816 resultados para farmland ponds


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This paper reveals how rural Cambodian people reconstructed their social relationships after the collapse of the Pol Pot regime by examining farmland, which was the most important means of production in rural areas at that time. Section 1 and 2 illustrate the process of returning from collective farming under the Pol Pot regime to the family farming system. Section 3 analyzes the structure of land ownership created through land distribution by Krom Samakki. Section 4 studies the actualities of tenant farming. Section 5 examines the changes of the land ownership structure during a decade years after the distribution of Krom Samakki. This paper concludes that the legacy of Krom Samakki started to fade as early as the 1990s.

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This paper investigates the impact of land rental market development on the efficiency of labor allocation and land utilization in rural China. To test the hypothesis that the shadow wage of a rent-in household with limited off-farm opportunities will increase with the development of a land rental market for households, a statistical comparison between the shadow wage and the estimated market wage was conducted. The results showed that the shadow wage for both rent-in households and non-rent-in households was significantly lower than the market wage, but that the wage for the rent-in households was statistically higher than that for non-rent-in households in Fenghua and Deqing, the two counties surveyed in this study. In addition, the estimated marginal product of farmland for rent-in households was statistically higher than the actual land rent that those households paid, while a null hypothesis that the actual rental fee accepted by rent-out households is equivalent to the marginal product of farmland for those households was not rejected in Fenghua county where land transactions by mutual agreement were more prevalent. These results indicate that the development of the land rental market facilitates the efficiency of labor allocation and farmland utilization in rural China.

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Agricultural cooperatives in China, known as Farmers' Professional Cooperatives (FPCs), are becoming popular and have been intensely promoted by the Chinese government to improve the economic welfare of small farmers. However, very few studies on Chinese agricultural cooperatives have measured the benefits to farmers who participate in FPCs after controlling for time-invariant attributes of farmers. This paper investigates the treatment effect of participation in a rice-producing cooperative in suburban China using propensity score matching (PSM) and difference-in-differences (DID) method. Estimated results show that no significant difference is observed between participants and non-participants of the cooperative in terms of net income from rice production when controlling for the difference in farmers' rice incomes before the treatment. In addition, there is no significant heterogeneity of the treatment effects between large and small farmers, although the probability of participation in the cooperative is significantly higher when the size of cultivated rice farmland is greater. These results indicate that the benefits of the cooperative appear to be overestimated considering the vigorous policy supports for FPCs from the Chinese government.

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The bridge over the Mittellandkanal is located in the municipality of Braunschweig, a city of Low Saxony located in Mid-North Germany, between Berlin and Hannover, 50 km away from this last city. The city of Braunschwig has 248.867 inhabitants (December 2010). The orography of the zone is practically even, with some slopes in the surrounding area, with a no important variation of the ground elevation, characterized by a big uniformity and a great visual quality. In this zone the canal flows from west to east, from the Dortmundkanal until the Elbe river, so it has a length of 325,3 km. The normal flora from the zone is farmland with some little forests not very big and not very important. But the Mittellandkanal lies at the North of Brauschweig, that means that in the zone of the canal there is a change between the urban area and the rural area. For this reason in the zone of the bridge we start to find farmlands and forest, however the constructions and buildings are still present in this area. The railway line that is going to be built will unite the North-center of Germany with the North-East of Germany because some of the following factors: •Overstress of the only existing line in the moment that connects Berlin with the North-East extreme of Germany. •No direct connection with the North-Easth Germany with other important German cities from South and West of Germany. •Replacement of the old existing one way line in the area that has to be renewed. •Modernization of the old railway lines of Germany. Schedule order by the European Union and the German Government. The actual lines of the zone do not have the necessary conditions and characteristics to satisfy the demand of the travelers that want to travel all over Germany with the railway avoiding using other transports like plan or car. For these reasons the necessity of the replacement of the old railway line and the aim to create a union with the North-East Germany that has a deficit of transport infrastructures and connections with the rest of the country and Europe. Although the new railway line provokes some disadvantages when constructing it is indispensable to build this railway line. The pass of the railway line through Braunschweig has not been random. The zone Braunschweig-Wolfsburg is a very industrialized area because of some companies like Wolkswagen and too because this zone is an important pass of important line from Berlin, South and East Germany. For all of these reasons the railway line goes through Braunschweig and connects to the city of Wolfsburg first, and after the North-East Germany zone.

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El presente proyecto pretende mostrar las posibilidades de la recarga artificial como elemento de gestión de los recursos de agua subterránea del acuífero aluvial del río Llobregat, en su sector de la Cubeta de Sant Andreu de la Barca (Barcelona), el cual es fuente de abastecimiento urbano, agrícola e industrial del entorno de Sant Andreu de la Barca. Igualmente, se revisa la efectividad de la aplicación de dicha técnica que se practica actualmente. Hace años, las condiciones naturales del río hacían posible la recarga natural de la Cubeta, pero la implantación de industrias en la zona y la regulación mediante la presa de La Baells desde el año 1976, han originado cambios en el comportamiento natural del acuífero, que se han manifestado básicamente en una disminución de la recarga natural como consecuencia de la impermeabilización de los suelos originada por la urbanización de los mismos. Se ha producido también un fenómeno de colmatación del lecho del río, al dificultarse la removilización de los materiales finos depositados en el fondo del cauce, produciendo también una disminución de la recarga al acuífero a través del lecho. Por último, la mayor demanda de suministro por parte del sector industrial ha influido negativamente en el almacenamiento del acuífero. Desde hace décadas, se lleva efectuando una recarga artificial en el lecho del río para tratar de paliar en lo posible estos efectos perjudiciales. La misma se efectúa mediante dos sistemas distintos: escarificando el lecho del río para aumentar su capacidad de infiltración, y mediante la utilización de balsas de recarga, a través de las cuales se infiltra el agua en el acuífero. El objetivo de este proyecto es analizar el efecto actual que la recarga mediante balsas está teniendo sobre el acuífero. Para ello, se utilizarán, entre otras técnicas, la elaboración de un modelo matemático con el que poder simular el efecto de la recarga. VIII ABSTRACT This project aims to show the possibilities of artificial recharge as groundwater resources management element in the alluvial aquifer of the Llobregat River, in the sector of the Basin of Sant Andreu de la Barca (Barcelona), which is a source of urban, agricultural and industrial supply of the Sant Andreu de la Barca area. Too, the effectiveness of the current implementation of this technique is reviewed. Years ago, natural river conditions made possible the natural recharge of the aquifer, but the establishment of industries in the area and the river regulation by the la Baells dam since 1976, have led to changes in the natural behavior of the aquifer, which basically are a decrease in natural recharge, because the soil has become impervious, due to land urbanization. There has been also a phenomenon of clogging of the river bed, caused by the difficult in the remobilization of fine materials deposited on the river bed, which has produced a decrease in the groundwater recharge through the river. Finally, the increase in water demand by the industrial sector, has diminished aquifer storage. For decades, artificial recharge in the river bed has been practiced to alleviate negative effects. It is done by two different systems: scratching the river bed to increase its infiltration capacity, and using recharge ponds, through which water infiltrates into the aquifer. The objective of this project is to analyze the current effect that recharge by ponds is having in the aquifer. Among other techniques, mathematical modeling has been used for simulating the effect of artificial recharge in the aquifer.

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El ser humano nunca ha tenido una capacidad semejante a la actual para alterar el medio en el que vive. A través fundamentalmente de cambios en el uso del hábitat, alteración de los ciclos biogeoquímicos, cambio climático y presencia de especies invasoras, la tasa de extinción de especies se ha acelerado enormemente. Al crecer más rápido la población humana dentro de las áreas en las que se concentra una mayor biodiversidad (biodiversity hotspots), las tasas de transformación son mayores, por lo que dicha biodiversidad se encuentra más amenazada. Entre los principales 25 biodiversity hotspots globales se encuentra la cuenca mediterránea. Las afecciones a la biodiversidad hacen por tanto que en dicha cuenca mediterránea sea necesario poner en práctica iniciativas innovadoras para su conservación. Pero además de una cuidadosa selección, es necesario el seguimiento y la evaluación de la eficacia y la eficienca de dichas medidas, para comprobar su idoneidad y mejorarlas cuando sea posible. Esta es la tarea de la ingeniería de la conservación. Esta Memoria busca analizar y proponer mejoras en cuatro acciones experimentales de conservación de la biodiversidad que tienen un marco común, la conservación de especies subrogadas del monte mediterráneo. En concreto de cinco especies amenazadas: conejo de monte (Oryctolagus cuniculus, especie llave), águila imperial ibérica (Aquila adalberti), águila perdicera (Aquila fasciata), cigüeña negra (Ciconia nigra) y lince ibérico (Lynx pardinus), todas ellas especies paraguas y bandera. Casi todas estas especies se enfrentan a amenazas comunes, como son la pérdida de la calidad del hábitat, la mortalidad de origen humano, la escasez de alimento o la falta de eficiencia en las técnicas de seguimiento. Las acciones destinadas a revertir o minimizar estas amenazas han tenido un marco geográfico y ecológico común, 49 fincas privadas de monte mediterráneo situadas en 9 espacios de la Red Natura 2000 del centro-occidental peninsular, en las que se ha podido trabajar merced a acuerdos de custodia del territorio. Dichas actividades han sido financiadas casi por completo con cargo a fondos LIFE Naturaleza de la Comisión Europea. El presente documento contribuye a aportar el conocimiento científico imprescindible para mejorar la eficacia y eficiencia de las medidas técnicas de gestión y conservación: la ingeniería de la conservación. Como resultados más relevantes se pueden citar que la selección del conejo de las zonas sembradas aumenta con la presencia tanto de isletas de matorral como de refugios y resulta inferior en las zonas de matorral más cerrado; que la electrocución es una de las principales causas de mortalidad de las rapaces amenazadas, así como que se ha detectado que la mortalidad se concentra en determinadas zonas que deben ser prioritarias para su corrección y que éstas deben pasar por las modificaciones estructurales; que la selección de zonas de alimentación por parte de la cigüeña negra se ve afectada por numerosos factores y que una adecuada ubicación y gestión de las charcas para ganadería y caza mayor puede favorecer no sólo la alimentación de esta especie, sino suponer un lugar de cría para diversas especies de anfibios y peces autóctonos, en franco declive; finalmente, hay que destacar que la mejora en el seguimiento de las poblaciones de lince ibérico pasa por la incorporación de métodos de seguimiento novedosos, como las cámaras infrarrojas en letrinas, dada la capacidad de aprendizaje de la especie. Abstract Nowadays the human being has reached its top ability to exchange its environment. Mainly through habitat change, altering biogeochemical cycles, climatic change and alien species, global extinction rate has increased dramatically. Population increases faster in biodiversity hotspots, thus change rates are higher. Mediterranean basin is included within the 25 most valuable biodiversity hotspots. Affections on biodiversity turns necessary to develop innovative actions to maintain the most threatened species in this hotspot. But further than a careful selection and implementarion, survey and evaluation of those practices is necessary to check its suitability. Those are actions for the conservation engineering. This Memory looks for to analyze and to put forward improvements in four experimental biodiversity conservation actions with a common framework: conservation of surrogate Mediterranean species. Those actions were specifically directed to five threatened species: the European wild rabbit (Oryctolagus cuniculus, key species), Spanish imperial eagle (Aquila adalberti) and Bonelli’s eagle (Aquila fasciata, both of the umbrella and flagship species), black stork (Ciconia nigra, umbrella and flagship species) and the Iberian lynx (Lynx pardinus, umbrella and flagship species). Those species have common threats: habitat loss, maninduced mortality, food shortening and lack of surveying efficiency. Actions aimed to minimize those threats also had a common geographical frame: 49 privately owned states within 9 Natura 2000 areas in Southwestern Spain. Actions were developed through lands tewardship agreements, and were even wholly undertaken through European Commision LIFE’s fund. This document contributes to develop cientific knowledge necessary for increasing efficacy and efficiency for implementing technical measures devoted to conservation, the conservation engineering. One of the most outstanding result might be the necessity of including bushy islets or rabbit shelter within sowings when enhacing rabbit populations is the goal. Electrocution is one of the commonest man-induced death causes for raptors, especially for the threatened ones. Areas of concentration of this mortality have been detected, and when mitigation measures have been evaluated, only structural modifications had results. The black stork’s selection of feeding areas is influenced by several factors. An adequate location and management of livestock’s ponds can favour not only this species, but also creating new breeding places for amphibians and indigenous fish species, most of them in a sharp decline. Finally, improving the survey of the Iberian lynx might be achieved through implementing newly developed surveying systems, such as the infrared cameras in latrines.

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Improved management of nitrogen (N) in agriculture is necessary to achieve a sustainable balance between the production of food and other biomass, and the unwanted effects of N on water pollution, greenhouse gas emissions, biodiversity deterioration and human health. To analyse farm N-losses and the complex interactions within farming systems, efficient methods for identifying emissions hotspots and evaluating mitigation measures are therefore needed. The present paper aims to fill this gap at the farm and landscape scales. Six agricultural landscapes in Poland (PL), the Netherlands (NL), France (FR), Italy (IT), Scotland (UK) and Denmark (DK) were studied, and a common method was developed for undertaking farm inventories and the derivation of farm N balances, N surpluses and for evaluating uncertainty for the 222 farms and 11 440 ha of farmland included in the study. In all landscapes, a large variation in the farm N surplus was found, and thereby a large potential for reductions. The highest average N surpluses were found in the most livestock-intensive landscapes of IT, FR, and NL; on average 202 ± 28, 179 ± 63 and 178 ± 20 kg N ha−1 yr−1, respectively. All landscapes showed hotspots, especially from livestock farms, including a special UK case with large-scale landless poultry farming. Overall, the average N surplus from the land-based UK farms dominated by extensive sheep and cattle grazing was only 31 ± 10 kg N ha−1 yr−1, but was similar to the N surplus of PL and DK (122 ± 20 and 146 ± 55 kg N ha−1 yr−1, respectively) when landless poultry farming was included. We found farm N balances to be a useful indicator for N losses and the potential for improving N management. Significant correlations to N surplus were found, both with ammonia air concentrations and nitrate concentrations in soils and groundwater, measured during the period of N management data collection in the landscapes from 2007–2009. This indicates that farm N surpluses may be used as an independent dataset for validation of measured and modelled N emissions in agricultural landscapes. No significant correlation was found with N measured in surface waters, probably because of spatial and temporal variations in groundwater buffering and biogeochemical reactions affecting N flows from farm to surface waters. A case study of the development in N surplus from the landscape in DK from 1998–2008 showed a 22% reduction related to measures targeted at N emissions from livestock farms. Based on the large differences in N surplus between average N management farms and the most modern and N-efficient farms, it was concluded that additional N-surplus reductions of 25–50%, as compared to the present level, were realistic in all landscapes. The implemented N-surplus method was thus effective for comparing and synthesizing results on farm N emissions and the potentials of mitigation options. It is recommended for use in combination with other methods for the assessment of landscape N emissions and farm N efficiency, including more detailed N source and N sink hotspot mapping, measurements and modelling.

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The aim was to measure the behaviour of various mortars employed in livestock media in central Spain and to analyse the aggressiveness of pig slurry to cement blended with fly ash mortars. To achieve this, mortar specimens were immersed in ponds storing pig slurry. Mortar specimens, of 40 ? 40 ? 160 mm, were made from four types of cement commonly used and recommended for rural areas. The types were a sulphate-resistant Portland cement and three cements blended in different proportions with fly ash and limestone filler. After 3, 6, 12, 24, 36, 48 and 60 months of exposure, three or four specimens of each cement type were removed from the pond and washed with water. Their compressive strength and microstructure (X-ray diffraction, mercury intrusion pore-symmetry, thermal analysis and scanning electron microscopy) were then measured. Sulphate-resistant Portland cement (SR-PC), found to be more susceptible to degradation due to its greater proportion of macro-pores and increased total porosity, was found not to be suitable for use with livestock. After 60 months of immersion in the pig slurry medium, CEM II-A (40.3%) mortar retained the greatest compressive strength. Mortars with less than 20% replacement of cement by fly ash were found to be the most durable, with the most suitable mechanical behaviour.

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Water is fundamental to human life and the availability of freshwater is often a constraint on human welfare and economic development. Consequently, the potential effects of global changes on hydrology and water resources are considered among the most severe and vital ones. Water scarcity is one of the main problems in the rural communities of Central America, as a result of an important degradation of catchment areas and the over-exploitation of aquifers. The present Thesis is focused on two critical aspects of global changes over water resources: (1) the potential effects of climate change on water quantity and (2) the impacts of land cover and land use changes on the hydrological processes and water cycle. Costa Rica is among the few developing countries that have recently achieved a land use transition with a net increase in forest cover. Osa Region in South Pacific Costa Rica is an appealing study site to assess water supply management plans and to measure the effects of deforestation, forest transitions and climate change projections reported in the region. Rural Community Water Supply systems (ASADAS) in Osa are dealing with an increasing demand of freshwater due to the growing population and the change in the way of life in the rural livelihoods. Land cover mosaics which have resulted from the above mentioned processes are characterized by the abandonment of marginal farmland with the spread over these former grasslands of high return crops and the expansion of secondary forests due to reforestation initiatives. These land use changes have a significant impact on runoff generation in priority water-supply catchments in the humid tropics, as evidenced by the analysis of the Tinoco Experimental Catchment in the Southern Pacific area of Costa Rica. The monitoring system assesses the effects of the different land uses on the runoff responses and on the general water cycle of the basin. Runoff responses at plot scale are analyzed for secondary forests, oil palm plantations, forest plantations and grasslands. The Oil palm plantation plot presented the highest runoff coefficient (mean RC=32.6%), twice that measured under grasslands (mean RC=15.3%) and 20-fold greater than in secondary forest (mean RC=1.7%). A Thornthwaite-type water balance is proposed to assess the impact of land cover and climate change scenarios over water availability for rural communities in Osa Region. Climate change projections were obtained by the downscaling of BCM2, CNCM3 and ECHAM5 models. Precipitation and temperature were averaged and conveyed by the A1B, A2 and B1 IPCC climate scenario for 2030, 2060 and 2080. Precipitation simulations exhibit a positive increase during the dry season for the three scenarios and a decrease during the rainy season, with the highest magnitude (up to 25%) by the end of the 21st century under scenario B1. Monthly mean temperature simulations increase for the three scenarios throughout the year with a maximum increase during the dry season of 5% under A1B and A2 scenarios and 4% under B1 scenario. The Thornthwaite-type Water Balance model indicates important decreases of water surplus for the three climate scenarios during the rainy season, with a maximum decrease on May, which under A1B scenario drop up to 20%, under A2 up to 40% and under B1 scenario drop up to almost 60%. Land cover scenarios were created taking into account current land cover dynamics of the region. Land cover scenario 1 projects a deforestation situation, with forests decreasing up to 15% due to urbanization of the upper catchment areas; land cover scenario 2 projects a forest recovery situation where forested areas increase due to grassland abandonment on areas with more than 30% of slope. Deforestation scenario projects an annual water surplus decrease of 15% while the reforestation scenario projects a water surplus increase of almost 25%. This water balance analysis indicates that climate scenarios are equal contributors as land cover scenarios to future water resource estimations.

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The Barriga Dam (Burgos, Spain) is a unique case study because its trapezoid spillway is located on the dam body and is composed of wedge-shaped concrete blocks (WSB) that include certain relevant improvements. This note summarizes the main features of the studies, the key aspects of the final design of the WSB and their placement on the dam, and important details of the spillway design. The design team concluded the study by showing the suitability of this enhanced technology for application to small dams and ponds in the short term, even with unit flows above 5 m2/s.

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La pérdida de bosques en la Tierra, principalmente en ecosistemas amazónicos, es un factor clave en el proceso del cambio climático. Para revertir esta situación, los mecanismos REDD (Reducing Emission from Deforestation and forest Degradation) están permitiendo la implementación de actividades de protección del clima a través de la reducción de emisiones por deforestación evitada, según los esquemas previstos en el Protocolo de Kioto. El factor técnico más crítico en un proyecto REDD es la determinación de la línea de referencia de emisiones, que define la expectativa futura sobre las emisiones de CO2 de origen forestal en ausencia de esfuerzos adicionales obtenidos como consecuencia de la implementación del programa REDD para frenar este tipo de emisiones. La zona del estudio se ubica en la región de San Martín (Perú), provincia cubierta fundamentalmente por bosques tropicales cuyas tasas de deforestación son de las más altas de la cuenca amazónica. En las últimas décadas del siglo XX, la región empezó un acelerado proceso de deforestación consecuencia de la integración vial con el resto del país y la rápida inmigración desde zonas rurales en busca de nuevas tierras agrícolas. Desde el punto de vista de la investigación llevada a cabo en la tesis doctoral, se pueden destacar dos líneas: 1. El estudio multitemporal mediante imágenes de satélite Landsat 5/TM con el propósito de calcular las pérdidas de bosque entre períodos. El estudio multitemporal se llevó a cabo en el período 1998-2011 utilizando imágenes Landsat 5/TM, aplicando la metodología de Análisis de Mezclas Espectrales (Spectral Mixtures Analysis), que permite descomponer la reflectancia de cada píxel de la imagen en diferentes fracciones de mezcla espectral. En este proceso, las etapas más críticas son el establecimiento de los espectros puros o endemembers y la recopilación de librerías espectrales adecuadas, en este caso de bosques tropicales, que permitan reducir la incertidumbre de los procesos. Como resultado de la investigación se ha conseguido elaborar la línea de referencia de emisiones histórica, para el período de estudio, teniendo en cuenta tanto los procesos de deforestación como de degradación forestal. 2. Relacionar los resultados de pérdida de bosque con factores de causalidad directos e indirectos. La determinación de los procesos de cambio de cobertura forestal utilizando técnicas geoespaciales permite relacionar, de manera significativa, información de los indicadores causales de dichos procesos. De igual manera, se pueden estimar escenarios futuros de deforestación y degradación de acuerdo al análisis de la evolución de dichos vectores, teniendo en cuenta otros factores indirectos o subyacentes, como pueden ser los económicos, sociales, demográficos y medioambientales. La identificación de los agentes subyacentes o indirectos es una tarea más compleja que la de los factores endógenos o directos. Por un lado, las relaciones causa – efecto son mucho más difusas; y, por otro, los efectos pueden estar determinados por fenómenos más amplios, consecuencia de superposición o acumulación de diferentes causas. A partir de los resultados de pérdida de bosque obtenidos mediante la utilización de imágenes Landsat 5/TM, se investigaron los criterios de condicionamiento directos e indirectos que podrían haber influido en la deforestación y degradación forestal en ese período. Para ello, se estudiaron las series temporales, para las mismas fechas, de 9 factores directos (infraestructuras, hidrografía, temperatura, etc.) y 196 factores indirectos (económicos, sociales, demográficos y ambientales, etc.) con, en principio, un alto potencial de causalidad. Finalmente se ha analizado la predisposición de cada factor con la ocurrencia de deforestación y degradación forestal por correlación estadística de las series temporales obtenidas. ABSTRACT Forests loss on Earth, mainly in Amazonian ecosystems, is a key factor in the process of climate change. To reverse this situation, the REDD (Reducing Emission from Deforestation and forest Degradation) are allowing the implementation of climate protection activities through reducing emissions from avoided deforestation, according to the schemes under the Kyoto Protocol. Also, the baseline emissions in a REDD project defines a future expectation on CO2 emissions from deforestation and forest degradation in the absence of additional efforts as a result of REDD in order to stop these emissions. The study area is located in the region of San Martín (Peru), province mainly covered by tropical forests whose deforestation rates are the highest in the Amazon basin. In the last decades of the twentieth century, the region began an accelerated process of deforestation due to road integration with the rest of the country and the rapid migration from rural areas for searching of new farmland. From the point of view of research in the thesis, we can highlight two lines: 1. The multitemporal study using Landsat 5/TM satellite images in order to calculate the forest loss between periods. The multitemporal study was developed in the period 1998-2011 using Landsat 5/TM, applying the methodology of Spectral Mixture Analysis, which allows decomposing the reflectance of each pixel of the image in different fractions of mixture spectral. In this process, the most critical step is the establishment of pure spectra or endemembers spectra, and the collecting of appropriate spectral libraries, in this case of tropical forests, to reduce the uncertainty of the process. As a result of research has succeeded in developing the baseline emissions for the period of study, taking into account both deforestation and forest degradation. 2. Relate the results of forest loss with direct and indirect causation factors. Determining the processes of change in forest cover using geospatial technologies allows relating, significantly, information of the causal indicators in these processes. Similarly, future deforestation and forest degradation scenarios can be estimated according to the analysis of the evolution of these drivers, taking into account other indirect or underlying factors, such as economic, social, demographic and environmental. Identifying the underlying or indirect agents is more complex than endogenous or direct factors. On the one hand, cause - effect relationships are much more diffuse; and, second, the effects may be determined by broader phenomena, due to superposition or accumulation of different causes. From the results of forest loss obtained using Landsat 5/TM, the criteria of direct and indirect conditioning that might have contributed to deforestation and forest degradation in that period were investigated. For this purpose, temporal series, for the same dates, 9 direct factors (infrastructure, hydrography, temperature, etc.) and 196 underlying factors (economic, social, demographic and environmental) with, in principle, a high potential of causality. Finally it was analyzed the predisposition of each factor to the occurrence of deforestation and forest degradation by statistical correlation of the obtained temporal series.

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El Anillo Verde metropolitano, definido por el Plan General de Ordenación Urbana del Área Metropolitana de Madrid en 1963 siguiendo los modelos planteados por la cultura urbanística internacional, como armadura de la estructura urbana del AMM, espacio protagonista dentro del sistema de espacios libres, lugar de uso público destinado al recreo y contacto con la naturaleza de la población madrileña, se convierte en realidad en una reserva de suelo que va entrando en juego motivado por las alianzas entre el poder institucional y la clase social dominante actuando al margen del planeamiento, poniendo en evidencia la escasez de recursos legales y culturales disponibles para la salvaguarda de los intereses comunes y, donde los condicionantes geográficos y naturales del territorio madrileño han influido decisivamente en la especialización funcional y espacial del Área Metropolitana de Madrid. Así pues considerando esta idea como HIPÓTESIS, el objetivo de la TESIS sería demostrarla, para lo cual se hace necesario primero, acotar espacial y temporalmente el objeto de estudio, es decir, del Anillo Verde metropolitano1, segundo, contextualizar histórica y disciplinarmente los presupuestos teóricos que conformaban la idea del Anillo Verde, tercero, reconocer, localizar y documentar las piezas que han ido materializando la ocupación urbana del Anillo Verde, clasificándolas según parámetros temporales, funcionales, urbanísticos y, formales, lo que permite analizar la geografía, uso, instrumentación y forma de su transformación a escala general metropolitana y, cuarto, profundizar a modo de comprobación a escala municipal y urbana en dos escenarios representativos del conjunto metropolitano: el municipio de Pozuelo de Alarcón y el distrito de Hortaleza-Barajas. El contenido del documento se divide en tres bloques, el bloque I, se centra en las bases teóricas, el bloque II sitúa el hilo argumental de la tesis a escala metropolitana y el bloque III comprueba el fenómeno a escala municipal y urbana. De esta forma, se comienza por la comprensión del significado del concepto del Anillo Verde, que va más allá de la dimensión instrumental asignada de límite y contención urbana frente al crecimiento de la ciudad industrial de principios del siglo XX, basada en la descentralización de la ciudad tradicional, para adquirir un significado más complejo, como gran espacio de reserva y salvaguarda de valores naturales y culturales que se expresaban en su territorio y que permitirían alcanzar el equilibrio entre la ciudad y sus habitantes, es decir, entre el hombre y el espacio que habita. Se hace un recorrido por las principales corrientes urbanísticas que se van nutriendo de distintas disciplinas (economía, sociología, geografía, biología, ecología) para plantear teorías que permitieran materializar un nuevo orden urbano según principios de equidad social, económica y ambiental, en una secuencia donde Europa y Estados Unidos realizaban un constante intercambio -el movimiento de la Ciudad Jardín o el Regionalismo, que dieron paso a propuestas como el Greater London o el Gran Berlín, donde la figura del Anillo Verde tenía un papel protagonista, y del que también participaría nuestro país y la ciudad de Madrid, con modelos regionales como el Plan Besteiro y urbanos como el Plan Bidagor, antecedentes directos del Plan General de Ordenación Urbana del Área Metropolitana de Madrid de 1963 que pone en marcha la ordenación del crecimiento metropolitano de Madrid. El hilo argumental de la tesis se organiza en una doble aproximación: un acercamiento a escala metropolitana a partir del reconocimiento del modelo de ciudad definido en los distintos planes generales que acompañaron el desarrollo metropolitano (municipio de Madrid y de los siete términos municipales que rodeaban a este y que tenían suelo destinado a Anillo Verde), haciendo referencia además a las relaciones con el planeamiento regional, concretando en una escala de aproximación municipal que avanza hasta la interpretación urbana detallada. El primer acercamiento tiene lugar en el bloque II y se organiza en tres capítulos. El capítulo 4 se dedica al punto obligado de partida de la geografía local, describiendo las características biofísicas de los terrenos que formaban parte del Anillo Verde, que han marcado históricamente la forma de aprovechamiento del territorio, desde las extensiones de bosques mediterráneos al norte y al oeste continuación del Monte del Pardo, a los distintos tipos de cultivo que se adaptaban al sustrato geológico y la forma del terreno (de las suaves ondulaciones de sedimentos arcósicos al norte a las extensas plataformas arenosas y yesíferas del sur), además de las zonas de huertos aprovechando las depresiones y los cursos de agua (arroyo del Monte Carmelo, arroyo de Valdebebas, arroyo del Quinto, arroyo del Santo, arroyo Butarque, arroyo Meaques y arroyo Pozuelo). Una vez reconocida la realidad física, el capítulo 5, avanza en la descripción de los distintos modelos de ciudad propuestos desde el planeamiento urbanístico, en sus distintas escalas, la regional y la municipal, como respuesta a la coyuntura social, económica y política que ha caracterizado el proceso de ocupación del Anillo Verde al compás de la construcción del AMM. Se han reunido las propuestas de planeamiento municipal de los distintos municipios que disponían de terreno calificado como Anillo Verde: Madrid, Coslada, Getafe, Leganés, Alcorcón, Boadilla del Monte y Pozuelo de Alarcón. Además se han incorporado las distintas propuestas de ordenación territorial que han servido de referencia al planeamiento municipal, en todas sus versiones, desde las sectoriales, de mayor éxito y apoyo institucional, a los distintos intentos de ordenación integral, de mayor complejidad pero de menor calado, precisamente por la dificultad de consenso entre la ordenación física y el desarrollo económico, entre los intereses privados y el beneficio público. El primer horizonte, comienza con la formulación del Plan General de Ordenación Urbana del Área Metropolitana de Madrid de 1963, su desarrollo y la puesta en marcha de los primeros planes municipales en la década de los años setenta, donde se comprueba la necesidad de un marco regional que “ordene” el territorio de forma integral y sirva de referencia a las actuaciones sectoriales que habían marcado el primer desarrollo metropolitano. El segundo, se sitúa dos décadas más tarde con la aprobación del Plan General de Ordenación Urbana de Madrid de 1985 y el conjunto de planes municipales de los términos limítrofes, que siguen su filosofía de austeridad en cuanto a crecimiento territorial. El tercero se inicia en 1997 con la siguiente generación de planes de corte neoliberal que imponen un modelo territorial basado en las grandes operaciones metropolitanas de centralidad, infraestructuras y equipamiento, que consumen de forma indiscriminada la totalidad del territorio madrileño. Será en el último capítulo del segundo bloque (capítulo 6) donde se represente gráficamente a escala metropolitana y se analicen las 229 piezas que han ido colmatando el espacio destinado a Anillo Verde, según los parámetros de estudio, en base a las cuales se plantean las primeras conclusiones generales de la tesis, poniendo de manifiesto que las alianzas entre los agentes soberanos en la construcción de la ciudad y su entorno han trasgredido sucesivamente las determinaciones del Planeamiento en su definición de modelo de ciudad y territorio, acusando la carencia de recursos instrumentales y jurídicos que alentaron el proceso de su desmantelamiento, y revelando la influencia de los condicionantes geográficos y naturales en la especialización funcional y segregación social en el conjunto del Área Metropolitana de Madrid. Se remata el discurso metropolitano con una batería de conclusiones que interpretan el fenómeno de ocupación del anillo de verdor metropolitano confirmando las hipótesis iniciales, reconociendo los valores medioambientales y culturales trasgredidos, sus diversos actores, las numerosas operaciones urbanísticas desarrolladas con distintos usos y envergadura, así como los instrumentos de planeamiento utilizados, en base a las cuales se materializa la construcción del AMM según un modelo extendido (spread), dibujando una mancha de aceite (o grase-spots según Geddes) que precisamente había querido evitarse desde el planeamiento urbanístico con la definición de un Anillo Verde, espacio inmune a la edificación, que se aleja de su papel estructurante (equilibrador entre la ciudad y sus habitantes) para convertirse en armadura de la estructura comunicativa, que una vez consolidada se convierte en la mejor aliada de la máquina inmobiliaria. El último paso, se desarrolla en el bloque III que se divide en los capítulo 7,8 y 9 y supone la comprobación de lo descrito en el conjunto de escala metropolitana, en dos aspectos fundamentales, la falta de consideración por los valores culturales y medioambientales que han modelado el territorio, imprimiéndole un carácter singular y específico y, la estructura del dominio del suelo, donde se reconoce de forma precisa el grupo social y los agentes encargados en cada momento de comercializar los suelos del anillo, que bajo el paraguas de la urgencia social y el engañoso beneficio popular, obtienen importantes beneficios económicos. Con esa intención, se da un salto hacia la escala municipal y urbana, seleccionando dos escenarios de estudio, el municipio de Pozuelo de Alarcón, que representa la materialización del crecimiento suburbano de la élite madrileña ocupando las zonas de mayor valor ecológico del anillo, y el distrito de Hortaleza-Barajas que ofrece su territorio a las grandes operaciones metropolitanas, apoyándose en el eje de actividad marcado por la conexión Madrid-Barcelona y el sistema aeroportuario de escala global, ambos situados al norte de la línea de borde entre la Sierra y la Mancha, ocupando por tanto los lugares más valiosos de la geografía madrileña (estructura funcional anticipada por Bidagor en 1946 en su modelo de ciudad adaptada al territorio madrileño) Una vez descrito este proceso trasgresor de límites, de normas, de conductas, y desde una perspectiva del fenómeno suficientemente documentada, en el capítulo 10, se realiza una reflexión sobre la incidencia real de la propuesta urbanística del Anillo Verde en la construcción del AMM, de la misma forma que se sugieren nuevos roles al planeamiento en un formato intencionado de largo recorrido en oposición a lo inmediato y circunstancial, que permita hacer una nueva lectura de los presupuestos teóricos que conformaban la idea del Anillo Verde, espacio articulador (medioambiental, social y cultural) del territorio madrileño. ABSTRACT The Metropolitan Greenbelt was defined by the 1963 Master Plan for the Madrid Metropolitan Area (MMA), following established international models of urban development, as the structural framework of the MMA, the principal open space within its network of open spaces and a public area of recreation and contact with nature for the residents of Madrid. In reality, however, it ha become a reserve of land in which various alliances between the institutional authorities and the dominant social class have been operating on the margin of the original plan, exposing a scarcity of legal and cultural resources for the safeguarding of common interests, and in which the geographical and natural characteristics of the territory itself have come to play an influential role in the functional specialization and spatial segregation of the MMA. With that idea as its HYPOTHESIS, the aim of this THESIS is to demonstrate its reality. The first step in this is to delineate, temporally and spatially, the object of study; i.e. the Metropolitan Greenbelt2. The second is to contextualize historically and disciplinarily those theoretical ideas which conform to the greenbelt concept. The third is to acknowledge, locate and document the elements which have characterized the urban occupation of the Greenbelt and classify these according to the parameters of time, function, urban development and form, which in turn would enable the geography, use, instrumentation and form of its transformation to be analysed on a general metropolitan scale. The fourth step, as a method of verification, is an in-depth analysis of two representative settings within the metropolitan network: the municipality of Pozuelo de Alarcón and the Hortaleza-Barajas district. The content of the document is divided into three parts. Part I focuses on the study’s theoretical foundations, Part II establishes a line of argument at the metropolitan level and Part III examines the phenomenon from a municipal and urban perspective. The thesis, then, begins with a study of the greenbelt concept itself and its meaning, which is far more complex than the accepted instrumental dimension of limiting and containing urbanization in response to the growth of the industrial city of the early 20th century, and which is based on a decentralization of the traditional city. This wider purpose is the setting aside of a large reserved space to safeguard the natural and cultural values of the region and thereby achieve a balance between the city and its residents; that is to say, between man and the space he inhabits. The principal currents of thought in urban planning will then be examined. These have drawn upon a variety of disciplines (economics, sociology, geography, biology, ecology) to develop theories for establishing a new urban order according to the principles of social, economic and environmental equity, and have involved a constant interchange between Europe and the United States. Thus, the City Garden and Regionalist movements would clear the way for proposals such as Greater London and Great Berlin, Chicago and Washington, in which the greenbelt would play a fundamental role. The participation of our own country and the city of Madrid is also discussed, through regional models such as the Besteiro Plan and urban ones like the Bidagor Plan, direct forerunners of 1963’s General Organizational Plan for the Madrid Metropolitan Area, which would set into motion the organization of Madrid’s metropolitan growth. The line of argument followed in this thesis is two-fold: first, an examination of metropolitan development in keeping with the city model as defined in the various General Plans for the development of both the municipality of Madrid and the seven surrounding municipalities which have land designated for its Greenbelt; and second, an examination of this growth in relation to Regional Planning measures, is detailed on a smaller scale (municipal and district), where the conditioning factors affecting the land property structure and the network of biophysical units may be analysed in depth. The first of these is dealt with in Part II and organized into three chapters (4, 5 and 6). Chapter 4 is dedicated to the obligatory starting point of the geographical setting itself. The biophysical characteristics of the territories set aside for the Greenbelt, and which historically have played a role in the area’s exploitation, are described here. These range from expanses of Mediterranean woodland to the north and west of Monte del Pardo to the various types of farmland that have been adapted to the geological substratum and the contours of the terrain (gentle undulations of arkosic sediment in the north, and wide sandy and gypsiferous tableland in the south), as well as orchards planted in low valleys and along watercourses (the creeks of Monte Carmelo, Valdebebas, Quinto, Santo, Butarque, Meaques and Pozuelo). Once this physical reality ha been detailed, in Chapter 5 will examine the various city models proposed by urban planners, both regionally and municipally, in response to the confluence of social, economic and political interests that have characterized the process of occupation in the Greenbelt area during the construction of the MMA. Municipal planning proposals will be collected and examined for the various municipalities which have land designated for the Greenbelt: Madrid, Coslada, Getafe, Leganés, Alcorcón, Boadilla del Monte and Pozuelo de Alarcón. Furthermore, the various territorial organization proposals which have served as references for municipal planning will also be addressed here, in all of their versions –from the sectorial, which have met with more success and institutional approval, to the many attempts at integration, which have been more complex but less influential, precisely for the difficulty of reconciling physical organization with economic development, and private interest with public benefit. The first period in this process was the development of the General Plan of 1963, followed by the first municipal development plans of the 1970s, in which the need for a regional framework that “organized” the territory in an integral fashion was defined. This would serve as a reference for the sectorial actions that marked the metropolitan area’s initial development. The second came two decades later with the approval of the General Plan of 1985, and the network of municipal plans for the surrounding communities, which followed the same philosophy of austerity with regard to territorial growth. The third would begin to take form in 1997, as a new generation of neo-liberal development plans imposed a territorial model based on centralized large-scale metropolitan operations of infrastructure and equipment, which would indiscriminately consume the totality of Madrid’s land. At the end of the Part II, in Chapter 6, the metropolitan area will be represented graphically and the 229 pieces that have been gradually encroaching upon land designated for the Greenbelt will be analysed. This analysis will be carried out according to the parameters defined for the study, and the first general conclusions of the thesis will be based on its findings. It will show how alliances between the various governing authorities in the construction of the city and its environment have successively violated established plans with regard to the definitions of city and territory, how shortages of instrumental and judicial resources have accentuated the dismantling process, and how natural and geographical factors have influenced functional specialization and social segregation in the Madrid Metropolitan Area. The final step, detailed in Part III, will address two fundamental aspects of what has just been described: the lack of consideration for the cultural and environmental values which have shaped this territory and imprinted upon it a specific and unique character; and the structure of land domination, with a precise identification of the social group and agents responsible at each stage of the Greenbelt’s commercialization, who, under an umbrella of social urgency and deceptive public benefit, have used it to obtain substantial financial rewards. For this purpose, a closer look is taken at two specific areas: the municipality of Pozuelo de Alarcón, representative of the suburban growth of an elite population which has occupied the Greenbelt areas of the greatest ecological value; and the Hortaleza-Barajas district, which has offered its territory to large metropolitan business interests, based on activities centred on the connection between Madrid and Barcelona and the system of international air travel. Both of these settings are located to the north of the line which divides the Sierra from La Mancha, and thus occupy the most valuable land in the Madrid region (a functional structure anticipated by Bidagor in 1946, with his city model adapted to the territory of Madrid). Finally, an attempt will be made to interpret the phenomenon of metropolitan Greenbelt occupation, confirming initial hypotheses, specifying the environmental and cultural values that have been violated, and identifying the various players involved, as well as numerous urbanization operations of varying sizes and interests, and the instruments of planning they have used. It will be seen from this that the construction of the MMA has in fact followed a “spread” model, a “grease spot” (as Geddes calls it) which, from the outset of the planning process and according to the definition of a greenbelt as a construction-free zone, was precisely to be avoided. This structural role (to provide a balance between a city and its residents) has thus been abandoned and the Greenbelt converted instead into a communicative framework which, once consolidated, has become the greatest ally of the real estate machine. After this process of violating limits, norms and established behaviour has been described and solidly documented, a reflection will be made on the real influence of the Greenbelt proposal in the construction of the MMA. At the same time, new roles will be suggested for future planning, roles which are deliberate and long term, in opposition to the immediate and circumstantial. This will enable a new interpretation of the theoretical principles behind the greenbelt concept, a space designed to connect the territory of Madrid environmentally, socially and culturally.

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El riesgo asociado a la rotura de un depósito de agua en entorno urbano (como la ocurrida, por ejemplo, en la Ciudad Autónoma de Melilla en Noviembre de 1997) y los potenciales daños que puede causar, pone en duda la seguridad de este tipo de infraestructuras que, por necesidades del servicio de abastecimiento de agua, se construyen habitualmente en puntos altos y cercanos a los núcleos de población a los que sirven. Sin embargo, la baja probabilidad de que se produzca una rotura suele rebajar los niveles de alerta asociados a los depósitos, haciéndose hincapié en la mejora de los métodos constructivos sin elaborar metodologías que, como en el caso de las presas y las balsas de riego, establezcan la necesidad de clasificar el riesgo potencial de estas infraestructuras en función de su emplazamiento y de estudiar la posible construcción de medidas mitigadoras de una posible rotura. Por otro lado, para establecer los daños que pueden derivarse de una rotura de este tipo, se hace imprescindible la modelización bidimensional de la ola de rotura por cuanto la malla urbana a la que afectaran no es susceptible de simulaciones unidimensionales, dado que no hay un cauce que ofrezca un camino preferente al agua. Este tipo de simulación requiere de una inversión económica que no siempre está disponible en la construcción de depósitos de pequeño y mediano tamaño. Esta tesis doctoral tiene como objetivo el diseño de una metodología simplificada que, por medio de graficas y atendiendo a las variables principales del fenómeno, pueda estimar un valor para el riesgo asociado a una posible rotura y sirva como guía para establecer si un deposito (existente o de nueva implantación) requiere de un modelo de detalle para estimar el riesgo y si es conveniente implantar alguna medida mitigadora de la energía producida en una rotura de este tipo. Con carácter previo se ha establecido que las variables que intervienen en la definición de riesgo asociado a la rotura, son el calado y la velocidad máxima en cada punto sensible de sufrir daños (daños asociados al vuelco y arrastre de personas principalmente), por lo que se ha procedido a estudiar las ecuaciones que rigen el problema de la rotura del depósito y de la transmisión de la onda de rotura por la malla urbana adyacente al mismo, así como los posibles métodos de resolución de las mismas y el desarrollo informático necesario para una primera aproximación a los resultados. Para poder analizar las condiciones de contorno que influyen en los valores resultantes de velocidad y calado, se ha diseñado una batería de escenarios simplificados que, tras una modelización en detalle y un análisis adimensional, han dado como resultado que las variables que influyen en los valores de calado y velocidad máximos en cada punto son: la altura de la lamina de agua del depósito, la pendiente del terreno, la rugosidad, la forma del terreno (en términos de concavidad) y la distancia del punto de estudio al deposito. Una vez definidas las variables que influyen en los resultados, se ha llevado a cabo una segunda batería de simulaciones de escenarios simplificados que ha servido para la discusión y desarrollo de las curvas que se presentan como producto principal de la metodología simplificada. Con esta metodología, que solamente necesita de unos cálculos simples para su empleo, se obtiene un primer valor de calado y velocidad introduciendo la altura de la lámina de agua máxima de servicio del depósito cuyo riesgo se quiere evaluar. Posteriormente, y utilizando el ábaco propuesto, se obtienen coeficientes correctores de los valores obtenidos para la rugosidad y pendiente media del terreno que se esta evaluando, así como para el grado de concavidad del mismo (a través de la pendiente transversal). Con los valores obtenidos con las curvas anteriores se obtienen los valores de calado y velocidad en el punto de estudio y, aplicando la formulación propuesta, se obtiene una estimación del riesgo asociado a la rotura de la infraestructura. Como corolario a la metodología mencionada, se propone una segunda serie de gráficos para evaluar, también de forma simplificada, la reducción del riesgo que se obtendría con la construcción de alguna medida mitigadora como puede ser un dique o murete perimetral al depósito. Este método de evaluación de posible medidas mitigadoras, aporta una guía para analizar la posibilidad de disminuir el riesgo con la construcción de estos elementos, o la necesidad de buscar otro emplazamiento que, si bien pueda ser no tan favorable desde el punto de vista de la explotación del depósito, presente un menor riesgo asociado a su rotura. Como complemento a la metodología simplificada propuesta, y además de llevar a cabo la calibración de la misma con los datos obtenidos tras la rotura del depósito de agua de Melilla, se ha realizado una serie de ejemplos de utilización de la metodología para, además de servir de guía de uso de la misma, poder analizar la diferencia entre los resultados que se obtendrían con una simulación bidimensional detallada de cada uno de los casos y el método simplificado aplicado a los mismos. The potential risk of a catastrophic collapse of a water supply reservoir in an urban area (such as the one occurred in Melilla in November 1997) and the damages that can cause, make question the security in this kind of infrastructures, which, by operational needs, are frequently built in high elevations and close to the urban areas they serve to. Since the likelihood of breakage is quite low, the alert levels associated to those infrastructures have also been downgraded focussing on the improvement of the constructive methods without developing methodologies (like the ones used in the case of dams or irrigation ponds) where there is a need of classifying the potential risk of those tanks and also of installing mitigating measures. Furthermore, to establish the damages related to a breakage of this kind, a twodimensional modelling of the breakage wave becomes imperative given that the urban layout does not provide a preferential way to the water. This kind of simulation requires financial investment that is not always available in the construction of small and medium sized water tanks. The purpose of this doctoral thesis is to design a simplified methodology, by means of charts and attending to the main variables of the phenomenon, that could estimate a value to the risk associated to a possible breakage. It can also be used as a guidance to establish if a reservoir (existing or a new one) requires a detailed model to estimate the risk of a breakage and the benefits of installing measures to mitigate the breakage wave effects. Previously, it has been established that the variables involved in the risk associated to a breakage are the draft and the maximum speed in every point susceptible to damages (mainly damages related to people). Bellow, the equations ruling the problem of the reservoir breakage have been studied as well as the transmission of the breakage wave through the urban network of the city and the possible methods to solve the equations and the computer development needed to a first approach to the results. In order to be able to analyse the boundary conditions affecting the values resulting (speed and draft), a set of scenarios have been designed. After a detailed modelling and a dimensionless analysis it has been proved that the variables that influence the operational draughts and the maximum speed in every point are the water level in the tank, the slope, the roughness and form (in terms of concavity) of the terrain and the distance between the tank and the control point. Having defined the involving variables, a second set of simulations of the simplified scenarios has been carried out and has helped to discuss and develop the curves that are here presented as the final product of the simplified methodology. This methodology only needs some simple calculations and gives a first value of draft and speed by introducing the maximum water level of the tank being evaluated. Subsequently, using the suggested charts, the method gives correction coefficients of the measured values for roughness and average slope of the assessed terrain as well as the degree of concavity (through transverse gradient).With the values from the previous curves (operational draughts and speed at the point of survey) and applying the proposed formulation, an estimation of the risk associated to the breakage of the infrastructure is finally obtained. As a corollary of the mentioned methodology, another set of diagrams is proposed in order to evaluate, in a simplified manner also, the risk reduction that could be gained with the construction of some mitigating measures such as dikes or retaining walls around the reservoir. This evaluating method provides a guide to analyse the possibility to reduce the risk, constructing those elements or even looking for a different site that could be worse in terms of exploitation of the tank but much safer. As a complement to the simplified methodology here proposed, and apart from completing its calibration with the obtained data after the reservoir breakage in Melilla, a number of examples of the use of the methodology have been made to be used as a user guide of the methodology itself, as well as giving the possibility of analysing the different results that can be obtained from a thorough two-dimensional simulation or from the simplified method applied to the examples.

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La presente investigación se presenta como una alternativa para la reducción de la contaminación por nutrientes que produce el vertido de aguas residuales provenientes de núcleos urbanos que acaban en lagos, lagunas o embalses acelerando los procesos de eutrofización de los mismos. El objetivo de esta tesis es analizar la reducción de nutrientes, fundamentalmente nitrógeno, fósforo y potasio, del agua residual doméstica sometida a tratamiento a través de cultivos hidropónicos en un determinado periodo de tiempo, observando a su vez la evolución del cultivo seleccionado. El sistema se diseñó para funcionar en circuito cerrado con el agua residual circulando por entre las raíces de los vegetales estudiados. El cultivo seleccionado fue el “kenaf”, aunque después de mucho tiempo dedicado a la obtención de semillas de “kenaf “por diferentes proveedores, se decidió comenzar un primer ensayo utilizando plantas de aloe vera durante un periodo de un mes de verano. Se procedió a la colocación de plantas en un tubo conteniendo agua residual de una fosa séptica domiciliaria. La reducción de la DBO5 y la DQO fue notable aunque los resultados de la variación de nitratos y fosfatos no fueron concluyentes. Las altas temperaturas alcanzada en esas fechas por el agua circulante, finalmente imposibilitó la continuación del ensayo. Si bien esta primera puesta en marcha no resultó como se esperaba, aportó numerosa información para modificar el planteo del estudio, la forma de llevarlo a cabo y la puesta a punto de la propia instalación. El segundo ensayo se llevó a cabo en otoño con plantas de kenaf obtenidas del ensayo previo en suelo en una parcela piloto en los llanos de Villamartín, en la provincia de Cádiz. Antes de incorporar el agua al sistema hidropónico se analizaron todos los parámetros requeridos por la normativa española del agua para determinar su clasificación como agua residual doméstica. Luego se le dio seguimiento a la variación de los nutrientes, nitrógeno, fósforo y potasio a lo largo de varias semanas para evaluar la efectividad del tratamiento. Las plantas de kenaf continuaron su desarrollo utilizando las sustancias disueltas en el agua residual como única fuente de nutrientes disponible. This research is presented as an alternative to reduce the pollution that wastewater discharges from towns generate when they end in lakes, ponds and reservoirs, by accelerating the eutrophication processes. The objective of this thesis is to analyze the reduction of nutrients, mainly nitrogen, phosphorus and potassium, of domestic wastewater treated through hydroponics crops in a given period of time, noting at the same time the evolution of the selected crop. The system was designed to operate in closed circuit with the wastewater circulating through the roots of the studied plants. The selected crop was "kenaf", although after much time spent in obtaining seeds of "kenaf"by different vendors and the impossibility of achieving its germination; it was decided to start a first test using Aloe Vera plants for a period of one month in the summer. The plants were introduced in the holes of a tube containing septic wastewater. The BOD5 and COD reduction was remarkable though the results of the variation in nitrates and phosphates were inconclusive. High temperatures achieved in those dates by circulating water, eventually precluded the continuation of the test. Although this first implementation was not running as expected, it provided information to modify the proposal of the study, the way to carry it out and the development of the installation itself. The second test was conducted in autumn with kenaf plants obtained from the previous test in a pilot plant in the flatness of Villamartín, province of Cádiz. Before adding the water to the hydroponic system all the parameters required by the Spanish water regulations were analyzed to determine their classification as domestic waste water. Then, the variation of nutrients, nitrogen, phosphorus and potassium was tracking over several weeks to evaluate the effectiveness of the treatment. Kenaf plants continued its development using the substances dissolved in wastewater as sole source of nutrients available.