Artificial infiltration has been increasing in popularity in Sweden as a way to combat over-abstraction of groundwater aquifers from growing municipalities. However, enteric virus contamination of drinking water sources is a concern as infiltrating surficial waters are easily contaminated from human activities. Therefore, it is imperative that effective drinking water treatment is maintained to prevent infection throughout the municipalities. Furthermore, a better quantification of environmental parameters affect-ing virus mobility could significantly improve infiltration schemes for virus removal purposes. In this study, the removal efficiency of MS2 bacteriophage was investigated in relation to dissolved organic matter and ionic strength on new and used sand from the Tunåsen infiltration basin in Uppsala, Sweden. Virus removal was measured by static batch equilibrium experiments and first order decay models were used as interpretative models. Soil associated organic matter displayed the greatest effect on virus removal between all parameters. The highest removal efficiency was seen in samples containing low soil associated organic matter. Similarly, an inverse relationship with dissolved organic matter and virus removal rate was determined. Samples without soil showed the opposite relationship between dis-solved organic matter and virus removal. A higher decrease in MS2 phage was observed with higher dissolved organic matter in soil-negative samples. The removal kinetics of MS2 with higher ionic strength had a closer correlation with the linear time-invariant removal model, whereas samples with low ionic strength had a closer relation with the nonlinear time-dependent removal model. However, ionic strength was shown to have very little effect on overall virus removal efficiency. Fastest and slowest viral removal rates were modeled in the HYDRUS 1D program to determine the amount of potential contamination of the water table beneath the Uppsala Esker. The degree of contamination at the bottom of the infiltration basins was also determined. The sample with the highest rate of virus removal displayed an 11.77% greater decrease in phage concentration at the water table than samples with the lowest rate of removal. However the approximation of maximum contamination was deemed unrealistic due to the assumption that the entire esker was made of sand. On the other hand, the sample with the highest rate of removal showed only a 0.60% greater decrease in phage concentration following the infiltration basin. This study therefore suggests that a more frequent replacement of quartz sand in infiltration basins has little value in overall drinking water quality. / I Sverige har så kallad konstgjord infiltrering, det vill säga perkolation av ytvatten ned i grundvattensystem, blivit ett allt vanligare tillvägagångssätt för att tillmötesgå den ökande efterfrågan av färskt dricksvatten bland Sveriges växande kommuner. Tyvärr är föroreningar av virus i dricksvatten ett vanligt bekymmer eftersom ytvatten enkelt förorenas genom mänskliga aktiviteter, vilket bland annat har observerats genom en ökning av diarréfall under vintermånaderna. Därför är det viktigt att en bra vattenbehandling upprätthålls för att förebygga fler insjuknanden hos befolkningen.Tidigare studier visar att ökning av organiskt material bidrar till förhöjd transport av virus i konstgjorda infiltreringsprojekt. Detta eftersom organiskt material binder till jordpartiklar och därför tar upp den plats som viruset annars skulle bundit till. Istället för att viruset binder till jorden och tas bort från vattnet, stannar det kvar och transporteras vidare i grundvattensystemet och kan då nå den vattentäkt där dricksvatten tas till samhället. Ökad förekomst av organiskt material skulle alltså kunna öka risken att kommunalt dricksvatten förorenas av virus.I denna studie användes prover tagna från det område i Uppsala där ytvatten infiltreras i marken för att genomgå naturlig rening. Proverna undersöktes för att se hur mycket virus som tas bort under den naturliga rengöringsprocessen. Borttagningen av virus mättes i en så kallad ”static batch equilibrium experiments”, vilket innebär att mängden virus i vattnet uppskattas utifrån tre olika parametrar, mätt över tid. De testade parametrarna är mängd organisk materia löst i vattnet, lösningens jonstyrka och mängd organisk materia bunden till jorden. För att jämföra de olika parametrarna och för att bestämma hur snabbt virus tas bort från vattnet, användes olika linjära modeller.Resultaten visade att organiskt material bundet till jord var den parameter som hade störst effekt på virusborttagning, där låg halt organiskt material är bunden till jord avlägsnades mest virus. Halten organisk materia löst i vatten har en liknande trend där en hög halt inte avlägsnar så mycket virus, medan en låg halt däremot avlägsnar mer virus. Proverna utan jord visade motsatt effekt mellan löst organisk materia och virusborttagning, det vill säga mer virus avlägsnades ju mer organisk materia som var löst i vattnet. Jonstyrkan hade ingen signifikant effekt på virusborttagningen.Två olika scenarion, värsta och bästa tänkbara, modellerades i programmet HYDRUS 1D för att kunna bestämma inom vilket intervall en eventuell förorening i Uppsalaåsens grundvatten skulle kunna ligga. Även graden av förorening längst ner i infiltreringsbassängen, bestående av ett metertjockt lager sand som placerats ovanpå Uppsalaåsen för att bidra till reningsprocessen, modellerades och bestämdes för att bättre kunna förutse när byte av sand är lämpligast.Provet som visade högst virusborttagning, det vill säga det bästa tänkbara scenariot, var 11.77 % effektivare än provet med långsammast virusborttagning. Däremot bestämdes det att uppskattningen av maximal förorening var orealistisk eftersom det i modellen antogs att hela åsen bestod av sand, medan åsar i själva verket består av många andra fraktioner och jordarter utöver sand, till exempel grus och sten.Provet med snabbast virusborttagning hade bara 0.60 % större minskning i koncentration av virus efter att vattnet passerat infiltreringsbassängen, än provet med lägst virusborttagning. Denna studie föreslår därför att det är av litet värde att byta ut sanden i infiltrationsbassängen då denna procedur har liten påverkan på dricksvattenkvalitén generellt.

Les extrémités des chromosomes eucaryotes linéaires ont une structure nucléoprotéique particulière, et sont appelées télomères. Étant donnés leur structure et le mécanisme semi-conservatif de la réplication de l’ADN, la longueur des séquences télomériques est instable. Au fil des divisions cellulaires, les réplications successives de l’ADN entraînent une réduction progressive des séquences télomériques. Des télomères courts ne sont plus fonctionnels, ce qui entraîne l’arrêt du cycle cellulaire et de l’instabilité génomique. Il est donc essentiel de prévenir ce raccourcissement. Une enzyme spécialisée rallonge les télomères : la télomérase. La télomérase est une ribonucléoprotéine (RNP) qui maintient les télomères par un mécanisme d’ajout de répétitions de la séquence télomérique. Afin de former un complexe actif, les sous-unités protéiques de l’enzyme doivent s’assembler autour d’un ARN non-codant, nommé Tlc1 chez la levure Saccharomyces cerevisiae. Cependant, le fait que la RNP nécessite plusieurs sous-unités pour son activité implique un assemblage précis et coordonné. Peu de données existent au sujet de l’assemblage de la RNP en un complexe actif, mais il semble qu’un trafic nucléo-cytoplasmique soit requis dans le cycle fonctionnel de l’enzyme. Caractériser le mécanisme d’assemblage de la télomérase permettra de mieux comprendre les phénomènes de régulation de l’activité de l’enzyme, et donc du maintien des télomères chez S. cerevisiae. À cette fin, j’ai d’abord vérifié l’état stoechiométrique de l’enzyme in vivo par des méthodes de FISH sur des molécules individuelles. J’ai ainsi pu montrer que la télomérase ne comportait qu’un seul ARN Tlc1. Ces données in vivo corrèlent avec des données publiées précédemment grâce à des techniques de biochimie, et suggèrent que l’enzyme n’est composée que de complexes individuels contenant une seule copie de chaque sous-unité protéique. Dans le but d’étudier les mécanismes d’assemblage de la télomérase, j’ai aussi développé un système de contrôle de la transcription d’une forme taguée de Tlc1. Cet outil génétique, basé sur les systèmes Cre-Lox et MS2-GFP, permet l’insertion d’un tag MS2 dans le gène TLC1. Ce tag donne la possibilité de suivre des ARN Tlc1 in vivo et en temps réel par microscopie confocale à spinning-disk. Ce système, baptisé CrEMGaT, a permis de montrer que l’insertion du tag dans le gène entraîne l’apparition de Tlc1-MS2, et que ces ARN forment des agrégats nucléaires ayant des caractéristiques similaires aux T-Recs précédemment caractérisés lors d’une collaboration avec le Pr Chartrand. De plus, des résultats préliminaires obtenus avec le CrEMGaT suggèrent que les ARN Tlc1-MS2 finissent leur cycle fonctionnel au cytoplasme. Dans l’ensemble, les données produites et l’outil développé au cours de cette thèse donnent une meilleure idée de l’état d’assemblage de la télomérase. / Abstract : In the eukaryotic kingdom, the extremities of the linear chromosomes have a particular nucleoproteic structure, and are called telomeres. Because of this structure and the semi-conservative nature of DNA replication, telomere length is unstable. DNA replications during consecutive cell divisions leads to a progressive shortening of telomeric sequences. Below a certain threshold, telomeres are not functional, triggering cell-cycle arrest and genomic instability. It is therefore essential to prevent this shortening. A specialized enzyme elongates telomeres: Telomerase. Telomerase is a ribonucleoprotein (RNP) that adds repeats of the telomeric sequence to the end of telomeres. The enzyme formation requires protein subunits to assemble onto a scaffolding ncRNA, Tlc1 in Saccharomyces cerevisiae. The fact that several subunits are needed for RNP activity implies a precise and coordinated assembly occurs. However, data are lacking about telomerase assembly into an active complex, but different observations point towards a nucleo-cytoplasmic trafficking requirement during the enzyme life-cycle. Characteristics about telomerase assembly mechanism would provide useful information in the quest for understanding the phenomena regulating the enzyme activity, and therefore telomere maintenance in S. cerevisiae. Engaged in this quest, I first verified telomerase stoichiometry in vivo. By quantitative single-molecule FISH, the results showed that the enzyme only contains one Tlc1 RNA per RNP in the cell. These in vivo data correlate with previous publications which, based on biochemical experiments, suggested single copies of the different subunits are present in the complex. Taken together, these findings are dismantling a previous dogma that stipulated telomerase is composed of two complexes, and suggest telomerase quaternary arrangement stays simple. Aiming to study telomerase assembly mechanisms, I also developed an inducible genetic system governing the transcription of a tagged version of Tlc1 (i.e. Tlc1-MS2). This system, based on the Cre-Lox and MS2-GFP systems, allows to control the insertion of a MS2 tag into the TLC1 gene. In this system, dubbed CrEMGaT, the genetic insertion is controllable and indeed leads to Tlc1-MS2 appearance. It is then possible to track these tagged RNAs in vivo and in real time with a spinning disk confocal microscope. Furthermore, these RNAs form nuclear aggregates with characteristics of the T-Recs previously described in a collaboration between our lab and Pr Chartrand’s. Finally, preliminary data obtained with the CrEMGaT suggest cytoplasm is the last cellular compartment visited by Tlc1-MS2 RNA. Overall, these data and the system developed during my thesis will give insights into telomerase assembly in vivo.

Thesis advisor: Gregory R. Chiklis / Thesis advisor: Kathleen Dunn / In molecular diagnostics, the polymerase chain reaction (PCR) is used to amplify small amounts of nucleic acids found in patient samples, allowing for detection of diseases within hours of infection. This early detection allows medical professionals to diagnose and treat patients with greater success. It is crucial that internal controls, such as NATtrol™-treated microorganisms, are used in these PCR assays to avoid false-negative results and ensure accurate diagnosis of patients. NATtrol™ treatment renders microorganisms non-infectious while leaving them fully intact with their complete RNA or DNA genomes. Therefore, NATtrol™-treated microorganisms can be used in PCR as full-process internal controls that are spiked into patient samples and co-extracted and co-amplified within the sample. If the spiked NATtrol™ control returns expected results on the test, then the patient sample result can also be trusted. Here, we performed studies to validate the use of NATtrol™-treated MS2 virus as a universal full-process internal molecular control. In these studies, a quantitative, real-time, reverse-transcription PCR (qRT-PCR) assay was performed on the Roche LightCycler 480 instrument. Studies included working range validation, limit of detection, within-run precision, between-run precision, real-time stability, freeze-thaw (transport) stability, and open-vial (use-life) stability. All studies demonstrated the precision and stability of the MS2 NATtrol™ molecular control. / Thesis (BS) — Boston College, 2014. / Submitted to: Boston College. College of Arts and Sciences. / Discipline: College Honors Program. / Discipline: Biology Honors Program. / Discipline: Biology.

My research focuses on structures of the genomes of single-stranded RNA viruses. The first project is concerned with the sequence and secondary structure of HIV-1 RNA. Based on the secondary structure that Watts et al. determined, I performed a series of analysis and the results suggested that the abundance of Adenosines at the wobble position of the codons leads to an unusual structure with numerous unpaired nucleotides. The findings indicated how the virus balances evolutionary pressures on the genomic RNA secondary structure against pressures on the sequence of the viral proteins. The second project is the modeling of satellite tobacco mosaic virus (STMV). STMV is a T=1 icosahedral virus with a single piece of RNA that has 1058 nucleotides. X-ray crystallography studies of this RNA have revealed a structure containing 30 helices. The linkers between the helices, the possible structures at the interior of the icosahedron, and the sequence of the RNA were all missing in the crystal structure. To explore how the genome is organized within the protein capsid, I built a 3D model based on the RNA secondary structure predicted by Susan Schroeder. Being the first all-atom model of any virus, this model is highly correlated with the crystal structure; and the comparison with the in vitro structure of the same RNA supports the hypothesis that capsid protein plays an important role in RNA folding during assembly. The third project includes the modeling of bacteriophage MS2 (MS2) and the examination of the compactness of RNA in different viruses. MS2 is a T=3 RNA virus, and the cryo-EM studies have revealed a double-shell conformation of the genome. My final model of MS2 recaptures the double-shell structure of the RNA presented in the cryo-EM density. In addition, the predicted secondary structure that I used for the construction of the model shares a strong similarity with the in vitro structure determined in 1980s. This similarity contrasts with the striking difference between in vivo and in vitro RNA structures observed in STMV. Inspired by this finding, I examined the compactness of the RNA of several different viruses. The results strongly suggest that the RNAs of viruses requiring packaging signals have evolved to be structurally compact, which facilitates post-replicational RNA packaging. In contrast, viruses that do not depend on packaging signals probably adopt co-replicational RNA packaging.

This research aimed to address the knowledge gaps in the literature regarding the removal of waterborne pathogens (viruses and protozoa) by modified multistage slow sand filtration. In the current study, two pilot-scale multistage slow sand filtration systems were operated continuously for over two years. The pilot systems treated agricultural- and urban-impacted raw river water of variable quality with turbidity peaks over 300 NTU and seasonal cold temperatures <2°C. The first system (Pilot 1) consisted of two independent trains that included pre-ozonation, shallow-bed upflow gravel roughing filtration, and shallow-bed slow sand filtration. Pilot 1 was a pilot-scale version of an innovative, commercially available full-scale system. The second system (Pilot 2) included a full-depth upflow gravel roughing filter, a full-depth slow sand filter, and a second shallow-depth slow sand filter in series. The SSFs of both pilots were operated at high hydraulic loading rates (typically 0.4 m/h) at the upper limit of the literature recommended range (0.05 to 0.4 m/h). Both pilot systems provided excellent turbidity removal despite the high filtration rates. Effluent turbidity of all multistage SSF pilot systems were within the regulated effluent limits in Ontario for full-scale SSFs (below 1 NTU at least 95% of the time and never exceeded 3 NTU), despite raw water turbidity peaks over 100 NTU. The roughing filters contributed to approximately 60-80% of the full-train turbidity removal, compared to and 20-40% for the slow sand filters. On average, the second slow sand filter in pilot 2 provided almost no additional turbidity removal. The slow sand filter run lengths were short because of frequent high raw water turbidity, with about 50-80% of the runs in the range of 1-3 weeks. To prevent excessive SSF clogging and maintenance, filtration rates should be decreased during periods of high turbidity. Seven Cryptosporidium and Giardia challenge tests were conducted on the slow sand filters of both pilot systems at varying filtration rates (0.4 or 0.8 m/h), temperatures (2 to 25°C), and biological maturities (4 to 20 months). Removal of oocysts and cysts were good regardless of sand depth, hydraulic loading rate, and water temperature in the ranges tested. Average removals in the SSFs ranged from 2.6 to >4.4 logs for Cryptosporidium oocysts and ranged from >3.8 to >4.5 logs for Giardia cysts. This was consistent with findings in the literature, where oocyst and cyst removals of >4 logs have been reported. Cryptosporidium oocyst removals improved with increased biological maturity of the slow sand filters. At a water temperature of 2°C, average removal of oocysts and cysts were 3.9 and >4.5 logs, respectively, in a biologically mature SSF. Doubling the filtration rate from 0.4 to 0.8 m/h led to a marginal decrease in oocyst removals. Sand depths in the range tested (37-100 cm) had no major impact on oocyst and cyst removals, likely because they are removed primarily in the upper section of slow sand filter beds by straining. In general, good oocyst and cyst removals can be achieved using shallower slow sand filter bed depths and higher filtration rates than recommended in the literature. There are very few studies in the literature that quantify virus removal by slow sand filtration, especially at high filtration rates and shallow bed depths. There are no studies that report virus removal by slow sand filtration below 10°C. As such, 16 MS2 bacteriophage challenge tests were conducted at varying water temperatures (<2 to >20°C) and filtration rates (0.1 vs. 0.4 m/h) between February and June 2006 on biologically mature slow sand filters with varying bed depths (40 vs. 90 cm). Biologically mature roughing filters were also seeded with MS2. Average MS2 removals ranged from 0.2 to 2.2 logs in the SSFs and 0.1 to 0.2 logs in the RFs under all conditions tested. Virus removal by slow sand filtration was strongly dependant on hydraulic loading rate, sand depth, and water temperature. Virus removal was greater at a sand depth of 90 cm vs. 40 cm, at an HLR of 0.1 m/h vs. 0.4 m/h, and at warm (20-24°C) vs. cold (<2-10°C) water temperatures when sufficient warm water acclimation time was provided. Increased sand depth likely increased MS2 removal because of greater detention time for predation and greater contact opportunities for attachment to sand grains and biofilms. A lower HLR would also increase MS2 removal by increasing detention time, in addition to decreasing shear and promoting attachment to filter media and biofilms. Greater MS2 removal at warmer water temperatures was attributed to improved biological activity in the filters. Schmutzdecke scraping was found to have only a minor and short-term effect on MS2 removals. Virus removal can be optimized by providing deep SSF beds and operating at low filtration rates. Virus removal may be impaired in cold water, which could affect the viability of using SSF/MSF at northern climates if communities do not use disinfection or oxidation. As a stand-alone process, slow sand filtration (with or without roughing filtration) may not provide complete virus removal and should be combined with other treatment processes such as disinfection and oxidation to protect human health.

A comparison was made of bacteriophage MS2 RNA translation in infected Escherichia coli cells and in a defined cell-free system. A number of temperature-sensitive mutants were used as hosts for viral RNA translation at permissive and restrictive temperatures. The amount of viral coat protein synthesis was determined after gel electrophoresis of proteins from the cell lysates. These results were compared to those obtained with cell-free translation assays conducted with ribosomes isolated from the same mutants. Compared with control cells, a reduced activity in vivo and in vitro was found for each mutant examined at elevated temperatures. A good correlation between the two types of translational assays was observed. These findings are discussed in terms of the translational defects known to be a characteristic of some of these mutant strains.

<p>A series of experiments were carried out to gain a better understanding of the mechanisms governing the transport of biological and non-biological particles through single, saturated dolomite fractures at the laboratory scale. Fracture apertures and general roughness were characterized using hydraulic and conservative solute tracer experiments.</p> <p>The effects of particle size, surface characteristics and ionic strength of carrying solution were all evaluated. Particulate material studied included MS2, <em>E. coli</em> and two sizes of carboxylated microspheres. To elucidate the effect of ionic strength on particulate transport, the ionic strength of the carrying solution was altered during each experiment. All particulate experiments were completed at a specific discharge of 15 m/day to facilitate comparisons.</p> <p>Recovery of biological particulate material was found to be much less relative to the carboxylated microspheres, even though the energy profiles predicted similar interactions with the fracture surface. This suggests that the biological surface has a significant impact on retention within the fracture. Further, altering the ionic strength of the carrying solution did not spur significant elution of additional particulate material, regardless of surface characteristics. Therefore, it was determined that retention within the secondary energy minimum was negligible under these operating conditions.</p> <p>With respect to carboxylated microspheres, increased retention was observed within the less variable fracture. This suggests that increased variability within a fracture results in increased eddying within the aperture field. This eddying effectively reduces the aperture region available for particle transport, lessening the particle/fracture interaction. Overall, while mean residence times were similar, recovery of biological particles was poorly replicated by microspheres.</p> / Master of Applied Science (MASc)

Dans les dernières décennies, la plupart des pays du monde ont connu une pénurie d'eau et l’augmentation du taux de consommation. Aujourd'hui, tous les pays dans le monde essayent de trouver des alternatives pour remédier à cette pénurie. Une solution consiste en la réutilisation des eaux grises (GW) pour l'irrigation après traitement. Les GW correspondent aux eaux usées générée dans une maison à l'exception de l'eau des toilettes. Les risques associés à la réutilisation de ces eaux est la présence de microorganismes pathogènes qui peuvent infecter les humains, les animaux et les plantes. Dans cette thèse centrée sur l'étude de la survie des représentants d'agents pathogènes, comme E. coli, P. aeruginosa, et le bactériophage MS2 qui sont trouvés dans les eaux grises. Il a été étudié l’effet de quelques facteurs physico-chimiques tels que; température (6 ± 2,23 ± 2 et 42 ± 2 ° C), la salinité (1,75 and 3.5% de NaCl), de l'oxygène (aérobie et anaérobie), des éléments nutritifs (milieu riche et de milieux pauvres), la lumière avec la photocatalyse (lampes UV et visible) et filtre à sable lent (sable du désert égyptien et le sable piscine). Une combinaison de la température, la lumière du soleil et de haute photocatlysis sont principalement responsables de la baisse rapide des bactéries et du coliphage MS2. Le filtre à sable lent a une influence nettement moindre sur la survie des bactéries dans les eaux grises, mais il est efficace pour diminuer la turbidité et de la DCO. / In recent decades, most countries of the world have experienced a shortage of water and increase its rate of consumption. Today, every country in the world are interested in this problem by trying to find alternatives to address this shortage. One solution is reuse greywater (GW) for irrigation after treatment. GW is all water generated from Household except toilet water. The risks associated with the reuse of these waters are the presence of pathogens that can infect humans, animals and plants. In this thesis focused on studying treatment by slow sand filtration and the survival of representatives of pathogens, such as E. Coli, P. aeruginosa , E. Faecalis and Bacteriophage MS2 which could be found in the greywater. The study factors was a physico-chemicals factors such as; temperature (6±2,23±2,42±2°c), salinity (1.75 and 3.5% Nacl), oxygen (aerobic and anaerobic condition), nutrient ( rich media , 50%: 50% salt and poor media ), light with photocatalysis ( UV and Visible lights) and slow sand filter (Egyptian desert sand and swimming pool sand). A combination of high temperature, sunlight and photocatlysis are mainly responsible for the rapid decline of bacteria and MS2 coliphage. Slow sand filter have clearly less influence on the survival of bacteria in the greywater, but it effective to decline turbidity and COD for short times.

Diese Arbeit untersucht den Einsatz von keramischen Materialien in der Trinkwasseraufbereitung mittels Filtration und fokussiert dabei die Entfernung von Viren. Herkömmliche, auf Kieselgur basierende Tiefenfilter (Filterkerzen) mit Porengrößen im unteren Mikrometerbereich, werden hinsichtlich ihres Rückhaltevermögens gegenüber Kolloiden (Viren sowie Polystyrolpartikel) untersucht, um deren Einsatzfähigkeit in der Entfernung von Mikroorganismen im Allgemeinen abschätzen zu können. Ferner wird gezeigt, wie durch ein einfaches Verfahren solche Filter modifiziert werden können, um auch kleinste Viren mit ca. 30 nm Durchmessern aus dem Rohwasser zu entfernen. Die Zugabe von MgO während der Granulierungsstufe im Herstellungsprozess der Filterkerzen bewirkt eine erhebliche Verbesserung des Virenrückhalts bis zu über 99.9999%. Die experimentellen Ergebnisse wurden dabei mit theoretischen Modellen verglichen, um Aussagen über die Mechanismen der Virenentfernung treffen zu können.

Les différents rejets aqueux de types industriel, artisanal et/ou hospitalier, contiennent différents contaminants organiques ou inorganiques qu’il convient d’éliminer. Selon le type de l’industrie et de l’utilisation, ces rejets auront besoin de subir un ou plusieurs traitements. Il existe de nombreuses méthodes de traitement des eaux adaptées à chaque pollution et à chaque usage. Dans le cadre de ce travail, nous nous sommes intéressés à l’utilisation d’une méthode peu onéreuse qui met en jeu les ions ferriques, ions ferreux, oxygène moléculaire et la lumière solaire (Fe(III)/Fe(II)/O2/hν) pour induire la transformation de composés organiques appartenant à deux familles de pesticides : les sulfonylurées et les organophosphorés. L’objectif majeur de l’étude consiste à la compréhension du rôle des ions de fer(II) dans le processus photocatalytique largement reporté dans la littérature ainsi que d’identifier les principaux produits formés au cours du processus. L’étude de la dégradation des sulfonylurées par excitation UV du peroxyde a démontré, sans aucune surprise, une réelle efficacité du processus. La réaction met en jeu les radicaux hydroxyles qui ont été clairement mis en évidence et quantifiés sous irradiation continue et par photolyse laser. Le processus dépend de la concentration initiale du substrat, du pH et de la concentration du photoinducteur (H2O2). La présence dans le milieu de la plupart des ions inorganiques conduit à une inhibition partielle de la dégradation. Dans le cas des ions étudiés, l’ordre de la réactivité est SO42- > Cl- > NO3- > CO32- . Cet aspect est très important à considérer lorsqu’il s’agit de traiter des eaux par le procédé UV/H2O2 . Lors de l’étude du comportement photochimique du complexe [Fe(H2O)5(OH)]2+ sous excitation à 365 nm et en simulateur solaire, la principale espèce réactive mise en jeu est le radical hydroxyle. En présence de composés organiques, une dégradation totale a pu être obtenue et ceci même pour de faibles concentrations en complexe de fer(III) (1,0x10-6 mol L-1). Il y a donc une régénération in situ et sous irradiation du fer(III). L’ensemble des expériences entreprises a permis de montrer que la régénération met en jeu non seulement le fer(II) mais également l’oxygène. La présence simultanée du fer(III) à l’état de trace et du fer(II) joue un rôle clé. En effet, l’excitation du fer(III) permet la production d’état excités qui transfèrent l’énergie aux ions de fer(II). Ces derniers états excités de fer(II) réagissent avec l’oxygène moléculaire par un processus de transfert d’électrons pour générer du fer(III) et l’anion superoxyde. La solution se trouve ainsi de plus en plus enrichie en fer(III) au fur et à mesure de l’excitation lumineuse. Sur le plan analytique, nous avons utilisé la technique LC/MS et LC/ESI/MS2 pour appréhender la structure chimique des photoproduits formés par l’étude précise des processus de fragmentation. Parmi toutes les réactions habituelles du radical hydroxyl (hydroxylation du noyau aromatique, scission du pont sulfonylurée et déméthylation), nous avons montré que certaines sulfonylurées conduisent, en milieu légèrement acide, à un processus de scission du squelette triazinique. Une telle réaction a également pu être confirmée par des études théoriques au niveau B3LYP/6-31G (d,p). La présence simultanée d’un groupement methoxy et d’une amine secondaire adjacente au cycle triazine est une condition essentielle pour une telle ouverture. L’ouverture du cycle est une étape importante pour atteindre l’objectif de l’étude qui est d’obtenir la minéralisation des solutions et ainsi le traitement des rejets aqueux de types industriel, artisanal et/ou hospitalier. / Waste waters resulting from industrial and artisanal activities as well as from hospital discharges contain numerous toxic organic and inorganic contaminants that require efficient treatment. In the present work, we employed various combinations of ferric and ferrous ions, oxygen, hydrogen peroxide and sunlight (Fe(III)/Fe(II)/O2/hν) to induce the transformation of two pesticide families: sulfonylureas and organophosphorus. The main objective of the study was devoted to the role of iron(II) species in the whole transformation process and also to the elucidation of the generated byproducts. In a first step, we used the system H2O2/ hν as a preliminary process for the degradation of the pollutant. This allowed a complete and fast removal of sulfonylureas. The reaction mainly involves hydroxyl radicals that were identified and quantified by nanosecond laser photolysis technique. The process highly depends on the initial substrate concentration, pH and the concentration of the photoinductor (H2O2). The presence of inorganic ions that could be present in waste waters was shown to inhibit the degradation, in the following decreasing order: SO42- > Cl- > NO3- > CO32- . In a second step, the study of the photochemical behavior of the iron(III) aquacomplex, [Fe(H2O)5(OH)]2+, upon light excitation at 365 nm as well as by using a solar simulator also showed the generation of hydroxyl radical together with iron(II) species. A complete elimination of studied pesticides was obtained even at low concentrations of iron(III) complex (1,0x10-6 mol L-1), indicating the high efficiency of the process. To gain insight into the degradation mechanism, the evolution of iron species upon irradiation was investigated in the absence and in the presence of molecular oxygen. The results suggested that a regeneration mechanism of iron(III) occurs through two consecutives steps. First, the excitation of iron(III) in trace concentrations, leads to the formation of iron(II) excited states through energy transfer process followed an electron transfer process that involves molecular oxygen and iron(II) excited state. As a conclusion, the solution becomes more and more enriched by iron(III) via the light excitation and in the presence of oxygen revealing the photocatalytic behavior of [Fe(H2O)5(OH)]2+. Within this work, a special attention was also devoted to the identification of products formed during the above photocatalytic process. This was performed by using liquid chromatography coupled to tandem mass spectrometry LC/ESI/MS2. The close investigation of the fragmentation processes of the generated products, permitted the establishment of precise chemical structures. In addition to the classical degradation of sulfonylureas by hydroxyl radicals (hydroxylation of the aromatic ring, the scission of sulfonylurea bridge and demethylation) a ring opening of the triazine skeleton was also obtained. This was observed under acidic conditions and was clearly confirmed by theoretical studies at the B3LYP / 6-31G (d, p) level. This triazine scission was only obtained with sulfonylures that contain a methoxy group and a secondary amine adjacent to the triazine moiety. Such ring opening constitutes an important and fundamental step when decontamination or/and mineralization of waste waters are concerned.