Made available in DSpace on 2014-10-09T12:35:55Z (GMT). No. of bitstreams: 0 / Made available in DSpace on 2014-10-09T14:03:25Z (GMT). No. of bitstreams: 0 / O fosfogesso, também denominado gesso agrícola, sub produto das industrias de fertilizantes fosfatados, pode ser utilizado como condicionador do solo devido a sua capacidade de proporcionar melhorias ao sistema solo-planta. No entanto, este resíduo concentra os radionuclídeos das séries do U e Th, presentes na rocha fosfatada usada como matéria prima, que podem impactar o meio ambiente. Com a finalidade de se verificar a concentração dos radionuclídeos biodisponíveis , foram analisadas amostras de fosfogesso e de fertilizantes fosfatados monoamônio fosfato e fertilizante superfosfato triplo, de duas procedências nacionais. A determinação da concentração de 226Ra, 228Ra e 210Pb se iniciou com a análise por espectrometria gama. Em seguida as amostras foram submetidas a um processo de extração branda com solução de EDTA-NH4 (0,05M) para que então o material lixiviado fosse analisado por meio de contagem alfa e beta total em detector proporcional de fluxo gasoso. Foram obtidos valores médios de extração de 1,6% - 1,7% para 210Pb, 0,5% - 1,4% para o 226Ra e 0,1% - 1,0% para o 228Ra nas amostras de fosfogesso. A baixa porcentagem de extração obtida para os radionuclídeos pode ser explicada tendo-se em vista que a solubilidade do fosfogesso variou de 7,7% a 16%. Para os fertilizantes fosfatados do tipo monoamônio fosfato os valores médios de extração foram inferiores a 26% para o 226Ra, inferiores a 10% para o 228Ra e inferiores a 10% para o 210Pb. Apesar da solubilidade da ordem de 77% dos fertilizantes fosfatados do tipo monoamônio fosfato, muito pouco dos radionuclídeos, presentes inicialmente, se concentraram na solução extraida. Para os fertilizantes fosfatados do tipo superfosfato triplo os valores médios de extração foram de 2,3% para o 226Ra, 1,2% para o 228Ra e 11,3% para o 210Pb. Mesmo com a solubilidade de 66% os fertilizantes fosfatados do tipo superfosfato triplo, muito pouco dos radionuclídeos, presentes inicialmente, se concentraram na solução extraida. / Dissertação (Mestrado) / IPEN/D / Instituto de Pesquisas Energeticas e Nucleares - IPEN-CNEN/SP

La compréhension des processus de recharge et de l’hydrodynamique des systèmes aquifères karstiques est indispensable pour estimer la vulnérabilité et la disponibilité des réserves en eau souterraine. Afin d’améliorer cette compréhension, de nombreuses études ont utilisé l’information issue du comportement de plusieurs éléments chimiques et des isotopes naturels dans les eaux souterraines. Parmi eux, les quatre isotopes du radium (223Ra, 224Ra, 226Ra et 228Ra) et le radon (222Rn), tous radioactifs, sont de plus en plus utilisés. Ces traceurs naturels permettent d’identifier l’origine des différentes masses d’eau et leurs processus de transport et de mélange dans plusieurs types de systèmes aquifères. Cependant, leur application aux systèmes karstiques est principalement développée dans les systèmes côtiers ou thermaux, dont les eaux sont souvent riches en Ra. Très peu de travaux ont été menés dans les aquifères karstiques continentaux, probablement en raison de la faible activité de ces radionucléides, qui les rend difficiles à quantifier et nécessitant le prélèvement de plusieurs litres d’eau. La première partie de ce travail a donc consisté au développement d’un nouveau dispositif de prélèvement capable de concentrer in-situ le radium contenu dans plusieurs dizaines de litres d’eau (20-300 L) à l’aide de de fibre acrylique imprégnée de MnO2 et d’améliorer la mesure des activités par spectrométrie gamma. Grâce à cette méthode, nous avons été capables de mesurer, pour la première fois, les faibles activités des quatre isotopes de Ra (0,4 à < 7,0 mBq/L pour 226Ra, 228Ra et 224Ra et de 0,05 à 0,3 mBq/L pour 223Ra) dans les eaux de deux hydrosystèmes karstiques continentaux Méditerranéens, les systèmes du Haut Vidourle et du Lez (Sud de la France). La méthode de quantification de 222Rn a également été optimisée. L’étude du comportement des isotopes de Ra et de Rn dans la zone d’étude a mis en évidence les diverses applications avérées ou potentielles de la mesure de ces radionucléides dans les aquifères karstiques. En général, les valeurs des activités de 226Ra et du rapport (228Ra/226Ra) des eaux sont cohérentes avec le type de lithologie dans lesquelles elles circulent ou sont stockées. Nous avons pu ainsi mieux préciser l’influence des eaux du Vidourle à la recharge allogénique de l’aquifère de Sauve. Nous avons montré que parfois, les activités des isotopes de Ra correspondent plutôt à des valeurs typiques des différents compartiments aquifères qu’à celles de la roche encaissante. Ces résultats nous ont permis de déterminer les proportions de mélange des trois différents pôles géochimiques composant le flux d’eau qui s’écoule à la source du Lez suivant les conditions hydrodynamiques. Les isotopes à longue période (226Ra et 228Ra) combinés aux isotopes à courte période (224Ra et 223Ra), permettent potentiellement de déterminer, en même temps, les taux de mélange et le temps de transfert des eaux. De plus, l’excès des isotopes à courte période traduirait l’arrivée d’eaux souterraines en surface, 223Ra et 224Ra devenant de meilleurs traceurs des échanges superficiels que Rn car ils ne subissent pas de processus de dégazage vers l’atmosphère. Par contre, l’étude de l’évolution temporelle du radon à la source du Lez a mis en évidence que ce gaz radioactif naturel est un très bon traceur des processus de recharge diffuse des aquifères karstiques. Les relations entre 223Ra et 222Rn, ainsi qu’entre 210Pb et 222Rn, peuvent fournir des informations sur le temps de transfert des eaux souterraines. Cependant, des études complémentaires et à plus long terme sont nécessaires. / Understanding recharge processes and hydrodynamics of karstic systems is an essential rule to assess their vulnerability and their groundwater resource availability. Numerous studies use the behavior of natural geochemical elements and isotopes in groundwaters to improve this understanding. The radium quartet (223Ra, 224Ra, 226Ra and 228Ra) and the radon (222Rn), natural radioactive elements, have been commonly applied for studies devoted to the identification of water mass origins and to their mixing and transfer processes in different type of aquifers. Nevertheless, the applications to karstic systems are mainly concerned to coastal and thermal systems, because of their uncommon Ra enrichment. Just a few works have been undertaken in continental karstic aquifers, probably because of these radionuclide low activities in such environments. This statement makes their quantification not easy and requires large water sampling. The first part of our research work has been devoted to the development of a new sampling system able to pre-concentrate in situ the radium present in several tens of liters of water (20-300 L) with MnO2-fibers and to improve the determination of Ra quartet activities by means of gamma spectrometry. This method gave us the ability of measuring, for the first time, the very low activities of the four radium isotopes (0.4 to < 7.0 mBq/L for 226Ra, 228Ra et 224Ra and from 0.05 to 0.3 mBq/L for 223Ra) in the waters of two Mediterranean karstic hydrosystems, the Haut Vidourle and the Lez systems (both located in South of France). The radon measuring method has also been optimized and improved. The study of the Ra isotope and Rn behavior over the survey area put in evidence the multiple applications of measuring these radionuclides in karstic aquifers. 226Ra activities and (228Ra/ 226Ra) ratios in water are in agreement with the existing lithologies into which the waters flow or are stored. The effective participation of Vidourle river water to the allogenic recharge of the Sauve aquifer has been specified. We showed that sometimes, the Ra isotope activities correspond to characteristic values of the aquifer compartments instead of the bedrock. These data also allow us to estimate the mixing proportions of the three geochemical endmembers composing the waters flowing at the Lez karstic spring in relation with hydrodynamic conditions. Coupling the long-lived radium isotopes (226Ra and 228Ra) together with the short life isotopes (223Ra and 224Ra) potentially led us, at the same time, to determine the mixing rates and the transfer time of the groundwaters. Moreover, the short life isotope excess would express groundwater venues at surface, 223Ra and 224Ra becoming more reliable tracers of superficial exchanges than radon because insensitive to degassing processes towards the atmosphere. On the other end, the study of the radon time evolution at the Lez spring confirmed that this natural radioactive gas is a good tracer of the diffuse recharge processes of karstic aquifers. The relations between 223Ra and 222Rn as well as between 210Pb and 222Rn, could give access to the transfer time of groundwater. However, more exhaustive researches are needed.

Comparer de manière approfondie la réponse des différents outils isotopiques choisis (Li, B et U) durant l’altération chimique dans un profil déjà connu (e.g. le profil du Sommet sur le Bassin versant du Strengbach ; Ackerer, 2017) afin de dégager les mécanismes moteurs des fractionnements isotopiques de chacun de ces éléments pour faire le lien entre la réponse de ces outils lors de l’altération chimique et remonter ainsi au régime d’altération des roches. Développer les observations réalisées sur le profil du Sommet et les appliquer sur cinq autres profils d’altération répartis sur l’ensemble du bassin versant en se concentrant sur la fraction <2µm. Cela permettra de voir si les observations faites dans le premier profil se retrouvent dans les autres profils et si nous sommes capables de remonter au régime d’altération. Étudier de manière préliminaire comment évolue le signal isotopique de l’altération chimique acquis dans les profils d’altération au cours du transport sédimentaire et s’il est possible de déterminer le régime d’altération d’un bassin versant à partir des sédiments de ce même bassin. / In-depth comparison of the response of various selected isotopic tools (Li, B and U) during chemical weathering in an already known profile (eg the Summit profile in the Strengbach watershed, Ackerer, 2017) to identify the driving mechanisms of isotopic fractionations of these elements to link the response of these tools compared to the chemical alteration to go back to the alteration regime. Develop the observations made on the Summit profile and apply them to five other weathering profiles distributed over the entire watershed focusing on the <2μm fraction. This will make it possible to see if the observations made in the first profile are found in the other profiles and if we are able to go back to the alteration regime. Preliminarily investigate how the isotopic signal of chemical alteration acquired in alteration profiles evolves during the sediment transportation and if it is possible to determine the alteration regime of a watershed from it sediments.

Zielsetzung der Arbeit war vorrangig die Entwicklung bzw. Weiterentwicklung von Methoden zur verbesserten Interpretation der hydraulischen Gegebenheiten in einem Grundwasserleiter mit Hilfe der Bestimmung von Radiumisotopenverhältnissen im Verlauf von Pumpversuchen. Daneben wurden 222Rn/226Ra-Verhältnisse betrachtet und interpretiert. Des Weiteren wurden Gesteinsuntersuchungen durchgeführt sowie Untersuchungen an Gesteinsoberflächen (Sekundärminerale) um Aussagen über das Löslichkeitsverhalten bzw. die Mobilität von Radium im Grundwasser zu erhalten. Die Grundwasser- und Gesteinsproben stammten vor allem aus dem Umfeld der kontinentalen Tiefbohrung (KTB Oberpfalz) sowie aus der Vorbohrung zur KTB, aber auch aus benachbarten Bundesländern und der Tschechischen Republik (Egergraben). Im Ergebnis zeigte sich, dass sich die Untersuchung der Isotopenverhältnisse zur vertiefenden Aquiferdiagnose gut eignet. Die geochemischen Untersuchungen erlaubten einen Einblick in das Löslichkeitsverhalten der untersuchten Radionuklide.

Summary: This thesis is focused on mapping of contaminants released into the environment probably due to uranium mining. These chemical contaminants are used to reconstruct the sedimentary processes. In the thesis we evaluate geochemical situation in the catchment area in the locality Borecek (part of the municipality Ralsko) using the overbank sediments as sedimentary archives of pollution during the last decades by elements U, Ba, Zn, Ni and 226 Ra. A map of aerial survey of gamma activity was used to select the area of interest, for more accurate localisation we used a surface gamma spectrometry. On Borecek we retrieved ten depth profiles of alluvial sediments (up to 230 cm) and one in Mimon, all samples were subjected to X-ray fluorescence spectral analysis (XRF), across the floodplain we performed gamma wire logs. For interpretations of floodplains architecture electrical resistivity tomography (ERT) was used and selected profiles were analysed for the activity of 226 Ra and 210 Pb. Interrelation of 226 Ra and Ba proved that radiobarite is the main source of the gamma activity. 210 Pb / 226 Ra ratio was used as sediment age indicator. With enrichment factor (LEF), we performed chemostratigraphic correlation of the sediments, for that the concentration of the target elements is corrected for varying...

Summary: This thesis is focused on mapping of contaminants released into the environment probably due to uranium mining. These chemical contaminants are used to reconstruct the sedimentary processes. The aim of the thesis was both the geochemical assessment of the situation in the catchment area of the Ploucnice River in Boreček using the flood sediments from the research points as sedimentary archives pollution for last decades. With depth profiles, gamma wire log, XRF and enrichment factors (LEF), we have tried to perform chemostratigraphic correlation of the sediments. As target elements U, Ba, Zn and Ni were chosen, whose concentrations are related to the grain size of the sediment. Furthermore, the theory of secondary pollution is developed.

As unconventional drilling has emerged as a major industry in the US and around the world, many environmental health and pollution risks have surfaced. One emerging concern is the risk of environmental contamination arising from unconventional wastes that are enriched in naturally-occurring radioactive materials (NORM). Although NORM has been a well-documented contaminant of oil and gas wastes for decades, there are new challenges associated with unconventional drilling. This thesis discusses several of these challenges, focusing on NORM from black shale formations. Chapter 1 provides background information on environmental radioactivity and unconventional drilling. Chapter 2 describes the potential for NORM to migrate into groundwater around unconventional drilling operations. Chapters 3 and 4 describe radiochemical methods developed for the analysis of Marcellus Shale unconventional drilling wastes. Chapter 5 describes environmental partitioning of Marcellus Shale unconventional drilling wastes. Collectively, this thesis attempts to broaden the scientific understanding of NORM in unconventional drilling wastes so that potential environmental impacts may be mitigated.

Informe de Seminario para optar al grado de Licenciado en Historia

<p>Prior studies of groundwater systems have associated increasing salinity and anoxic conditions with increasing radium (Ra) activities in water due to the decreasing effectiveness of Ra removal processes. However, the components of salinity (e.g. Ca vs. Na and SO₄^2- vs. Cl^--dominated waters), and the relative importance of salinity-sensitive vs. redox-sensitive processes for Ra mobilization, are less well understood. In this research, the response of Ra to hydrochemical change was examined using a multiple tracer approach to obtain detailed information on divalent cation and Ra mobility. A range of salinity and redox conditions was examined in five field-based studies in the United States and Morocco: (1) fresh waters in fractured crystalline rocks in the Piedmont region of North Carolina; (2) the Willcox Basin, an oxic alluvial basin-fill aquifer in southeastern Arizona; (3) the Jordan sandstone aquifer, a carbonate-cemented quartz sandstone in southeastern Minnesota; (4) an unconfined coastal aquifer undergoing salinization in the city of Agadir, Morocco; and (5) the confined, fresh to saline Cretaceous and Pliocene aquifers of the Atlantic Coastal Plain in North Carolina.</p><p> </p><p>In addition to analysis of major element concentrations, trace metal concentrations, and ²²⁴Ra, ²²⁶Ra, and ²²⁸Ra activities, complementary isotope systems were applied to gain insights on the relative stability of chemical processes that remove radium and other alkaline earth metals: (1) strontium isotope ratios (⁸⁷Sr/⁸⁶Sr) trace divalent cation release from sources such as clay and carbonate minerals in the aquifer solids and also indicate conditions in which divalent cation release (rather than uptake) is dominant; (2) boron concentrations and isotopes (&delta;¹¹B) coincide with the opposite condition in freshening conditions of the Atlantic Coastal Plain, in which divalent cations are removed in exchange for Na; and (3) sulfur and oxygen isotopes (&delta;³⁴S, &delta;¹⁸O) of sulfate trace sulfate sources and provide information on sulfate-reducing conditions, which can inhibit barite (BaSO₄) from removing Ra by coprecipitation. In addition, other isotopic and ion measurements trace salinity sources and groundwater residence time, including &delta;²H, &delta;¹⁸O, ³H, Br^-/Cl^-, Na/Cl^-, and Ca/Na.</p><p>This dissertation documents correlations between salinity and radium in the brackish to saline North Carolina coastal plain aquifer with total dissolved solids (TDS) up to ~18,000 mg L^-1 and to some degree in the Moroccan coastal aquifer, but even the lower-salinity waters (TDS <3000 mg L^-1) exhibit a range of Ra activities spanning approximately 3 orders of magnitude. Among these low-TDS waters, the highest Ra activities were observed in the anoxic Jordan sandstone aquifer and the lowest were observed in the oxic Willcox Basin aquifer. Although the main control on radium activities in fresh groundwater is the U- and Th-series radionuclide content of the aquifer solids, important secondary controls include the stability of redox-sensitive radium adsorption sites (Mn and Fe oxides), the relative dominance of divalent vs. monovalent cations (e.g. the Ca/Na ratio), formation of the uncharged RaSO₄⁰ complex, and/or the saturation state with respect to barite. These processes interact in varied ways in the field-based studies. Increasing radium activities and decreasing ²²²Rn/²²⁶Ra ratios in the North Carolina fractured crystalline rock groundwater system are correlated with increasing Ba, Mn, and Fe concentrations and decreasing dissolved oxygen concentrations, related to weathering and/or organic carbon oxidation. Radium activities in the oxic, neutral to slightly basic Willcox Basin are very low (median ²²⁶Ra activity 2 mBq L^-1), probably due to a combination of effective Ra removal processes including adsorption to Mn and/or Fe oxides and the overall removal of divalent cations during groundwater evolution in this system. These are the same surface charge conditions that release arsenic, of regional water concern, in this pH range. Radium in Jordan aquifer groundwater is dependent on local variations in solid-phase radionuclide levels, probably hosted in the carbonate cement phase. Also, Ra is inefficiently adsorbed to the aquifer solids in the aquifer's anoxic conditions, resulting in the highest radium levels reported in this dissertation (²²⁶Ra up to 420 mBq L^-1) despite apparent barite precipitation that partially removes Ra. Radium-224 activity in the Moroccan coastal aquifer is associated with salinity, but Ra overall is apparently controlled by barite, indicated by conditions near BaSO₄ saturation. Radium activity in the saline waters of the Atlantic Coastal Plain aquifers is associated with TDS concentrations, but the cation exchange properties of the aquifer may provide a major mechanism of Ra removal in the Na-HCO₃^- and Na-Cl^- waters. Overall, the complex interaction between groundwater chemistry and Ra-removing processes implies that in waters with TDS below approximately 3,000 mg L^-1, dissolved solids concentration alone does not fully describe radium's response to hydrochemical conditions, but rather that aquifer-specific examination of Ra removal mechanisms is needed.</p> / Dissertation

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