959 resultados para Ecosystem services valuation
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Pinus pinaster Ait. es la conífera con mayor área de distribución en la Península Ibérica y es, a día de hoy, la única especie resinada en nuestro país. La inducción del flujo de resina al exterior para su recolección a través de distintos tipos de heridas ha sido practicada desde hace miles de años por distintas culturas. En todos los casos, las técnicas desarrolladas se basan en la estimulación del característico sistema de defensa de las pináceas. En los últimos siete años se viene observando una tendencia de incremento sustancial de la superficie resinada en España, acompañada por avances tecnológicos dirigidos a la mecanización y mejora de estimulantes. El aprovechamiento resinero se perfila como un sector estratégico en la generación de empleo rural y la conservación de ecosistemas. La industria resinera demanda métodos de extracción más eficaces, una selvicultura adecuada y actualizada, y condiciones laborales de los resineros más dignas con objeto de llegar a ser competitiva en el mercado internacional. Este trabajo se centra en ampliar el conocimiento sobre el sistema de defensa de P. pinaster, concretamente sobre las estructuras y procesos que pueden afectar a la producción de resina. Se analizan las relaciones entre las características anatómicas del xilema, destacando las relacionadas con los canales resiníferos, las variables dendrométricas y dasométricas de la masa y el flujo de resina (objetivo 1). Se estudia cómo estas relaciones son moduladas por las heridas de resinación dependiendo de la técnica de resinación aplicada (objetivo 2), el clima y el balance hídrico del suelo (objetivo 3). El material vegetal, las muestras de suelo y los datos de producción de resina y climáticos usados en esta tesis han sido recogidos en tres montes de utilidad pública; MUP 101 en Armuña, MUP 108 en Melque de Cercos y MUP 117 en Nieva (en esta última solo se recogieron los datos de producciones), todos ellos pinares monoespecíficos de P. pinaster localizados en la denominada Tierra de Pinares Segoviana. En los árboles de nuestro estudio se han aplicado cuatro métodos de resinación: método de pica de corteza con estimulante y método mecanizado con estimulante, ambos en sentido ascendente y descendente. En los trabajos realizados para el análisis de la influencia de la anatomía constitutiva en la producción de resina (objetivo 1) y el efecto del clima (objetivo 3), se obtuvieron muestras del xilema de 26 árboles resinados en Melque de Cercos y Armuña y 12 árboles control sin resinar. Para caracterizar los pies estudiados, se midió la altura, diámetro normal y porcentaje de copa viva. Las muestras de tejido fueron recogidas en una zona del tronco a una distancia del límite de la herida considerada en la bibliografía como no afectada (anatomía constitutiva). Para el análisis de las alteraciones anatómicas inducidas por la herida (objetivo 2), se recogieron muestras en ocho de los individuos en los que se habían realizado los distintos métodos de resinación descritos y en cinco árboles control. Se obtuvieron ocho muestras de tejido distribuidas en la parte superior, inferior, lateral y centro de la herida de cada uno de los árboles resinados. Para establecer las diferencias en la producción de resina según el método de resinación, se analizaron las producciones de 561 árboles resinados en 2012 con estos cuatro métodos en Nieva. Los principales resultados de estos trabajos muestran que la producción de resina está ligada al volumen de canales (axiales y radiales) y a la frecuencia de canales radiales existentes en el árbol antes de efectuar ninguna herida (sistema constitutivo). De esta manera, los árboles grandes productores de resina mostraron una red de canales más densa que aquellos con producciones medias. Una vez realizada la herida de resinación, observamos una disminución del ancho del anillo de crecimiento y del tamaño medio de los canales axiales a la vez que se incrementaba la frecuencia y área ocupada por mm2 de anillo de estos canales. Estos cambios perduraron en el árbol durante al menos tres años y fueron distintos dependiendo de la localización en el entorno de la herida y del método de resinación. Las respuestas más intensas a la herida se observaron el año siguiente a la realización de la misma, en dirección axial, para las distancias más próximas al límite de la herida y para los métodos de resinación en sentido ascendente. Además, se ha constatado que como consecuencia de las heridas de resinación se produjeron cambios en la anatomía del xilema en zonas alejadas de la herida, tanto en el año de la herida como años posteriores. Es decir, se observó una respuesta sistémica del árbol. Respecto al papel del clima como regulador de la respuesta del árbol, se ha evidenciado que la temperatura, la radiación y la ETP influyeron en la producción de resina, no solo durante la campaña de resinación, sino también durante los meses anteriores. El déficit hídrico favoreció la producción y la formación de canales axiales pero, a partir de un determinado umbral, esa relación se invirtió y las lluvias estivales incrementaron la producción. Algunas de estas variables climáticas se asociaron a cambios en el tamaño y frecuencia de las estructuras secretoras, las cuales posiblemente modulan la respuesta defensiva de la planta. La dendrometría del árbol (evaluada a través del diámetro normal, altura y porcentaje de copa viva), la densidad de la masa y el tipo de suelo influyeron en el potencial de producción de resina de P. pinaster. Árboles más vigorosos, parcelas con menores densidades y suelos con más capacidad para la retención de agua y nutrientes presentaron producciones mayores. Estos trabajos se complementan en anexos con una caracterización del sistema socio-ecológico del pinar en resinación. En ese trabajo se identifican sus potenciales servicios ecosistémicos y se evalúa su grado de vinculación con el aprovechamiento resinero con objeto de valorar su funcionalidad y aproximar una valoración económica de modo que sea posible apreciar la importancia económica de los mismos. Para concluir, podemos resaltar que son necesarios más trabajos de carácter científico para avanzar en la comprensión de los procesos anatómicos y fisiológicos que regulan la secreción de resina en P. pinaster y sus interacciones con el medio. Esto permitiría avances certeros hacia el desarrollo de métodos de extracción más eficaces, una selvicultura óptima, el reconocimiento de los beneficios socio-ecológicos y económicos del aprovechamiento y, de manera general, una bibliografía amplia y fiable para la consulta y desarrollo de futuras mejoras que posibiliten la reactivación y conservación de la resinación como aprovechamiento rentable. ABSTRACT Pinus pinaster Ait. is the most widespread conifer in Spain and is now the only species tapped for its oleoresin. External induction of resin secretion, based on the defense system of Pinus trees, has been performed by humans since Classical times through various methods. The socio-economic implication of this practice in Spain justifies a new approach to improve tapping methodology and understand the effects of this activity on the tree. In the last five years, sharp increases in the price of natural resins, accompanied by technological advances directed toward mechanization, have made resin tapping a strategic activity for rural development and forest conservation. The resin industry demands more efficient tapping methods and forest management plans as a way to increase competitiveness in a global market. In this way, this work focuses on the study of the defense system of P. pinaster, with the aim to understand the effects of anatomical and physiological characteristics and environmental conditions on resin yield. The relationships between anatomical variables -with special focus on resin canals-, dendrometric and dasometric variables, and resin yield will be evaluated (objective 1). The tapping wound effects (objective 2) and the intra- and inter-annual variability of climate conditions and soil water availability influence (objective 3) on resin yield will be also studied. The plant and soil material and the resin yield and climatic data used in this thesis have been collected in stands of three public forests of P. pinaster; Armuña, Melque de Cercos and Nieva, located in Segovia (Central Spain). Trees were tapped using two different methods: mechanized or traditional tool, in both upwards and downwards direction. Twenty-six tapped trees of contrasting resin yield classes and twelve non-tapped (control) trees, growing in two locations (Armuña y Melque de Cercos) with the same climate but different stand density and soil characteristics, were selected for studying the role of tree size, xylem anatomy at distal parts aside from the tapping wound (objective 1) and climate influence (objective 3) on resin yield. Concerning the tree defenses induced by the tapping wound (objective 2), the xylem of eight trees, tapped with the two described methods in both upwards and downwards direction, were analyzed. From each tapped tree, eight cores were collected at different locations and varying distances from the tapping wound. In each core, a histological analysis was made. Growth ring width, earlywood and latewood width, and axial canal frequency, area, mean size and location were measured. The effect of the tapping method on resin yield was assessed in 561 P. pinaster tapped trees in a stand in Nieva. In tissues not affected by the tapping wound, the frequency of radial resin canals and the total volume of resin canals were related to resin yield. The frequency of radial canals and the resin yield were strongly related to tree diameter and percentage of live crown. High area of axial resin canals per mm2 was related to high yielding trees, but only in the location with higher plant density and poorer soil quality. In tapped trees, an increase in axial canal frequency and area was found during the three years following the start of tapping activity, suggesting that canal formation is a systemic induced response to wounding. The highest mean annual resin yield was found using the traditional tool in upwards direction, which also induced the highest increase in axial canal frequency and area. The lowest yield was found for mechanized tapping, which showed no differences between the upwards and downwards directions. The strongest induction of systemic induced responses in terms of resin canal frequency and area was detected one year after tapping for upwards tapping. This suggests the involvement of signaling processes that spread mainly upwards, and the importance of adaptive processes as a defense against periodic insect attacks. Intra-annual variation in resin yield was strongly correlated with temperature, solar radiation, potential evapotranspiration and soil water deficit. Inter-annual variation in resin yield and resin canal abundance were correlated with temperature and water deficit in spring, but above a certain threshold of cumulated water deficit in summer rainfall favored resin yield. Under adverse climate scenarios where resource optimization is desirable, a reduced tapping season during the warmest months (June–September) would be advisable, assuming a very small production loss relative to traditional tapping season. Similarly, in years with a rainy summer and/or dry spring, a slightly longer tapping season could be suggested, as resin yield increases after these events. Tree diameter and percentage of live crown, and radial resin canal frequency could be useful criteria for estimating resin yields in P. pinaster. Vigorous trees in lower density stands and growing up in good quality soils will be the most productive. These conclusions could be applied to improve tapping management and breeding programs. These works are complemented with socio-ecological characterization, the identification of the main ecosystem services and an assessment of the possible economic impact derived from the tapping practice. To conclude, more scientific studies are necessary for understanding the anatomical and physiological processes behind resin synthesis and their interactions with the environment. This would afford further progresses towards an extensive and reliable bibliography and improved tapping methods and optimal selvicultural guide lines.
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The introduction of cover crops in the intercrop period may provide a broad range of ecosystem services derived from the multiple functions they can perform, such as erosion control, recycling of nutrients or forage source. However, the achievement of these services in a particular agrosystem is not always required at the same time or to the same degree. Thus, species selection and definition of targeted objectives is critical when growing cover crops. The goal of the current work was to describe the traits that determine the suitability of five species (barley, rye, triticale, mustard and vetch) for cover cropping. A field trial was established during two seasons (October to April) in Madrid (central Spain). Ground cover and biomass were monitored at regular intervals during each growing season. A Gompertz model characterized ground cover until the decay observed after frosts, while biomass was fitted to Gompertz, logistic and linear-exponential equations. At the end of the experiment, carbon (C), nitrogen (N), and fibre (neutral detergent, acid and lignin) contents, and the N fixed by the legume were determined. The grasses reached the highest ground cover (83–99%) and biomass (1226–1928 g/m2) at the end of the experiment. With the highest C:N ratio (27–39) and dietary fibre (527–600 mg/g) and the lowest residue quality (~680 mg/g), grasses were suitable for erosion control, catch crop and fodder. The vetch presented the lowest N uptake (2·4 and 0·7 g N/m2) due to N fixation (9·8 and 1·6 g N/m2) and low biomass accumulation. The mustard presented high N uptake in the warm year and could act as a catch crop, but low fodder capability in both years. The thermal time before reaching 30% ground cover was a good indicator of early coverage species. Variable quantification allowed finding variability among the species and provided information for further decisions involving cover crop selection and management.
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Acknowledgements This work was supported by the UK Energy Research Centre Phase 2, under its Energy and Environment theme Grant Number NE/J005924/1 and NE/G007748/1. Open Access funded by Natural Environment Research Council
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The recent intensification of agriculture, and the prospects of future intensification, will have major detrimental impacts on the nonagricultural terrestrial and aquatic ecosystems of the world. The doubling of agricultural food production during the past 35 years was associated with a 6.87-fold increase in nitrogen fertilization, a 3.48-fold increase in phosphorus fertilization, a 1.68-fold increase in the amount of irrigated cropland, and a 1.1-fold increase in land in cultivation. Based on a simple linear extension of past trends, the anticipated next doubling of global food production would be associated with approximately 3-fold increases in nitrogen and phosphorus fertilization rates, a doubling of the irrigated land area, and an 18% increase in cropland. These projected changes would have dramatic impacts on the diversity, composition, and functioning of the remaining natural ecosystems of the world, and on their ability to provide society with a variety of essential ecosystem services. The largest impacts would be on freshwater and marine ecosystems, which would be greatly eutrophied by high rates of nitrogen and phosphorus release from agricultural fields. Aquatic nutrient eutrophication can lead to loss of biodiversity, outbreaks of nuisance species, shifts in the structure of food chains, and impairment of fisheries. Because of aerial redistribution of various forms of nitrogen, agricultural intensification also would eutrophy many natural terrestrial ecosystems and contribute to atmospheric accumulation of greenhouse gases. These detrimental environmental impacts of agriculture can be minimized only if there is much more efficient use and recycling of nitrogen and phosphorus in agroecosystems.
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A sustentabilidade da paisagem trata-se de um tema central no que se refere às questões de conservação e desenvolvimento de paisagens altamente antropizadas. Está embasada nos conceitos tradicionais de desenvolvimento sustentável, que visam balancear o desenvolvimento humano com a proteção ambiental, pautada na equidade intra e extra-geração. Considera, ainda, os conceitos de bem-estar humano nesta esfera. Paralelamente, os conceitos de serviços ecossistêmicos reconhecem a dependência das atividades antrópicas e seu bem-estar à qualidade dos ecossistemas, reacendendo os debates sobre capital natural e desenvolvimento sustentável. Neste contexto, este trabalho aborda a sustentabilidade da paisagem questionando a potencialidade dos remanescentes florestais em fornecer, de maneira equilibrada, diferentes serviços ecossistêmicos na bacia do rio Corumbataí. Para isso, o trabalho foi dividido em duas etapas. A primeira buscou analisar questões de demanda e oferta por múltiplos serviços ecossistêmicos (controle de erosão, regulação hídrica, regulação microclimática, informação estética e qualidade de habitat). Isso baseado em indicadores da paisagem, como a dinâmica do uso do solo e padrões do meio físico e antrópico. A segunda investigou a viabilidade de integrar o sinergismo entre os serviços de controle de erosão e qualidade de habitat às prioridades de conservação e restauração florestal. Isso baseado no cenário atual da paisagem e por meio de diferentes simulações de incremento em 10% da cobertura florestal na paisagem, inserindo florestas nos locais de alta erodibilidade (situação criteriosa) ou de forma randômica. Os resultados demonstraram que, apesar do aumento de 60% na cobertura florestal durante os últimos 30 anos, apenas 37% das florestas possuem alto potencial para ofertar serviços ecossistêmicos e que, quando ponderadas perante as demandas da paisagem, apenas 20% das florestas encontram-se em equilíbrio. Além disso, foi verificado sinergismo entre os serviços de controle de erosão e qualidade de habitat em aproximadamente 80% da cobertura florestal. No entanto, nos cenários de restauração florestal, o sinergismo foi alcançado em todas as situações, sejam elas criteriosas ou randômicas. Deste modo, ficou evidente o limite das florestas e áreas protegidas como potenciais prestadoras de serviços ecossistêmicos na paisagem. Também ficou evidente que, em paisagens com alto grau de fragmentação e baixa proporção florestal, os processos de restauração não necessariamente devem almejar o sinergismo entre serviços ecossistêmicos. Por fim, atribui-se grande importância ao papel das áreas agrícolas e pastagens para compensar demandas, restaurar serviços ecossistêmicos, almejando, portanto, a sustentabilidade da paisagem.
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A presente dissertação de mestrado consiste em um estudo de caso de três programas de pagamento por serviços ecossistêmicos - PSE, que ajudaram a definir o papel que o direito deve assumir na implementação e manutenção desses mecanismos. Buscou-se, primeiramente, delimitar algumas bases teóricas, sobretudo, o que se entende por desenvolvimento sustentável e sustentabilidade institucional. Para tanto, optamos por demonstrar a evolução conceitual de serviços ambientais para serviços ecossistêmicos e entender este como uma segunda fase daquele, destacando os reflexos desse entendimento na estrutura jurídica dos programas de pagamento por serviços ambientais, que optamos por chama-lo de pagamento por serviços ecossistêmicos. Em seguida, descrevemos toda a evolução das discussões sobre REDD+, exemplo de PSE, para enfatizar os desafios que o direito assume com essa nova concepção de serviços ecossistêmicos. A experiência indica que o sucesso dos programas analisados são, em grande medida, consequência da ideia de função promocional do direito, bem como da observação das suas funcionalidades, quais sejam, orquestração, sinergia, flexibilização e legitimidade, que garantem, antes de mais nada, a sustentabilidade institucional dos mecanismos, permitindo sua perfeita adequação à realidade em que se insere e, mais do que isso, permitindo a manutenção desses instrumentos, mesmo diante de mutações do meio em que estão inseridos.
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Since the passage of the Federal-Aid Highway Act of 1956, the automobile has become the primary form of transportation on the Mississippi Gulf Coast. As the rate of motor vehicle use continues to rise faster than population growth, the benefits of the current transportation system are coming at a price that rivals annual household expenditures for housing. Furthermore, the automobile-centric transportation system incurs environmental costs. Carbon dioxide emissions, motor fuel use, health care costs for chronic illness, and the loss and impairment of natural resources due to sprawling development, continue to escalate. This project analyzes the environmental costs associated with automobile-centric planning for the urbanized area of the Mississippi Gulf Coast and compares these costs to those of alternative transportation modes.
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Restoration efforts in the Mediterranean Basin have been changing from a silvicultural to an ecological restoration approach. Yet, to what extent the projects are guided by ecological restoration principles remains largely unknown. To analyse this issue, we built an on-line survey addressed to restoration practitioners. We analysed 36 restoration projects, mostly from drylands (86%). The projects used mainly soil from local sources. The need to comply with legislation was more important as a restoration motive for European Union (EU) than for non-EU countries, while public opinion and health had a greater importance in the latter. Non-EU countries relied more on non-native plant species than EU countries, thus deviating from ecological restoration guidelines. Nursery-grown plants used were mostly of local or regional provenance, whilst seeds were mostly of national provenance. Unexpected restoration results (e.g. inadequate biodiversity) were reported for 50% of the projects and restoration success was never evaluated in 22%. Long term evaluation (> 6 years) was only performed in 31% of cases, and based primarily on plant diversity and cover. The use of non-native species and species of exogenous provenances may: i) entail the loss of local genetic and functional trait diversity, critical to cope with drought, particularly under the predicted climate change scenarios, and ii) lead to unexpected competition with native species and/or negatively impact local biotic interactions. Absent or inappropriate monitoring may prevent the understanding of restoration trajectories, precluding adaptive management strategies, often crucial to create functional ecosystems able to provide ecosystem services. The overview of ecological restoration projects in the Mediterranean Basin revealed high variability among practices and highlighted the need for improved scientific assistance and information exchange, greater use of native species of local provenance, and more long-term monitoring and evaluation, including functional and ecosystem services' indicators, to improve and spread the practice of ecological restoration.
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Using the results from the NCAR CSM1.4-coupled global carbon cycle– climate model under the Intergovernmental Panel on Climate Change (IPCC) emission scenarios SRES A2 and B1, we estimated the effects of both global warming and ocean acidification on the future habitats of corals in the seas around Japan during this century. As shown by Yara et al. (Biogeosciences 9:4955–4968,2012), under the high-CO₂-emission scenario (SRES A2), coral habitats will be sandwiched and narrowed between the northern region, where the saturation state of the carbonate mineral aragonite (Ωarag) decreases, and the southern region, where coral bleaching occurs. We found that under the low-emission scenario SRES B1, the coral habitats will also shrink in the northern region by the reduced Ωarag but to a lesser extent than under SRES A2, and in contrast to SRES A2, no bleaching will occur in the southern region. Therefore, coral habitats in the southern region are expected to be largely unaffected by ocean acidification or surface warming under the low-emission scenario. Our results show that potential future coral habitats depend strongly on CO₂ emissions and emphasize the importance of reducing CO₂ emissions to prevent negative impacts on coral habitats.
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The spatial data set delineates areas with similar environmental properties regarding soil, terrain morphology, climate and affiliation to the same administrative unit (NUTS3 or comparable units in size) at a minimum pixel size of 1km2. The scope of developing this data set is to provide a link between spatial environmental information (e.g. soil properties) and statistical data (e.g. crop distribution) available at administrative level. Impact assessment of agricultural management on emissions of pollutants or radiative active gases, or analysis regarding the influence of agricultural management on the supply of ecosystem services, require the proper spatial coincidence of the driving factors. The HSU data set provides e.g. the link between the agro-economic model CAPRI and biophysical assessment of environmental impacts (updating previously spatial units, Leip et al. 2008), for the analysis of policy scenarios. Recently, a statistical model to disaggregate crop information available from regional statistics to the HSU has been developed (Lamboni et al. 2016). The HSU data set consists of the spatial layers provided in vector and raster format as well as attribute tables with information on the properties of the HSU. All input data for the delineation the HSU is publicly available. For some parameters the attribute tables provide the link between the HSU data set and e.g. the soil map(s) rather than the data itself. The HSU data set is closely linked the USCIE data set.
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Thesis (Master's)--University of Washington, 2016-06
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In order for policy makers to plan effectively for sustainable development, there is a need for measures of welfare that consider changes in the natural capital stock. Current measures based on conventional national accounting are flawed because they are based solely on flow measures and do not account for environmental effects. In this paper, we use an expanded measure of wealth to estimate the value of natural capital for Queensland. The state's stock of natural capital is valued at A$355.6 billion, of which non-timber forest resources account for 45.3%, ecosystem services 20.0%, and mineral resources 17.6%. This figure is a conservative estimate of the true value since some significant components such as the ecological and life-support functions of the environment are excluded. The estimates highlight the relative importance of different forms of natural capital and can be used to draw the attention of policymakers to the need to give adequate weight to the value of such services in decision-making processes. (c) 2005 Elsevier Ltd. All rights reserved.
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Mangrove forest structure and sediment characteristics were examined in the extensive mangroves of Bocas del Toro, Republic of Panama. Forest structure was characterized to determine if spatial vegetation patterns were repeated over the Bocas del Toro landscape. Using a series of permanent plots and transects we found that the forests of Bocas del Toro were dominated by Rhizophora maugle with very few individuals of Avicennia germinans and Laguncularia racemosa. Despite this low species diversity, there was large variation in forest structure and in edaphic conditions (salinity, concentration of available phosphorus, Eh and sulphide concentration). Aboveground biomass varied 20-fold, from 6.8 Mg ha(-1) in dwarf forests to 194.3 Mg ha(-1) in the forests fringing the land. But variation in forest structure was predictable across the intertidal zone. There was a strong tree height gradient from seaward fringe (mean tree height 3.9 m), decreasing in stature in the interior dwarf forests (mean tree height 0.7 m), and increasing in stature in forests adjacent to the terrestrial forest (mean tree height 4.1 m). The predictable variation in forest structure emerges due to the complex interactions among edaphic and plant factors. Identifying predictable patterns in forest structure will aid in scaling up the ecosystem services provided by mangrove forests in coastal landscapes.
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The failures of traditional target-species management have led many to propose an ecosystem approach to fisheries to promote sustainability. The ecosystem approach is necessary, especially to account for fishery-ecosystem interactions, but by itself is not sufficient to address two important factors contributing to unsustainable fisheries: inappropriate incentives bearing on fishers and the ineffective governance that frequently exists in commercial, developed fisheries managed primarily by total-harvest limits and input controls. We contend that much greater emphasis must be placed on fisher motivation when managing fisheries. Using evidence from more than a dozen natural experiments in commercial fisheries, we argue that incentive-based approaches that better specify community and individual harvest or territorial rights and price ecosystem services and that are coupled with public research, monitoring, and effective oversight promote sustainable fisheries.
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In order to take an interest in environmental issues, people need an idea of what ‘the environment’ is, and to have access to something worth caring about. In the UK, around 90% of us already live in towns or cities, and by 2030, around 60% of the world’s population will live in urban areas. But without a vocal set of ‘owners’, public land such as parks and allotments can easily be lost. The majority of the UK's ‘natural’ areas have historically been created, managed or modified by humans. and we should appreciate urban habitats just as much as pristine reserves for the ecosystem services they provide. In particular, scruffy and overlooked brownfield sites can be amazing refugia for insect and plant species which can no longer persist in a countryside dominated by industrialised agriculture.