583 resultados para acido polilattico termoformatura biochar propietà meccaniche


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Negli ultimi anni la produzione di materiale ceramico si è spostata su formati di grandi dimensioni. Questo processo è stato possibile grazie allo sviluppo di nuove tecnologie adeguate alla produzione di lastre in grès porcellanato con spessore sempre più ridotto e in formati sempre più grandi. Molte aziende si sono quindi orientate alla produzione delle grandi lastre servendosi di queste nuove tecnologie innovative, proprio perché questi prodotti sono risultati essere particolarmente versatili. Come le piastrelle di formato tradizionale, anche questi grandi formati devono essere certificati con il marchio CE, quindi devono essere eseguite delle prove di caratterizzazione delle loro caratteristiche fisiche-meccaniche. Tuttavia, cambiando notevolmente le dimensioni, per queste grandi lastre si possono introdurre anche nuovi test di prova per determinare nuove caratteristiche, come ad esempio la possibilità di flettersi per adattarsi alla forma della superficie dove vengono collocate (facciate di edifici, rivestimenti di gallerie autostradali, etc.). Di conseguenza nasce l’esigenza di valutare questi nuovi parametri, tra cui il raggio di curvatura è particolarmente rilevante per valutare appunto la flessibilità della lastra. Nel presente lavoro di tesi sono state svolte prove di caratterizzazione delle proprietà fisiche-meccaniche di piastrelle ceramiche di grande formato. I campioni sono stati sottoposti a prove per la determinazione della freccia e del raggio di curvatura sotto il peso proprio e a rottura nelle configurazioni fronte e retro. Dall’analisi dei dati sperimentali sono state dedotte conclusioni in merito alla possibile dipendenza della freccia e del raggio di curvatura dalle caratteristiche dei campioni. Oltre alle prove di determinazione della freccia e conseguente raggio di curvatura, a completamento del lavoro sperimentale svolto sono state eseguite anche prove di assorbimento di acqua e di analisi d’immagine per determinare la porosità totale.

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Biochar is a carbon-rich material that is similar to charcoal. It is produced when biomass is burned in the absence of oxygen, a process otherwise known as pyrolysis. Pyrolysis and the production of biochar are currently being promoted as a means to both produce domestic fuel (bio-oil) while concurrently producing a co-product that increases crop yield and sequesters carbon in the soil (biochar). While there may be many potential benefits in the application of biochar to agricultural soils, such as enhanced soil fertility and improved soil water status, there are no studies of higher-order ecological and ecosystem effects of biochar and its potential synergistic interactions (either positive or negative) on complex perennial systems. The goal of this field experiment is to determine how biochar and manure addition directly affect ecosystem structure and function in perennial systems, specifically soil nutrients, water, plants, and soil organisms.

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A pot experiment was conducted to determine the effects of three biochars and compost on plant growth and the immobilisation of Cu in a contaminated soil obtained from a former wood preservation site in the Gironde County Saint Médard d'Eyrans, France (N 44° 43.353, W 0° 30.938). To assess Cu mobility, amended soils were analysed using CaCl**2 leaching tests pre- and post-incubation, and post-growth. Amended and unamended soils were planted with sunflower, and the resulting plant material was assessed for yield (mass and height) and Cu concentration. All amendments significantly reduced leachable Cu compared to the unamended soil, however, the greatest reductions in leachable Cu were associated with the higher biochar application rate. The greatest improvements in plant yields were obtained with the higher application rate of biochar in combination with compost. pH, DOC, EH were measured in soils to help explain the leaching and plant growth trends. Soil pore water was collected during plant growth and analysed for metal concentration, pH and EH. Prior to treatment, background analyses were carried out on the soil and individual amendments (including PAH + metal concentrations measured by gas chromatography mass spectrometry and ICP-AES respectively).

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Semi-arid soils cover a significant area of Earth s land surface and typically contain large amounts of inorganic C. Determining the effects of biochar additions on CO2 emissions fromsemi-arid soils is therefore essential for evaluating the potential of biochar as a climate change mitigation strategy. Here, we measured the CO2 that evolved from semi-arid calcareous soils amended with biochar at rates of 0 and 20 t ha?1 in a full factorial combination with three different fertilizers (mineral fertilizer, municipal solid waste compost, and sewage sludge) applied at four rates (equivalent to 0, 75, 150, and 225 kg potentially available N ha?1) during 182 days of aerobic incubation. A double exponential model, which describes cumulative CO2 emissions from two active soil C compartments with different turnover rates (one relatively stable and the other more labile), was found to fit verywell all the experimental datasets. In general, the organic fertilizers increased the size and decomposition rate of the stable and labile soil C pools. In contrast, biochar addition had no effects on any of the double exponential model parameters and did not interact with the effects ascribed to the type and rate of fertilizer. After 182 days of incubation, soil organic and microbial biomass C contents tended to increase with increasing the application rates of organic fertilizer, especially of compost, whereas increasing the rate of mineral fertilizer tended to suppress microbial biomass. Biochar was found to increase both organic and inorganic C contents in soil and not to interactwith the effects of type and rate of fertilizer on C fractions. As a whole, our results suggest that the use of biochar as enhancer of semi-arid soils, either alone or combined with mineral and organic fertilizers, is unlikely to increase abiotic and biotic soil CO2 emissions.

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Las turberas realizan la función de sumidero de carbono en los ecosistemas terrestres pero debido a su excesivo uso como combustible o como medio de cultivo se está produciendo la sobreexplotación de este recurso no renovable. En los últimos años se han llevado a cabo diversas investigaciones con el objetivo de encontrar sustratos procedentes de diferentes residuos orgánicos que sean de alta calidad y bajo coste con el fin de disminuir el consumo de turba.

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The effect of biochar on the soil carbon mineral- ization priming effect depends on the characteristics of the raw materials, production method and pyrolysis conditions. The goal of the present study is to evaluate the impact of three different types of biochar on physicochemical properties and CO2 emissions of a sandy loam soil. For this purpose, soil was amended with three different biochars (BI, BII and BIII) at a rate of 8 wt % and soil CO2 emissions were measured for 45 days. BI is produced from a mixed wood sieving from wood chip production, BII from a mixture of paper sludge and wheat husks and BIII from sewage sludge. Cumulative CO2 emissions of biochars, soil and amended soil were well fit to a simple first-order kinetic model with correlation coef- ficients (r 2 ) greater than 0.97. Results show a negative prim- ing effect in the soil after addition of BI and a positive prim- ing effect in the case of soil amended with BII and BIII. These results can be related to different biochar properties such as carbon content, carbon aromaticity, volatile matter, fixed carbon, easily oxidized organic carbon or metal and phenolic substance content in addition to surface biochar properties. Three biochars increased the values of soil field capacity and wilting point, while effects over pH and cation exchange capacity were not observed.

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Este trabajo aborda el estudio del uso de restos de poda, lodos de depuradora y diferentes biochares obtenidos a partir de dichos residuos, así como biochar comercial, como componentes de sustratos de cultivo en sustitución de la turba. Para ello, se han llevado a cabo varios experimentos usando dichos residuos originales y pirolizados, de forma individual o mezclándolos en distintas proporciones con turba con el fin de estudiar sus características químicas e hidrofísicas, su posible fitotoxicidad y el cultivo en macetas de Lactuca sativa. Los resultados obtenidos indican que es posible preparar sustratos de cultivo adecuados a partir de algunos de estos materiales, logrando así una forma de recuperación y valorización de los mismos, a la vez que se minimiza el consumo de turba. En general, la adición de biochar de restos de poda a la turba mejora la germinación y aumenta el crecimiento de Lactuca sativa respecto a la utilización de turba sola. ABSTRACT This research deals with the study of the use of pruning wastes, sewage sludges and different biochars obtained from these materials, as well as a commercial biochar, as growing media components to replace peat. Several experiments were conducted using original wastes and pyrolyzed ones, individually or mixed in different proportions with peat, in order to study their chemical and hydrophysical characteristics, its possible phytotoxicity and the pot cultivation of Lactuca sativa. The results obtained indicate that it is possible to prepare suitable growing media from some of these materials, not only achieving a recovery and valorisation of them, but also minimizing the consumption of peat. In general, the addition of pruning waste biochar to peat improves germination and increases the growth of Lactuca sativa in comparison with peat alone.

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Biochar is a carbon-rich solid obtained by the thermal decomposition of organic matter under a limited supply of oxygen and at relatively low temperatures. Biochar can be prepared from the pyrolysis of different organic feed- stocks, such as wood and biomass crops, agricultural by-products, different types of waste or paper industry waste materials . The pyrolysis procedure of waste, i.e. sewage sludge, has mainly two advantages, firstly, it removes pathogens from waste and, secondly, biochar can reduce the leaching of heavy metals present in raw sewage sludge. This trend of the use of waste material as feedstocks to the preparation of biochar is increasing in the last years due to industrial development and economic growth imply an increase in waste generation. The application of biochar may have positive effects on soil physical properties as water holding capacity and structure or on soil biological activity and soil quality. Also, biochar can be used to remove water pollutants and can be used in multiple ways in soil remediation due to its adsorption of pesticides or metals. Also, biochar contribute to carbon sequestration due to carbon stability of biochar materials. The objective of this presentation is to review the positive effects of the biochar prepared from organic waste on soil properties.

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In the last years, intensive animal husbandry production has led to a large concentration of animals in small areas. This has resulted in the production of excessive amounts of manures with insufficient nearby land for application. One of this areas is the Amblés Valley located in the centre of Spain, near to Ávila city, with an extension of 167472 ha of which 88.9% is agricultural land. This valley has an important livestock focused on pig, cattle, chicken production which is associated with the generation of more than 200,000 t/year of manure. There are a number of environmental problems associated with these intensive agricultural systems, including N and P pollution of water bodies, methane emissions and odour pollution. These serious environmental threats are called for innovative environmental management approaches. A feasible technology for the management of manures, offering a potential to valorise these wastes, is pyrolysis, which results in the production of biochar. The objective of this work is evaluated the technical and economic feasibility of the production of biochar in Amblés Valley (Spain).

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El biochar es un material rico en carbono que se obtiene tras la pirólisis de la biomasa. Este material ha despertado en los últimos años un gran interés en la comunidad científica principalmente por su capacidad para mejorar la productividad de los suelos, influenciando las propiedades fisicoquímicas de los mismos y como medio de fijación de carbono, reduciendo, por tanto, las emisiones de CO2 a la atmósfera. Sin embargo, lo cierto es que hasta la fecha, no existen conclusiones claras o avances definitivos que permitan crear una estandarización para la comercialización del biochar, debido a la variabilidad de sus propiedades (considerando la materia prima de origen y las condiciones de reacción en la pirólisis). En este estudio, partiendo de un análisis exhaustivo de las distintas publicaciones existentes sobre la materia, se trata de dar respuesta a la pregunta sobre cuál sería el verdadero potencial de producción de biochar en España, al tiempo que se trata de cuantificar cuál sería la reducción de las emisiones de CO2 a la atmósfera que conllevaría gestionar los residuos (industria papelera, lodos de EDAR, RSU y residuos ganaderos) a través de la pirólisis. En particular, se ha cuantificado la reducción de las emisiones de CO2 a la atmósfera y se ha evaluado cuánto biochar se debería producir a partir de residuos papeleros, lodos de EDAR o residuos ganaderos para aumentar en un 1% la cantidad de materia orgánica en un suelo y para llevar el contenido en materia orgánica de los suelos agrícolas españoles a un 3,5%. En primer lugar, sobre la cuantificación de la reducción de las emisiones, cabe concluir que, en todos los residuos estudiados, y bajo todas las condiciones de reacción consideradas, la reducción de las emisiones de CO2 a la atmósfera sería realmente notable, oscilando entre un 22,53% y un 96,12 %. En segundo lugar, para aumentar en un 1% el contenido medio en materia orgánica de la superficie agrícola española, sería necesario un aporte de 2,03816*108 t de materia orgánica, que supondría una demanda mínima de biochar de 255.408.361 t en el caso de la aplicación de biochar de estiércol de vacuno a Por otro lado, para llevar la materia orgánica de los suelos agrícolas a un 3,5%, la demanda de biochar variaría entre un mínimo de 158.937 t en el (Comunidad Autónoma con menor necesidad de aporte de materia orgánica) illa la Mancha (Comunidad Autónoma que, por el contrario, necesitaría mayor aporte). ABSTRACT Biochar is a carbon-rich material obtained after a biomass pyrolysis procedure. This material has aroused in recent years a great interest in the scientific community, mainly for its ability to improve the productivity of soils, influencing the physico-chemical properties of soils and as means of carbon storage, reducing emissions of CO2 into the atmosphere). Despite the interest that may raise this matter, the fact is that to date, no clear conclusions or definitive progress have been done to create a standardization for the commercialization of biochar, due to the variability of its properties (considering the raw material and the reaction conditions in the pyrolysis). This study, based on a thorough analysis of the various existing literature on the subject and, leaving other approaches that could have been taken of the interest of the subject in question, attempts to provide answers to the question about what would be the true potential production of biochar in Spain and what would be the reduction of CO2 emissions into the atmosphere, which would entail waste management through pyrolysis. In particular, this study has identified the reduction of CO2 emissions into the atmosphere and has analyzed whether the production of biochar could increase the organic matter content of Spanish agricultural soils. Firstly, regarding the quantification of emissions reductions, by referring to the values contained in the work, it can be concluded that the reduction of CO2 emissions to the atmosphere would be really remarkable, ranging from 22.53% to 96.12%. Secondly, to increase by 1% the average content of organic matter in the spanish agricultural area would require a contribution of 2.03816*108 t of organic matter, which would demand a minimum of 255.408.361 t of cattle manure biochar and a maximum demand of 1.746.494.190 t of deinking sludge pyrolyzed at 500C. On the other hand, to reach a 3.5%, the demand for biochar would vary from a minimum of 158.937 t, in case of cattle manure biochar at C applied to the Canary Islands (Autonomous Community with less need for input of organic matter), and a maximum of 694.695.081 in case of applying deinking sludge biochar at C to Castilla la Mancha (Autonomous Region, which needs the highest contribution).

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A diversidade microbiana é geralmente considerada por seu papel nos principais processos do ecossistema, tais como a decomposição da matéria orgânica e ciclos biogeoquímicos. No entanto, informações sobre o impacto da diversidade em funções menores, como degradação de xenobióticos são escassas. Nós estudamos a partir da abordagem da \'diluição para extinção\', o papel da diversidade sobre a capacidade da comunidade microbiana em degradar o fungicida clorotalonil (organoclorado). Também estudamos o comportamento da comunidade bacteriana após aplicação do pesticida no solo com e sem biochar. A diversidade microbiana do solo natural foi alterada artificialmente por diluição, constituindo um gradiente de diversidade (SN > 10-1 > 10-3 > 10-6), seguido pela inoculação em amostras de solo estéril e posterior reestruturação (15 dias). Após a reestruturação da comunidade, as amostras foram manejadas com biochar (1% m/m) e tratadas com a dose de campo do CHT. O comportamento da comunidade bacteriana foi estudo por PCR-DGGE e qPCR do gene 16S rDNA através de um experimento com molécula fria (não radiomarcada). Enquanto a capacidade de degradação do CHT foi estudada por radiorespirometria (14C-CHT). Inicialmente, a comunidade de bactérias foi influenciada pelo gradiente de diversidade obtido por diluição. A separação dos grupos bacterianos se mostrou bastante similar nos três primeiros períodos pré-aplicação do CHT (SN > 10-1 - 10-3 > 10-6), enquanto que no período de 15 dias, a dinâmica de grupos foi alterada (SN > 10-1 > 10-3 - 10-6). O fungicida e o biochar não exerceram efeitos na comunidade bacteriana no tempo zero (imediatamente após a aplicação), a modificação no perfil da comunidade foi atribuído à diluição. Nos períodos de 21 e 42 dias, o perfil comunidade bacteriana apresentou forte modificação. Os grupos bacterianos se mostraram mais dispersos quando considerado somente o CHT. Embora, a análise de ANOSIM indicou não haver diferença nas amostras com e sem biochar, sugerindo que o clorotalonil foi quem mais contribuiu na dispersão dos grupos bacterianos. No período de 42 d, a comunidade apresentou resposta positiva, sendo observado aumentos no número de bandas e no índice de Shannon em todos tratamentos. Isto possivelmente, devido a menor concentração do fungicida disponível na solução do solo, diminuindo assim, os efeitos deletérios sobre a comunidade. Os dados de qPCR não apresentaram alteração no número de copias do gene 16S rDNA em todos os tratamentos. A remoção da diversidade impactou fortemente a capacidade da comunidade bacteriana de degradar o clorotalonil. Apesar da capacidade de degradar não ter sido perdida, a mínima alteração na diversidade promoveu elevada redução na taxa de mineralização do CHT. A dissipação do CHT se mostrou rápida (D50 < 1 dia) em todos os tratamentos, além disso, a formação de 14C-resíduos não extraíveis foi constituiu um dos principais mecanismos de dissipação do CHT. A partir da degradação do fungicida, foram detectados três metabólitos. Conclui-se que a modificação por diluição da diversidade bacteriana promoveu impacto negativo na mineralização do clorotalonil. E que a formação de resíduos não extraíveis consistiu no principal mecanismo de dissipação do CHT em ambos solos.

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Les réactions de transfert de proton se retrouvent abondamment dans la nature et sont des processus cruciaux dans plusieurs réactions chimiques et biologiques, qui se produisent souvent en milieu aqueux. Les mécanismes régissant ces échanges de protons sont complexes et encore mal compris, suscitant un intérêt des chercheurs en vue d’une meilleure compréhension fondamentale du processus de transfert. Le présent manuscrit présente une étude mécanistique portant sur une réaction de transfert de proton entre un acide (phénol fonctionnalisé) et une base (ion carboxylate) en phase aqueuse. Les résultats obtenus sont basés sur un grand nombre de simulations de dynamique moléculaire ab-initio réalisées pour des systèmes de type « donneur-pont-accepteur », où le pont se trouve à être une unique molécule d’eau, permettant ainsi l’élaboration d’un modèle cinétique détaillé pour le système étudié. La voie de transfert principalement observée est un processus ultra-rapide (moins d’une picoseconde) passant par la formation d’une structure de type « Eigen » (H9O4+) pour la molécule d’eau pontante, menant directement à la formation des produits. Une seconde structure de la molécule d’eau pontante est également observée, soit une configuration de type « Zündel » (H5O2+) impliquant l’accepteur de proton (l’ion carboxylate) qui semble agir comme un cul-de-sac pour la réaction de transfert de proton.

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Les réactions de transfert de proton se retrouvent abondamment dans la nature et sont des processus cruciaux dans plusieurs réactions chimiques et biologiques, qui se produisent souvent en milieu aqueux. Les mécanismes régissant ces échanges de protons sont complexes et encore mal compris, suscitant un intérêt des chercheurs en vue d’une meilleure compréhension fondamentale du processus de transfert. Le présent manuscrit présente une étude mécanistique portant sur une réaction de transfert de proton entre un acide (phénol fonctionnalisé) et une base (ion carboxylate) en phase aqueuse. Les résultats obtenus sont basés sur un grand nombre de simulations de dynamique moléculaire ab-initio réalisées pour des systèmes de type « donneur-pont-accepteur », où le pont se trouve à être une unique molécule d’eau, permettant ainsi l’élaboration d’un modèle cinétique détaillé pour le système étudié. La voie de transfert principalement observée est un processus ultra-rapide (moins d’une picoseconde) passant par la formation d’une structure de type « Eigen » (H9O4+) pour la molécule d’eau pontante, menant directement à la formation des produits. Une seconde structure de la molécule d’eau pontante est également observée, soit une configuration de type « Zündel » (H5O2+) impliquant l’accepteur de proton (l’ion carboxylate) qui semble agir comme un cul-de-sac pour la réaction de transfert de proton.