No description available.

Adsorption is a versatile purification technique to selectively separate different peptide fractions from a mixture using mild operation conditions. Porous carbons are ideally suited to separate ACE-inhibiting dipeptides by combining tailored size exclusion and polarity selectivity. The desired peptide fraction is mostly hydrophobic and very small and should adsorb inside hydrophobic micropores. The second topic of this thesis is linked to energy storage. The lithium-sulfur battery is a promising alternative to common lithium-ion batteries with theoretical capacities of up to 1672 mAh g−1 sulfur. The second aim of this thesis is to conduct an in-depth investigation of polysulfides interacting with selected carbon materials in a simplified battery electrolyte environment. The focus of this study is laid on the impact of surface polarity and pore size distribution of the carbon to develop a quantitative correlation between polysulfide retention and porosity metrics. Both, the enrichment of ACE-inhibitors and the retention of polysulfides rely on liquid phase adsorption in porous materials, linking the above mentioned topics. This thesis not only aims to develop an enrichment process or to find a superior battery cathode but also strives to explore structure-property relationships that are universally valid. Understanding the complex interplay of pore size and polarity leading to selective interactions between pore wall and the adsorbed species is given a high priority.

<p>  </p> <p>Room-temperature sodium-sulfur (RT Na-S) batteries are an emergent new technology that are highly attractive due to their low raw materials cost and large theoretical specific energy. However, many fundamental problems still plague RT Na-S batteries that prevent their progression from the research and development phase to the commercial phase. Sulfur and its final discharge product are insulators, and intermediate polysulfide discharge products are soluble in commonly used liquid electrolytes. As a result, RT Na-S cells exhibit large capacity defects, low coulombic efficiencies, and rapid capacity fading. Additionally, the reactive sodium metal anode can form dendrites during cycling, which reduces capacity and shortens cell life. One way to combat these issues is the judicious selection of electrolyte components. In this study, the effects of monoglyme (G1), diglyme (G2), and tetraglyme (G4) glyme ether electrolyte solvents on RT Na-S cell performance are investigated. Galvanostatic cycling of Na/Na symmetric coin cells reveals that the G2 solvent enable stable cycling at low overpotentials over a wide range of current densities. In contrast, the G1-based cells show evidence of dendritic plating, and G4-based cells are not suitable for use at high current densities. Electrochemical impedance spectroscopy during cycling confirms that the G2 solvent facilitates the formation of a strong, stable SEI on the Na electrode surface. Results from galvanostatic cycling of RT Na-S full coin cells demonstrates that G1-based cells deliver the highest initial specific discharge capacities among the three cell types, but G4-based cells are the most reversible. Infinite charging, the indefinite accrual of charge capacity at the high charge voltage plateau, affects all cell types at different cycle numbers and to different extents. This behavior is linked to the strength of the polysulfide shuttle during charge. Optical microscopy experiments show that G2 and G4 facilitate the formation of the S3•- sulfur radical, which reduces capacity. G1 minimizes the radical formation and thus delivers higher initial specific discharge capacity. In order to fully optimize the electrolyte for RT Na-S cells, future work should study glyme solvent blends, additives, and concentrated salts.</p>

No description available.

<p>As the future of energy looks increasingly electrified, the development of safe and sustainable battery technologies has never been more relevant. This is particularly critical for applications in stationary energy storage and transportation, where batteries must be produced and stored at large scale. Sustainability is necessary to meet the volume of demand at reasonable cost without straining resources. Safety is also paramount since fires can easily spread from one cell to the next and result in catastrophe when batteries are stored in proximity for large power banks or EVs. The focus of this thesis is thus to design and engineer materials for rechargeable batteries, which improve safety and sustainability while still enhancing the electrochemical performance. Towards this end, polymers play a central role throughout this thesis work due to their tunable chemical and physical properties.</p>

No description available.

[pt] Esta dissertação apresenta os resultados obtidos no processo de remediação de uma área contaminada por cromo hexavalente por meio da técnica de remediação química in situ (ISCR). A área de estudo localiza-se na cidade do Rio de Janeiro e foi ocupada por uma fábrica de vidros por cerca de quarenta anos e comprada para construção de condomínios residenciais. A área de estudo passou um processo de gerenciamento ambiental que contemplou diversos estudos ambientais para aquisição de dados e delimitar a contaminação, horizontal e verticalmente. O teste de bancada realizado com o reagente químico polissulfeto de cálcio demonstrou ser eficiente para reduzir as concentrações de cromo hexavalente em solo e água subterrânea. Com base nos dados adquiridos neste teste foi possível calcular a dose de injeção do polissulfeto de cálcio. Foram realizados setenta pontos de sondagem, pela técnica direct push, para injetar duzentos e cinquenta e dois mil e trinta litros de solução de polissulfeto de cálcio e água, sendo aproximadamente três mil e quinhentos litros por ponto de injeção. Os resultados após a injeção demonstraram que o polissulfeto de cálcio conseguiu remover o cromo hexavalente que estava adsorvido ao solo e reduziu a concentração de cromo hexavalente na água subterrânea entre quarenta e seis e sessenta e sete e noventa e nove e noventa e cinco por cento , após dezenove meses da injeção. Dessa forma, comprovou a eficiência deste reagente químico para remediação de áreas contaminadas por cromo hexavalente, assim como foi observado nos artigos técnicos de estudos de casos nos Estados Unidos e Europa. / [en] This dissertation presents the results obtained in the remediation process remediation of a contaminated area by hexavalent chromium applying the technology in situ chemical remediation (ISCR). The study area is located in the Rio de Janeiro city and was occupied by a glass factory for forty years and purchased for construction of residential condominiums. This dissertation presents the results obtained in the remediation process remediation of a contaminated area by hexavalent chromium applying the technology in situ chemical remediation (ISCR). The study area is located in the Rio de Janeiro city and was occupied by a glass factory for forty years and purchased for construction of residential condominiums. Chromium is an important metal for the industry and is used in various products and processes, such as electroplating, leather treatment, pulp, wood preservation, and refractory manufacturing. The trivalent chromium is essential from a nutritional point of view, non-toxic and poorly absorbed in the body, acting in the maintenance of some functions. Cr(III) is the most common being found and occurs naturally, since the element Cr(VI) can occur naturally, but in low concentrations, if the groundwater has geochemical conditions the Cr (III) can be oxidize to Cr (VI). The hexavalent chromium is the most dangerous valence state and, according to ATSDR (two thousand and twelve), have greater mobility in the groundwater, being carcinogenic by inhalation of high doses of soluble chromate salts. The mobility of hexavalent chromium is high in soil and groundwater because it is not adsorbed by the soil in that valence state, on the other hand when it is in trivalent form is strongly adsorbed by the soil, forming insoluble precipitates, having low mobility in soil and groundwater. The hexavalent chromium remediation by in situ chemical reduction using calcium polysulfide has been the subject of several field studies documented in the literature, both for soil and groundwater from the Chromite Ore Processing Residue (COPR) (Storch, et al., two thousand and two; Graham, et al., two thousand and six ; Charboneau, et al., two thousand and six ; Wazne, et al., two thousand seven a; Wazne, et al., two thousand seven b; Chrysochoou, et al., two thousand and ten ; Chrysochoou & Ting, two thousand and eleven ; Pakzadeh & Batista, two thousand and eleven ; Chrysochoou, et al., two thousand and twelve ). Calcium polysulfide is a fertilizer to soil and commercially available and has been used in some remediation studies cases for reducing hexavalent chromium in soil and groundwater. Being commercially available and used as fertilizer, it is a relatively cheap chemical reagent in comparison with other chemical compounds exclusively developed for this purpose. The stoichiometric demand and the chemical kinetics of the reduction of Cr (VI) by the calcium polysulfide in aqueous solution was studied by Graham et al. (two thousand and six) from the chromite ore processing residue (COPR). With this study it was reported that a molar ratio of a point sixty-six is required (close to the theoretical value of one point five) and a first-order kinetics with an initial concentration of twenty-six eight point mg/L and pH of the CPS solution around eleven point five, with the presence of oxygen. Thus, the hexavalent chromium is reduced to chromium hydroxide, slightly water soluble compound which is precipitated to the soil. The trivalent chromium has low solubility, toxicity, mobility, reactivity and is considered stable. There are various application techniques of chemical reagents in the underground environment, and choosing the most appropriate method for each area depends on the type of contaminant, geological environment, groundwater and surface interference, depth, thickness and size of the contaminated area. As described by Suthersan (mil novecentos ninety-six), the injection of chemical reagents has to achieve two objectives: (one) creating and maintaining an ideal redox environment and other parameters such as pH, presence or absence of dissolved oxygen, etc.; and (two) the delivery and distribution of the necessary reagents for a homogeneous way throughout the injection area, both horizontally and vertically. Thus, it is essential that the conceptual model of the study area is very detailed, so there is no doubt in the choice of chemical reagent application methodology. Although there are numerous laboratory studies on hexavalent chromium remediation using calcium polysulfide, there are few reports in the literature on the field application, especially case studies in Brazil, therefore, this case study becomes a demonstration applying calcium polysulfide as a remediation technique for hexavalent chrome, with geochemical data, which are important for monitoring chemical reduction. This case study shows the effectiveness, dosage and concentration of the study area, and may apply to other hexavalent chromium remediation projects. Materials and Methods A former glass factory (the Site ) operated in the North Zone of Rio de Janeiro / RJ, Brazil from the mid-thousand nine hundred and fifty s to two thousand and five. A portion of the facility was used to store raw material to produce glass, including arsenic oxide, and another portion of the Site was used to conduct industrial plating using hexavalent chromium (Cr(VI)) in the glass molds. In two thousand and nine, the Site was purchased for mixed use redevelopment, demanding an environmental assessment and subsequent remediation. Between two thousand and nine and two thousand and twelve several phases of site investigation was conducted. The results of the investigation indicated that Cr(VI) was present in soil at concentrations up to approximately twenty one mg/kg and in groundwater at concentrations up to approximately thirty mg/L. These concentrations exceeded regulatory criteria of three hundred mg/Kg for soil and zero point zero five mg/L for groundwater. A phased remedial approach was developed consisting of the following: (a) excavation and off-site disposal of two and four hundred ton of Cr(VI) impacted soil from the source area, performed in the unsaturated and saturated zone soils in the Cr(VI) source area; (b) post-excavation monitoring of the groundwater conditions; and (c) groundwater treatment following the excavation program. Hexavalent chromium concentrations in groundwater decreased significantly following the excavation, however, additional reduction of concentrations of Cr(VI) contaminant in groundwater was required. Then was designed and implemented a set of bench-scale treatability tests in order to evaluate groundwater remediation alternatives. Several proprietary and non-proprietary reductants for co-treatment of Cr(VI) were evaluated. Calcium polysulfide were selected to treat Cr(VI). To reduce residual Cr(VI) concentrations in the groundwater plume located downgradient of the former excavated source area, dois e seven hundred cubic meters were targeted for active treatment. The groundwater remediation approach consisted of the injection of thirty liters of CPS (twenty nine percent) diluted in two hundred and twenty liters of water, yielding a total of two hundred and fifty liters of solution injected using direct push technology into seventy two locations. Groundwater Monitoring As part of chemical reagent injection stage was performed the baseline monitoring with collection of soil and groundwater samples. The soil sampling was performed by direct push technique using PVC liner with two inches in diameter, to analyze the total and hexavalent chromium concentrations. Six months after the injection were installed sixteen monitoring wells, eight shallow wells (five meters) and eight deep wells (nine meters) spread upstream, side, middle and downstream of the injection area. Groundwater geochemical parameters (i.e., temperature, total solids dissolved, specific conductance, pH, oxidation-reduction potential, and temperature) were measured at the time groundwater samples were collected. Groundwater samples were collected and analyzed for total and dissolved chromium, hexavalent chromium, iron, arsenic, manganese, calcium, sulfate, and sulfide. Samples were field-filtered with disposable zero point forty-five μm polyethylene filter capsules prior to collecting samples for dissolved metals. Results and Discussion Dose calculations for the reduction of hexavalent chromium have been performed with the data obtained in the bench-scale treatability test and resulted in a stoichiometric demand of four mlCPS/kg soil to the treatment of the study area. Therefore thirty liters of solution was used containing twenty-nine percent calcium polysulfide and approximately two hundred and twenty two liters to perform their mixture, totaling two hundred and fifty-two thousand and thirty liters of solution. For solution injection were performed seventy two soil borings with eight point five meters deep, and the product was injected range between two point five and eightpoint five meters. The depth of injection was from two point five mbgl covered any change in water level due to seasonal variation. In each soil boring was injected chemical reagent solution comprised four hundred and seventeen liters of calcium polysulfide diluted in tree and eighty-three liters of water for a total volume of tree and a half liters of solution injected per point. The comparative analysis results of the third monitoring campaign ( eighteen months post-injection) with the baseline campaign (september/two thousand and twelve) indicated reduction of hexavalent chromium concentrations between forty-six point sixty-seven and ninety-nine and ninety-five percent. Regarding the second monitoring campaign (twelve months post-injection), the hexavalent chromium concentrations reduced between twenty-three point ninety-nine and ninety nine point seventy-nine percent in five of the fifteen monitoring wells that were sampled. In three of the fifteen monitoring wells the hexavalent chromium concentrations remained below the quantitation limit used by the analytical laboratory method. There was no increase in hexavalent chromium concentration, compared the results of the third and second monitoring campaign. The evaluation of the Eh and pH values measured in the monitoring campaigns showed that the pH value was in the acidic range (about four ) and after removal of contaminated soil with hexavalent chromium pH raised to between five and six, after the chemical reagent injection pH increased to the basic range (above seven point five). In the second and third campaign the pH reduced to acid range (below six point five), which can be regarded as the pH value of the area background. The Eh has inversely proportional behavior, increasing between the first and third campaign, and in the third campaign the measured values are in the ranges considered as moderately reducing (hundred to four hundred mV) and oxidizer (> four hundred mV). The pH variation also showed a relationship between increased concentrations of calcium, iron, manganese and sulfate (in some monitoring wells). There were also reductions in hexavalent chromium concentrations in monitoring wells. Conclusion This case study indicates that the use of different remediation techniques when applied together (excavation and chemical reduction), reducing the time required for remediation of a contaminated site without impacting the final cost of remediation. The chemical reduction of hexavalent chromium using calcium polysulfide was effective to reduce the concentration to less than the quantification limit of the analytical method used. Therefore, as presented it is necessary to carry out several studies to detail the hexavalent chromium concentration in the site, as well as understand the geochemistry of groundwater and performing bench-scale tests to evaluate the effectiveness of the chemical reagent in the site study hydrogeological environment and calculate the required dose. The treatability test with calcium polysulfide demonstrated the feasibility of using this chemical reagent by In Situ Chemical Reduction (ISCR) to reduce the hexavalent chrome concentration in soil and groundwater. The test resulted in a stoichiometric demand of four mlCPS /kg soil to the treatment of the study area. Soil samples collected six months after injection showed that the calcium polysulfide could desorb hexavalent chromium from the soil, since, contaminant concentrations were not detected in the samples. neteen months after the injection of the chemical reagent the groundwater concentrations of hexavalent chromium reduced from forty-six point sixty-seven to ninety-nine and ninety-five percent in relation to baseline campaign. And, of the fifteen monitoring wells in just three wells hexavalent chromium concentrations were detected. This demonstrates the effectiveness of using calcium polysulfide to remediate hexavalent chromium in soil and groundwater, confirming the studies by Storch et al. (two thousand and two), Graham et al (two thousand and six), Charboneau et al. ( two thousand and six), Wazne et al. (two thousand and seven a), Wazne et al. (two thousand and seven b), Chrysochoou et al. (two thousand and ten), Chrysochoou & Ting (two thousand and eleven), Pakzadeh & Batista (two thousand and eleven), Chrysochoou et al (2012) in several areas in United States and Europe.

<p>Two studies incorporated providing the groundwork for a blueprint to design sodium sulfur cells from electrode fabrication to choices in electrolyte such as DME, DEGDME, TEGDME and two different salts NaClO4 and NaPF6. First study describes role of the binder within the system comparing carboxymethyl cellulose and carboxymethyl cellulose with a styrene butadiene elastomer addition. The second study focuses on methods to prevent polysulfide shuttling within room temperature sodium sulfur system</p>

La maîtrise de l’additivation est l’un des enjeux majeurs de la formulation des lubrifiants, notamment pour l’industrie automobile. La formulation d’une huile est toutefois très complexe en raison du nombre important d’additifs et des nombreuses interactions possibles entre additifs, notamment entre les additifs de surface. Les phosphites organiques et les polysulfures organiques ont déjà montré leur efficacité en tant qu’additifs de surface. Toutefois malgré leur usage répandu dans les formulations des lubrifiants automobiles, peu d’études traitent des interactions pouvant avoir lieu entre ces deux types de composés. Ce travail de thèse a pour objectif la compréhension des mécanismes d’interaction (antagonisme/synergie) pouvant exister entre les phosphites organiques et les polysulfures organiques. Pour cela, une approche originale sur la lubrification par la phase gazeuse s’est avérée très pertinente. Le couplage du Tribomètre à Environnement Contrôlé (TEC) avec les systèmes d’analyses de surface XPS/Auger a permis d’analyser les tribofilms générés in situ et d’éviter ainsi toute contamination et/ou oxydation du tribofilm avant analyse. Les molécules choisies sont les additifs de lubrification industriels (polysulfures tertaires) à faibles poids moléculaires ou alors des molécules à faible poids moléculaires ayant les mêmes fonctions chimiques que les additifs usuels : trimethyl phosphite (TMPi), dimethyl phosphite (DMPi). L’étude des réactions des tribochimiques des molécules phosphorés a permis de mettre en évidence le rôle ambivalent du DMPi qui se comporte à la fois comme un phosphite pour former un phosphure de fer et comme un phosphate. Le mécanisme formation du phosphure de fer a peu être étayé par la réalisation de calculs ab initio sur l’adsorption dissociative du TMPi sur une surface de fer. Les TPS étudiés génèrent quant à eux des tribofilms à base disulfure de fer. Les mélanges binaires réalisés en phase gazeuse ont permis de mettre en évidence l’importance des rapports de concentrations des vapeurs introduites et du mode d’introduction des molécules dans le tribomètre. Les résultats obtenus en tribologie en phase gazeuse ont été corroborés par des essais complémentaires en phase liquide. / Mastering the addivation is one of the biggest issues for the lubricants formulation, especially in the automobile industry. However automotive lubricants are very complex systems due to the numerous additives mixed with base oils. Many interactions can occur between additives, especially between surface additives. Organic phosphites and organic polysulphides have already demonstrated their effectiveness as surface additives. However, despite their widespread use in the formulations of automotive lubricants, few studies deal with the interactions taking place between these two types of compounds. The aim of this study is to understand the interactions, antagonistic or synergetic effect between these kinds of additives using Gas Phase Lubrication (GPL) approach. A Environmental Controlled Tribometer (TEC) was used as a tool to simulate the interaction between organophosphate additives and polysulfurous additives. In situ surface analysis was performed in the tribofilm formed during friction using of X-ray Photoelectron Spectroscopy (XPS) and Auger Electron Spectroscopy(AES) in order to avoid any oxidation or air contamination. The molecules selected for the study can be same as the additive like the TPS molecules which are widely used as lubricant additives. Howeverto simulate the phosphite chemical function of phosphite additives, we need to select smaller molecule having the same chemical function. These molecules are dimethyl phosphite (DMPi), trimethylphosphate (TMPi) for simulating the phosphite chemical function and organic polysulphides (TPS44and TPS32). The study of the tribochemical reactions of organic phopshites allowed to clearly characterise the ambivalence of DMPi, which can react like a phosphite and induce iron phosphide formation or react like a phosphate. Ab initio numerical simulation on TMPi dissociative adsorption was carried out to identify the reactions pathways leading to iron phosphide formation. The tribochemical reaction of TPS44 on metallic iron surface leads to the formation of iron disulphidebased tribofilm. The binary vapours mixtures studied by GPL allowed to clearly identify the importance of the vapour concentration ratio between phosphite and polysulphide. Liquid phase experiments were also carried out to confirm the trend observed in GPL approach.

Ces travaux ont permis d’approfondir les connaissances du mécanisme de déchargepeu conventionnel de l’accumulateur Li/S et de ses limitations. L’ensemble desrésultats a convergé vers une unique conclusion, à savoir que le système Li/S estprincipalement limité par le phénomène de passivation de l’électrode positive en finde décharge. Les polysulfures de lithium à chaines courtes précipitent à la surface del’électrode positive de soufre. Isolants électroniques, ils sont responsables de la perteprogressive de surface active de l’électrode et de la fin prématurée de la décharge.Ainsi, les performances électrochimiques ont pu être significativement améliorées entravaillant sur la morphologie de l’électrode positive, et sur la composition del’électrolyte. En augmentant la surface spécifique de l’électrode, la quantité depolysulfures de lithium qui peut précipiter en fin de décharge est augmentée, et lapassivation totale de l’électrode est retardée. En augmentant la solubilité despolysulfures de lithium dans l’électrolyte, la précipitation des espèces est retardée etla décharge prolongée. Dans cette optique, les solvants de type PEGDME semblentêtre les plus prometteurs à ce jour. Enfin, un mécanisme possible de réduction dusoufre en électrolyte de type éther a pu être proposé. / This work aimed at better understanding the Li/S cell discharge mechanism and itslimiting parameters. A general conclusion was following from these data: the Li/Ssystem is mainly limited by the passivation process of the sulfur positive electrode,occurring at the end of discharge. Insulating lithium polysulfides precipitate on thepositive electrode surface, thus leading to a gradual loss of the electrode activesurface and to the early end of discharge. As a consequence, the electrochemicalperformances can be significantly improved by working either on the positiveelectrode morphology or on the organic electrolyte composition. Increasing thespecific surface of the positive electrode enables to increase the amount ofpolysulfide compounds that can precipitate on the electrode, thus delaying the fullpassivation of the sulfur electrode and the end of discharge. Working on the organicelectrolyte composition enables to increase the polysulfide solubility and to preventthem from quickly precipitating, thus delaying the end of discharge too. To thispurpose, PEGDME solvents seem to be quite promising. Finally, a possiblemechanism for sulfur reduction in ether-based electrolytes could be proposed.