Os pegmatitos estudados estão associados à fácies albita granito do granito Madeira, a qual corresponde ao depósito de Sn-Nb-Ta (F, ETR, U, Th) Madeira, na mina Pitinga (AM) e estão associados a falhas de orientação N320/60SW. Estas rochas contêm minerais poucos comuns como gagarinita (NaCaYF6), genthelvita (Zn4Be3(SiO4)3S) e polilitionita (KLi2AlSi4O10(F, OH)2), além de grandes quantidades de criolita (Na3AlF6). Com base na composição química e mineralógica, estes pegmatitos foram classificados em três tipos: PEG ANF (teores médios de K e Na, com alta concentração de anfibólios), PEG POL (rico em K e com alta concentração de polilitionita) e PEG CRIO (rico em Na e com alta concentração de criolita). Estes pegmatitos contêm altos teores de ETR (especialmente ETRP) e Y, que estão concentrados principalmente na xenotima e na gagarinita. Estes elementos também ocorrem em elevados teores na grande parte dos demais minerais analisados. Também se destacam as concentrações anômalas de F, muito superiores às detectadas nos pegmatitos de outras localidades, e que promoveram o enriquecimento em Li, Na, K, Rb e Cs. A similaridade na composição química do AGN com os pegmatitos indica que eles possuem a mesma fonte. / The pegmatites studied are associated with the albite granite facies of the Madeira granite, which corresponds to the Sn-Nb-Ta (F, ETR, U, Th) Madeira deposit at the Pitinga mine (AM). They are associated with N320/60SW orientation faults. These rocks contain few common minerals such as gagarinite (NaCaYF6), genthelvite (Zn4Be3(SiO4)3S) and polylithionite (KLi2AlSi4O10(F,OH)2), as well as large amounts of cryolite (Na3AlF6). Based on the chemical and mineralogical composition, these pegmatites were classified into three groups: PEG ANF (medium K and Na, with high concentration of amphiboles), PEG POL (K rich and with high polylithionite concentration) and PEG CRIO (rich in Na and with high concentration of cryolite). These pegmatites contain high levels of REE (especially HREE) and Y, which are mainly concentrated in xenotime and gagarinite. These elements also occur at high levels in most of the other minerals analyzed. Anomalous concentrations of F, much higher than those detected in pegmatites from other localities, were also highlighted, and promoted enrichment in Li, Na, K, Rb and Cs. The similarity in the chemical composition of AGN with pegmatites indicates that they have the same source.

O problema de rejeitos radioativos é uma preocupação de âmbito mundial, uma vez que não há, ainda, um local definido para a construção de um repositório para rejeitos radioativos de alto nível. Uma das etapas preliminares para a escolha do local mais apropriado é o estudo geológico associado a estudos experimentais de adsorção das espécies químicas envolvidas nos processo. Neste trabalho foi utilizado uma amostra de rocha basáltica, da região sul da Formação Serra Geral, coletada em Frederico Westphalen (RS), que servirá como candidata à rocha hospedeira para locação de rejeitos radioativos. Foram realizados dois experimentos, a saber: "Batch Test" e percolação, ambos sob pressão atmosférica, à temperatura ambiente de 25°C, com a finalidade de estudar a capacidade de sorção dos elementos terras raras - ETR. Os ETR são utilizados neste trabalho em função de sua analogia com os actinídeos, visando a investigar o comportamento geoquímico e a especiações dos mesmos em águas naturais, buscando a possibilidade de armazenamento geológico de rejeitos radioativos, uma vez que a adsorção dos ETR depende de variáveis do ambiente como pH, força iônica, temperatura e presença de ligantes, como carbonatos e constituintes de superfícies dos minerais. Foi realizado experimento de percolação dos ETR, a 100ppb, no basalto (com granulometria 80 mesh) em soluções com força iônica I= 0,025 M e I=0,5 M de NaCl. O pH foi controlado em uma faixa de 5,6 a 7,6 com adição de HNO3. As concentrações foram analisadas por ICP-MS. O "Batch Test" é uma eficiente forma de se obter isotermas de sorção/dessorção, além de valores da razão entre as distribuições sólido/solução e estimar a solubilidade. O experimento de percolação, foi realizado sob pH controlado em torno de 6, e permitiu verificar a "preferência" dos ETR pesados em relação aos ETR leves. / The problem of radioactive wastes is a concern of world-wide scope, a time that does not still have a defined local for the construction of a repository for radioactive wastes of high level. One of the preliminary stages for the choice of the place more appropriate is the geologic study associated to the experimental studies of adsorprtion of the involved chemical species in the process. In this work, a sample of basaltic rock was used, of the South Region of the Formation Serra Geral, collected in Frederico Westphalen Town (RS), that it will be probably a candidate to the rock hostess for location of radioactive wastes. Two experiments have been carried out through, namely: "Test Batch" and Percolating, both under atmospheric pressure, at the ambient temperature of 25°C, with the purpose to study the capacity of sorption of the rare earth elements - REE. The REE are used in this work in function of its analogy with the actinídes, aiming at to investigate the chemistry behavior and the speciations of the same in natural waters, searching the possibility of geologic storage of radioactive wastes, a time that the adsorption of the REE depends on variables of the environment as pH, ionic strengh, temperature and presence of ligants, as carbonates and constituent of surfaces of minerals. Experiment of percolating of the REE was carried through, 100ppb, in the basalt (with 80 mesh) in solutions with ionic strengh I= 0,025 M and I=0,5 M of NaCl. pH was controlled in a range of 5,6 the 7,6 with HNO3 addition. The concentrations were analyzed by ICP-MS. The "Batch Test" is an efficient form of studing sorption/dessorption isotherms, beyond values of the reason between the distributions solid/solution and estimation of the solubility. The percolating experiment, was carried through under pH controlled around 6, and allowed to verify the behaviour of heavy REE in comparison with the light REE.

A cultura de citros exige aplicações constantes de fertilizantes para atingir níveis satisfatórios de produtividade. Fertilizantes contêm outros elementos químicos além daqueles de interesse, como, por exemplo, os elementos terras raras (ETR). Estudos mostram que aplicações de ETR podem aumentar o crescimento e a produtividade das plantas como também causar efeitos nocivos ao ambiente e ao homem. No Brasil, não é prática comum a adição de ETR em fertilizantes, porém alguns insumos contêm em sua composição. Os objetivos deste trabalho foram quantificar os ETR nos compartimentos planta, solo e insumos de agroecossistemas citrícolas, avaliar o modelo de distribuição, identificar as principais fontes de ETR e estudar os efeitos desses elementos na planta cítrica. Para determinação dos ETR, utilizou-se da análise por ativação neutrônica instrumental (INAA) e espectrometria de massas com plasma indutivamente acoplado (ICP-MS). Foram feitos experimentos no campo e em casa-de-vegetação. O experimento de campo foi realizado em quatro propriedades de citros, sendo duas sob sistema de produção orgânico e duas sob o sistema de produção convencional, na região de Borborema, SP, com a variedade Valência (Citrus sinensis L. Osbeck) enxertada sobre limão cravo (Citrus limonia Osbeck),. Amostraram-se 15 plantas em cada propriedade, sendo coletados folhas, frutos, solos e os principais insumos empregados. As concentrações de ETR nas folhas bem como o fator de transferência solo-planta foram semelhantes aos de plantas bioacumuladoras. As folhas assim como as partes do fruto apresentaram depleção de Ce. Na fruta cítrica, a concentração dos ETR apresentou a seguinte distribuição: casca > polpa > sementes = suco. As maiores concentrações de ETR nos insumos foram observadas para os fertilizantes fosfatados. O delineamento experimental utilizado nos dois experimentos em casa-de vegetação foi em blocos ao acaso. Nos experimentos em casa-de-vegetação com superfosfato simples e cloreto de lantânio realizou-se a semeadura de sementes de limão cravo em tubetes de polipropileno. Para o experimento com superfosfato simples, as plantas de limão cravo permaneceram nos tubetes por 6 meses e, a partir desse período, iniciou-se o transplante para sacos plásticos. Os tratamentos constituíram-se de diferentes doses de superfosfato simples (50 g, 100 g, 200 g, 400 g) aplicadas ao substrato. Após 2 meses, coletaram-se as plantas de limão cravo e analisaram-se as folhas e o caule. No experimento com cloreto de lantânio, a aplicação dos tratamentos (50 mg, 100 mg, 200 mg, 400 mg) deuse após 98 dias da semeadura. Três semanas após, coletaram-se as plantas. A planta de citros do estudo pode ser considerada uma bioacumuladora de ETR. Houve discriminação entre os sistemas de produção em 2005, 2006 e 2007 para Eu, Tb, Yb e Sc nos compartimentos solo e folha, com uma concentração significativamente (p<0,05) maior no sistema de produção orgânico. O limão cravo absorve ETR do fertilizante superfosfato simples. A planta de citros teve sua fisiologia alterada com a aplicação de lantânio, isto é, dependendo da dose pode haver um efeito benéfico ou prejudicial no crescimento, sugerindo seu potencial uso como fertilizante na citricultura / The citrus crop requires repeated application of fertilizer to achieve satisfactory levels of productivity. Fertilizers contain other chemical elements in addition to those of interest, such as the rare earth elements (REE). Some studies show that applications of REE may increase plant growth and productivity, but it can also be harmful to both the environment and man. In Brazil, adding REE to fertilizers is not a common practice, however it may be found in the composition of some inputs. The objectives of this study were to quantify the REE in plant, soil and inputs in citrus agroecosystems, to identify the inputs acting as REE sources to the citrus plant, to study the effects of REE in citrus and to evaluate the REE distribution model. The instrumental neutron activation analysis (INAA) and the mass spectrometry with inductively coupled plasma (ICP-MS) were performed to determine the REE. Field and greenhouse experiments were conducted. The field experiment was performed in four citrus properties, with Valencia variety (Citrus sinensis L. Osbeck) grafted onto \'Rangpur\' lime (Citrus limonia Osbeck), two under an organic production system and two under the conventional production system in the region of Borborema, SP. Fifteen plants were sampled in each property and leaves, fruits, soils and the main input used in these properties. REE concentrations in leaves as well as the REE soil-plant transfer factor were similar to those of bioaccumulator plants. Likewise the fruit parts, the leaves showed Ce depletion. The REE concentration in the citrus fruit was distributed as follows: skin > pulp > seeds = juice. The higher concentrations of REE in the inputs were determined for the phosphate fertilizers. The greenhouse experiments with simple superphosphate and lanthanum chloride included the sowing of \'Rangpur\' lime seeds in polypropylene tubes. Both greenhouse experiments had a randomized block design. For the simple superphosphate the \'Rangpur\' lime plants remained in the tubes for 6 months and then were transplanted into plastic bags. The treatments comprised different doses of simple superphosphate (50 g, 100 g, 200 g, 400 g) applied into the substrate. Two months later the \'Rangpur\' lime plants were collected and their leaves and stalk were analyzed. In the experiment with lanthanum chloride heptahydrate the application of the treatments (40 mg, 100 mg, 200 mg, 400 mg) occurred 98 days following sowing. Three weeks following the application of the lanthanum chloride the plants were collected. It can infer that this citrus plant can be considered a REE bioaccumulator. There was discrimination between the production system in 2005, 2006 and 2007 for Eu, Tb, Yb and Sc in the soil and leaves compartments, with a concentration significantly (p <0.05) higher in the organic production system. The \'Rangpur\' lime uptakes REE from the simple superphosphate fertilizer. The citrus plant physiology had changed with the application of lanthanum, ie depending on the dose may be a beneficial or harmful effect on growth, suggesting its potential use as fertilizer in citriculture

京都大学 / 0048 / 新制・課程博士 / 博士(工学) / 甲第22425号 / 工博第4686号 / 新制||工||1731(附属図書館) / 京都大学大学院工学研究科都市社会工学専攻 / (主査)教授 小池 克明, 教授 立川 康人, 准教授 柏谷 公希 / 学位規則第4条第1項該当 / Doctor of Philosophy (Engineering) / Kyoto University / DGAM

The Caledonian alum shales of Sweden host a vast number of economically interesting metals. In Fetsjön, Västerbotten, the shales contain significant amounts of rare-earth elements, vanadium, molybdenum and uranium. As metals with a multitude of high-technological applications, the former rare-earth elements (REEs) are particularly attractive in a world where the supply may be exhausted as the demand continuously increase while new deposits are not being discovered fast enough. Meanwhile, the latter uranium notably constitutes as an unwanted secondary product during the extraction of rare-earth elements. As the mineral association of the REEs in Fetsjön is unknown, the intent of this study is to analyze and thus determine their mineralogical expression. The assumed REE-bearing mineral apatite was confirmed to host the rare-earths in the Fetsjön shales after microscopy and spectrometry analyses.

The lower Mount Rogers Formation (LMRF) is described by Rankin (1993) as a sequence of intercalated metabasalts and volcanogenic sediments with minor metarhyolite. We have chosen to examine the sequence of the LMRF units exposed along Elk Garden Ridge, a high shoulder between the summits of Whitetop Mountain and Mount Rogers in the Mount Rogers National Recreation Area in SW Virginia. This sequence represents an uplifted block of LMRF units enclosed by exposures of Whitetop and Wilburn metarhyolites. In the field, progressive lithologic changes can be observed walking up-section along Elk Garden ridge that are indicative of changes in lava compositions and eruptive environments. From the bottom of the section, massive basalts with distinctive 1-2 cm long swallowtail plagioclase phenocrysts grade into vesicular basalts, then into sheet flow basalts, followed by a thick sequence of aphyric and amygdaloidal pillow basalts. Further up section, eruptive products transition into rhyolitic ignimbrites and ash and lapilli tuffs. Boulders of cobble conglomerates near the middle of the sequence and sedimentary layers in between individual sheet flows suggest short periods of relative eruptive quiescence. The only unit broken out in the LMRF by Rankin (1993), Fees Rhyolite, is not observed in the field area, suggesting local differences in topography, eruptive products and eruptive styles across the outcrop area during the deposition of these eruptive products. Petrographically, the rocks reflect the regional greenschist facies metamorphic conditions with chlorite and epidote as primary metamorphic minerals, and unakite-like zones of mineralization. Relict plagioclase and pyroxene phenocrysts persist, as do primary igneous textures and structures. Compositionally, all of the rocks in the Elk Garden Ridge sequence are strongly enriched in alkali metals, with elevated Na2O and K2O contents, and high TiO2 in the basalts. Major and trace element systematics suggest that the chemical signatures of the metabasalts are primary controlled by shallow-level crystallization processes. The LMRF metabasalts share many compositional affinities with later (~570 Ma) rift-related basalts preserved in the Appalachians, suggesting that all of these lavas were formed by melting of a compositionally uniform mantle source, followed by shallow crystallization, despite being separated from one another by large stretches of time and space.

<p>Rare earth elements (REEs) are 15 elements in the lanthanide series plus scandium and yttrium. They are essential for clean energy, defense, and other high-tech industries. Production of high-purity REEs, however, is limited to a few countries, posing great supply risks. Separation of crude REE mixtures into individual REEs is the most challenging step because of similar physical and chemical properties of the REEs. Conventional REE purification processes are based on solvent extraction methods, which are inefficient, require thousands of separator units, and produce large amounts of waste. Chromatography methods are inherently more efficient than solvent extraction methods because of orders of magnitude higher interfacial area per unit volume. Low-cost chromatography sorbents, however, do not have sufficient selectivity for REE purification. </p><p>In this dissertation, ligand-assisted displacement (LAD) chromatography was developed for the separation and purification of REEs from complex mixtures. A ligand, which is selective for REEs, can be added in the mobile phase or immobilized in the sorbent to achieve REE separation and purification. Constant-pattern design methods and a general zone splitting strategy were developed for producing high-purity REEs with high yields and high productivities from complex mixtures. The new methods were tested for producing three high-value REEs, called the magnets REEs, which are the key ingredients in permanent magnets, neodymium (Nd), praseodymium (Pr), and dysprosium (Dy), from waste magnets, bastnäsite concentrates, and monazite concentrates. </p><p>A two-zone LAD was designed and tested for recovering high-purity <a>neodymium (Nd), praseodymium (Pr), and dysprosium (Dy) </a>from waste magnets. Three-zone LAD was designed to recover high purity Nd and Pr from bastnäsite and monazite concentrates. High purity REEs (>99.5%) were produced with high yields (>99%) and high productivities (>100 kg REEs/m³/day). </p><p>Compared to conventional solvent extraction methods, the LAD methods are inherently safer and greener, since they do not require flammable organic solvents or toxic extractants and generate much less waste. LAD methods require only a few zones with a small number of columns. They have more than 10 times higher productivity, or less than10 time the footprint, than solvent extraction. The LAD methods are also versatile and adaptable to a wide range of product purity requirement, feedstock composition, or production scale. </p><p>The LAD methods have the potential to transform the conventional solvent extraction methods with low efficiency and high environmental impact into more efficient and environmentally friendly chromatography methods. They can enable the production of the magnet REEs domestically and provide a driving force to change the current linear path of the REEs, from ores to permanent magnets, to landfills, into a more sustainable circular REE economy.</p>

Microbes exert extensive control on redox element cycles. They participate directly orindirectly in the concentration and fractionation of elements by influencing the partitioningbetween soluble and insoluble species. Putative microbially mediated manganese (Mn) oxidesof the birnessite-type, enriched in rare earth elements (REE) + yttrium (Y) were recentlyfound in the Ytterby mine, Sweden. A poorly crystalline birnessite-type phyllomanganate isregarded as the predominant initial phase formed during microbial Mn oxidation. Owing to ahigher specific surface area, this biomineral also enhances the known sorption property of Mnoxides with respect to heavy metals (e.g. REE) and therefore has considerable environmentalimpact.The concentration of REE + Y (2±0.5% of total mass, excluding oxygen, carbon and silicon)in the Ytterby Mn oxide deposit is among the highest ever observed in secondary precipitateswith Mn and/or iron. Sequential extraction provides evidence of a mineral structure where theREE+Y are firmly included, even at pH as low as 1.5. Concentration ratios of Mn oxideprecipitates to fracture water indicate a strong preference for the trivalent REE+Y overdivalent and monovalent metals. A culture independent molecular phylogenetic approach wasadopted as a first step to analyze the processes that microbes mediate in this environment andspecifically how the microbial communities interact with the Mn oxides. Plausible players inthe formation of the investigated birnessite-type Mn oxides are mainly found within theferromanganese genera Hyphomicrobium and Pedomicrobium and a newly identified YtterbyBacteroidetes cluster most closely related to the Terrimonas. Data also indicate that thedetected microorganisms are related to the environmental constraints of the site including lowconstant temperature (8°C), absence of light, high metal content and possibly proximity to theformer storage of petroleum products.

No description available.

Froth flotation has long been regarded as the best available technology for ultrafine particles separation. However, froth flotation has extreme deficiencies for recovering ultrafine particles that are less than 30-50 μm in size for coal and 10-20 μm for minerals. Furthermore, dewatering of flotation products is difficult and costly using currently available technologies. Due to these problems, coal and mineral fines are either lost to tailings streams inadvertently or discarded purposely prior to flotation. In light of this, researchers at Virginia Tech have developed a process called hydrophobic-hydrophilic separation (HHS), which is based originally on a concept known as dewatering by displacement (DbD). The process uses non-polar solvents (usually short-chain alkanes) to selectively displace water from particle surfaces and to agglomerate fine coal particles. The resulting agglomerates are subsequently broken (or destabilized) mechanically in the next stage of the process, whereby hydrophobic particles are dispersed in the oil phase and water droplets entrapped within the agglomerates coalesce and exit by gravity along with the hydrophilic particles dispersed in them. In the present work, further laboratory-scale tests have been conducted on various coal samples with the objective of commercial deployment of the HHS process. Test work has also been conducted to explore the possibility of using this process for the recovery of ultrafine minerals such as copper and rare earth minerals. Ultrafine streams produced less than 10% ash and moisture consistently, while coarse coal feed had no observable degradation to the HHS process. Middling coal samples were upgraded to high-value coal products when micronized by grinding. All coal samples performed better with the HHS process than with flotation in terms of separation efficiency. High-grade rare earth mineral concentrates were produced with the HHS process ranging from 600-2100 ppm of total rare earth elements, depending on the method and reagent. Additionally, the HHS process produced copper concentrates assaying greater than 30% Cu for both artificial and real feed samples, as well as, between 10-20% Cu for waste samples, which all performed better than flotation. / Master of Science / Froth flotation has long been regarded as the best available technology for separating fine particles. Due to limitations in particle size with froth flotation, and high downstream dewatering costs, a new process has been developed called the hydrophobic-hydrophilic separation (HHS) process. This process was originally based on a concept known as dewatering by displacement (DbD) which was developed by researchers at Virginia Tech in 1995. The process uses hydrocarbon oils, like pentane or heptane, to selectively collect hydrophobic particles, such as coal, for which it was originally developed. In coal preparation plants, a common practice is to purposefully discard the ultrafine stream that flotation cannot recover and has an increased dewatering cost. The HHS process can effectively recovery this waste stream and produce highgrade salable product, with significantly reduced cost of dewatering. In the work presented, laboratory-scale tests have been conducted on various coal samples with the objective of commercial deployment of the HHS process. In this respect, several varying plant streams have been tested apart from the traditional discard stream. Additionally, test work has expanded into mineral commodities such as copper and rare earth minerals. In this work, salable high-value coal products were achievable with the HHS process. Ultrafine streams consistently produced less than 10% ash and moisture. Coarse coal feeds had no observable degradation to the HHS process and were able to produce single digit ash and moisture values. Middling coal samples were upgraded to high-value coal products when micronized by grinding. All coal samples performed better with the HHS process than with flotation in terms of separation efficiency. High-grade rare earth mineral concentrates were produced with the HHS process ranging from 600- 2100 ppm of total rare earth elements depending on the method and reagent. Additionally, the HHS process produced copper concentrates assaying greater than 30% Cu for an artificial and feed samples, as well as, between 10-20% Cu for waste samples, which all performed better than flotation.