436 resultados para Slurry
Resumo:
I policlorobifenili (PCB) sono un gruppo di 209 congeneri di bifenili policlorurati altamente tossici e persistenti che, a causa della loro elevata lipofilia, tendono ad accumularsi in sedimenti anaerobici marini, tramite i quali possono entrare nella catena alimentare. I PCB possono essere degradati mediante processi di declorurazione riduttiva mediati da popolazioni microbiche anaerobiche in grado di utilizzarli fortuitamente come accettori finali della catena respiratoria. Il processo consiste quindi nella bioconversione di congeneri ad alto grado di clorurazione in PCB basso clorurati, meno tossici, meno bioaccumulabili e più facilmente biodegradabili in condizioni aerobiche. Nel presente elaborato è stata investigata la capacità di una popolazione microbica arricchita su congeneri coplanari di PCB da un sedimento contaminato del Canale Brentella (Prima Zona Industriale di Porto Marghera, laguna di Venezia), di declorurare miscele commerciali di PCB (Aroclor 1254) in condizioni geobiochimiche di laboratorio che riproducono quelle presenti in sito. Il processo è quindi stato studiato in microcosmi anaerobici slurry di sedimento sospeso nella stessa acqua del sito e monitorato con un approccio chimico e microbiologico integrato. Ai fini di caratterizzare e stimolare i microganismi responsabili del processo degradativo sono state utilizzate tecniche convenzionali basate sull’inibizione selettiva di diversi gruppi microbici. Dopo una fase di latenza di 7 settimane, la coltura microbica ha declorurato velocemente ed estesamente la miscela commerciale di PCB saggiata, bioconvertendo il 70% dei congeneri ad alto grado di clorurazione (da penta- a octa- clorurati) in PCB di- e tri-clorurati. Il processo ha esibito selettività nei confronti delle posizioni meta dei gruppi 2,3- e 2,3,4-clorofenile e para dei gruppi 3,4- e 3,4,5-clorofenile, secondo il modello di declorurazione H’. Il monitoraggio delle attività microbiche in presenza dei diversi inibitori saggiati ha permesso inoltre di concludere che i batteri metanogeni e i batteri solfato-riduttori non sono direttamente coinvolti nel processo degradativo, suggerendo invece che le specie decloruranti siano appartenenti o strettamente correlate al genere Dehalococcoides. Poiché lo studio è stato eseguito in condizioni geobiochimiche di laboratorio che mimano quelle presenti in sito, i risultati ottenuti indicano che la popolazione microbica dei sedimenti del canale Brentella, se opportunamente stimolata, è potenzialmente in grado di mediare in situ la declorurazione riduttiva dei PCB preesistenti nel sedimento, contribuendo alla natural attenuation dei sedimenti contaminati.
Resumo:
Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.
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Hepatitis E is an infectious viral disease with clinical and morphological features of acute hepatitis. The aetiological agent is the Hepatitis E virus (HEV). The disease represents an important Public Health problem in developing countries where is frequently epidemic and primarily transmitted by fecal-oral route. In the last few years, a certain number of sporadic cases have been also described in industrialized countries, Italy included. A swine HEV was first identified in 1997 and is now considered an ubiquitous virus. Human and swine strains from the same geographical region have shown to have a high level of nucleotidic omology and in experimental infections, the possibility of interspecific transmission of swine strains to humans and of human strains to non-human primates has been demonstrated. Furthermore, some seroepidemiological studies have demonstrated that people working in contact with swine have a higher risk to get infected than normal blood donors. Recently, cases of HEV hepatitis have been directly associated to the ingestion of uncooked tissues from pigs, wild boar or deer and today the disease is considered an emerging zoonosis. The aims of this thesis were: evaluate HEV prevalence in Italian swine herds (both in fattening and in breeding animals); investigate the possibility of finding HEV in livers used for human consumption; investigate if there is any correlation between HEV infection and the presence of macroscopical lesions; investigate HEV prevalence in a demographic managed wild boar population; phylogenetically analyse viral strains identified. During an internship period at Veterinary Laboratories Agency (Weybridge, UK), furthermore, swine samples at different stages of production and slurry lagoons have been analysed. Six swine herds located in North Italy have been sampled at different stage of production. The overall prevalence resulted 42%, and both breeding and fattening animals were positive for HEV infection. A longitudinal study has been conducted in a herd across all stages of production until the slaughtering age. Livers have been collected from the animals at the abattoir and 11.8% of them were positive for HEV infection. No correlations have been identified between HEV infection and macroscopical lesions in pigs affected by different pathological conditions. Of 86 wild boars tested 22 (25%) were positive for HEV. Of the swine tested in UK 21,5 % and 2 of the 9 slurry lagoons (22,2%) were positive for HEV infection. All the strains identified belonged to genotype 3 and showed high percentages of nucleotidic identity with humans and swine strains identified in Europe. The high prevalence detected in these studies confirms the widespread diffusion of HEV in swine populations in Italy and in UK. Phylogenetical analysis of identified strains, similar to those identified in autochthonous human hepatitis E cases of the same geographical area, confirm the hypothesis that pigs can be a font of zoonotical infection. The finding that a fraction of the livers inserted in the food chain are positive for HEV infection it’s of some concern for Public Health. The finding of a high HEV prevalence in all examined farms, together with the observation that infection may be sub-clinical and affect animals at slaughtering age, raise concern because of the possible risk of transmission of HEV to humans by either direct contact with infected pigs, indirect contact with environment and working instruments contaminated with pig feces, or ingestion of contaminated undercooked meat.
Resumo:
I policlorobifenili (PCB) sono inquinanti tossici e fortemente recalcitranti che contaminano suoli e sedimenti di acqua dolce e marini. Le tecnologie attualmente impiegate per la loro rimozione (dragaggio e trattamento chimoco-fisico o conferimento in discarica) sono molto costose, poco efficaci o ad alto impatto ambientale. L’individuazione di strategie alternative, di natura biologica, consentirebbe lo sviluppo di un processo alternativo più sostenibile. Nel processo di declorurazione riduttiva i congeneri di PCB a più alto grado di clorurazione, che sono i più tossici, recalcitranti e maggiormente tendenti al bioaccumulo, vengono utilizzati da alcuni microrganismi anaerobici come accettori finali di elettroni nella catena respiratoria e bioconvertiti in congeneri a minor grado di clorurazione, meno pericolosi, che possono essere mineralizzati da parte di batteri aerobi. La declorurazione riduttiva dei PCB è stata spesso studiata in colture anaerobiche di arricchimento in terreno minerale ottenute a partire da sedimenti di acqua dolce; questi studi hanno permesso di dimostrare che batteri del phylum dei Chloroflexi e appartenenti al genere Dehalococcoides o filogeneticamente facenti parte del gruppo dei Dehalococcoides-like sono i decloruranti. Sono tuttavia scarse le informazioni riguardanti l'occorrenza della declorurazione dei PCB in ambienti marini, nei quali l'alta salinità e concentrazione di solfati influenzano diversamente l'evoluzione delle popolazioni microbiche. In sedimenti contaminati della laguna di Venezia è stata osservata declorurazione sia dei PCB preesistenti che di congeneri esogeni; questi studi hanno permesso l'ottenimento di colture di arricchimento fortemente attive nei confronti di 5 congeneri di PCB coplanari. In questa tesi, a partire dalle colture capaci di declorurare i PCB coplanari, sono stati allestiti nuovi passaggi di arricchimento su Aroclor®1254, una miscela di PCB più complessa e che meglio rappresenta la contaminazione ambientale. Le colture sono state allestite come microcosmi anaerobici in fase slurry, preparati risospendendo il sedimento nell'acqua superficiale, ricreando in tal modo in laboratorio le stesse condizioni biogeochimiche presenti in situ; gli slurry sterili sono stati inoculati per avviare le colture. Per favorire la crescita dei microrganismi decloruranti e stimolare così la decloruraazione dei PCB sono stati aggiunti inibitori selettivi di metanogeni (Bromoetansulfonato o BES) e solfato-riduttori (molibdato), sono state fornite fonti di carbonio ed energia (eD), quali acidi grassi a corta catena e idrogeno, utilizzate di batteri decloruranti noti, e per semplificare la comunità microbica sono stati aggiunti antibiotici cui batteri decloruranti del genere Dehalococcoides sono resistenti. Con questo approccio sono stati allestiti passaggi di arricchimento successivi e le popolazioni microbiche delle colture sono state caratterizzate con analisi molecolari di fingerprinting (DGGE). Fin dal primo passaggio di arricchimento nei microcosmi non ammendati ha avuto luogo un'estesa declorurazione dell'Aroclor®1254; nei successivi passaggi si è notato un incremento della velocità del processo e la scomparsa della fase di latenza, mentre la stessa stereoselettività è stata mantenuta a riprova dell’arricchimento degli stessi microrganismi decloruranti. Le velocità di declorurazione ottenute sono molto alte se confrontate con quelle osservate in colture anaerobiche addizionate della stessa miscela descritte in letteratura. L'aggiunta di BES o molibdato ha bloccato la declorurazione dei PCB ma in presenza di BES è stata riscontrata attività dealogenante nei confronti di questa molecola. La supplementazione di fonti di energia e di carbonio ha stimolato la metanogenesi e i processi fermentativi ma non ha avuto effetti sulla declorurazione. Ampicillina e vancomicina hanno incrementato la velocità di declorurazione quando aggiunte singolarmente, insieme o in combinazione con eD. E' stato però anche dimostrato che la declorurazione dei PCB è indipendente sia dalla metanogenesi che dalla solfato-riduzione. Queste attività respiratorie hanno avuto velocità ed estensioni diverse in presenza della medesima attività declorurante; in particolare la metanogenesi è stata rilevata solo in dipendenza dall’aggiunta di eD alle colture e la solfato-riduzione è stata inibita dall’ampicillina in microcosmi nei quali un’estesa declorurazione dei PCB è stata osservata. La caratterizzazione delle popolazioni microbiche, condotte mediante analisi molecolari di fingerprinting (DGGE) hanno permesso di descrivere le popolazioni batteriche delle diverse colture come complesse comunità microbiche e di rilevare in tutte le colture decloruranti la presenza di una banda che l’analisi filogenetica ha ascritto al batterio m-1, un noto batterio declorurante in grado di dealogenare un congenere di PCB in colture di arricchimento ottenute da sedimenti marini appartenente al gruppo dei Dehalococcoides-like. Per verificare se la crescita di questo microrganismo sia legata alla presenza dei PCB, l'ultimo passaggio di arricchimento ha previsto l’allestimento di microcosmi addizionati di Aroclor®1254 e altri analoghi privi di PCB. Il batterio m-1 è stato rilevato in tutti i microcosmi addizionati di PCB ma non è mai stato rilevato in quelli in cui i PCB non erano presenti; la presenza di nessun altro batterio né alcun archebatterio è subordinata all’aggiunta dei PCB. E in questo modo stato dimostrato che la presenza di m-1 è dipendente dai PCB e si ritiene quindi che m-1 sia il declorurante in grado di crescere utilizzando i PCB come accettori di elettroni nella catena respiratoria anche in condizioni biogeochimiche tipiche degli habitat marini. In tutte le colture dell'ultimo passaggio di arricchimento è stata anche condotta una reazione di PCR mirata alla rilevazione di geni per dealogenasi riduttive, l’enzima chiave coinvolto nei processi di dealogenazione. E’ stato ottenuto un amplicone di lughezza analoga a quelle di tutte le dealogenasi note in tutte le colture decloruranti ma un tale amplificato non è mai stato ottenuto da colture non addizionate di PCB. La dealogenasi ha lo stesso comportamento di m-1, essendo stata trovata come questo sempre e solo in presenza di PCB e di declorurazione riduttiva. La sequenza di questa dealogenasi è diversa da tutte quelle note sia in termini di sequenza nucleotidica che aminoacidica, pur presentando due ORF con le stesse caratteristiche e domini presenti nelle dealogenasi note. Poiché la presenza della dealogenasi rilevata nelle colture dipende esclusivamente dall’aggiunta di PCB e dall’osservazione della declorurazione riduttiva e considerato che gran parte delle differenze genetiche è concentrata nella parte di sequenza che si pensa determini la specificità di substrato, si ritiene che la dealogenasi identificata sia specifica per i PCB. La ricerca è stata condotta in microcosmi che hanno ricreato fedelmente le condizioni biogeochimiche presenti in situ e ha quindi permesso di rendere conto del reale potenziale declorurante della microflora indigena dei sedimenti della laguna di Venezia. Le analisi molecolari condotte hanno permesso di identificare per la prima volta un batterio responsabile della declorurazione dei PCB in sedimenti marini (il batterio m-1) e una nuova dealogenasi specifica per PCB. L'identificazione del microrganismo declorurante permette di aprire la strada allo sviluppo di tecnologie di bioremediation mirata e il gene della dealogenasi potrà essere utilizzato come marker molecolare per determinare il reale potenziale di declorurazione di miscele complesse di PCB in sedimenti marini.
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A new type of pavement has been gaining popularity over the last few years in Europe. It comprises a surface course with a semi-flexible material that provides significant advantages in comparison to both concrete and conventional asphalt, having both rut resistance and a degree of flexibility. It also provides good protection against the ingress of water to the foundation, since it has an impermeable surface. The semi-flexible material, generally known as grouted macadam, comprises an open-graded asphalt skeleton with 25% to 35% voids into which a cementitious slurry is grouted. This hybrid mixture provides good rut resistance and a surface highly resistant to fuel and oil spillage. Such properties allow it to be used in industrial areas, airports and harbours, where those situations are frequently associated with heavy and slow traffic. Grouted Macadams constitute a poorly understood branch of pavement technology and have generally been relegated to a role in certain specialist pavements whose performance is predicted on purely empirical evidence. Therefore, the main objectives of this project were related to better understanding the properties of this type of material, in order to predict its performance more realistically and to design pavements incorporating grouted macadam more accurately. Based on a standard mix design, several variables were studied during this project in order to characterise the behaviour of Grouted Macadams in general, and the influence of those variables on the fundamental properties of the final mixture. In this research project, one approach was used to the design of pavements incorporating Grouted Macadams: a traditional design method, based on laboratory determined of the stiffness modulus and the compressive strength.
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Enzyveba, a partially characterized complex consortium of not-adapted microorganisms developed through prolonged stabilization of organic wastes, was found to markedly intensify the aerobic remediation of aged PAH- and PCB-contaminated soil by acting as a source of exogenous specialized microorganisms and nutrients. Thus, Enzyveba was tested in the bioremediation of Diesel (G1) and HiQ Diesel (G2) contaminated soils under aerobic slurry-phase conditions by means of a chemical, microbiological, ecotoxicological integrated analytical procedure. The addition of Enzyveba resulted in a higher availability of cultivable specialized bacteria and fungi but this resulted in a slight intensification of soil remediation, probably because of the high content of nutrients and specialized microorganisms of the soil. In many cases, the biotreatability of soils impacted by diesel fuel is limited by their poor content of autochthonous pollutant-degrading microorganisms. Thus, bioaugmentation with stable and reproducible cultures with the required broad substrate specificity might be the solution for a successful remediation. Two microbial consortia, ENZ-G1 and ENZ-G2, were enriched from Enzyveba on G1 and G2. Both consortia consist of a similar composition of bacterial and fungal species. They exhibited a comparable and significant biodegradation capability by removing about 90% of 1 g/l of diesel fuel under liquid culture conditions. Given their remarkable biodegradation potential, richness of quite diverse microbes, stability and resistance after cryopreservation at -20 °C for several months, both consortia appear very interesting candidates for bioaugmentation on site. The mycoflora of a soil historically contaminated by high concentration of PCBs was characterised before, at the beginning and at the end of the biotreatment mentioned above. Several mitosporic fungi isolated from soil grew in presence of a mixture of three PCBs congeners when also glucose was provided. This is the first study in which 5 strains of mitosporic species able to biodegrade PCB are reported in the literature.
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Lo scopo di questa tesi è stato la produzione di un elettrolizzatore ad ossidi solidi (SOEC) mediante tecniche economiche e facilmente industrializzabili. Fondamentale a questo scopo è stata la realizzazione di una semicella costituita da un anodo poroso a base di La0.8Sr0.2MnO3-Ce0.8Gd0.2O2-δ (LSM-GDC) ed un elettrolita denso a base di Ce0.8Gd0.2O2-δ (GDC). Le tecniche utilizzate per la produzione di questo sistema sono state il colaggio su nastro e la serigrafia. Anche se generalmente, le celle SOEC vengono prodotte catodo supportate, in questo studio, l’elemento supportante scelto è stato l’anodo poiché questo garantisce una migliore stabilità meccanica all’intera cella. Tale substrato è stato ottenuto mediante colaggio su nastro accoppiato con un metodo innovativo di sinterizzazione denominato sinterizzazione reattiva, processo che prevede la formazione della fase di interesse durante un unico trattamento termico di eliminazione degli additivi organici e consolidamento del manufatto finale. La membrana elettrolitica per l’ottenimento del bilayer anodo-elettrolita, è stata prodotta mediante sia serigrafia che colaggio su nastro. L’accurato studio dell’evoluzione di fase della polvere anodica, l’ottimizzazione della sospensione per colaggio su nastro e dei trattamenti termici hanno permesso l’ottenimento di anodi (fino a dimensioni di 10x10 cm2). Lo studio dei profili di sinterizzazione delle polveri anodica ed elettrolitica e dell’influenza della tecnica di formatura sulla sinterabilità dei layer elettrolitici prodotti hanno inoltre permesso l’ottenimento di una semicella planare costituita da un elettrodo poroso ed una membrana elettrolitica densa adatte per applicazioni SOEC.
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La conoscenza e la determinazione dell’equazione cinetica è indispensabile per lo studio, la progettazione e l’ottimizzazione di qualsiasi reattore chimico. Normalmente l’analisi cinetica viene eseguita con reattori che operano in maniera quanto più prossima a condizioni ideali in modo da rendere più facile e meno affetta da errori l’interpretazione dei risultati sperimentali. In fotocatalisi è invece di fatto impossibile realizzare, anche in presenza di una perfetta miscelazione, un sistema ideale in cui si abbia un’uniforme distribuzione di tutti i parametri che influenzano la velocità di reazione. Infatti in un reattore fotocatalitico il campo di radiazione è intrinsecamente non uniforme poiché l’assorbimento della radiazione e quindi la sua attenuazione sono necessari per l’attivazione della reazione. Pertanto l’impossibilità di realizzare un sistema fotocatalitico che operi in condizioni quanto più possibile prossime all’idealità e l’incapacità di misurare sperimentalmente i valori locali di velocità di reazione e di velocità di assorbimento dei fotoni possono rendere complessa una corretta analisi cinetica. In questo lavoro vengono studiate le modalità con cui condurre comunque una rigorosa analisi cinetica di un sistema fotocatalitico slurry, nel quale il fotocalizzatore è disperso come polvere fine in sospensione nella soluzione reagente. La reazione studiata è quella di mineralizzazione dell’acido formico. Sono stati impiegati due reattori con geometrie ed illuminazioni differenti: un reattore piano illuminato con luci LED ed un reattore anulare con lampada lineare fluorescente blacklight. È stata verificata la validità di una particolare equazione cinetica, che tiene conto dell’effetto non lineare della velocità specifica (cioè per unità di massa di catalizzatore) di assorbimento dei fotoni e delle concentrazioni del reagente, dell’ossigeno e del fotocatalizzatore. Sono state inoltre determinate le condizioni critiche che possono portare ad errori nell’analisi cinetica ed è stata dimostrata l’utilità di un modello matematico che tiene conto dei bilanci di energia raggiante, di materia nonché del campo di moto. Il modello matematico, in cui compare un solo parametro aggiustabile (il tempo caratteristico di reazione od equivalentemente la costante cinetica), è in grado di riprodurre molto soddisfacentemente i risultati sperimentali in tutte le diverse condizioni operative: diversa geometria di reattore, diversa illuminazione, differente spessore ottico, diverse contrazioni di substrato e di fotocatalizzatore. Infine è stato mostrato come l’equazione cinetica ad una sola costante cinetica, che è stata adottata, descriva meglio la cinetica della reazione fotocatalitica in esame di altre equazioni a due o più costanti cinetiche spesso utilizzate in fotocatalisi e basate sulla teoria di Langmuir-Hinshelwood, a dimostrazione di un diverso meccanismo di reazione.
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The aim of the study was to assess the thickness of softened enamel removed by toothbrushing. Human enamel specimens were indented with a Knoop diamond. Softening was performed with citric acid or orange juice. The specimens were brushed in a brushing machine with a manual soft toothbrush in toothpaste slurry or in artificial saliva. Enamel loss was calculated from the change in indentation depth of the same indent before and after abrasion. Mean surface losses (95% confidence interval) were recorded in treatment groups (in nanometers): (1) citric acid, abrasion with slurry = 339 (280-398); (2) citric acid, abrasion with artificial saliva = 16 (5-27); (3) orange juice, abrasion with slurry = 268 (233-303); (4) orange juice, abrasion with artificial saliva = 14 (5-23); (5) no softening, abrasion with slurry = 28 (10-46). The calculated thickness of the softened enamel varied between 254 and 323 nm, depending on the acid used.
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It was the aim of the study to evaluate the clinical and antibacterial effect of a dentifrice containing an anti-inflammatory plant extract (SB) versus a placebo (PLA) using an experimental gingivitis model. Forty subjects (20 per group) discontinued all oral hygiene measures for four teeth for a period of 21 days using a shield (to generate a possible gingivitis) while they could brush the other teeth normally. After brushing, the shield was removed and teeth were treated with the randomly assigned toothpaste slurry for 1 min. Löe and Silness gingival index (GI), Silness and Löe plaque index (PI), and biofilm vitality (VF%) were assessed at days 0, 14, and 21, respectively. Subjects of the PLA group developed a GI of 0.82?±?0.342 (day 14) and 1.585?±?0.218 (day 21), while the data of the SB group were significantly reduced (0.355?±?0.243 and 0.934?±?0.342, p?0.001). While PI was significantly reduced at all follow-up appointments, reductions in VF reached the level of significance only at day 21. The results suggest that the new toothpaste formulation was able to significantly reduce the extent of gingivitis, plaque development, and vital flora.
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Objectives: This in vitro study aimed to investigate the protective effect of four commercial novel agents against erosion. Methods: Ninety human molars were distributed into 9 groups, and after incubation in human saliva for 2 h, a pellicle was formed. Subsequently, the specimens were submitted to demineralization (orange juice, pH 3.6, 3 min) and remineralization (paste slurry containing one of the tested novel agents, 3 min) cycles, two times per day, for 4 days. The tested agents were: (1) DenShield Tooth; active ingredient: 7.5% W/W NovaMin® (calcium sodium phosphosilicate); (2) Nanosensitive hca; active ingredient: 7.5% W/W NovaMin®; (3) GC Tooth Mousse; active ingredient: 10% Recaldent™ (CPP-ACP); (4) GC MI Paste Plus; active ingredients: 10% Recaldent™, 900 ppm fluoride. Two experimental procedures were performed: in procedure 1, the tested agents were applied prior to the erosive attack, and in procedure 2 after the erosive attack. A control group receiving no prophylactic treatment was included. Surface nanohardness (SNH) of enamel specimens was measured after pellicle formation and after completion of daily cyclic treatment. Results: SNH significantly decreased at the end of the experiment for all groups (p < 0.05). In both procedures, there was no statistically significant difference between the control group and those treated with paste slurries (p > 0.05). In addition, the changes in SNH (ΔSNH = SNHbaseline − SNHfinal) did not show statistically significant difference between both procedures (p > 0.05). Conclusion: Tooth erosion cannot be prevented or repaired by these novel agents, regardless of fluoride content.
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The osteogenic potential of autogenous bone grafts is superior to that of allografts and xenografts because of their ability to release osteoinductive growth factors and provide a natural osteoconductive surface for cell attachment and growth. In this in vitro study, autogenous bone particles were harvested by four commonly used techniques and compared for their ability to promote an osteogenic response. Primary osteoblasts were isolated and seeded on autogenous bone grafts prepared from the mandibles of miniature pigs with a bone mill, piezo-surgery, bone scraper, and bone drill (bone slurry). The osteoblast cultures were compared for their ability to promote cell attachment, proliferation, and differentiation. After 4 and 8 hrs, significantly higher cell numbers were associated with bone mill and bone scraper samples compared with those acquired by bone slurry and piezo-surgery. Similar patterns were consistently observed up to 5 days. Furthermore, osteoblasts seeded on bone mill and scraper samples expressed significantly elevated mRNA levels of collagen, osteocalcin, and osterix at 3 and 14 days and produced more mineralized tissue as assessed by alizarin red staining. These results suggest that the larger bone graft particles produced by bone mill and bone scraper techniques have a higher osteogenic potential than bone slurry and piezo-surgery.
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Background: Autogenous bone grafts obtained by different harvesting techniques behave differently during the process of graft consolidation; the underlying reasons are however not fully understood. One theory is that harvesting techniques have an impact on the number and activity of the transplanted cells which contribute to the process of graft consolidation. Materials and Methods: To test this assumption, porcine bone grafts were harvested with four different surgical procedures: bone mill, piezosurgery, bone drilling (bone slurry), and bone scraper. After determining cell viability, the release of molecules affecting bone formation and resorption was assessed by reverse transcription polymerase chain reaction and immunoassay. The mitogenic and osteogenic activity of the conditioned media was evaluated in a bioassay with isolated bone cells. Results: Cell viability and the release of molecules affecting bone formation were higher in samples harvested by bone mill and bone scraper when compared with samples prepared by bone drilling and piezosurgery. The harvesting procedure also affected gene expression, for example, bone mill and bone scraper samples revealed significantly higher expression of growth factors such as bone morphogenetic protein-2 and vascular endothelial growth factor compared with the two other modalities. Receptor activator of nuclear factor kappa B ligand expression was lowest in bone scraper samples. Conclusion: These data can provide a scientific basis to better understand the impact of harvesting techniques on the number and activity of transplanted cells, which might contribute to the therapeutic outcome of the augmentation procedure.
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The effect of the swirl component of air injection on the performance of an airlift pump was examined experimentally. An airlift pump is a device that pumps a liquid or slurry using only gas injection. In this study, the liquid used was water and the injected gas was air. The effect of the air swirl was determined by measuring the water discharge from an airlift pump with an air injection nozzle in which the air flow had both axial and tangential components and then repeating the tests with a nozzle with only axial injection. The induced water flow was measured using an orifice meter in the supply pipeline. Tests were run for air pressures ranging from 10 to 30 pounds per square inch, gauge (psig), at flow rates from 5 standard cubic feet per minute (scfm) up the maximum values attainable at the given pressure (usually in the range from 20 to 35 scfm). The nozzle with only axial injection produced a water flow rate that wasequivalent to or better than that induced by the nozzle with swirl. The swirl component of air injection was found to be detrimental to pump performance for all but the smallest air injection flow rate. Optimum efficiency was found for air injection pressures of 10 psig to 15 psig. In addition, the effect of using auxiliary tangential injection of water to create a swirl component in the riser before air injection on the overall capacity (i.e., flow rate) and efficiencyof the pump was examined. Auxiliary tangential water injection was found to have no beneficial effect on the pump capacity or performance in the present system.
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New toothpastes with anti-erosion claims are marketed, but little is known about their effectiveness. This study investigates these products in comparison with various conventional NaF toothpastes and tin-containing products with respect to their erosion protection/abrasion prevention properties. In experiment 1, samples were demineralised (10 days, 6 × 2 min/day; citric acid, pH 2.4), exposed to toothpaste slurries (2 × 2 min/day) and intermittently stored in a mineral salt solution. In experiment 2, samples were additionally brushed for 15 s during the slurry immersion time. Study products were 8 conventional NaF toothpastes (1,400-1,490 ppm F), 4 formulations with anti-erosion claims (2 F toothpastes: NaF + KNO(3) and NaF + hydroxyapatite; and 2 F-free toothpastes: zinc-carbonate-hydroxyapatite, and chitosan) and 2 Sn-containing products (toothpaste: 3,436 ppm Sn, 1,450 ppm F as SnF(2)/NaF; gel: 970 ppm F, 3,030 ppm Sn as SnF(2)). A mouth rinse (500 ppm F as AmF/NaF, 800 ppm Sn as SnCl(2)) was the positive control. Tissue loss was quantified profilometrically. In experiment 1, most NaF toothpastes and 1 F-free formulation reduced tissue loss significantly (between 19 and 42%); the Sn-containing formulations were the most effective (toothpaste and gel 55 and 78% reduction, respectively). In experiment 2, only 4 NaF toothpastes revealed significant effects compared to the F-free control (reduction between 29 and 37%); the F-free special preparations and the Sn toothpaste had no significant effect. The Sn gel (reduction 75%) revealed the best result. Conventional NaF toothpastes reduced the erosive tissue loss, but had limited efficacy regarding the prevention of brushing abrasion. The special formulations were not superior, or were even less effective.