963 resultados para 090702 Environmental Engineering Modelling


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The episodic occurrence of debris flow events in response to stochastic precipitation and wildfire events makes hazard prediction challenging. Previous work has shown that frequency-magnitude distributions of non-fire-related debris flows follow a power law, but less is known about the distribution of post-fire debris flows. As a first step in parameterizing hazard models, we use frequency-magnitude distributions and cumulative distribution functions to compare volumes of post-fire debris flows to non-fire-related debris flows. Due to the large number of events required to parameterize frequency-magnitude distributions, and the relatively small number of post-fire event magnitudes recorded in the literature, we collected data on 73 recent post-fire events in the field. The resulting catalog of 988 debris flow events is presented as an appendix to this article. We found that the empirical cumulative distribution function of post-fire debris flow volumes is composed of smaller events than that of non-fire-related debris flows. In addition, the slope of the frequency-magnitude distribution of post-fire debris flows is steeper than that of non-fire-related debris flows, evidence that differences in the post-fire environment tend to produce a higher proportion of small events. We propose two possible explanations: 1) post-fire events occur on shorter return intervals than debris flows in similar basins that do not experience fire, causing their distribution to shift toward smaller events due to limitations in sediment supply, or 2) fire causes changes in resisting and driving forces on a package of sediment, such that a smaller perturbation of the system is required in order for a debris flow to occur, resulting in smaller event volumes.

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There is a growing trend towards using thinner wafers in order to reduce the costs of solar energy. But the current tools employed during the solar cells production are not prepared to work with thinner wafers, decreasing the industrial yield due to the high number of wafers broken. To develop new tools, or modify existing ones, the mechanical properties have to be determined. This paper tackles an experimental study of the mechanical properties of wafers. First, the material characteristics are detailed and the process to obtain wafers is presented. Then, the complete test setup and the mechanical strength results interpreted by a described numerical model are shown.

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System identification deals with the problem of building mathematical models of dynamical systems based on observed data from the system" [1]. In the context of civil engineering, the system refers to a large scale structure such as a building, bridge, or an offshore structure, and identification mostly involves the determination of modal parameters (the natural frequencies, damping ratios, and mode shapes). This paper presents some modal identification results obtained using a state-of-the-art time domain system identification method (data-driven stochastic subspace algorithms [2]) applied to the output-only data measured in a steel arch bridge. First, a three dimensional finite element model was developed for the numerical analysis of the structure using ANSYS. Modal analysis was carried out and modal parameters were extracted in the frequency range of interest, 0-10 Hz. The results obtained from the finite element modal analysis were used to determine the location of the sensors. After that, ambient vibration tests were conducted during April 23-24, 2009. The response of the structure was measured using eight accelerometers. Two stations of three sensors were formed (triaxial stations). These sensors were held stationary for reference during the test. The two remaining sensors were placed at the different measurement points along the bridge deck, in which only vertical and transversal measurements were conducted (biaxial stations). Point estimate and interval estimate have been carried out in the state space model using these ambient vibration measurements. In the case of parametric models (like state space), the dynamic behaviour of a system is described using mathematical models. Then, mathematical relationships can be established between modal parameters and estimated point parameters (thus, it is common to use experimental modal analysis as a synonym for system identification). Stable modal parameters are found using a stabilization diagram. Furthermore, this paper proposes a method for assessing the precision of estimates of the parameters of state-space models (confidence interval). This approach employs the nonparametric bootstrap procedure [3] and is applied to subspace parameter estimation algorithm. Using bootstrap results, a plot similar to a stabilization diagram is developed. These graphics differentiate system modes from spurious noise modes for a given order system. Additionally, using the modal assurance criterion, the experimental modes obtained have been compared with those evaluated from a finite element analysis. A quite good agreement between numerical and experimental results is observed.

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The boundary element method (BEM) has been applied successfully to many engineering problems during the last decades. Compared with domain type methods like the finite element method (FEM) or the finite difference method (FDM) the BEM can handle problems where the medium extends to infinity much easier than domain type methods as there is no need to develop special boundary conditions (quiet or absorbing boundaries) or infinite elements at the boundaries introduced to limit the domain studied. The determination of the dynamic stiffness of arbitrarily shaped footings is just one of these fields where the BEM has been the method of choice, especially in the 1980s. With the continuous development of computer technology and the available hardware equipment the size of the problems under study grew and, as the flop count for solving the resulting linear system of equations grows with the third power of the number of equations, there was a need for the development of iterative methods with better performance. In [1] the GMRES algorithm was presented which is now widely used for implementations of the collocation BEM. While the FEM results in sparsely populated coefficient matrices, the BEM leads, in general, to fully or densely populated ones, depending on the number of subregions, posing a serious memory problem even for todays computers. If the geometry of the problem permits the surface of the domain to be meshed with equally shaped elements a lot of the resulting coefficients will be calculated and stored repeatedly. The present paper shows how these unnecessary operations can be avoided reducing the calculation time as well as the storage requirement. To this end a similar coefficient identification algorithm (SCIA), has been developed and implemented in a program written in Fortran 90. The vertical dynamic stiffness of a single pile in layered soil has been chosen to test the performance of the implementation. The results obtained with the 3-d model may be compared with those obtained with an axisymmetric formulation which are considered to be the reference values as the mesh quality is much better. The entire 3D model comprises more than 35000 dofs being a soil region with 21168 dofs the biggest single region. Note that the memory necessary to store all coefficients of this single region is about 6.8 GB, an amount which is usually not available with personal computers. In the problem under study the interface zone between the two adjacent soil regions as well as the surface of the top layer may be meshed with equally sized elements. In this case the application of the SCIA leads to an important reduction in memory requirements. The maximum memory used during the calculation has been reduced to 1.2 GB. The application of the SCIA thus permits problems to be solved on personal computers which otherwise would require much more powerful hardware.

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This paper presents a simplified finite element (FE) methodology for solving accurately beam models with (Timoshenko) and without (Bernoulli-Euler) shear deformation. Special emphasis is made on showing how it is possible to obtain the exact solution on the nodes and a good accuracy inside the element. The proposed simplifying concept, denominated as the equivalent distributed load (EDL) of any order, is based on the use of Legendre orthogonal polynomials to approximate the original or acting load for computing the results between the nodes. The 1-span beam examples show that this is a promising procedure that allows the aim of using either one FE and an EDL of slightly higher order or by using an slightly larger number of FEs leaving the EDL in the lowest possible order assumed by definition to be equal to 4 independently of how irregular the beam is loaded.

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Análisis de precisión en modelos digitales de elevación globales. ABSTRACT: Terrain-Based Analysis results in derived products from an input DEM and these products are needed to perform various analyses. To efficiently use these products in decision-making, their accuracies must be estimated systematically. This paper proposes a procedure to assess the accuracy of these derived products, by calculating the accuracy of the slope dataset and its significance, taking as an input the accuracy of the DEM. Based on the output of previously published research on modeling the relative accuracy of a DEM, specifically ASTER and SRTM DEMs with Lebanon coverage as the area of study, analysis have showed that ASTER has a low significance in the majority of the area where only 2% of the modeled terrain has 50% or more significance. On the other hand, SRTM showed a better significance, where 37% of the modeled terrain has 50% or more significance. Statistical analysis deduced that the accuracy of the slope dataset, calculated on a cell-by-cell basis, is highly correlated to the accuracy of the input DEM. However, this correlation becomes lower between the slope accuracy and the slope significance, whereas it becomes much higher between the modeled slope and the slope significance.

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Actualmente en nuestro planeta producimos 1.300 millones de toneladas de residuos urbanos al año. Si los extendemos sobre la superficie de un cuadrado de lado 100 m (una hectárea) alcanzarían una altura de 146 km. ¿Cuál es el origen de nuestros residuos? ¿A dónde va esta basura? ¿Cómo nos afecta? ¿Tiene alguna utilidad? Se trata de un problema antiguo que, en los últimos tiempos, ha adquirido una nueva dimensión por el tipo y la cantidad de residuos generados. Las primeras preocupaciones de la ciudad por ordenar estos problemas dieron lugar al establecimiento de espacios o lugares específicos para la acumulación de los residuos urbanos: los vertederos. Los desechos hoy se generan más rápidamente que los medios disponibles para reciclarlos o tratarlos. Los vertederos de residuos urbanos son y seguirán siendo, a corto y medio plazo, soluciones válidas por ser un método de gestión relativamente barato, sobre todo en los países en vías de desarrollo. Como consecuencia y necesidad de lo anterior, se plantea demostrar que la recuperación y la transformación de estos vertederos de residuos urbanos (lugares del deterioro), una vez abandonados, es posible y que además pueden dar lugar a nuevos espacios públicos estratégicos de la ciudad contemporánea. Son espacios de oportunidad, vacíos monumentales producto de una reactivación arquitectónica y paisajística realizada a partir de complejos procesos de ingeniería medioambiental. Pero las soluciones aplicadas a los vertederos de residuos urbanos desde mediados del siglo XX se han realizado exclusivamente desde la ingeniería para tratar de resolver cuestiones técnicas, un modelo agotado que ya no puede gestionar la magnitud que este problema ha alcanzado, haciéndose necesaria e inevitable la participación de la arquitectura para abrir nuevas líneas de investigación y de acción. En estos primeros compases del siglo XXI existe una “nueva” preocupación, un “nuevo” interés en los paradigmas de lo ecológico y de la sostenibilidad, también un interés filosófico (que igualmente otorga un nuevo valor al residuo como recurso), que dirigen su mirada hacia un concepto de paisaje abierto y diferente a modelos anteriores más estáticos, recuperando como punto de partida el ideal pintoresco. El landscape urbanism se consolida como una disciplina capaz de dar respuesta a lo natural y artificial simultáneamente, que sustituye a las herramientas tradicionales de la arquitectura para solucionar los problemas de la ciudad contemporánea, incorporando las infraestructuras de gran escala, como un vertedero de residuos urbanos, y los paisajes públicos que generan como el verdadero mecanismo de organización del urbanismo de hoy. No se trata solo de un modelo formal sino, lo que es más importante: de un modelo de procesos. Esta nueva preocupación permite abordar la cuestión del paisaje de manera amplia, sin restricciones, con un alto grado de flexibilidad en las nuevas propuestas que surgen como consecuencia de estos conceptos, si bien los esfuerzos, hasta la fecha, parecen haberse dirigido más hacia el fenómeno de lo estético, quedando todavía por explorar las consecuencias políticas, sociales, económicas y energéticas derivadas de los residuos. También las arquitectónicas. El proyecto del landscape urbanism se ocupa de la superficie horizontal, del plano del suelo. Desde siempre, la preparación de este plano para desarrollar cualquier actividad humana ha sido un gesto fundacional, un gesto propio necesario de toda arquitectura, que además ahora debe considerarlo como un medio o soporte biológicamente activo. En términos contemporáneos, el interés disciplinar radica en la continuidad y en la accesibilidad del suelo, diluyendo los límites; en que funcione a largo plazo, que se anticipe al cambio, a través de la flexibilidad y de la capacidad de negociación, y que sea público. La recuperación de un vertedero de residuos urbanos ofrece todas estas condiciones. Un breve recorrido por la historia revela los primeros ejemplos aislados de recuperación de estos lugares del deterioro, que han pasado por distintas fases en función de la cantidad y el tipo de los desechos producidos, evolucionando gracias a la tecnología y a una nueva mirada sobre el paisaje, hasta desarrollar una verdadera conciencia de lo ecológico (nacimiento de una ideología). El Monte Testaccio en Roma (siglos I-III d.C.) constituye un caso paradigmático y ejemplar de vertedero planificado a priori no solo como lugar en el que depositar los residuos, sino como lugar que será recuperado posteriormente y devuelto a la ciudad en forma de espacio público. Una topografía de desechos generada por acumulación, organizada y planificada durante tres siglos, que nos hace reflexionar sobre los temas de producción, consumo y proyecto arquitectónico. El Monte Testaccio revela una fuente de inspiración, un arquetipo de gestión sostenible de los recursos y del territorio. A través de la experiencia en la recuperación y transformación en espacios públicos de casos contemporáneos, como el antiguo vertedero de Valdemingómez en Madrid o el de El Garraf en Barcelona, se han analizado las técnicas y las soluciones empleadas para establecer nuevas herramientas de proyecto planteadas en clave de futuro, que revelan la importancia de los procesos frente a la forma, en los cuales intervienen muchos factores (tanto naturales como artificiales), entre ellos la vida y el tiempo de la materia viva acumulada. Son lugares para nuevas oportunidades y ejemplos de una nueva relación con la naturaleza. La reactivación de los vertederos de residuos, a través del proyecto, nos propone una nueva topografía construida en el tiempo, el suelo como soporte, como punto de encuentro de la naturaleza y los sistemas tecnológicos de la ciudad que posibilitan nuevos modos de vida y nuevas actividades. Los vertederos de residuos son inmensas topografías naturales surgidas de procesos artificiales, atalayas desde las que divisar un nuevo horizonte, un nuevo mundo, un nuevo futuro donde sea posible lograr la reversibilidad de nuestros actos del deterioro. Pero la voluntad de estas recuperaciones y transformaciones no consiste exclusivamente en su reintegración al paisaje, sino que han servido como muestra de las nuevas actitudes que la sociedad ha de emprender en relación a los temas medio ambientales. ABSTRACT Here on our planet we currently produce 1.3 billion tonnes of urban waste per year. If we were to spread this over a surface of 100m2 (one hectare), it would reach a height of 146km. What is the origin of this waste? Where does our refuse go? How does it affect us? Does it have any uses? We are dealing with an old problem which, in recent times, has taken on a new dimension due to the type of waste and the amount generated. Cities’ first concerns in resolving these problems gave rise to the establishment of areas or specific places for the accumulation of urban waste: landfills. These days, waste is generated more quickly than the available resources can recycle or process it. Urban waste landfills are and will continue to be, in the short and mid-term, valid solutions, given that they constitute a relatively cheap method for waste management, especially in developing countries. Consequently and necessarily, we plan to demonstrate that it is possible to recover and transform these urban waste landfills (areas of deterioration) once they have been abandoned and that they can give rise to new strategic public areas in contemporary cities. They are areas of opportunity, monumental vacancies produced by an architectural reactivation of the landscape, which is achieved using complex processes of environmental engineering. But the solutions applied to urban waste landfills throughout the 20th century have used engineering exclusively in the attempt to resolve the technical aspects. This is a worn-out model which can no longer handle the magnitude which the problem has attained and therefore, there is an inevitable need for the participation of architecture, which can open new lines of research and action. In these first steps into the 21st century, there is a “new” concern, a “new” interest in the paradigms of environmentalism and sustainability. There is also a philosophical interest (which assigns the new value of ‘resource’ to waste) and all is aimed towards the concept of an open landscape, unlike the previous, more static models, and the intention is to recover picturesque ideals as the starting point. Landscape urbanism has been established as a discipline capable of simultaneously responding to the natural and the artificial, replacing the traditional tools of architecture in order to resolve contemporary cities’ problems. It incorporates large scale infrastructures, such as urban waste landfills, and public landscapes which are generated as the true organisational mechanism of modern day urbanism. It is not merely a formal model, it is more important than that: it is a model of processes. This new concern allows us to address the matter of landscape in a broad way, without restrictions, and with a great degree of flexibility in the new proposals which come about as a consequence of these concepts. However, efforts to date seem to have been more directed at aesthetic aspects and we have yet to explore the political, social, economic and energetic consequences derived from waste – nor have we delved into the architectural consequences. The landscape urbanism project is involved with the horizontal surface, the ground plane. Traditionally, the preparation of this plane for the development of any human activity has been a foundational act, a necessary act of all architecture, but now this plane must be considered as a biologically active medium or support. In contemporary terms, the discipline’s interest lies in the continuity and accessibility of the land, diffusing the limits; in long term functionality; in the anticipation of change, via flexibility and the ability to negotiate; and in it being a public space. The recovery of an urban waste landfill offers all of these conditions. A brief look through history reveals the first isolated examples of recovery of these spaces of deterioration. They have gone through various phases based on the quantity and type of waste produced, they have evolved thanks to technology and a new outlook on the landscape, and a real environmental awareness has been developed (the birth of an ideology). Monte Testaccio in Rome (1st to 3rd Century AD) constitutes a paradigmatic and exemplary case of a landfill that was planned a priori not only as a place to deposit waste but also as a place that would be subsequently recovered and given back to the city in the form of a public space. This spoil mound, generated by organised and planned accumulation over three centuries, makes us reflect on the themes of production, consumption and architectural planning. Monte Testaccio reveals a source of inspiration, an archetype of the sustainable management of resources and land. Using our experience of contemporary cases of land recovery and its transformation into public spaces, such as the former Valdemingómez landfill in Madrid or the Garraf in Barcelona, we analysed the techniques and solutions used in order to establish new project tools. These are proposed with an eye on the future, seeing as they reveal the importance of the processes over the form and involve many factors (both natural and artificial), including the life and age of the accumulated living matter. They are places for new opportunities and examples of our new relationship with nature. The reactivation of landfills, via this project, is a proposal for a new topography built within time, using the ground as the support, as the meeting point between nature and the technological systems of the city which make it possible for new ways of life and new activities to come about. Landfills are immense natural topographical areas produced by artificial processes, watchtowers from which to discern a new horizon, a new world, a new future in which it will be possible to reverse our acts of deterioration. But the intention behind these recoveries and transformations does not only hope for landscape reintegration but it also hopes that they will also serve as a sign of the new attitudes that must be adopted by society with regard to environmental matters.

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Sodium phosphates are a class of chemicals that have been widely employed in commercial and consumer applications. However, declining use of these chemicals due to environmental concerns has lead to restructuring within the industry that has caused, and is likely to continue to cause, reduction of sodium phosphate production capacity. Closure of a sodium phosphate manufacturing plant necessitates decommissioning and decontamination activities that are subject to a variety of federal, state, and local regulations. A compliance plan was developed to provide a blueprint for ensuring that all federal regulatory requirements are met, however, site dependent state and local requirements were excluded. The compliance plan provides a framework that addresses project team formation and project planning, regulatory requirements, identification of affected processing equipment, plant pre-shutdown activities, waste stream identification and waste management facilities, safety, training, and emergency preparedness planning, and project decommissioning remedial actions. This regulatory compliance plan will enable sodium phosphate plant operators to complete decontamination and decommissioning work in a timely, efficient, compliant, and cost effective manner.

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