Arsenic (As) is a toxic metalloid and the remediation of soils and waters from this contaminant as well as the prevention of future contamination are still pending tasks in Chile. There are bacteria able to live in environments polluted with arsenic, as they have tolerance mechanisms for this metalloid, or even can use it for energy metabolism. The potential tolerance mechanisms include the production of siderophores, metabolites with chelating activity that can decrease the toxicity of metals and metalloids. Although a correlation between siderophore production and metalloid tolerance has been described, the structure of arsenic-binding siderophores and their implications in tolerance have not been elucidated yet. In this work, it is proposed that bacteria isolated from contaminated environments produce arsenic-binding siderophores. The main aims of this work are to study the production of the siderophores by arsenic-tolerant bacteria, to characterize these compounds and to determine their relation with tolerance to arsenic. Fourteen arsenic-tolerant bacteria were isolated from contaminated water, From these, four strains belonging to the species Rhodococcus erythropolis, Arthrobacter oxydans and Kocuria rosea were selected, in addition to the previously isolated Rhodococcus erythropolis S43, for a more detailed study. The isolates were used to produce siderophore extracts, which were then evaluated for their iron- and arsenic-binding activity. To detect the latter, a new method (As-mCAS) was set up, based on the Chrome Azurol S (CAS) test, an assay to detect iron-chelating activity of siderophores. After testing the extracts, R. erythropolis S43 was selected as the strain with the best arsenic-binding activity. For the subsequent chemical characterization, siderophores were produced under control conditions (iron-free M9 medium) and under stress conditions with arsenic (iron-free M9 medium with sodium arsenite). HPLC analysis of the extracts for both culture conditions showed the presence of a single compound with both an iron-chelating and an arsenic-binding activity. Analyses by nuclear magnetic resonance (NMR) spectroscopy and mass spectrometry (MS) for both culture conditions suggested the main presence of the siderophore heterobactin B. In addition, the genome of strain S43 was sequenced. A cluster of ars-genes was predicted, probably responsible for the arsenic-tolerance of the strain. In addition, a complete gene cluster for heterobactin production was found. However, no significant difference was obtained in the expression of these determinants in the presence or absence of arsenic, suggesting that the production of this siderophore in strain S43 is not responsible for the tolerance to the metalloid.

This thesis describes the syntheses, the crystal structures, and the physical properties of some new ternary and quaternary rare-earth coinage metal arsenides, selenides and oxides. All ternary compounds LnCu1+[delta]As2 (Ln = Y, La, Ce, Nd, Sm, Gd - Lu), LnAg1+[delta]As2 (Ln = La - Nd, Sm), and LnAuAs2 (Ln = Pr, Sm, Gd, Tb) adopt structures closely related to the HfCuSi2 type consisting of PbO-like layers of T and As atoms, square layers of As atoms and layers of Ln atoms separating the former two building units. All copper compounds of this series contain regular square nets of As atoms, whereas the respective nets in the silver and gold compounds are distorted. Two principally different patterns of distortion have been found: [As] zigzag chains in LnAgAs2 (Ln = Pr, Nd, Sm) and [As] cis-trans chains in LaAg1.01(1)As2, CeAgAs2, and PrAuAs2. Both patterns can undergo a further reduction of symmetry to end up with a pattern of As2 dumb-bells as can be seen in SmAuAs2, GdAuAs2, and TbAuAs2. Stoichiometric samples LnCuAs2 (Ln = Y, Pr, Nd, Sm, Gd, Tb, Dy, Er) have been used for measurements of the conductivity [rho], magnetic susceptibility [chi] and heat capacity cp. All investigated compounds exhibit metallic conductivity and, except for Y, order antiferromagnetically at temperatures below 10 K. In contrast to LnCuAs2 compounds, the silver compound CeAgAs2 shows semiconducting behavior throughout the temperature range from 4 to 350 K, whereas in PrAgAs2 metallic conductivity is preserved. The crystal structure of Sm2CuAs3O contains two different PbO-like layers formed either by Sm and O or Cu and As atoms. Both PbO-type layers are separated by sheets of Sm and distorted square nets of As atoms. The As atoms are arranged in planar zigzag chains, like those found in NdAgAs2. Sm2CuAs3O is thus the first quaternary rare-earth pnictide oxide with a distorted As net. The quaternary potassium rare-earth copper selenides KGd2CuSe4, KLn2Cu3Se5 (Ln = Ho, Er, Tm), and K2Ln4Cu4Se9 (Ln = Dy, Y) extend three series of previously described sulfide and selenide compounds. All three series adopt a three-dimensional tunnel structure built up by [LnSe6] octahedra and [CuSe4] tetrahedra. The K atoms reside in the tunnels with a bicapped trigonal prismatic coordination of eight Se atoms for KGd2CuSe4 and KLn2Cu3Se5 (Ln = Ho, Er, Tm), while for K2Ln4Cu4Se9 (Ln = Dy, Y), the K atoms are coordinated by seven Se atoms in monocappped trigonal prisms.

The objective of the work described in this thesis was to understand sorption reactions of uranium occurring at the water-clay mineral interfaces in the presence and absence of arsenic and other inorganic ligands. Uranium(VI) removal by clay minerals is influenced by a large number of factors including: type of clay mineral, pH, ionic strength, partial pressure of CO2, load of the sorbent, total amount of U present, and the presence of arsenate and other inorganic ligands such as sulfate, carbonate, and phosphate. Both sulfate and carbonate reduced uranium sorption onto IBECO bentonite due to the competition between SO42- or CO32- ions and the uranyl ion for sorption sites, or the formation of uranyl-sulfate or uranyl-carbonate complexes. Phosphate is a successful ligand to promote U(VI) removal from the aqueous solution through formation of ternary surface complexes with a surface site of bentonite. In terms of the type of clay mineral used, KGa-1b and KGa-2 kaolinites showed much greater uranium sorption than the other clay minerals (STx-1b, SWy-2, and IBECO montmorillonites) due to more aluminol sites available, which have higher affinity toward uranium than silanol sites. Sorption of uranium on montmorillonites showed a distinct dependency on sodium concentrations because of the effective competition between uranyl and sodium ions, whereas less significant differences in sorption were found for kaolinite. A multisite layer surface complexation model was able to account for U uptake on different clay minerals under a wide range of experimental conditions. The model involved eight surface reactions binding to aluminol and silanol edge sites of montmorillonite and to aluminol and titanol surface sites of kaolinite, respectively. The sorption constants were determined from the experimental data by using the parameter estimation code PEST together with PHREEQC. The PEST- PHREEQC approach indicated an extremely powerful tool compared to FITEQL. In column experiments, U(VI) was also significantly retarded due to adsorptive interaction with the porous media, requiring hundreds of pore volumes to achieve breakthrough. Concerning the U(VI) desorption, columns packed with STx-1b and SWy-2 exhibited irreversible sorption, whereas columns packed with KGa-1b and KGa-2 demonstrated slow, but complete desorption. Furthermore, most phenomena observed in batch experiments were recognized in the column experiments, too. The affinity of uranium to clay minerals was higher than that of arsenate. In systems containing uranium and arsenate, the period required to achieve the breakthrough in all columns was significantly longer when the solution was adjusted to pH 6, due to the formation of the uranyl-arsenate complex. In contrast, when pH was adjusted to 3, competitive sorption for U(VI) and As(V) accelerated the breakthrough for both elements. Finally, experiments without sorbing material conducted for higher concentrations of uranium and arsenic showed no loss of total arsenic and uranium in non-filtered samples. In contrast, significant loss was observed after filtration probably indicating the precipitation of a U/As 1:1 phase.

Ph.d.-afhandling. Danmarks Tekniske Universitet, 2006. / Haves også i trykt udg. Thesis (Ph.D.). 11 ill., 6 tables; approx. 260 ref. Summaries (Da, En).

This article presents nano composite TiO2.Fe2O3/laterite materials, which were successfully prepared by hydrometallurgical method. The materials were modified using urea as the nitrogen source. The particles size of the materials is from 20-30 nanometers. The obtained materials can not only absorb arsenic compounds but also enhance the ability of converting As (III) or As (V) into Aso, which is removed from solution. Arsenic removal efficiency of these materials is high. Using sunlight in a hydraulic retention time, about 180 minutes, the arsenic value at the inflow was about 10 mg/L but the outflow was negligible. Covering TiO2.Fe2O3 nano on laterite have brought high economical efficiency, on one hand, it saved material and on the other hand, it can be continuously operated without the centrifugal separation of the nano material. / Bài báo này giới thiệu về phương pháp điều chế vật liệu nano TiO2.Fe2O3 biến tính nitơ được phủtrên đá ong bằng phương pháp thủy luyện. Vật liệu nano thu được có kích thước 20-30 nm. Vật liệu thu được không những có khả năng hấp phụ các hợp chất của asen mà còn có khả năng khử As (III) hoặc As (V) thành Asokhi được chiếu sáng. Sử dụng ánh sáng mặt trời chiếu vào hệ thống xử lý trong thời gian 180 phút có thể loại bỏ được gần như hoàn toàn asen ra khỏi nước mặc dù hàm lượng đầu vào là 10 mg/l. Việc phủ vật liệu TiO2.Fe2O3 nano lên đá ong đã mang lại hiệu quả kinh tế cao, một mặt nó tiết kiệm được vật liệu, mặt khác, vật liệu có thể sử dụng một cách liên tục mà không cần phải tách bằng phương pháp ly tâm.

The Red River Delta in Vietnam is one of the regions whose quaternary aquifers are polluted by arsenic. Chronic toxification by arsenic can cause severe illnesses such as cancer, skin lesions, developmental defects, cardiovascular and neurological diseas-es, and diabetes. In this study, a food processing craft village in the Red River Delta was investigated regarding the potential risk faced by the population due to arsenic. The potential sources of arsenic are the groundwater, the crops grown in the sur-roundings, and animal products from local husbandry. However, the occurrence of arsenic in nature is variable, and its bioavailability and toxicity depend very much on its specification: trivalent compounds are more toxic and often more mobile than pen-tavalent compounds, while inorganic species are generally more toxic than organic ones. Local conditions, such as the redox potential, strongly influence its specification and thus potential bioavailability. The introduction to this work elucidates the key factors which potentially cause human exposure to arsenic: the geological setting of the study area, land and water use pat-terns, and the current state of research regarding the mobilization, bioavailability and plant uptake of arsenic. Although the study area is located in a region where the groundwater is known to be moderately contaminated by arsenic, the level of arsenic in the groundwater in the village had not previously been determined. In this study, water use in the village was examined by a survey among the farmers and by water analyses, which are present-ed in the following chapters. Four main water sources (rain, river, tube well and a pub-lic municipal waterworks) are used for the different daily activities; the highest risk to human health was found to be the bore well water, which is pumped from the shallow Holocene aquifer. The water from the bore wells is commonly used for cleaning and washing as well as to feed the animals and for food processing. Products like noodles and rice wine were examined as well as local pork and poultry. Vegetables from the gardens and rice plants from the surrounding paddy fields were sampled and ana-lyzed. All plants were found to have accumulated arsenic, leafy vegetables showing the highest arsenic concentrations. The results are discussed and compared, and conclusions are drawn in the last part. The reducing conditions in the paddy fields are likely to have a strong influence on arsenic uptake in rice plants and on transport to the aquifer. The installation of a wastewater treatment plant under the research project INHAND, which was funded by the BMBF German Ministry of Education and Research, led to lower arsenic concen-trations in the groundwater. Soaring industrialization, the growing population, and the consumers’ changing behav-ior will widely affect land and water use and hence the potential mobilization of arse-nic. In order to mitigate further human exposure to arsenic, wastewater needs to be treated and the reducing conditions in the rice fields need to be decreased by means of enhanced cultivation methods.

The topic of this diploma thesis was the speciation analysis of the toxicological important forms of the arsenic in urban particulate matter samples. The detection technique used in this work was atomic absorption spectrometry with quartz atomizer. Acetic acid, ammonium acetate, hydroxylamine, potassium hydroxide and sodium carbonate are recommended leaching agents for extraction of metals from urban particulate matter samples. Results of the presenting work are following: Acidic extraction reagents can be not recommended for the speciation analysis of the arsenic, because these reagents lower sensitivity of the determination of As3+ and As5+ too and destroy the quartz atomizer. Alkaline extraction reagents don't lower sensitivity of the determination of As3+ and these reagents don't destroy the atomizer, but lower sensitivity of the determination of As5+ was obtained. Recommended reagents aren't useful for extraction of the metals from urban particulate matter samples for the speciation analysis.

Atomization of arsine in a novel hydride atomizer for atomic absorption spectrometry (HG-AAS) was thoroughly optimized. This plasma atomizer is based on a dielectric barrier discharge (DBD). Sensitivity and detection limit reached 0.48 s ng-1 As and 0.16 ng ml-1 As, respectively, under optimum atomization conditions (Ar discharge using a flow rate of 60 ml min-1 Ar, DBD power 17 W). Analytical figures of merit reached in DBD are comparable to those found in an externally heated quartz tube multiatomizer (MMQTA) that was chosen as a model of conventional approach to hydride atomization in HG-AAS. An extent of interferences (Se, Sb, Bi) during As determination was investigated comparing both MMQTA and DBD atomizers. The later one was found to be more resistant towards interferences. A simple preconcentration of As in a DBD atomizer was reached after oxygen introduction into the Ar plasma in the DBD resulting in analyte retention in the atomizer followed by its volatilization once the oxygen flow is switched off. Preconcentration efficiency of 100 % was reached and detection limit improvement by a factor of ten was achieved (0.01 ng ml-1 As, preconcentration period 300 s).

Ehemalige Urangruben tragen durch das anfallende Flutungswasser maßgeblich zur Ausbreitung von Schadstoffen wie Uran und Arsen in teils dicht besiedelte Gebiete bei. Um die Prozesse in den unterirdischen Gruben besser zu verstehen und alternative Strategien zur konventionellen, kostenintensiven Wasserbehandlung entwickeln zu können, war das Ziel der Arbeit, mikrobielle Gemeinschaften aus drei gefluteten Uranerzbergwerken in Sachsen, namens Pöhla, Schlema und Zobes, die unterschiedliche Flutungsstadien repräsentierten, zu charakterisieren und den mikrobiellen Einfluss auf die Mobilität von Uran und Arsen zu untersuchen. Um herauszufinden, welche Mikroorganismen die hydrochemischen Vorgänge im Untergrund der Uranerzbergwerke beeinflussen könnten, wurde die Diversität und Zusammensetzung mikrobieller Gemeinschaften mittels Pyrosequenzierung eines Fragments des 16S rRNA Gens (16S rDNA) und CARD-FISH ermittelt. Wenngleich Clusteranalysen zeigten, dass sich die planktonischen Gemeinschaften hinsichtlich ihrer bakteriellen Zusammensetzung zwischen den drei Uranerzbergwerken unterschieden, wurden alle von chemolithotrophen Schwefeloxidierern der Beta- und Epsilonproteobacteria dominiert, die mit den Gattungen Thiobacillus und Sulfuritalea bzw. Sulfuricurvum und Sulfurimonas vertreten waren. Im Unterschied zu den planktonischen Gemeinschaften bestanden in situ Biofilme, die auf BACTRAPs während einer 3-monatigen Exposition im Flutungswasser anwuchsen, laut Pyrosequenzierung zu einem wesentlichen, mitunter dominanten Anteil aus metall- bzw. sulfatreduzierenden Deltaproteobacteria. In Biofilmgemeinschaften aus Zobes wurden hauptsächlich Geobacter sp. detektiert, die als Fe(III)- und U(VI)-Reduzierer bekannt sind. Obwohl Archaea basierend auf den Ergebnissen der CARD-FISH-Analyse nur einen sehr geringen Anteil der planktonischen Gemeinschaften ausmachten, wurden mittels Pyrosequenzierung planktonische Euryarchaeota der Thermoprotei in allen Gruben detektiert. In planktonischen Gemeinschaften und 3-monatigen Biofilmen aus Pöhla und Zobes wurden zudem methanogene Crenarchaeota, vor allem Methanobacteria und teilweise Methanomicrobia, ermittelt. Die 16S rRNA-Analyse, die ergänzend zum DNA-basierten Ansatz durchgeführt wurde, lieferte Hinweise darauf, dass die detektierten, dominanten Mikroorganismen, Bacteria sowie Archaea, in der planktonischen Gemeinschaft aus Schlema und den Biofilmgemeinschaften stoffwechselaktiv waren. In der planktonischen Gemeinschaft aus Zobes wurden im Vergleich zur DNA-basierten Analyse höhere Abundanzen für Verrucomicrobia, Acidobacteria und Alphaproteobacteria ermittelt, deren Bedeutung offen bleibt. Untersuchungen zum mikrobiellen Stoffwechselpotential planktonischer Gemeinschaften mittels CFU- und MPN-Analysen ergaben, dass Mikroorganismen aus allen Urangruben ein breites Spektrum anaerober Reaktionen (Nitrat-, Eisen-, Mangan-, Arsenat- und Sulfatreduktion und Acetogenese) unter Laborbedingungen abdeckten. In guter Übereinstimmung mit den Sequenzierungsergebnissen konnten methanogene Mikroorganismen nur im Flutungswasser aus Pöhla und Zobes detektiert werden. Die Metaproteomanalyse ergab, dass 61,6% der Peptide in der planktonischen Gemeinschaft aus Schlema von den dominanten Epsilonproteobacteria stammten. Dagegen wurden für Zobes detektierte Peptide mehrheitlich methylotrophen und eisenoxidierenden Betaproteobacteria der Familien Methylophilaceae bzw. Gallionellaceae sowie methylotrophen Gammaproteobacteria der Methylococcaceae zugewiesen. Obwohl die Mehrheit der Proteine an der Translation beteiligt war, konnten insgesamt 49 Proteingruppen ermittelt werden, deren Vertreter für den mikrobiellen Energiestoffwechsel relevant waren. Insbesondere planktonische Gammaproteobacteria aus Zobes konnten so mit dem Kohlenstoff- und Schwefelkreislauf in Zusammenhang gebracht werden. Mithilfe von Labormikrokosmen wurde der potentielle Einfluss mikrobieller Gemeinschaften aus Schlema auf die Mobilität von Arsen und Uran im Flutungswasser mit Acetat als Elektronendonor unter anaeroben Bedingungen über einen Zeitraum von 98 Tagen untersucht. Im Vergleich zu den Kontrollen konnten sowohl die stimulierte, planktonische Gemeinschaft als auch Biofilme natürliches Arsen aus der wässrigen Phase fast vollständig entfernen. Allerdings wies der spätere Anstieg des gelösten Arsens daraufhin, dass der immobilisierte Zustand langfristig nicht stabil blieb. In stimulierten Biofilm-Ansätzen wurde Uran mit bis zu 39 ± 9% (in Anwesenheit von 7 µM natürlichem Uran) bzw. 34 ± 8% (bei Zugabe von 50 µM U(VI)) aus der wässrigen Phase langfristig (98 Tage) immobilisiert. Laserfluoreszenzspektroskopische Untersuchungen zeigten, dass Uran im Biofilm reduziert wurde.

The Red River Delta in Vietnam is one of the regions whose quaternary aquifers are polluted by arsenic. Chronic toxification by arsenic can cause severe illnesses such as cancer, skin lesions, developmental defects, cardiovascular and neurological diseas-es, and diabetes. In this study, a food processing craft village in the Red River Delta was investigated regarding the potential risk faced by the population due to arsenic. The potential sources of arsenic are the groundwater, the crops grown in the sur-roundings, and animal products from local husbandry. However, the occurrence of arsenic in nature is variable, and its bioavailability and toxicity depend very much on its specification: trivalent compounds are more toxic and often more mobile than pen-tavalent compounds, while inorganic species are generally more toxic than organic ones. Local conditions, such as the redox potential, strongly influence its specification and thus potential bioavailability. The introduction to this work elucidates the key factors which potentially cause human exposure to arsenic: the geological setting of the study area, land and water use pat-terns, and the current state of research regarding the mobilization, bioavailability and plant uptake of arsenic. Although the study area is located in a region where the groundwater is known to be moderately contaminated by arsenic, the level of arsenic in the groundwater in the village had not previously been determined. In this study, water use in the village was examined by a survey among the farmers and by water analyses, which are present-ed in the following chapters. Four main water sources (rain, river, tube well and a pub-lic municipal waterworks) are used for the different daily activities; the highest risk to human health was found to be the bore well water, which is pumped from the shallow Holocene aquifer. The water from the bore wells is commonly used for cleaning and washing as well as to feed the animals and for food processing. Products like noodles and rice wine were examined as well as local pork and poultry. Vegetables from the gardens and rice plants from the surrounding paddy fields were sampled and ana-lyzed. All plants were found to have accumulated arsenic, leafy vegetables showing the highest arsenic concentrations. The results are discussed and compared, and conclusions are drawn in the last part. The reducing conditions in the paddy fields are likely to have a strong influence on arsenic uptake in rice plants and on transport to the aquifer. The installation of a wastewater treatment plant under the research project INHAND, which was funded by the BMBF German Ministry of Education and Research, led to lower arsenic concen-trations in the groundwater. Soaring industrialization, the growing population, and the consumers’ changing behav-ior will widely affect land and water use and hence the potential mobilization of arse-nic. In order to mitigate further human exposure to arsenic, wastewater needs to be treated and the reducing conditions in the rice fields need to be decreased by means of enhanced cultivation methods.:Abstract III Zusammenfassung V Acknowledgements VII Contents IX List of abbreviations XIII List of tables XVII 1 Scope of this work 1 2 Introduction 2 2.1 Geographical and geological setting of the study area 2 2.2 Hydrological situation 5 2.2.1 Surface water 5 2.2.2 Impact of human activities on surface water quality and distribution 6 2.2.3 Hydrogeology 7 2.3 Arsenic occurrence 7 2.3.1 Arsenic toxicity 8 2.3.2 Risk potential of arsenic in diet 10 2.4 Arsenic contamination in the groundwater resources of the Red River Delta 11 2.4.1 Occurrence and origin of arsenic in the Red River Delta 12 2.4.2 Mobilization processes 13 2.4.3 As mobilization in paddy fields 15 2.5 Arsenic occurrence in daily rural activities 16 2.5.1 Arsenic in soil 17 2.5.2 Arsenic in drinking water 19 2.5.3 Phytoaccumulation: Current state of research 20 2.5.4 Bioavailablity 22 2.5.5 Arsenic uptake in rice plants 23 2.5.6 Arsenic in meat and animal products 26 2.5.7 Arsenic uptake in golden apple snails 27 2.5.8 Processing: Wine and noodles 28 2.5.9 Arsenic concentrations in wastewater, activated sludge and digestate 29 2.6 Iron and manganese in the nutrient chain 30 2.7 Land and water use in the Red River Delta 31 2.7.1 Historical and political aspects of rural development in Vietnam 33 2.7.2 Craft villages in the Red River Delta 34 3 Materials and methods 36 3.1 Soil sample analyses 36 3.2 Well sampling 37 3.3 Wastewater and sludge analyses 37 3.4 Food analyses 38 3.5 Site visit and field observations 39 3.6 Questionnaire 39 4 Results 40 4.1 Soil samples 40 4.1.1 Total arsenic and total heavy metal concentrations 40 4.1.2 Sequential fractionation procedure 41 4.2 Arsenic in the water cycle in Dai Lam 43 4.2.1 Groundwater analyses 43 4.2.2 Water use in Dai Lam 47 4.2.3 Wastewater in Dai Lam 50 4.3 Arsenic in sewage sludge 51 4.4 Arsenic in manure samples 52 4.5 Arsenic in food samples 52 4.5.1 Rice 52 4.5.2 Arsenic in leaf vegetables 53 4.5.3 Arsenic in poultry products 56 4.5.4 Arsenic in pork samples 57 4.5.5 Arsenic in snails 57 4.6 Economic and demographic development potential 58 5 Discussion 61 5.1 Soil samples 61 5.2 Groundwater samples 62 5.2.1 High arsenic concentrations 62 5.2.2 Strong temporal and spatial variation 63 5.2.3 Weak correlation between measured parameters 69 5.3 Wastewater and sewage sludge 70 5.4 Pig manure 71 5.5 Daily exposure to As from dietary intake 71 5.6 Effects of land and water use on water quality and public health 76 5.7 Against the background of the transition economy 77 6 Conclusion 80 7 Perspectives (further work) 85 8 References 86 9 Annex 110