963 resultados para Waste management models
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Directive 2008/98/EC released by the European Union represents a significant step forward in all relevant aspects of waste management. Under the already established, extended produced responsibility (EPR) principle, new policies have been enunciated to continuously achieve better overall environmental performance of key products throughout their life phases. This paper discusses how the directive is being articulated in Spain by the main integrated management system (IMS) for end-of-life (EOL) tyres since its creation in 2006. Focusing on the IMS technological, economic and legal aspects, the study provides a global perspective and evaluation of how the IMS is facing the current issues to resolve, the new challenges that have appeared and the management vision for the coming years.
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Environmental problems related to the use of synthetic fertilizers and to organic waste management have led to increased interest in the use of organic materials as an alternative source of nutrients for crops, but this is also associated with N2O emissions. There has been an increasing amount of research into the effects of using different types of fertilization on N2O emissions under Mediterranean climatic conditions, but the findings have sometimes been rather contradictory. Available information also suggests that water management could exert a high influence on N2O emissions. In this context, we have reviewed the current scientific knowledge, including an analysis of the effect of fertilizer type and water management on direct N2O emissions. A meta-analysis of compliant reviewed experiments revealed significantly lower N2O emissions for organic as opposed to synthetic fertilizers (23% reduction). When organic materials were segregated in solid and liquid, only solid organic fertilizer emissions were significantly lower than those of synthetic fertilizers (28% reduction in cumulative emissions). The EF is similar to the IPCC factor in conventionally irrigated systems (0.98% N2O-N N applied−1), but one order of magnitude lower in rainfed systems (0.08%). Drip irrigation produces intermediate emission levels (0.66%). Differences are driven by Mediterranean agro-climatic characteristics, which include low soil organic matter (SOM) content and a distinctive rainfall and temperature pattern. Interactions between environmental and management factors and the microbial processes involved in N2O emissions are discussed in detail. Indirect emissions have not been fully accounted for, but when organic fertilizers are applied at similar N rates to synthetic fertilizers, they generally make smaller contributions to the leached NO3− pool. The most promising practices for reducing N2O through organic fertilization include: (i) minimizing water applications; (ii) minimizing bare soil; (iii) improving waste management; and (iv) tightening N cycling through N immobilization. The mitigation potential may be limited by: (i) residual effect; (ii) the long-term effects of fertilizers on SOM; (iii) lower yield-scaled performance; and (iv) total N availability from organic sources. Knowledge gaps identified in the review included: (i) insufficient sampling periods; (ii) high background emissions; (iii) the need to provide N2O EF and yield-scaled EF; (iv) the need for more research on specific cropping systems; and (v) the need for full GHG balances. In conclusion, the available information suggests a potential of organic fertilizers and water-saving practices to mitigate N2O emissions under Mediterranean climatic conditions, although further research is needed before it can be regarded as fully proven, understood and developed.
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In this work, sewage sludge was used as precursor in the production of activated carbon by means of chemical activation with KOH and NaOH. The sludge-based activated carbons were investigated for their gaseous adsorption characteristics using CO2 as adsorbate. Although both chemicals were effective in the development of the adsorption capacity, the best results were obtained with solid NaOH (SBAT16). Adsorption results were modeled according to the Langmuir and Freundlich models, with resulting CO2 adsorption capacities about 56 mg/g. The SBAT16 was characterized for its surface and pore characteristics using continuous volumetric nitrogen gas adsorption and mercury porosimetry. The results informed about the mesoporous character of the SBAT16 (average pore diameter of 56.5 Å). The Brunauer-Emmett-Teller (BET) surface area of the SBAT16 was low (179 m2/g) in comparison with a commercial activated carbon (Airpel 10; 1020 m2/g) and was mainly composed of mesopores and macropores. On the other hand, the SBAT16 adsorption capacity was higher than that of Airpel 10, which can be explained by the formation of basic surface sites in the SBAT16 where CO2 experienced chemisorption. According to these results, it can be concluded that the use of sewage-sludge-based activated carbons is a promising option for the capture of CO2. Implications: Adsorption methods are one of the current ways to reduce CO2 emissions. Taking this into account, sewage-sludge-based activated carbons were produced to study their CO2 adsorption capacity. Specifically, chemical activation with KOH and NaOH of previously pyrolyzed sewage sludge was carried out. The results obtained show that even with a low BET surface area, the adsorption capacity of these materials was comparable to that of a commercial activated carbon. As a consequence, the use of sewage-sludge-based activated carbons is a promising option for the capture of CO2 and an interesting application for this waste.
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The difficulty of dealing with construction and demolition waste (CDW) on construction sites is not new and continues to be a significant environmental problem. Currently the CDW collection system in Spain is done in a decentralized manner by each sub-contracted company, being necessary to implement effective waste management measures ensuring a correct management and minimization. During the last years several measures have been launched in order to improve and encourage the reuse and recycling of CDW. A widespread solution for CDW recovery is using them as a landscaping aggregate or for road bases and sub-bases. However, measures encouraging onsite prevention still need to be enhanced. This paper studies the major work stage generating CDW and analyses the categories of CDW produced during its execution. For this, several real building sites have been analysed in order to quantify the estimation of CDW generated. Results of this study show that a significant contributor to the CDW generation on building construction sites in Spain are the masonry works. Finally, a Best Practices Manual (BPM) is proposed containing several strategies on masonry works aimed not only at CDW prevention, but also at improving their management and minimization. The use of this BPM together with the Study and Plan of CDW management --required by law--, promotes the environmental management of the company, favouring the cohesion of the construction process organization at all stages giving rise to establishing responsibilities in the field of waste and providing a greater control over the process. Keywords: construction and demolition waste, management, masonry works, good practice measures, prevention.
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La gestión de las tecnologías de la información tiene cada vez más importancia dentro de un mundo totalmente digitalizado y donde la capacidad de respuesta al cambio puede marcar el devenir de una compañía, y resulta cada vez más evidente que los modelos de gestión tradicionales utilizados en la mayoría de las compañías no son capaces de dar respuesta por si solos a estas nuevas necesidades. Aun teniendo identificado este área de mejora, son muchas las empresas reacias a abordar estos cambios, principalmente por el cambio rupturista que significa a nivel interno. De cara a facilitar esta transformación, se propone en este documento un modelo de transición controlada donde las grandes compañías puedan incorporar nuevas alternativas y herramientas ágiles de forma paulatina y asegurando que el proceso de cambio es seguro y efectivo. Mediante una modificación del ciclo de vida de proyecto dentro de la compañía, se incorporan en las áreas, equipos o dominios de la empresa que se identifiquen los nuevos modelos de gestión ágil, permitiendo así una transición gradual y controlada, y pudiendo además analizar los detalles sobre todo en etapas tempranas de la transformación. Una vez seleccionada el área o dominio objeto de la transformación, se realiza un análisis a nivel de Portfolio de proyectos, identificando aquellos que cumplen una serie de condiciones que les permiten ser gestionados utilizando modelos de gestión ágil. Para ello, se plantea una matriz de decisión con las principales variables a tener en cuenta a la hora de tomar una decisión. Una vez seleccionado y consensuado con los interesados el modelo de gestión utilizando la matriz de decisión, se plantean una serie de herramientas y métricas asociadas para que la gestión ágil del proyecto dé una visibilidad completa y detallada del estado en cada momento, asegurando un correcto proceso de gestión de proyectos para proveer visibilidad regular del progreso, riesgos, planes de contingencia y problemas, con las alertas y escalaciones adecuadas. Además de proponerse una serie de herramientas y métricas para la gestión ágil del proyecto, se plantean las modificaciones necesarias sobre las tipologías habituales de contrato y se propone un nuevo modelo de contrato: el Contrato Agile. La principal diferencia entre este nuevo modelo de contrato y los habituales es que, al igual que las metodologías ágiles, es ejecutado en segmentos o iteraciones. En definitiva, el objetivo de este documento es proveer un mecanismo que facilite la inclusión de nuevos modelos ágiles de gestión en grandes organizaciones, llevando a cabo una transición controlada, con herramientas y métricas adaptadas para tener visibilidad completa sobre los proyectos en todo momento.---ABSTRACT---The information technology management is every time more important in a totally digitized world, where the capacity to response the change could mark the future of a company, and results every time more evident that the traditional management models used in the most of the companies are not able to respond by themselves to these new necessities. Even having identified this improvement area, many companies are reluctant to address these changes, mainly due to the disruptive change that it means internally in the companies. In order to facilitate this transformation, this document proposed a controlled transition model to help the big companies to incorporate new alternatives and agile tools gradually and ensuring that the change process is safe and effective. Through a modification the project life cycle inside the company, the new agile management models are incorporated in the selected areas, teams or domains, permitting a gradual and controlled transition, and enabling further analyze the details above all in the early phases of the transformation. Once is selected the area or domain object of the transformation, a portfolio level analysis is performed, identifying those projects that meet a some conditions that allow them to be managed using agile management models. For that, a decision matrix is proposed with the principal variables to have into account at the time of decision making. Once the management model is selected using the decision matrix and it is agreed with the different stakeholders, a group of tools and metrics associated with the agile management projects are proposed to provide a regular visibility of the project progress, risks, contingency plans and problems, with proper alerts and escalations. Besides the group of tools and metrics proposed for agile project management, the necessary modifications over the traditional contract models and a new contract model are proposed: the Agile Contract. The main difference between this new contract model and the traditional ones is that, as the agile methodologies, it is executed in segments or iterations. To sum up, the objective of this document is to provide a mechanism that facilitates the inclusion of new agile management models in big companies, with a controlled transition and proposing adapted tools and metrics to have a full visibility over the project in all the phases of the project life cycle.
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Current EU Directives force the Member States to assure by 2020 that 70% of the Construction and Demolition (C&D) waste is recovered instead of landfilled. While some countries have largely achieved this target, others still have a long way to go. For better understanding the differences arising from local disparities, six factors related to technical, economic, legislative and environmental aspects have been identified as crucial influences in the market share of C&D waste recycling solutions. These factors are able to identify the causes that limit the recycling rate of a certain region. Moreover, progress towards an efficient waste management can vary through the improvement of a single factor. This study provides the background for further fine-tuning the factors and their combination into a mathematical model for assessing the market share of C&D recycling solutions.
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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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Gaseous emissions are an important problem in municipal solid waste (MSW) treatment plants. The sources points of emissions considered in the present work are: fresh compost, mature compost, landfill leaks and leachate ponds. Hydrogen sulphide, ammonia and volatile organic compounds (VOCs) were analysed in the emissions from these sources. Hydrogen sulphide and ammonia were important contributors to the total emission volume. Landfill leaks are significant source points of emissions of H2S; the average concentration of H2S in biogas from the landfill leaks is around 1700 ppmv. The fresh composting site was also an important contributor of H2S to the total emission volume; its concentration varied between 3.2 and 1.7 ppmv and a decrease with time was observed. The mature composting site showed a reduction of H2S concentration (<0.1 ppmv). Leachate pond showed a low concentration of H2S (in order of ppbv). Regarding NH3, composting sites and landfill leaks are notable source points of emissions (composting sites varied around 30–600 ppmv; biogas from landfill leaks varied from 160 to 640 ppmv). Regarding VOCs, the main compounds were: limonene, p-cymene, pinene, cyclohexane, reaching concentrations around 0.2–4.3 ppmv. H2S/NH3, limonene/p-cymene, limonene/cyclohexane ratios can be useful for analysing and identifying the emission sources.
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Furniture waste is mainly composed of wood and upholstery foam (mostly polyurethane foam). Both of these have a high calorific value, therefore, energy recovery would be an appropriate process to manage these wastes. Nevertheless, the drawback is that the energy content of these wastes is limited due to their low density mainly that of upholstery foam. Densification of separate foam presents difficulties due to its elastic character. The significance of this work lies in obtaining densified material by co-densification of furniture wood waste and polyurethane foam waste. Densification of furniture wood and the co-densification of furniture wood waste with polyurethane foam have been studied. On the one hand, the parameters that have an effect on the quality of the furniture waste briquettes have been analysed, i.e., moisture content, compaction pressure, presence of lignin, etc. The maximum weight percentage of polyurethane foam that can be added with furniture wood waste to obtain durable briquettes and the optimal moisture were determined. On the other hand, some parameters were analysed in order to evaluate the possible effect on the combustion. The chemical composition of waste wood was compared with untreated wood biomass; the higher nitrogen content and the concentration of some metals were the most important differences, with a significant difference of Ti content.
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Mode of access: Internet.
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Work performed for the Office of Solid Waste under contract no. 68-01-4381.
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"Contract number 68-03-0315."
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"Contract no. 68-01-4427"--Verso of t.p.
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Item 431-I-7
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Item 431-I-7