331 resultados para Woodland


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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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We report a unique case of a gene containing three homologous and contiguous repeat sequences, each of which, after excision, cloning, and expression in Escherichia coli, is shown to code for a peptide catalyzing the same reaction as the native protein, Gonyaulax polyedra luciferase (Mr = 137). This enzyme, which catalyzes the light-emitting oxidation of a linear tetrapyrrole (dinoflagellate luciferin), exhibits no sequence similarities to other luciferases in databases. Sequence analysis also reveals an unusual evolutionary feature of this gene: synonymous substitutions are strongly constrained in the central regions of each of the repeated coding sequences.

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In coming decades, global climate changes are expected to produce large shifts in vegetation distributions at unprecedented rates. These shifts are expected to be most rapid and extreme at ecotones, the boundaries between ecosystems, particularly those in semiarid landscapes. However, current models do not adequately provide for such rapid effects—particularly those caused by mortality—largely because of the lack of data from field studies. Here we report the most rapid landscape-scale shift of a woody ecotone ever documented: in northern New Mexico in the 1950s, the ecotone between semiarid ponderosa pine forest and piñon–juniper woodland shifted extensively (2 km or more) and rapidly (<5 years) through mortality of ponderosa pines in response to a severe drought. This shift has persisted for 40 years. Forest patches within the shift zone became much more fragmented, and soil erosion greatly accelerated. The rapidity and the complex dynamics of the persistent shift point to the need to represent more accurately these dynamics, especially the mortality factor, in assessments of the effects of climate change.

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No estudo das comunidades florestais, estabelecer a importância relativa dos fatores que definem a composição e a distribuição das espécies é um desafio. Em termos de gradientes ambientais o estudo das respostas das espécies arbóreas são essenciais para a compreensão dos processos ecológicos e decisões de conservação. Neste sentido, para contribuir com a elucidação dos processos ecológicos nas principais formações florestais do Estado de São Paulo (Floresta Ombrófila Densa de Terras Baixas, Floresta Ombrófila Densa Submontana, Floresta Estacional Semidecidual e Savana Florestada) este trabalho objetivou responder as seguintes questões: (I) a composição florística e a abundância das espécies arbóreas, em cada unidade fitogeográfica, variam conforme o gradiente edáfico e topográfico?; (II) características do solo e topografia podem influenciar na previsibilidade de ocorrência de espécies arbóreas de ampla distribuição em diferentes tipos vegetacionais? (III) existe relação entre o padrão de distribuição espacial de espécies arbóreas e os parâmetros do solo e topografia? O trabalho foi realizado em parcelas alocadas em unidades de conservação (UC) que apresentaram trechos representativos, em termos de conservação e tamanho, das quatro principais formações florestais presentes no Estado de São Paulo. Em cada UC foram contabilizados os indivíduos arbóreos (CAP ≥ 15 cm), topografia, dados de textura e atributos químicos dos solos em uma parcela de 10,24 ha, subdividida em 256 subparcelas. Análises de correspodência canônica foram aplicadas para estabelecer a correspondência entre a abundância das espécies e o gradiente ambiental (solo e topografia). O método TWINSPAN modificado foi aplicado ao diagrama de ordenação da CCA para avaliar a influência das variáveis ambientais (solo e topografia) na composição de espécies. Árvores de regressão \"ampliadas\" (BRT) foram ajustadas para a predição da ocorrência das espécies segundo as variáveis de solo e topografia. O índice de Getis-Ord (G) foi utilizado para determinar a autocorrelação espacial das variáveis ambientais utilizadas nos modelos de predição da ocorrência das espécies. Nas unidades fitogeográficas analisadas, a correspondência entre o gradiente ambiental (solo e topografia) e a abundância das espécies foi significativa, especialmente na Savana Florestada onde observou-se a maior relação. O solo e a topografia também se relacionaram com a semelhança na composição florística das subparcelas, com exceção da Floresta Estacional Semicidual (EEC). As principais variáveis de solo e topografia relacionadas a flora em cada UC foram: (1) Na Floresta Ombrófila Densa de Terras Baixas (PEIC) - teor de alumínio na camada profunda (Al (80-100 cm)) que pode refletir os teor de Al na superfície, acidez do solo (pH(H2O) (5-25 cm)) e altitude, que delimitou as áreas alagadas; (2) Na Floresta Ombrófila Densa Submontana (PECB) - altitude, fator que, devido ao relevo acidentado, influencia a temperatura e incidência de sol no sub-bosque; (3) Na Savana Florestada (EEA) - fertilidade, tolerância ao alumínio e acidez do solo. Nos modelos de predição BRT, as variáveis químicas dos solos foram mais importantes do que a textura, devido à pequena variação deste atributo no solo nas áreas amostradas. Dentre as variáveis químicas dos solos, a capacidade de troca catiônica foi utilizada para prever a ocorrência das espécies nas quatro formações florestais, sendo particularmente importante na camada mais profunda do solo da Floresta Ombrófila Densa de Terras Baixas (PEIC). Quanto à topografia, a altitude foi inserida na maioria dos modelos e apresentou diferentes influências sobre as áreas de estudo. De modo geral, para presença das espécies de ampla distribuição observou-se uma mesma tendência quando à associação com os atributos dos solos, porém com amplitudes dos descritores edáficos que variaram de acordo com a área de estudo. A ocorrência de Guapira opposita e Syagrus romanzoffiana, cujo padrão variou conforme a escala, foi explicada por variáveis com padrões espaciais agregados que somaram entre 30% e 50% de importância relativa no modelo BRT. A presença de A. anthelmia, cujo padrão também apresentou certo nível de agregação, foi associada apenas a uma variável com padrão agregado, a altitude (21%), que pode ter exercido grande influência na distribuição da espécie ao delimitar áreas alagadas. T. guianensis se associou a variáveis ambientais preditoras com padrão espacial agregado que somaram cerca de 70% de importância relativa, o que deve ter sido suficiente para estabelecer o padrão agregado em todas as escalas. No entanto, a influência dos fatores ambientais no padrão de distribuição da espécie não depende apenas do ótimo ambiental da espécie, mas um resultado da interação espécie-ambiente. Concluiu-se que: (I) características edáficas e topográficas explicaram uma pequena parcela da composição florística, em cada unidade fitogeográfica, embora a ocorrência de algumas espécies tenha se associado ao gradiente edáfico e topográfico; (II) a partir de características dos solos e da topografia foi possível prever a presença de espécies arbóreas, que apresentaram particularidades em relação a sua associação com o solo de cada fitofisionomia; (III) a partir de associações descritivas o solo e a topografia influenciam o padrão de distribuição espacial das espécies, na proporção em que contribuem para a presença das mesmas.

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Saproxylic beetle diversity is high at the Cabañeros National Park (central Spain), where woodland habitats exhibit remarkable heterogeneity. Our aim was to explain the diversity of saproxylic beetles, focusing on species turnover among mature woodland types. We surveyed five woodland types that represented the heterogeneity of the park’s woodland habitats. Beetles were collected using window traps over a period of 20 months. The Jaccard Similarity Index was used as indirect value of beta diversity among woodlands and to test the relation between species turnover and geographical distance. We also identified the contribution of species turnover to landscape diversity by using a partitioning model. Moreover, the presence of mixed woodlands (more than one tree species) allowed us to attempt to valorise the effect of tree species (coupled with their historical management) on species turnover among woodlands. Finally, we looked for different saproxylic beetle preferences for habitat and tree species using an indicator value method. We found that saproxylic beetle species composition varied significantly among the studied woodlands. The variation in species turnover was independent from the distance among woodlands, which suggested that beetle dispersal abilities could not explain this high turnover. Tree species within woodlands were a key factor that increased diversity turnover in woodlands and, consequently, the diversity of the park. Moreover, we found saproxylic beetle species that had different habitat and tree species preferences. We conclude that woodland heterogeneity (highly affected by woodland composition) seems to be the driving force for saproxylic beetle diversity in this protected area.

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Saproxylic diversity assessment is a major goal for conservation strategies in woodlands and it should consider woodland composition and configuration at site and tree level as key modelling factors. However, in Mediterranean woodlands little is known about the relation with the environmental factors that structure their assemblages, especially those linked to tree hollow microhabitats. We assessed the diversity of Syrphidae (Diptera) and Coleoptera saproxylic guilds that co-occurred in tree hollows located in three different Iberian Mediterranean woodlands in the Cabañeros National Park (Spain). Furthermore, we evaluated how differences in tree hollow microenvironmental variables (understood as the physical and biotic characteristics of a hollow and tree individual) influenced saproxylic guild diversity both within and among woodland sites. We found that woodland sites that provided greater heterogeneity of trees and hollow microhabitats determined higher saproxylic guild diversity. Nevertheless, certain species or even complete guilds can be favoured in woodlands where some hollow microhabitats predominate as a consequence of historical tree management. In general, hollow volume was the main determining factor for saproxylic guild richness and abundance in woodland sites, and large hollow volume was usually related to higher diversity, which highlighted the importance of multi-habitat hollow trees. Moreover, saproxylic guilds also responded to other different microenvironmental variables, which indicated different ecological preferences among guilds. The conservation of saproxylic insects in Iberian Mediterranean areas must be addressed to protect woodland sites that provide high diversity and large numbers of tree hollow microhabitats, and practices to enhance microhabitat heterogeneity should even be encouraged.

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The assessment of the relation between species diversity, species interactions and stability is a major goal for conservation strategies of saproxylic insects in Iberian Mediterranean woodlands. In these woodlands, tree hollows in standing living trees are key microhabitats for saproxylic biodiversity. We assess the variation in the tree hollow-saproxylic insect network among three woodland sites in the Cabañeros National Park (Spain), and evaluate their implications for saproxylic assemblages’ persistence, through simulations of three possible scenarios of loss of tree hollow microhabitats. The composition of tree hollows is closely related to biotic and ecological complexity of saproxylic networks, and together exhibit positive effects on network stability. By other side, different scenarios entail different reorganizations of saproxylic diversity of species and interactions, and the variation of the main interacting attributes. Woodlands providing higher proportion of large tree hollows are less sensitive to microhabitat loss. Conservation strategies for saproxylic insects in Iberian Mediterranean woodlands should consider woodland composition and configuration as key factors in the selection of priority conservation areas.

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The assessment of the relationship between species diversity, species interactions and environmental characteristics is indispensable for understanding network architecture and ecological distribution in complex networks. Saproxylic insect communities inhabiting tree hollow microhabitats within Mediterranean woodlands are highly dependent on woodland configuration and on microhabitat supply they harbor, so can be studied under the network analysis perspective. We assessed the differences in interacting patterns according to woodland site, and analysed the importance of functional species in modelling network architecture. We then evaluated their implications for saproxylic assemblages’ persistence, through simulations of three possible scenarios of loss of tree hollow microhabitat. Tree hollow-saproxylic insect networks per woodland site presented a significant nested pattern. Those woodlands with higher complexity of tree individuals and tree hollow microhabitats also housed higher species/interactions diversity and complexity of saproxylic networks, and exhibited a higher degree of nestedness, suggesting that a higher woodland complexity positively influences saproxylic diversity and interaction complexity, thus determining higher degree of nestedness. Moreover, the number of insects acting as key interconnectors (nodes falling into the core region, using core/periphery tests) was similar among woodland sites, but the species identity varied on each. Such differences in insect core composition among woodland sites suggest the functional role they depict at woodland scale. Tree hollows acting as core corresponded with large tree hollows near the ground and simultaneously housing various breeding microsites, whereas core insects were species mediating relevant ecological interactions within saproxylic communities, e.g. predation, competitive or facilitation interactions. Differences in network patterns and tree hollow characteristics among woodland sites clearly defined different sensitivity to microhabitat loss, and higher saproxylic diversity and woodland complexity showed positive relation with robustness. These results highlight that woodland complexity goes hand in hand with biotic and ecological complexity of saproxylic networks, and together exhibited positive effects on network robustness.

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La evolución del arbolado en la Península Ibérica pasó por numerosos episodios que le condujeron a una situación grave de deforestación. Tras varios intentos de reforestación en épocas distintas, finalmente la apuesta definitiva se produciría con la creación del Patrimonio Forestal del Estado y el Plan Nacional de Repoblación Forestal de España de 1939. La sustitución del PFE por el ICONA en 1971, supuso un nuevo contexto, en el que se puso en duda tanto la actuación repobladora, como las especies utilizadas, principalmente del género Pinus. Este trabajo trata de poner en valor la información que aportan distintas corrientes científicas, la botánica, la biogeografía, paleobotánica y los datos de otros estudios realizados en numerosos yacimientos arqueológicos en Andalucía, especialmente en la zona oriental. Estos trabajos ponen de manifiesto la presencia de especies del género Pinus en distintos periodos geológicos, con avances y retrocesos del binomio Pinus-Quercus, durante períodos más o menos extensos. La repoblación forestal supuso un avance a una de esas situaciones, que dió como resultado el marco de nuevas intervenciones de manejo del bosque por la Administración Andaluza, siendo las exigencias de conservación prioritarias en la gestión de los espacios forestales, muchos de ellos declarados Espacios Protegidos. Se trata pues, de poner en valor aquellas actuaciones que dieron lugar a la nueva situación en la que se apuesta por la conservación y en la que juegan un papel importante la genética y la productividad de las especies utilizadas en las intervenciones forestales.

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This layer is a georeferenced raster image of the historic, topographic paper map entitled: Topography of Jefferson County, Kentucky : from U.S. Geological Survey topographic atlas sheets surveyed in 1904-1910, U.S. Geological Survey ; in cooperation with Kentucky Geological Survey, C. J. Norwood, director. It was published by U.S. Geological Survey in 1912. Scale 1:62,500. The image inside the map neatline is georeferenced to the surface of the earth and fit to the Kentucky North State Plane NAD 1983 coordinate system (in Feet) (Fipszone 1601). All map collar and inset information is also available as part of the raster image, including any inset maps, profiles, statistical tables, directories, text, illustrations, index maps, legends, or other information associated with the principal map. This is a typical topographic map portraying both natural and manmade features. It shows and names works of nature, such as mountains, valleys, lakes, rivers, vegetation, etc. It also identify the principal works of humans, such as roads, railroads, boundaries, transmission lines, major buildings, etc. Relief is shown with standard contour intervals of 20 feet and spot heights. This layer is part of a selection of digitally scanned and georeferenced historic maps from The Harvard Map Collection as part of the Imaging the Urban Environment project. Maps selected for this project represent major urban areas and cities of the world, at various time periods. These maps typically portray both natural and manmade features at a large scale. The selection represents a range of regions, originators, ground condition dates, scales, and purposes.

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This layer is a georeferenced raster image of the historic paper map entitled: OKI regional land use : 1975. It was published by OKI Regional Planning Authority in 1975. Scale [ca. 1:5,000]. Covers Cincinnati Region, Ohio including Butler, Clermont, Hamilton, Warren counties, Ohio; Boone, Campbell, and Kenton counties, Kentucky; and Dearborn and Ohio counties, Indiana. The image inside the map neatline is georeferenced to the surface of the earth and fit to the Ohio South State Plane NAD 1983 coordinate system (in Feet) (Fipszone 3402). All map collar and inset information is also available as part of the raster image, including any inset maps, profiles, statistical tables, directories, text, illustrations, index maps, legends, or other information associated with the principal map. This map is colored to show land use categories: Urban residential ; Suburban residential ; Commercial ; Institutional/Service ; Utilities ; Industrial ; Resource extraction ; Recreational/Open space ; Cropland ; Grassland ; Woodland ; Water. It also shows features as major roads, drainage, administrative and political boundaries, and more. This layer is part of a selection of digitally scanned and georeferenced historic maps from The Harvard Map Collection as part of the Imaging the Urban Environment project. Maps selected for this project represent major urban areas and cities of the world, at various time periods. These maps typically portray both natural and manmade features at a large scale. The selection represents a range of regions, originators, ground condition dates, scales, and purposes.

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Dans ce mémoire, intitulé « Les dépotoirs dans le schème d’établissement iroquoien: exemple du site Mailhot-Curran», je m’attèle à définir les modes de rejets des déchets dans le contexte d’un schème d’établissement sédentaire semi-permanent au Sylvicole supérieur. Les dépotoirs des sites archéologiques ne semblent pas obtenir toute l’attention analytique qui leur est due et l’étude des modes de rejets a longtemps été négligée. Pourtant, les amas de déchets sont récurrents sur les sites du Nord-Est américain et ce depuis le Sylvicole moyen. L’étude approfondie de l’organisation d’un site iroquoien se doit de passer par la compréhension des modes d’élimination des déchets, puisque la gestion des rejets est généralement le reflet de la structure du site et du type de peuplement. Les dépotoirs peuvent fournir des informations précieuses sur les zones d’activité, la fonction du site ou encore la durée d’occupation. Le village de Mailhot-Curran témoigne de plusieurs concentrations d’objets. Je souhaite établir si ces concentrations de vestiges peuvent être qualifiées de dépotoirs et si oui, peut-on en distinguer différents types? D’autre part, je m’intéresse à l’aspect social qui encadre la mise en place de dépotoirs. Bien que les dépotoirs soient des indices associés aux premières traces de sédentarité saisonnière, leur présence est précisément liée au phénomène de sédentarisation annuelle. Il s’agit également de définir le geste culturel, l’assainissement d’un village étant un schéma culturel très répandu. De ce geste de rejet découle forcément le choix d’un emplacement, ainsi que le concept de «flux de déplacement» des déchets. Il s’agit de déterminer le lien entretenu entre les aires d’activités et les aires de dépôts primaires et secondaires. Pour ce faire, il est primordial d’évaluer la densité, l’hétérogénéité et le contenu des dépotoirs. Suite à la définition de l’ensemble de ces concepts appliqués au site Mailhot-Curran, je souhaite, à travers une étude comparative, répondre à la question suivante : Les dépotoirs peuvent-ils refléter une pratique culturelle commune aux villages iroquoiens de la région de Saint-Anicet?

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This paper assesses the complex interplay between global Renewable Energy Directives (RED) and the United Nations programme to Reduce Emissions from Deforestation and forest Degradation (REDD). We examine the interaction of the two policies using a scenario approach with a recursive-dynamic global Computable General Equilibrium model. The consequences of a global biofuel directive on worldwide land use, agricultural production, international trade flows, food prices and food security out to 2030 are evaluated with and without a strict global REDD policy. We address a key methodological challenge of how to model the supply of land in the face of restrictions over its availability, as arises under the REDD policy. The paper introduces a flexible land supply function, which allows for large changes in the total potential land availability for agriculture. Our results show that whilst both RED and REDD are designed to reduce emissions, they have opposing impacts on land use. RED policies are found to extend land use whereas the REDD policy leads to an overall reduction in land use and intensification of agriculture. Strict REDD policies to protect forest and woodland lead to higher land prices in all regions. World food prices are slightly higher overall with some significant regional increases, notably in Southern Africa and Indonesia, leading to reductions in food security in these countries. This said, real food prices in 2030 are still lower than the 2010 level, even with the RED and REDD policies in place. Overall this suggests that RED and REDD are feasible from a worldwide perspective, although the results show that there are some regional problems that need to be resolved. The results show that countries directly affected by forest and woodland protection would be the most economically vulnerable when the REDD policy is implemented. The introduction of REDD policies reduces global trade in agricultural products and moves some developing countries to a net importing position for agricultural products. This suggests that the protection of forests and woodlands in these regions reverses their comparative advantage as they move from being land-abundant to land-scarce regions. The full REDD policy setting, however, foresees providing compensation to these countries to cover their economic losses.

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Dans ce mémoire, intitulé « Les dépotoirs dans le schème d’établissement iroquoien: exemple du site Mailhot-Curran», je m’attèle à définir les modes de rejets des déchets dans le contexte d’un schème d’établissement sédentaire semi-permanent au Sylvicole supérieur. Les dépotoirs des sites archéologiques ne semblent pas obtenir toute l’attention analytique qui leur est due et l’étude des modes de rejets a longtemps été négligée. Pourtant, les amas de déchets sont récurrents sur les sites du Nord-Est américain et ce depuis le Sylvicole moyen. L’étude approfondie de l’organisation d’un site iroquoien se doit de passer par la compréhension des modes d’élimination des déchets, puisque la gestion des rejets est généralement le reflet de la structure du site et du type de peuplement. Les dépotoirs peuvent fournir des informations précieuses sur les zones d’activité, la fonction du site ou encore la durée d’occupation. Le village de Mailhot-Curran témoigne de plusieurs concentrations d’objets. Je souhaite établir si ces concentrations de vestiges peuvent être qualifiées de dépotoirs et si oui, peut-on en distinguer différents types? D’autre part, je m’intéresse à l’aspect social qui encadre la mise en place de dépotoirs. Bien que les dépotoirs soient des indices associés aux premières traces de sédentarité saisonnière, leur présence est précisément liée au phénomène de sédentarisation annuelle. Il s’agit également de définir le geste culturel, l’assainissement d’un village étant un schéma culturel très répandu. De ce geste de rejet découle forcément le choix d’un emplacement, ainsi que le concept de «flux de déplacement» des déchets. Il s’agit de déterminer le lien entretenu entre les aires d’activités et les aires de dépôts primaires et secondaires. Pour ce faire, il est primordial d’évaluer la densité, l’hétérogénéité et le contenu des dépotoirs. Suite à la définition de l’ensemble de ces concepts appliqués au site Mailhot-Curran, je souhaite, à travers une étude comparative, répondre à la question suivante : Les dépotoirs peuvent-ils refléter une pratique culturelle commune aux villages iroquoiens de la région de Saint-Anicet?