Les activités anthropiques entraînent une contamination des sédiments de rivière en de nombreux polluants et en particulier en éléments traces métalliques (ETM). Si la majorité des ETM se retrouvent piégés dans les sédiments, ceux-ci peuvent être remobilisés et passer en solution dans certaines conditions physico-chimiques et sous l’action des microorganismes autochtones. Les métaux relargués peuvent alors constituer un danger potentiel pour les organismes vivants dans les sédiments et dans la colonne d'eau. Dans le cas des sols, l’impact de l’activité microbienne autochtone sur la mobilité des ETM a souvent été rapporté. Cependant une telle activité de solubilisation n’a été que rarement étudiée dans le cas des sédiments. Une telle connaissance est pourtant importante pour la prédiction du comportement des métaux contenus dans les sédiments et la gestion de ces derniers, notamment lors de leur stockage suite aux opérations de dragage. Dans ce contexte, l’objectif de cette thèse a été de comprendre et d’évaluer l’importance de certains des processus microbiens et chimiques de mobilité des ETM dans les sédiments en conditions anaérobies. La première phase de notre étude qui a consisté à incuber des sédiments de Seine et de Marne en milieu anaérobie dopé en glucose avait pour objectif d’étudier la corrélation entre le métabolisme microbien et le comportement des métaux en solution et dans les sédiments. Dans ces conditions opératoires, une forte solubilisation du fer et du manganèse (sous forme réduite) associée à une solubilisation de métaux traces (Co, Cu, Ni) a été mise en évidence, ce qui a laissé supposer l’intervention de bactéries ferri-réductrices dans les phénomènes observés. Une activité fermentaire importante a été observée et caractérisée par la production d’acides organiques majoritaires tels que les acides acétique et butyrique. Un tel résultat souligne l’importance des bactéries fermentatrices dans les phénomènes de dissolution observés. La deuxième étape de ce travail a consisté à confirmer l’importance de l’activité ferri-réductrice et à en identifier les acteurs principaux. Les analyses moléculaires menées ont montré que les bactéries ferri-réductrices majoritairement identifiées, appartiennent aux espèces Clostridium butyricum et Paenibacillus polymyxa. L’utilisation d’un modèle géochimique nous a permis de montrer que les voies métaboliques supportant la réduction du fer et la mobilité des métaux étaient les fermentations butyrique et acétique. La troisième étape a consisté à comparer les impacts directs (réduction enzymatique) et indirects (propriétés des acides organiques produits) de Paenibacillus polymyxa et Clostridium butyricum sur la mobilité du fer, du manganèse et des autres métaux. Une telle étude a montré que les acides organiques produits (acétique, lactique, succinique, propionique et butyrique) ont un très faible impact sur la solubilisation aux pH rencontrés dans les sédiments et que la réduction enzymatique microbienne est le principal mécanisme de dissolution des éléments métalliques en milieu anaérobie / Antropic activities lead to the metallic contamination of river sediments. Most of trace metals are sorbed on sediments but a part of them can be released into aquatic environment when environmental conditions are modified. This is often due by the autochthonous microbial activity. Microbial activites and their consequences on the mobility of metals have been widely studied in soils. Metals are released through direct or indirect microbial mechanisms. Such studies in the case of sediments are very seldom. However, it can be usefull to understand the microbial mechanisms of metal release in sediments, and particularly for a good management of dredged sediments. In this environmental framework, the aim of this research work was to understand and to evaluate the role of the microbial and chemical mechanisms in the release of metals from river sediments in anaerobic conditions. Firstly, sediments from the Marne and Seine rivers were incubated in anaerobic conditions. A high solubilisation of iron and manganese occurred associated to the solubilisation of trace metals (Co, Cu, Ni, Pb). Meanwhile, organic acids were produced and the medium was acidified. Thus fermentation was supposed to be the main process of microbial metabolism. Furthermore these observations led us to suppose the presence of iron-reducing bacteria. In a second step, the extent of the iron-reducing activity was studied. The main iron-reducing bacteria identified in the Marne sediments belonged to the species Clostridium butyricum and Paenibacillus polymyxa. The use of a geochemical model revealed that fermentation and reduction of iron(III) were the main metabolic pathways. Finally direct (enzymatic reduction) and indirect (complexation with organic acids, acidification) impacts of iron-reducing bacteria on the release of metals were compared. Acidification and organic acids had a weak impact on metal solubility in the range of studied pH (between 6,5 and 5). Enzymatic reduction is the main mechanisms of metal release in anaerobic conditions. Indeed the metallic concentrations can be 40 times higher in the presence of iron-reducing bacteria

Stream chemistry changes in response to snowmelt, but does not typically reflect thechemistry of the snowpack. This suggests that flow processes between snowmelt and streamsystem, such as interactions with the soil and bedrock, have an important control on waterchemistry and highlight the complex flow pathways from the snowpack to stream. To investigateflow processes in the upper Provo River watershed, northern Utah, we sampled three sites on theriver ~20 times per year during 2016 and 2017. The sites, from highest elevations to lowest wereSoapstone, Woodland, and Hailstone, corresponding to locations of active stream gauges. Toidentify possible water sources to the stream during snowmelt, water samples were taken forsnow, ephemeral streams, soil water, lake, and spring water. To investigate potential impacts ofmineralogy, samples were taken for dust, soil and bedrock. The upper Provo River showeddistinct temporal variation in filtered (<0.45 microns) stream water for 87Sr/86Sr, dissolvedorganic carbon (DOC), silica (Si), and Lead (Pb) during the snowmelt season. The watershed hasdistinct 87Sr/86Sr ratios for bedrock (0.7449)

Amostras de água de chuva foram coletadas no campus da USP Ribeirão Preto (RP) de agosto de 2002 a dezembro de 2005. Cerca de 84% (n=127) das amostras apresentaram excesso de acidez, com pH médio de 5,12. Não se observou sazonalidade no pH de acordo com o período de safra da cana. As concentrações médias ponderadas pelo volume (MPV, em mol L-1): K+ 3,9 (n=175), Na+ 2,1 (n=172), Ca2+ 5,0 (n=175) e Mg2+ 1,8 (n=168), observadas em RP, bem como seus fluxos de deposição por via úmida, foram ligeiramente mais elevadas que aquelas encontradas em chuvas de regiões com características semelhantes. As concentrações destes cátions foram sazonais, com um aumento no período de safra, sendo que a maior diferença foi observada para o íon K+, indicando a sua importante fonte na queima de biomassa. A sazonalidade do íon Ca2+ aponta para a importância das atividades agrícolas, intensificadas no período de safra, na emissão deste cátion para a atmosfera. Observaram-se boas correlações lineares entre as concentrações de Na+ e K+ (0,67626) e de Na+ e Ca2+ (0,77822), indicando a possibilidade de emissões pirogênicas e a ressuspensão do solo serem fontes de emissão de Na+. A MPV de carbono orgânico dissolvido (COD) encontrada em RP foi mais elevada que na Amazônia, onde também há intensa queima de biomassa, porém seus fluxos por via úmida em ambas as regiões foram similares (0,42 molCm-2ano-1). As concentrações de COD em RP apresentaram correlações lineares significativas com K+ (0,70341) e com Ca2+ (0,61638), apontando para a queima de biomassa e ressuspensão do solo como fontes importantes de emissão de carbono orgânico para a atmosfera. As concentrações de COD nas chuvas de Araraquara foram ainda maiores que em RP, indicando pronunciadas fontes locais naquela cidade. As MPV (nmol L-1) de Cd 0,54 (n=56), Pb 3,02 (n=94) e Cu, 19,9 (n=98), encontradas nas chuvas de RP foram semelhantes a regiões urbanas e industriais do hemisfério norte, enquanto a concentração de Al (448 nmol L-1, n=126) foi menor, e a de Zn (405 nmol L-1, n=120) apresentou-se dentro das faixas de concentrações relatadas nestes locais. Com exceção de Cd, os demais metais analisados (Pb, Cu, Zn e Al) também apresentaram concentrações significativamente maiores (P=0,05) nas chuvas durante o período de safra, indicando que a queima de biomassa e as atividades agrícolas podem aumentar a emissão destes metais para a atmosfera de RP. A correlação linear significativa entre Pb e Ca2+ (0,53845), indica a participação da ressuspensão do solo no aporte atmosférico de Pb em RP, enquanto a ausência de correlação linear entre Zn e K+ (0,20182) parece indicar a presença de outras fontes significativas de Zn para a atmosfera de RP, além da queima de biomassa. O cálculo do fator de enriquecimento demonstra que Cd, Zn, Pb e Cu estão enriquecidos com relação ao solo na chuva de RP, sugerindo que estes podem ter fontes antrópicas locais e / ou distantes. A análise preliminar de componentes principais não esclareceu o peso das diferentes fontes de emissão atribuídas neste trabalho. / Rain water samples were collected based on events at the University of São Paulo - campus Ribeirão Preto - from August 2002 to December 2005. About 84% (n=127) of the samples had excess of acidity, with an average pH of 5.12. There was no correlation between the pH values and the sugar cane harvest period. The Volume Weighed Means (VWM, in mol L-1) for K+ 3.9 (n=175), Na+ 2.1 (n=172), Ca2+ 5.0 (n=175) and Mg2+ 1.8 (n=168), and their wet fluxes in RP were slightly higher than those reported to regions with similar characteristics. The concentrations for these cations were seasonal, with higher values during the harvest period. The largest difference was observed for K+, indicating its important source in the biomass burning activity. The seasonality showed for Ca2+ is probably related to the higher soil resuspension during the more intense agricultural activities. A good linear correlation observed between Na+ and K+ (0.67626) and between Na+ and Ca2+ (0.77822), suggest that Na+ may have important pirogenic as well as soil dust sources. The VWM for Dissolved Organic Carbon (DOC) in RP was higher than that reported for rainwater in the Amazon region (where the biomass burning is also intense); however, the wet fluxes from both sites were very similar (0.42 mol C m-2 ano-1). DOC concentrations were well correlated with K+ (0.70341) and Ca2+ (0.61638), suggesting that the biomass burning as well as soil dust can be important sources of organic carbon to the atmosphere. DOC concentrations in rainwater from Araraquara were even higher than those for RP, showing a high local source of organic carbon. The VWM (nmol L-1) for Cd 0.54 (n=56), Pb 3.02 (n=94) and Cu 19.9 (n=98) found in the rainwater from RP were similar to urban and industrialized regions of the Northern Hemisphere, while for Al (448 nmol L-1, n=126) it was lower, and for Zn (405 nmol L-1, n=120) the VWM was within the range reported for such areas. Except for Cd, all the other metals measured (Pb, Cu, Zn and Al) also showed higher concentrations (P=0.05) in rainwater samples during the harvest period, suggesting that biomass burning and intensive agricultural activities can increase these species concentrations in the atmosphere. The significant linear correlation between Pb and Ca2+ (0.53845) indicates that soil inputs can be of relevance for Pb atmospheric inputs in RP. On the other hand, the absence of linear correlation between Zn and K+ (0.20182) seems to indicate the presence of other important sources for Zn to the atmosphere besides biomass burning. The calculated Enrichment Factor showed that Cd, Zn, Pb and Cu are anomalously enriched in RP rainwater in relation to soil, suggesting these metals may have antroprogenic local sources as well as distant ones. The preliminary statistical analysis of principal components did not clarify the weight of the different sources of emission attributed in this work.

Les zones côtières du monde entier sont sous fort pression de contamination anthropique comme conséquence de la concentration de la plupart de la population mondiale et des activités économiques le long des côtes et des estuaires. La menace de contaminant sur les écosystèmes rend primordial le développement d'outils capable de détecter les modifications biogéochimiques en vue d'aider dans la prévention, la gestion, et la prédiction de risques dans les études environnementales. Dans ce but, cette thèse étudie la biogéochimie des isotopes du Zinc (Zn) en vue de développer un outil capable de tracer les sources naturelles et anthropiques, d'identifier les processus biogéochimiques et de permettre à la biosurveillance de la contamination par les métaux dans les zones côtières et les mangroves. A cette fin, les compositions isotopiques du Zn ont été déterminées à plusieurs échantillons naturels prélevés dans la baie de Sepetiba (au sud-est du Brésil), un estuaire lagunaire affecté par une côte industrialisée située près de Rio de Janeiro. Cette baie constitue un laboratoire naturel idéal pour valider le système isotopique du Zn. En effet, cette zone héberge des écosystèmes d'intérêt commercial et écologique -estuaire, mangrove, estran- menacés par la contamination d'une ancienne activité de galvanoplastie, et d'autres sources diffuses. Les échantillons collectés comprennent des carottes de sédiments, des sédiments de la superficie des mangroves, des matériaux particulaires en suspension (SPM), des feuilles provenant d'arbres de mangrove, des tissus de mollusques bivalves (huîtres et moules) et des roches. Minéraux de dépôt de Vazante (Brésil) ont été collecté pour representé matière première utilisée par l'industrie de la galvanoplastie. Tout d'abord, un travail initial de laboratoire a établi une méthode exacte et précise pour les déterminations isotopiques Zn en échantillons naturelles par spectrométrie de masse avec plasma couplé par induction et multicollecteur (MC-ICP-MS). Des analyses spatiales et temporelles des compositions isotopiques du Zn des échantillons de sédiments et de roches s'ajustent bien à un modèle de mélange entre trois principales extrémités : i) les matériaux continentaux charriés par les rivières ; ii) les sources marines ; et iii) une source anthropique majeure associée aux anciens déchets de galvanoplastie jetés dans la baie. Les carottes de sédiment collectées dans la vasière ont montré une haute corrélation entre la composition isotopique du Zn et le facteur d'enrichissement du Zn. Ceci suggère : i) une bonne préservation du registre isotopique des sources naturelle et anthropique, ii) l'absence de fractionnement isotopique significatif durant le transport de sédiments ou durant les réactions diagénétiques pos-dépositions dans le système estuarien. / Coastal areas worldwide are under strong pressure from anthropogenic contamination, as most of the global population and of economic activities are concentrated along the coasts and estuaries. The threaten of contaminant releasing into these ecosystems makes imperative the development of tools capable of detecting biogeochemical changes in order to help prevention, monitoring and prediction of risks in environmental studies. In this way, this thesis investigates the isotope biogeochemistry of Zinc (Zn) in order to develop a tool capable of tracing natural and anthropogenic sources, identifying biogeochemical processes and enabling the biomonitoring of metal contamination in coastal areas and mangroves. To this end, Zn isotopes compositions were determined in several natural samples collected from Sepetiba bay (southeastern Brazil), an estuarine-lagoon impacted by an industrialized coastal area near Rio de Janeiro. This bay constitutes an ideal natural laboratory for evaluating the Zn isotopic system to environmental issues, since it hosts important ecosystems of commercial and ecological interest - estuaries, mangroves and tidal flats - threaten by the metal contamination resultant of old electroplating activity and other anthropogenic diffuse sources. The collected samples include sediment cores, surface mangrove sediments, suspended particulate matter (SPM), leaves of mangrove's trees, tissues of bivalve mollusks (oysters and mussels) and rocks. Ores from Vazante deposit, Brazil were collected to represent the raw material used in the old electroplating industry. Firstly, an initial laboratory work established a method for accurate and precise determinations of Zn isotope compositions in natural samples by multi-collector inductively coupled plasma-mass spectrometry (MC-ICP-MS). Spatial and temporal analysis of Zn isotope compositions of sediment and rock samples fits well in a model of mixing between three main end-members: i) continental materials brought via rivers; ii) marine sources; and iii) a major anthropogenic source associated to the old electroplating wastes released into the bay. Sediment cores collected in the mud flat showed high correlation between Zn isotope compositions and Zn enrichment factors, suggesting (i) good preservation of isotopic records of natural and anthropogenic sources and (ii) no significant isotopic fractionation during sediment transport or as a result of diagenetic reactions post-deposition in the estuarine system. The sediment core sampled from a mangrove located in the zone impacted by the old electroplating activity presented levels of Zn up to 4% (dry weight) and preserved the isotopic signatures of electroplating wastes. However, there is evidence that biogeochemical processes triggered by hydrodynamics, bioturbation or rhizosphere processes slightly changed the isotopic signatures in some layers. Calculations based in this mixing model quantified contributions of the major anthropogenic source of Zn, ranging from negligible values in the pre-industrial period to nearly 80% during periods of electroplating activities between the 60's and 90's.

The purpose of this project is to develop a framework for quantifying and differentiating the effects of early historic land uses on characteristics of soils formed in loess at two historical archaeology sites in the Midwestern United States: New Philadelphia Historical Landmark (NPHL) in western Illinois and Plum Grove Historical Farmstead (PGHF) in eastern Iowa. The significance of this research to topics such as global climate change, the role of soils in the carbon and nitrogen cycles, the effects of land use on sustainable use of soils, and augmenting the historical record by revealing land use activities for areas that have limited record of past land use are presented in the Introduction. The Introduction also includes reviews of previous geochemical studies and studies of natural and anthropogenic effects on the physical and chemical properties of soils. Research efforts were conducted in three main phases and the results of each phase are presented as individual chapters herein. Phase one focuses on identifying physico-chemical signatures of land use effects on soils at NPHL and determining the minimal resolution required to discriminate these effects to develop a multi-prong methodological framework. Phase two is an exploration of the efficacy of using portable x-ray fluorescence to measure non-pollution level chemical impacts from land use activities in order to refine the methodological framework by targeting soil samples for more costly, higher precision analyses. Phase three is a test of the refined framework to examine land use effects on physico-chemical characteristics of soil at PGHF. In the Summary and Conclusions the physico-chemical results from NPHL and PGHF are compared and contrasted to evaluate the methodological framework and its utility for investigation of land use effects at other Midwestern locations. The final section discusses possible revisions to the approach and outlines opportunities for future investigations.

La resuspension de sédiments contaminés peut entraîner le relargage d'éléments traces métalliques (ETM) dans la phase dissoute. Pour anticiper le risque de remobilisation des ETM lors de la vidange des retenues de barrages et créer un modèle géochimique permettant de prédire ce risque, des expériences de resuspension de sédiments provenant de trois retenues ont été réalisées pendant une semaine dans un réacteur. Le pH et le potentiel redox ont été suivis en continu et des échantillons ont été prélevés afin de mesurer l'évolution des ETM dissous. Trois grandes tendances d'évolution des ETM ont été mises en évidence et ne sont pas modifiées par les variations des masses de sédiment en suspension (entre 2 et 9 g/L): 1) Cr, Cd et Zn ne sont pas relargués. 2) Mn, Fe Co, Pb, ainsi que As pour deux retenues, augmentent puis diminuent au cours du temps. Ces éléments sont contrôlés par les oxyhydroxydes de Fe et de Mn et l'évolution du potentiel redox dans la solution. 3) Mo, Al, ou As pour une retenue, continuent d'augmenter à la fin des expériences, révélant des processus de relargage plus lents et une stabilisation dans la phase dissoute. Dans les trois retenues, As est l'élément le plus fortement et durablement relargué. Ces données expérimentales ont été utilisées pour calibrer un nouveau modèle géochimique développé par EDF sur ECOLEGO, intégrant la cinétique des réactions d'échange des ETM entre la phase dissoute et trois types de phases solides: les oxydes, les particules organiques et les carbonates. La calibration des paramètres cinétiques permet de bien reproduire les évolutions temporelles des concentrations qui augmentent (relargage) puis diminuent (piégeage). / The resuspension of the contaminated sediments may promote the remobilization of trace metals to the dissolved phase, threatening the water quality. The dam reservoirs sometimes need to be fully drawn down and being able to anticipate the release of the contaminants is essential to improve the management of reservoirs and assess the risk of water quality degradation. Surface sediments were collected in three contaminated dam reservoirs and aliquots of wet sediments were resuspended for a week in a reactor. The pH and the redox potential were continuously measured, dissolved samples were collected and the evolution of dissolved trace elements concentrations were measured. Depending on the elements, different temporal trends can be highlighted during the resuspension experiments. These evolutions were reproducible, regardless of the mass of sediment used from 2 to 9 g/L. 1) Cd, Cr and Zn were not released; 2) Mn, Fe, Co, Pb and As for two reservoirs, increased and then decreased during the experiments and were regulated by the Fe- and Mn-oxyhydroxides and the redox potential; 3) Al, Mo, or As for one reservoir, were still increasing at the end of the experiments, showing slower release processes and the stabilization of these elements under dissolved forms. For theses three reservoirs, As showed the greatest and the most prolonged release during resuspension. The experimental trends of dissolved metals were used in the firts calibration steps of a new chemical speciation model developped by EDF, which takes several kinetic rates into account for the exchange reactions of dissolved metal between water and three types of solid phases.

The In Situ Aquifer Test Facility (ISATF) has been established on Suncor Energy Inc’s (Suncor) oil sands mining lease north of Fort McMurray, Alberta to investigate the fate and transport of oil sands process-affected (PA) water in the Wood Creek Sand Channel (WCSC) aquifer. In 2008, the ISATF was used for preliminary injection experiments in which 3,000 and 4,000 L plumes of PA water were created in the WCSC. Following injection, the evolution of the plumes was monitored to determine if naphthenic acids (NAs) naturally attenuated in the WCSC and if trace metals were mobilized from the aquifer solids due to changes in redox conditions. Post-injection monitoring found groundwater velocities through the aquifer were slow (~3-10 cm/day) despite hydraulic conductivities on the order of 10-3 m/s. While microbes in the WCSC were capable of metabolizing acetate under the manganogenic/ferrogenic redox conditions, field evidence suggests naphthenic acids behaved conservatively. Following the injections, there was an apparent enrichment in the dissolved concentrations of iron, manganese, barium, cobalt, strontium and zinc not attributable to elevated levels in the PA injectate. Given the manganogenic/ferrogenic conditions in the aquifer, Mn(II) and Fe(II) were likely released through reductive dissolution of manganese and iron oxide and oxyhydroxide mineral coatings on the aquifer solids. Because naphthenic acids make up the bulk of dissolved organic carbon (DOC) in the injectate and are apparently recalcitrant to oxidation in the WCSC, some question remains as to what functioned as the electron donor in this process.

The In Situ Aquifer Test Facility (ISATF) has been established on Suncor Energy Inc’s (Suncor) oil sands mining lease north of Fort McMurray, Alberta to investigate the fate and transport of oil sands process-affected (PA) water in the Wood Creek Sand Channel (WCSC) aquifer. In 2008, the ISATF was used for preliminary injection experiments in which 3,000 and 4,000 L plumes of PA water were created in the WCSC. Following injection, the evolution of the plumes was monitored to determine if naphthenic acids (NAs) naturally attenuated in the WCSC and if trace metals were mobilized from the aquifer solids due to changes in redox conditions. Post-injection monitoring found groundwater velocities through the aquifer were slow (~3-10 cm/day) despite hydraulic conductivities on the order of 10-3 m/s. While microbes in the WCSC were capable of metabolizing acetate under the manganogenic/ferrogenic redox conditions, field evidence suggests naphthenic acids behaved conservatively. Following the injections, there was an apparent enrichment in the dissolved concentrations of iron, manganese, barium, cobalt, strontium and zinc not attributable to elevated levels in the PA injectate. Given the manganogenic/ferrogenic conditions in the aquifer, Mn(II) and Fe(II) were likely released through reductive dissolution of manganese and iron oxide and oxyhydroxide mineral coatings on the aquifer solids. Because naphthenic acids make up the bulk of dissolved organic carbon (DOC) in the injectate and are apparently recalcitrant to oxidation in the WCSC, some question remains as to what functioned as the electron donor in this process.

Trace metals (e.g. Fe, Mn, Zn, Cu, Cd, Ni) are important micronutrients that have historically been regarded as toxic pollutants rather than essential components of riverine and estuarine environments. The toxicity and behavior of trace metals, in response to physical and biogeochemical processes, are determined by their individual physico-chemical properties. In this dissertation, the vertical transformation of trace metals across oxic-anoxic interfaces was investigated at two sites, a Fe-rich freshwater river with minimal sulfide and an estuary with elevated Mn and H2S concentrations. Sediment profiles obtained from the Chattahoochee River showed that dissolved arsenic, present as As(V) only, is scavenged by Fe-oxides and accumulates directly below the sediment-water interface. Depth profiles also indicate that As(V) fluxes into the overlying water during baseflow conditions as well as after storm events. The significant correlation between Fe(II) and As(V) suggest that As(V) is released from Fe-oxides during their microbial reduction. By implementing a series of sediment incubations under increasing As(V) loads, it was determined that adsorption onto Fe-oxides and microbially mediated reductive dissolution of these mineral phases drive arsenic cycling in this sediment. These incubations also reveal for the first time that arsenic, even in low concentrations, n turn, arsenic loading impacts iron cycling by stimulating anaerobic respiration of Fe-oxides and promoting recrystallization of authigenic Fe-oxides, up to a toxicity threshold up to a few micromolar in concentrations. A combination of in situ measurements with discrete water sampling was utilized to determine the effects of tidal cycling on the distribution of trace metals under changing redox conditions during two consecutive tidal cycles at Station 858 in the Chesapeake Bay. Estuarine circulation patterns driven by tidal oscillations, a defined pycnocline, and the shallow sill (~20 m) of the Chesapeake Bay promoted bottom water anoxia during the summer months that allowed dissolved sulfide and reduced manganese to accumulate below the oxycline. The distribution of barium (conservative freshwater tracer) and uranium (conservative seawater tracer) across the pycnocline over the two tidal cycles indicated that the source of dissolved species was surficial sediments. During ebb and flood tides, the shear stress from the bottom waters flowing over the sediment seems to episodically promote the advection of porewaters enriched in dissolved sulfide, manganese, uranium, barium, lead, chromium, and copper. The selective enrichment of these trace metals appears to be controlled by their reactivity with sulfide. In contrast, cobalt and nickel are retained in sediments by adsorbed or incorporated in FeS and FeS2, while arsenic co-precipitates with sulfide or iron sulfide minerals. Overall, this study demonstrates that natural aquatic systems are complex environments where the interplay between biological, chemical, and physical processes affects the distribution of trace metals over short time scales. While a great wealth of knowledge can be obtained by laboratory experiments with synthetic solutions or pure cultures of organisms, a combination of in situ measurements and incubations with real samples in necessary to characterize the processes regulating the cycling of trace metals in aquatic systems.

The presence of trace transition metal species in the atmosphere can be attributed to the emission of particulate matter into the atmosphere by anthropogenic activities, as well as from natural sources. Trace metals emitted into the atmosphere can cause adverse health–related and environmental problems. At present, limited data exists for trace metal concentrations in South Africa. In this investigation, the general aim was to determine the concentrations of trace metals in atmospheric aerosols in the industrialised western Bushveld Igneous Complex, as well as to link the presence of these species in the atmosphere to possible sources in the region. The measurement site was placed in Marikana, a small rural town situated 35 km east from Rustenburg in the North West Province of South Africa. It is surrounded by numerous industrial and metallurgical operations. MiniVolumeTM samplers and Teflon® filters (2 ;m pores) were utilised to collect PM2.5 and PM10 particulate samples. The MiniVolumeTM samplers were programmed to filter 5 litres of air per minute for 12 hours per day, over a six–day period. The starting time for sampling was altered every six days, in order to obtain both day and night samples. Sampling was performed for a period of one year. The collected samples were chemically analysed with inductively coupled plasma mass spectroscopy (ICP–MS). Surface analysis of the sampled filters was performed with a scanning electron microscope (SEM) in conjunction with energy–dispersive spectroscopy (EDS). The dataset was also subjected to factor analysis in an attempt to identify possible sources of trace metal species in the atmosphere. The concentrations of 27 trace metals (Be, B, Na, Mg, Al, K, Ca, Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Zn, As, Se, Pd, Cd, Ba, Pt, Au, Hg, Tl, Pb, U) were determined. Pd, Hg, Tl, U, Ca, Co, As, Cd, Ba and Au were above the detection limit 25% or less of the time during the sampling period. With the exception of Ni, none of the trace metals measured at Marikana during the sampling period exceeded local and international standards. Higher Ni levels were possibly due to base metal refining in the region. Pb, which is the only metal species that has a standard prescribed by the South African Department of Environmental Affairs (DEA), did not exceed any of the standards. It is also significant to refer to Hg that was below the detection limit of the analytical instrument for the entire sampling period. The impact of meteorological conditions revealed that wet removal of atmospheric PM10 trace metals was more significant than the wind generation thereof. During the dry months, the total trace metal concentrations in the PM10 fraction peaked, while PM10 particles were mostly washed out during the wet season. Wind speed showed an unexpected inverse pattern compared to wet deposition. A less significant seasonal trend was observed for the trace metal concentrations in the PM2.5 fraction, which was attributed to a faster replenishment of smaller particles into the atmosphere after rain events. Separation of trace metal concentrations into PM10–2.5 and PM2.5 fractions indicated that 79% of the total trace metal levels that were measured were in the PM2.5 fraction, which indicated a strong influence of industrial and/or combustion sources. Fractionalisation of each of the trace metal species detected showed that for each metal species, 40% and more of a specific metal was in the PM2.5 fraction, with Cr, V, Ni, Zn and Mn occurring almost completely in the PM2.5 fraction. Surface analysis with SEM supported results from the chemical analysis, which indicated that a large fraction of the particles was likely to originate from anthropogenic activities and from wind–blown dust. SEM–EDS also detected nonmetallic S that is usually associated with the Pt pyrometallurgical industry that is present in the western Bushveld Igneous Complex. Correlations between Cr, V, Ni, Zn and Mn revealed that the main sources of these species were pyrometallurgical industries. Explorative factor analysis of the unprocessed and Box–Cox transformed data for all 27 metals detected, resolved four meaningful emission sources, i.e. crustal, vanadium related, base metal related and chromium related. Comparison of trace metal species to other parameters measured (e.g. CO, BC) also indicated pyrometallurgical activities and wind–blown dust to be the main sources of trace metals in this region. / Thesis (M.Sc. (Chemistry))--North-West University, Potchefstroom Campus, 2011.