) é cumprida, com reflorestamento nas Áreas de Preservação Permanente ? APPs, referente às encostas com declividade acima de 45º e faixas de 30 metros de cada lado, ao longo dos cursos d´água, observa-se 62,17 % da área com taxas de perda de MO entre 0 a 0,5 t ha¯¹ ano¯¹, 36,86 % variam de 0,5 a 5 t ha¯¹ ano¯¹e os demais 0,97 % de área apresentam perdas de MO acima de 5 t ha¯¹ ano¯¹, chegando a atingir 37,28 t ha¯¹ ano¯¹em alguns pontos. Para um cenário onde a faixa de preservação é de apenas 5 metros de cada lado, ao longo dos cursos d´águas, de acordo com a legislação ambiental do Estado de Santa Catarina (Art. 114 da Lei Estadual 14.675, de 13 abril de 2009), observa-se que as taxas de perda de MO aumentam. No cenário anterior as perdas acima de 5 t ha¯¹ ano¯¹, atingem apenas 0,97% do total da área. Aplicando a legislação do Estado de Santa Catarina, as taxas de perda acima de 5 t ha¯¹ ano¯¹, atingem 1,03 % do total da área. As taxas baixas de perda de MO (abaixo de 0,5 t ha¯¹ ano¯¹) para o cenário de 30 metros de preservação chegam a 62,17% da área. Já no cenário com faixa de preservação de apenas 5 metros, as taxas baixas de perda de MO chegam a 53,16% da área. Apesar de ser uma diferença pequena de taxas de perda de MO, estas taxas apresentadas comprovam que a diminuição das faixas de preservação de 30 metros para cinco metros, acarretará em prejuízos ao meio ambiente. Em um cenário onde toda a faixa de preservação de 30 metros de cada lado, ao longo dos cursos d´água, é retirada, as taxas de perda de MO variam de 0 até 239,15 t ha¯¹ ano¯¹. Neste caso 53,16 % da área apresenta taxas de perda de MO entre 0 a 0,5 t ha¯¹ ano¯¹, 43,02 % variam de 0,5 a 5 t ha¯¹ ano¯¹ e 3,82 % de área apresentam perdas de MO acima de 5 t ha¯¹ ano¯¹, chegando a atingir 239,15 t ha¯¹ ano¯¹ em alguns pontos. Essas taxas de perda são equivalentes ao uso do solo atual da área. Isto ocorre pelo fato da microbacia do arroio Morungava apresentar grandes extensões de faixa de preservação ao longo desses cursos d´água, totalmente desmatadas. O cenário criado para desmatamento de 30 metros é semelhante à situação real da área. A partir dos resultados obtidos das coletas de campo e dados gerados em laboratório, conclui-se que a micro bacia do arroio Morungava está sofrendo processo erosivo acelerado com o decorrer dos anos, principalmente em zonas de maior declividade, onde predominam os argissolos. Já os solos em posição fisiográficas com baixa erosão potencial superficial, como os hidromórficos, atuam como zonas de acumulação de sedimentos e matéria orgânica. Verifica-se uma variação ampla nas taxas de perda de MO com o uso do solo atual, com teores elevados nas áreas com maior declividade. Estes teores, de acordo com cenários gerados de reflorestamento, podem diminuir com o cumprimento da legislação ambiental. Assim pode-se afirmar que a EUPS foi fundamental para avaliar a perda de matéria orgânica na microbacia. / Soil degradation is one of the main concerns regarding sustainable development, and one of the challenges to be faced on this century. Mankind actions on planning and development of Earth occupation, needs more and more a broader view of population needs, available terrestrial and hydric resources and knowledge over natural processes behavior, to rationally conciliate growing needs with limited resources. The worldwide growing soil degradation due to agricultural exploitation, over the last years awoke a concern with soil quality and agricultural production sustainability. The soil organic matter is a relevant factor for its quality, being energy and Carbone source and an electron donator to most organisms, which only shows how it is important to biota?s functions and promote soil proprieties. The objective of this study is to evaluate the soil degradation at the micro basin of the Morungava stream, using the Universal Soil Loss Equation (USLE), through temporal variation analysis of organic matter on superficial horizons, on hydromorphic and argillaceous soils, under cultivation on different usage periods (18 months of cultivation, 10 years of cultivation, 15 years of cultivation and more than 30 years of cultivation), utilizing areas of native forest as reference. In natural conditions argillaceous soils show an increase in organic matter (OM) as it deepens. On the analyzed cultivated soils superficial horizons, was observed a loss of OM due to erosion and superficial oxidation, with low vertical translocation. In this case, the superficial erosion hasten by anthropic influence, causes the B horizon of argillaceous soils to be near the surface, eventually exposed with time. On the hydromorphic soils, there are big initial losses with the removal of native forests, which can be in part caused by hasten oxidation of OM due to environmental changes. To hydromorphic soils with more than 15 years of usage, a inverse behavior is observed, occurring a significant increase of superficial OM, which can be due to the arrive of OM from the adjacent argillaceous soils. So, the alluvial plains, to usage periods greater than 15 years, probably act as OM accumulation zones on the basin. There is a probable process less intense of vertical translocation, which is observed during the first 10 years of hydromorphic soil usage. As for the spatial evaluation of OM loss, its observed with variation from 0 to 239,15 t.ha¯¹.year¯¹ with current soil usage. This way, 54,12% of the area presents OM loss rate between 0 and 0,5 t.ha¯¹.year¯¹, 42,21% varies from 0,5 to 5 t.ha¯¹.year¯¹, and the remaining 3,67% of the area show OM losses superior to 5 t.ha¯¹.year¯¹. In a scenery where the environmental legislation (Federal Forest Code ? Law 4.771 of 1965 and State Forest Code ? Law 9.519 of 1992) is followed, with reforesting of Permanent Preservation Areas (APPs), referring to acclivity superior to 45° and a 30 meters preservation band from the margins of any watercourse, is observed that 62,17% of the area have a OM loss rate between 0 and 0,5 t.ha¯¹.year¯¹, 36,86% varies from 0,5 to 5 t.ha¯¹.year¯¹ and the remaining 0,97% have a OM loss rate superior to 5 t.ha¯¹.year¯¹, peaking 37,28 t.ha¯¹.year¯¹ at some points. In a scenery where the preservation band is only 5 meters from the margin of watercourses, in accordance with the environmental legislation of Santa Catarina state (Art.114 State Law 14.675 from 2009, April 13), its observed an increase in the OM loss Rates. If in the previous scenery the OM losses over 5 t.ha¯¹.ano¯¹, were only 0,97% of total area, applying the Santa Catarina State Law, the OM losses over 5 t.ha¯¹.ano¯¹, are 1,03% of total area. The low OM loss rates (under 0,5 t.ha¯¹.ano¯¹,) on the 30 meters preservation scenery were 62,17% of the area, applying the Santa Catarina state 5 meters preservation scenery it drops to 53,16% of the area. Even if it is a small difference on OM loss rates, these rates testify that the reduction of the preservation bands will incur in harm to the environment. In a scenery where all the preservation band is removed along the watercourses, the OM loss rates varies from 0 to 239,15 t.ha¯¹.year¯¹. In which case 53,16% of the area presents OM loss rates from 0 to 0,5 t.ha¯¹.year¯¹, 43,02% varies from 0,5 to 5 t.ha¯¹.year¯¹ and 3,82% of the area show OM losses over 5 t.ha¯¹.year¯¹, peaking 239,15 t.ha¯¹.year¯¹ at some points. Those loss rates are equivalent to those of the current soil usage in this area. This is due to the fact that the micro basin of the Morungava stream presents great extensions of preservation bands along its watercourses totally depleted. The scenery created with no preservation band is similar to the current situation of the area. From the gotten results of the collections of field and data generated in laboratory, one concludes that the micro basin of the Morungava stream is suffering sped up erosive process with elapsing of the years, mainly in zones of bigger declivity, where the argissolos predominate. Already the ground in position fisiográficas with low superficial potential erosion, as the hidromórficos, act as zones of accumulation of sediments and organic matter. An ample variation in the taxes of loss ME with the use of the ground is verified current, with texts raised in the areas with bigger declivity. These texts, scenes in accordance with generated of reforestation, can diminish with the fulfilment of the ambient legislation. Thus it can be affirmed that the EUPS was basic to evaluate the loss of organic matter in the micron basin.

From the Proceedings of the 1975 Meetings of the Arizona Section - American Water Resources Assn. and the Hydrology Section - Arizona Academy of Science - April 11-12, 1975, Tempe, Arizona / The universal soil loss equation (USLE) is widely used for estimating annual and individual storm erosion from field-sized watersheds. Records from a single precipitation gage in climatic areas dominated by thunderstorms can be used to estimate the erosion index (EI) only for the point in question on individual storms or for a specific annual value. Extrapolating the results for more than about a mile leads to serious error in estimating the erosion by the use of the USLE. Short time intervals must be used to obtain an adequate estimate of the EI when using the USLE. The variability of the annual EI can be approximated with a log-normal distribution. All studies indicated that investigations are needed to facilitate estimating the average annual EI from precipitation data as reported by state climatological summaries for states west of the 104th meridian. Additional work is needed to facilitate estimating the EI value from the precipitation data available in most areas of the southwest where thunderstorms dominate the rainfall pattern.

Accelerated soil erosion is drawing a growing attention with the recognition that the rate of soil loss is too great to be met by soil formation rate. Weenen Game Reserve (WGR) is an area with an unfortunate history of prolonged soil erosion due to excessive overgrazing that led to severe land degradation with prominent visible scars. This problem triggered the general objective of estimating and mapping potential soil erosion in WGR. Assessing soil loss in the area objectively has important implications for the overall management plans as it is reserved for ecological recovery. The most important variables that affect soil erosion are considered as inputs in soil loss estimation models. In this study the RUSLE model, which uses rainfall, soil, topography, and cover management data, was employed. From the rainfall data, an erosivity factor was generated by using a regression equation developed by relating EI30 index and total monthly rainfall. The soil erodibility factor was calculated using the soil erodibility nomograph equation after generating the relevant data from laboratory analysis of soil samples gathered from the study area. Using exponential ordinary kriging, the point values of this factor were interpolated to fill in the non-sampled areas. The topographic effect, which is expressed as the combined impact of slope length and slope steepness, was extracted from the DEM of the study area using the flow accumulation method. For mapping of the land cover factor, in situ measurements of cover from selected sites were undertaken and assigned values from the USLE table before being related with MSAVI of Landsat 7 ETM+ image. These values were then multiplied to get the final annual soil loss map. The resulting potential soil loss values vary between 0 and 346 ton ha-1 year-l with an average of 5 ton ha-1 year-l. About 58% of the study area experiences less than 1 ton ha-1 year-1 indicating the influence of the highest values on the average value. High soil erosion rates are concentrated in the central part extending as far as the south and the north tips along the eastern escarpments and these areas are the ones with the steepest slopes. The results indicate a high variation of soil loss within the study area. Nevertheless, the majority of the area falling below the average might foresee that the soil erosion problem of the area can be minimized significantly depending largely on soil management. The most important areas for intervention are the medium and low erosion susceptible parts of WGR, which are mainly found in the flatter or gently sloping landscapes. The steepest areas are mostly covered with rocks and/or vegetation and hence less effort must be spent in managing them. Overall, the reported increasing density of the vegetation community in the area that reduces the exposure of soil from the impact of direct raindrops and surface-flowing water must be pursued further. / Thesis (M.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2004.

The aim of this work is to explore the area of the Complex Land Consolidation Poněšice in the view of the pedology, hydrogeology and climatology. Further make a erosion threat calculations using the USLE and Curve Number method and afterwards review the application of the erosion control measures in another section of the chapter Main terriorial systems. In conclusion, to estimate the economic aspects of the proposed measures.

Submitted by PAULO SÉRGIO MARTIN (paulosergiomartin@gmail.com) on 2018-07-14T03:59:20Z No. of bitstreams: 1 Martin_PS_Dissert_MP_Estradas_Rurais_2018.pdf: 5079449 bytes, checksum: 5b99661ef6b9e4b120ee8a099ee40004 (MD5) / Approved for entry into archive by ALESSANDRA KUBA OSHIRO ASSUNÇÃO (alessandra@fct.unesp.br) on 2018-07-16T12:21:43Z (GMT) No. of bitstreams: 1 martin_ps_me_prud.pdf: 5079449 bytes, checksum: 5b99661ef6b9e4b120ee8a099ee40004 (MD5) / Made available in DSpace on 2018-07-16T12:21:43Z (GMT). No. of bitstreams: 1 martin_ps_me_prud.pdf: 5079449 bytes, checksum: 5b99661ef6b9e4b120ee8a099ee40004 (MD5) Previous issue date: 2018-06-04 / Neste presente trabalho buscou-se identificar as diversas variáveis do potencial de perda de solo no município de Ouro Verde/SP, considerando como parâmetro a classificação de solos, geologia, relevo, precipitação pluvial, o uso e ocupação da terra, as práticas de manejo conservacionista, mapeando as áreas com potencial de erosão laminar dos solos e o cruzamento das informações com a situação atual das estradas rurais não pavimentadas. As estradas não pavimentadas foram classificadas em trechos-tipos, destacando-se algumas características importantes, como altura de barranco, se está “encaixada”. O uso do MDE (Modelo Digital de Elevação) possibilitou a representação do relevo da superfície terrestre e com os dados vetoriais do município de Ouro Verde, baixados através do site do IBGE, foi possível a interpretação visual da área de estudo, analisadas através das imagens do satélite Sentinel-2. O objetivo foi identificar as estradas rurais ou trechos prioritários para readequação, através do Sistema de Informação Geográfica (SIG), com mapeamento das áreas do município e realizando o cruzamento de informações e, aplicação da Equação Universal de Perdas de Solo (USLE) e do programa InVEST®, estimando perdas de solo por erosão laminar. Servir de orientação para os gestores públicos (Prefeitura Municipal e FEHIDRO) na análise e tomada de decisão. Para determinação do Fator R para o município de Ouro Verde, a precipitação pluvial foi analisada através de uma série histórica, fornecida pelo Escritório de Desenvolvimento Rural de Dracena. Para determinação dos valores do fator R para os demais municípios que compõem as Unidades de Gerenciamento de Recursos Hídricos 20 e 21, utilizou-se o software livre netErosividade SP. Para realização da priorização dos trechos críticos das estradas, foram utilizados os parâmetros (estruturas e situações), adaptado do Projeto de Desenvolvimento Rural Sustentável – Microbacias Hidrográficas II – Acesso ao mercado, obtendo-se o enquadramento das Classes de priorização. O programa InVEST® possibilitou explorar cenários com resultados futuros prováveis, e assim foram gerados os diversos mapas de potencialidade de erosão para o município de Ouro Verde: Mapa de Susceptibilidade à Erosão Laminar, Mapa do Potencial à Erosão, Mapa do Potencial de Erosão Laminar Total por Microbacias Hidrográficas e Mapa final de Priorização das Estradas Não Pavimentadas. Obteve-se o Mapa Final de Priorização utilizando alguns parâmetros, mas é possível cruzar tantas informações quanto forem necessárias, subjetivas e objetivas, e assim chegar no objetivo, que é a priorização de trechos críticos de Estradas Rurais Não Pavimentadas. / This work aimed to identify the various variables of soil loss potential in the municipality of Ouro Verde / SP, considering as a parameter the classification of soils, geology, relief, rainfall, land use and occupation, management practices conservationist, mapping the areas with potential of laminar erosion of the soils and the crossing of the information with the current situation of the unpaved rural roads. Unpaved roads have been classified into parts-types, highlighting some important characteristics, such as height of ravine, if it is "docked". The use of the MDE (Digital Elevation Model) made possible the representation of the land surface and the vectorial data of the municipality of Ouro Verde, downloaded through the IBGE website, it was possible the visual interpretation of the study area, analyzed through the images of the Sentinel-2 satellite. The objective was to identify the rural roads or priority stretches for readjustment, through the Geographic Information System (GIS), with mapping of the areas of the municipality and carrying out the information crossing and, applying the Universal Soil Loss Equation (USLE) and the InVEST® program, estimating soil losses due to laminar erosion. To serve as guidance for public managers (City Hall and FEHIDRO) in the analysis and decision making. To determine the R factor for the municipality of Ouro Verde, rainfall was analyzed through a historical series, provided by the Office of Rural Development of Dracena. To determine the R factor values for the other municipalities that make up the Water Resources Management Units 20 and 21, the free software netErosividade SP was used. For the prioritization of the critical stretches of the roads, the parameters (structures and situations), adapted from the Sustainable Rural Development Project - Hydrographic Microbasins II - Access to the market, were used to obtain the prioritization classes. The InVEST® program made it possible to explore scenarios with probable future results, thus generating the various erosion potential maps for the municipality of Ouro Verde: Laminar Erosion Susceptibility Map, Erosion Potential Map, Total Laminar Erosion Potential Map by Hydrographic Microbasins and Final Map of Prioritization of Non-Paved Roads. The final Prioritization Map was obtained using some parameters, but it is possible to cross as much information as necessary, subjective and objective, and thus reach the objective, which is the prioritization of critical sections of Non-Paved Rural Roads.

The contents of this thesis is an examination and assessment of erosion processes in the catchment Budského stream. The area of interest falls into three cadastral territory, Malče, Besednice a Soběnov. Catchment area is 7.1 km2. Integral part of work is the pedological and hydrological research. It was evaluated the impact of waste in the surrounding villages. In the catchment basin, has a significant influence Besednice reservoir. It was assessing its impact on the environment and erosion control functions. Using the acquired information has been calculated N-year water and the amount of drifted soil by Wischmeier and Smith. Another goal is to process this data using software modeling and evaluate output. Against this background and the results are recommended measures to reduce soil loss from these plots.

Die Dissertation erforscht die Unsicherheit, Sensitivität und Grenzen großskaliger Erosionsmodelle. Die Modellierung basiert auf der allgemeinen Bodenabtragsgleichung (ABAG), Sedimenteintragsverhältnissen (SDR) und europäischen Daten. Für mehrere Regionen Europas wird die Bedeutung der Unsicherheit topographischer Modellparameter, ABAG-Faktoren und kritischer Schwebstofffrachten für die Anwendbarkeit empirischer Modelle zur Beschreibung von Sedimentfrachten und SDR von Flusseinzugsgebieten untersucht. Der Vergleich alternativer Modellparameter sowie Kalibrierungs- und Validierungsdaten zeigt, dass schon grundlegende Modellentscheidungen mit großen Unsicherheiten behaftet sind. Zur Vermeidung falscher Modellvorhersagen sind kalibrierte Modelle genau zu dokumentieren. Auch wenn die geschickte Wahl nicht-topographischer Algorithmen die Modellgüte regionaler Anwendungen verbessern kann, so gibt es nicht die generell beste Lösung. Die Ergebnisse zeigen auch, dass SDR-Modelle stets mit Sedimentfrachten und SDR kalibriert und evaluiert werden sollten. Mit diesem Ansatz werden eine neue europäische Bodenabtragskarte und ein verbessertes SDR-Modell für Einzugsgebiete nördlich der Alpen und in Südosteuropa abgeleitet. In anderen Regionen Europas ist das SDR-Modell bedingt nutzbar. Die Studien zur jährlichen Variabilität der Bodenerosion zeigen, dass jahreszeitlich gewichtete Niederschlagsdaten geeigneter als ungewichtete sind. Trotz zufriedenstellender Modellergebnisse überwinden weder sorgfältige Algorithmenwahl noch Modellverbesserungen die Grenzen europaweiter SDR-Modelle. Diese bestehen aus der Diskrepanz zwischen modellierten Bodenabtrags- und maßgeblich zur beobachteten bzw. kritischen Sedimentfracht beitragenden Prozessen sowie der außergewöhnlich hohen Sedimentmobilisierung durch Hochwässer. Die Integration von nicht von der ABAG beschriebenen Prozessen und von Starkregentagen sowie die Disaggregation kritischer Frachten sollte daher weiter erforscht werden. / This dissertation thesis addresses the uncertainty, sensitivity and limitations of large-scale erosion models. The modelling framework consists of the universal soil loss equation (USLE), sediment delivery ratios (SDR) and European data. For several European regions, the relevance of the uncertainty in topographic model parameters, USLE factors and critical yields of suspended solids for the applicability of empirical models to predict sediment yields and SDR of river catchments is systematically evaluated. The comparison of alternative model parameters as well as calibration and validation data shows that even basic modelling decisions are associated with great uncertainties. Consequently, calibrated models have to be well-documented to avoid misapplication. Although careful choices of non-topographic algorithms can also be helpful to improve the model quality in regional applications, there is no definitive universal solution. The results also show that SDR models should always be calibrated and evaluated against sediment yields and SDR. With this approach, a new European soil loss map and an improved SDR model for river catchments north of the Alps and in Southeast Europe are derived. For other parts of Europe, the SDR model is of limited use. The studies on the annual variability of soil erosion reveal that seasonally weighted rainfall data is more appropriate than unweighted data. Despite satisfactory model results, neither the careful algorithm choice nor model improvements overcome the limitations of pan-European SDR models. These limitations are related to the mismatch of modelled soil loss processes and the relevant processes contributing to the observed or critical sediment load as well as the extraordinary sediment mobilisation during floods. Therefore, further research on integrating non-USLE processes and heavy-rainfall data as well as on disaggregating critical yields is needed.