437 resultados para biogas


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L’emanazione del Decreto 5 dicembre 2013, ha inaugurato una nuova stagione per il settore energetico italiano, dando vita anche in Italia, in linea con gli altri paesi europei, alla possibilità di valorizzare il biogas, prodotto a seguito di un processo di digestione anaerobica, come biometano, un gas con maggiore contenuto energetico che a seguito di opportuni trattamenti, può essere paragonabile al gas naturale. Il lavoro svolto pertanto si pone come obiettivo quello di individuare gli elementi peculiari che potrebbero favorire lo sviluppo e la crescita del biometano nel contesto italiano.

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La presente tesi di laurea tratta la valorizzazione degli scarti della lavorazione degli agrumi. Tutti i processi di trasformazione utilizzati nell’industria agrumaria danno origine a tre prodotti principali: succo, olio essenziale e pastazzo; il terzo, sottoprodotto a basso valore o scarto di lavorazione, è una biomassa vegetale costituita da scorze, detriti di polpa, semi e frutti di scarto. Questo lavoro si è concentrato su due aspetti fondamentali: lo studio dei possibili utilizzi del pastazzo di agrumi, che si può considerare una fonte di sostanze ad alto valore aggiunto, e la valorizzazione di tale sottoprodotto mediante digestione anaerobica per la produzione di biogas. La composizione chimica degli scarti della lavorazione degli agrumi offre ampie possibilità di utilizzazione: come alimento zootecnico, per la produzione di compost, per l’estrazione di pectina, fibre alimentari e oli essenziali, per il recupero di limonene e per produrre bioetanolo. Infine di recente il pastazzo è stato individuato come componente nella produzione di biogas, attraverso la digestione anaerobica; ciò risulta coerente con il quadro normativo riguardante gli incentivi per la produzione di biogas. E' stato analizzato un caso pratico, l’impianto di produzione di biogas alimentato a biomasse, situato in Sicilia, in contrada Nuova Scala a Mussomeli (CL); l’impianto ha una potenza di 999 KW ed è attivo dal 31 Dicembre 2012. In generale, affinchè si realizzi un corretto dimensionamento di un impianto di produzione di biogas, è necessario conoscere il potenziale metanigeno, che esprime la quantità di biogas metano massimo potenzialmente ottenibile da una biomassa, e la quantità di biomasse disponibili. In particolare, per l’impianto in questione, sono stati elaborati dati relativi alle analisi chimiche condotte sulle singole matrici in input all’impianto, sulla base delle quali è possibile dare un primo giudizio di fermentescibilità dei vari substrati e della rispettiva resa in biogas.

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L'opera preliminarmente in una accurata analisi della configurazione e delle interrelazioni dei sistemi energetici presenti nello stabilimento produttivo Caviro Enomondo. Successivamente è svolto un approfondimento del quadro normativo relativo all’incentivazione delle fonti energetiche rinnovabili non fotovoltaiche e delle sue recenti evoluzioni, andando ad identificare tutte le possibili vie di sviluppo per impianti di produzione di biogas promosse a livello nazionale e che possono potenzialmente trovare applicazione nell’impianto in esame; questo studio è effettuato con particolare attenzione alla opportunità di effettuare un upgrading di tale impianto per realizzare ad una raffinazione totale o parziale del biogas a biometano. A seguito dell’identificazione della tipologia di prodotto e/o di processo che offre le migliori prospettive per una implementazione industriale e delle caratteristiche chimico-fisiche che questo deve rispecchiare, si prosegue quindi individuando lo schema impiantistico ottimale per adeguare l’attuale sistema di produzione al nuovo target. A seguire, approfondendo lo studio delle varie tecnologie disponibili ad oggi allo stato dell’arte, si identificano quelle maggiormente promettenti, mettendone in evidenza peculiarità positive e negative di ciascuna e giungendo alla identificazione della combinazione ottimale in termini di economicità, capacità produttiva, sicurezza ed impatto ambientale. Una volta individuate le caratteristiche di massima dell’impianto si procede ad un dimensionamento più accurato dello stesso andandone a valutare anche entità dei costi di investimento e di gestione. Attraverso l’instaurazione di contatti con ditte specializzate operanti nel settore industriale di riferimento, si giunge all’individuazione specifica dei modelli dei macchinari ed impianti richiesti. Il progetto si sviluppa successivamente andando a valutare le possibili modalità di utilizzo del prodotto finale che offrono maggiori prospettive di valorizzazione per l’azienda, identificando le varie soluzioni e gli interventi necessari per ciascuna di essa. La parte successiva dell’elaborato consiste in un confronto, in termini di valutazioni economiche, sull’opportunità di ognuna delle soluzioni prospettate, tenendo in considerazione i costi di investimento, di esercizio, i ricavi, e la componente incentivante. Si va infine a concludere il progetto proponendo una road-map per la realizzazione della soluzione che si evidenzia come la più promettente, con crono-programma degli interventi da eseguire, e aspettative di sviluppo a medio-lungo termine dell’investimento.

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The first part of this essay aims at investigating the already available and promising technologies for the biogas and bio-hydrogen production from anaerobic digestion of different organic substrates. One strives to show all the peculiarities of this complicate process, such as continuity, number of stages, moisture, biomass preservation and rate of feeding. The main outcome of this part is the awareness of the huge amount of reactor configurations, each of which suitable for a few types of substrate and circumstance. Among the most remarkable results, one may consider first of all the wet continuous stirred tank reactors (CSTR), right to face the high waste production rate in urbanised and industrialised areas. Then, there is the up-flow anaerobic sludge blanket reactor (UASB), aimed at the biomass preservation in case of highly heterogeneous feedstock, which can also be treated in a wise co-digestion scheme. On the other hand, smaller and scattered rural realities can be served by either wet low-rate digesters for homogeneous agricultural by-products (e.g. fixed-dome) or the cheap dry batch reactors for lignocellulose waste and energy crops (e.g. hybrid batch-UASB). The biological and technical aspects raised during the first chapters are later supported with bibliographic research on the important and multifarious large-scale applications the products of the anaerobic digestion may have. After the upgrading techniques, particular care was devoted to their importance as biofuels, highlighting a further and more flexible solution consisting in the reforming to syngas. Then, one shows the electricity generation and the associated heat conversion, stressing on the high potential of fuel cells (FC) as electricity converters. Last but not least, both the use as vehicle fuel and the injection into the gas pipes are considered as promising applications. The consideration of the still important issues of the bio-hydrogen management (e.g. storage and delivery) may lead to the conclusion that it would be far more challenging to implement than bio-methane, which can potentially “inherit” the assets of the similar fossil natural gas. Thanks to the gathered knowledge, one devotes a chapter to the energetic and financial study of a hybrid power system supplied by biogas and made of different pieces of equipment (natural gas thermocatalitic unit, molten carbonate fuel cell and combined-cycle gas turbine structure). A parallel analysis on a bio-methane-fed CCGT system is carried out in order to compare the two solutions. Both studies show that the apparent inconvenience of the hybrid system actually emphasises the importance of extending the computations to a broader reality, i.e. the upstream processes for the biofuel production and the environmental/social drawbacks due to fossil-derived emissions. Thanks to this “boundary widening”, one can realise the hidden benefits of the hybrid over the CCGT system.

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Research was to investigate the effects of increasing levels of carbon dioxide addition to the combustion of methane with air. Using an atmospheric-pressure, swirl-stabilized dump combustor, emissions data and flame stability limitations were measured and analyzed.

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There is a need for biomethane capture and carbon dioxide sequestration to mitigate evident global climate change. This research work investigated the potential for microalgae to remove CO2 from biogas as a biotechnical method for upgrading the thermal value for subsequent compression, liquification, or introduction to natural gas pipelines. Because biogas is largely methane, the effect of high methane environments on mixed microalgae was explored and found that specific carbon utilization rates were not statistically different when microalgae were exposed to biogas environments (70% v/v CH4) , relative to high CO2 environment. The uses of conventional bubbled column photobioreactors (PBR) were assessed for CO2 removal and subsequent CH4 enrichment. A continuously-bubbled biogas PBR (cB-PBR5) and intermittently-bubbled biogas PBR (iB-PBR) experienced CO2 loading rates of about 1664 and 832 mg C/L*day and showed 30.0 and 60.1 % carbon removal, respectively. However, a lack of biogas enrichment and issues associated growth inhibition due to high CO2 environments as well as stripping the dissolved gases, namely oxygen and nitrogen, from the bulk liquid and introduction to the outlet gas prompted the consideration for gas/liquid separation using nonporous hollow-fiber (HF) membranes for CO2 transfer. The potential for two non-porous HF membrane materials [polydimethylsiloxane (PDMS) and composite polyurethane (PU)] were modeled along fiber length using a mechanistic model based on polymeric material transport properties (Gilmore et al., 2009). Based on a high CO2:CH4 permeability selectivity for PU of 76.2 the model predicted gas enrichment along an 8.5 cm fiber length. Because PDMS permeability selectivity is low (3.5), evident gas transfer was not predicated along a 34.3 cm length. Both of these HF materials were implemented in hollow-fiber membrane-carbonated biofilm (HFMcB) PBRs for microalgal-mediated biogas enrichment. Phototrophic biofilm colonization occurred on the membrane, where CO2 concentration was greatest. The presence of a biofilm demonstrated greater resiliency to high CO2 environments, compared to the conventional PBRs. However, as the PDMS model predicted, the PDMS HFMcBs did not demonstrate gas enrichment. These reactors received CO2 loading rates of 200 mg C/L*day based on PDMS permeability flux and showed approximately 65% removal of the total C transferred across the membrane. Thus, the HFMcBs demonstrated controlled carbonation of the bulk liquid via a nonporous HF membrane. Likewise, the experimental PU HFMcB did not show gas enrichment yet this result should be further explored due to the high permeability selectivity of the polymeric material. Chemical stratifications, namely pH and dissolved O2, present in a PDMS membrane-carbonated biofilm were analyzed using electrochemical microsensors. Results indicated that high DO (20 mg L-1) exists at surface of the biofilm where light availability is greatest and low pH microenvironments (pH=5.40) exist deep in the biofilm where the diffusive flux of CO2 drives transfer through the biofilm. The presence of a 400-600 ¿m liquid phase boundary layer was evident from microsensor profiles. Cryosectioning of the biofilm samples showed the biofilm to be approximately 1.17 ± 0.07 mm thick, suggesting that the high localized concentration of biomass associated with the phototrophic biofilm aided in overcoming inhibition in a microenvironment dominated by CO2(aq). Challenges of biofilm detachment and PBR fouling as well as microalgal growth inhibition in the presence of high CO2 content remain for applications of microalgae for biogas enrichment.

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Utilization of biogas can provide a source of renewable energy in both heat and power generation. Combustion of biogas in land-based gas turbines for power generation is a promising approach to reducing greenhouse gases and US dependence on foreign-source fossil fuels. Biogas is a byproduct from the decomposition of organic matter and consists primarily of CH4 and large amounts of CO2. The focus of this research was to design a combustion device and investigate the effects of increasing levels of CO2 addition to the combustion of pure CH4 with air. Using an atmospheric-pressure, swirl-stabilized dump combustor, emissions data and flame stability limitations were measured and analyzed. In particular, CO2, CO, and NOx emissions were the main focus of the combustion products. Additionally, the occurrence of lean blowout and combustion pressure oscillations, which impose significant limitations in operation ranges for actual gas turbines, was observed. Preliminary kinetic and equilibrium modeling was performed using Cantera and CEA for the CH4/CO2/Air combustion systems to analyze the effect of CO2 upon adiabatic flame temperature and emission levels. The numerical and experimental results show similar dependence of emissions on equivalence ratio, CO2 addition, inlet air temperature, and combustor residence time. (C) 2014 Elsevier Ltd. All rights reserved.

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Arsenic is a class 1 non-threshold carcinogen which is highly ubiquitous. Arsenic undergoes many different transformations (biotic or abiotic) between and within environmental compartments, leading to a number of different chemical species possessing different properties and toxicities. One specific transformation is As biotic volatilization which is coupled with As biomethylation and has been scarcely studied due to inherent sampling issues. Arsenic methylation/volatilization is also linked with methanogenesis and occurs in anaerobic environments. In China, rice straw and animal manure are very often used to produce biogas and both can contain high amounts of As, especially if the rice is grown in areas with heavy mining or smelting industries and if Roxarsone is fed to the animals. Roxarsone is an As-containing drug which is widely used in China to control coccidian intestinal parasites, to improve feed efficiency and to promote rapid growth. Previous work has shown that this compound degrades to inorganic As under anaerobic conditions. In this study the focus is on biotic transformations of As in small microcosms designed as biogas digester models (BDMs) using recently validated As traps, thus, enabling direct quantification and identification of volatile As species. It is shown that although there was a loss of soluble As in the BDMs, their conditions favored biomethylation. All reactors produced volatile As, especially the monomethylarsonic acid spiked ones with 413 ± 148 ng As (mean ± SD, n = 3) which suggest that the first methylation step, from inorganic As, is a limiting factor. The most abundant species was trimethylarsine, but the toxic arsine was present in the headspace of most of the BDMs. The results suggest that volatile As species should be monitored in biogas digesters in order to assess risks to humans working in biogas plants and those utilizing the biogas.

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The energetic performance of landfill biogas (LB) and biodigester biogas (BB) from municipal waste was examined in consumption tests. These tests were performed in situ at a gas generation plant associated with a landfill facility in Madrid (Spain) and following the standard UNE-EN 30-2-1 (1999). The jets of a domestic cooker commonly used for natural gas (NG) or liquefied petroleum gas (LPG) were modified to operate with the biogases produced at the facility. The working pressures best suited to the tested gases, i.e., to avoid flashback and flame lift, and to ensure the stability and correct functioning of the flame during combustion, were determined by trial and error. Both biogases returned optimum energetic performance for the transfer of heat to water in a metallic recipient (as required by the above standard) at a supply pressure of 10 mbar. Domestic cookers are normally supplied with NG at a pressure of 20 mbar, at which pressure the energetic performance of G20 reference gas was higher than that of both biogases (52.84% compared to 38.06% and 49.77% respectively). Data concerning these issues involving also unexplored feedstock are required for the correct conversions of domestic cookers in order to avoid risks of serious personal injuries or property damages.

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La composición del purín varía en función de la dieta, los procesos fisiológicos y bioquímicos en el animal y el manejo, entre otros. La composición del purín es determinante en las emisiones de metano (CH 4 ) y amoniaco (NH 3 ) (Moset y col., 2012) y condiciona su aptitud para ser usado como fertilizante o como sustrato para la producción de biogás. Las materias primas comúnmente utilizadas en la fabricación de piensos poseen valores variables de nitrógeno ligado a fibra (N- FND) y determinadas combinaciones de ingredientes modifican de manera considerable la concentración de N-FND en los piensos. La ingesta de diferentes cantidades de N-FND puede dar lugar a cambios en la composición del purín y en su potencial de producción de NH 3 ,CH 4 y biogás. El objetivo del presente estudio fue evaluar los efectos de la modificación de la calidad del nitrógeno (N) en piensos de cebo en cerdos y sus implicancias en la producción de NH 3, CH 4 y biogás a partir del purín. Este ensayo es parte del proyecto GasPorc (AGL2011-30023-C03) que evalúa la relación que existe entre la composición de la dieta, características del purín y su potencial de producción de gases y valor fertilizante.

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Concentrating Solar Power (CSP) plants typically incorporate one or various auxiliary boilers operating in parallel to the solar field to facilitate start up operations, provide system stability, avoid freezing of heat transfer fluid (HTF) and increase generation capacity. The environmental performance of these plants is highly influenced by the energy input and the type of auxiliary fuel, which in most cases is natural gas (NG). Replacing the NG with biogas or biomethane (BM) in commercial CSP installations is being considered as a means to produce electricity that is fully renewable and free from fossil inputs. Despite their renewable nature, the use of these biofuels also generates environmental impacts that need to be adequately identified and quantified. This paper investigates the environmental performance of a commercial wet-cooled parabolic trough 50 MWe CSP plant in Spain operating according to two strategies: solar-only, with minimum technically viable energy non-solar contribution; and hybrid operation, where 12 % of the electricity derives from auxiliary fuels (as permitted by Spanish legislation). The analysis was based on standard Life Cycle Assessment (LCA) methodology (ISO 14040-14040). The technical viability and the environmental profile of operating the CSP plant with different auxiliary fuels was evaluated, including: NG; biogas from an adjacent plant; and BM withdrawn from the gas network. The effect of using different substrates (biowaste, sewage sludge, grass and a mix of biowaste with animal manure) for the production of the biofuels was also investigated. The results showed that NG is responsible for most of the environmental damage associated with the operation of the plant in hybrid mode. Replacing NG with biogas resulted in a significant improvement of the environmental performance of the installation, primarily due to reduced impact in the following categories: natural land transformation, depletion of fossil resources, and climate change. However, despite the renewable nature of the biofuels, other environmental categories like human toxicity, eutrophication, acidification and marine ecotoxicity scored higher when using biogas and BM.

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Funded by UK Natural Environment Research Council ESPA project. Grant Number: NE/K010441/1 Afri-Flame

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An exhaustive characterization of the biogas from some waste disposal facilities has been carried out. The analysis includes the main components (methane, carbon dioxide, nitrogen and oxygen) as well as trace components such as hydrogen sulphide, ammonia and VOCs (volatile organic compounds) including siloxanes and halogenated compounds. VOCs were measured by GC/MS (Gas Chromatography/Mass Spectrometry) using two different procedures: thermal desorption of the Tenax TA and Carbotrap 349 tubes and SPME (Solid Phase Micro-Extraction). A method has been established to measure the total halogen content of the biogas with the AOX (adsorbable organically bound halogens) technique. The equipment used to analyze the samples was a Total Organic Halogen Analyzer (TOX-100). Similar results were obtained when comparing the TOX (Total Organic Halogen) values with those obtained by GC/MS. The halogen content in all the samples was under 22 mg Cl/Nm3 which is below the limit of 150 mg/Nm3 proposed in the Spanish Regulations for any use of the biogas. The low chlorine content in the biogas studied, as well as the low content of other trace compounds, makes it suitable for use as a fuel for electricity generating engines.

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The siloxanes present in the biogas produced during anaerobic digestion damage the mechanism of cogeneration equipment and, consequently, negatively affect the energy valorization process. For this reason, the detection and elimination of these silicon-derived chemical compounds are a priority in the management of cogeneration facilities. In this regard, the objectives of this paper are, firstly, to characterize the siloxanes in the biogas and, secondly, to qualitatively evaluate the influence of the dose of iron chloride on its elimination. The research was performed at the Rincón de León Wastewater Treatment Plant (Alicante, Spain). The outflow biogas of the digesters and of the pressurized gasometers was sampled and analyzed. The results obtained made it possible to demonstrate, firstly, the absence of linear siloxanes and that, of the cyclic siloxanes, the predominant type was decamethylcyclopentasiloxane, and, secondly, that the addition of iron chloride in the digesters significantly reduces the siloxane content in the biogas. Additionally, it was demonstrated that the process of compression of the biogas, with the elimination of condensates, also produces significant reductions in the concentration of siloxanes in the biogas.