Le motif biaryl contenant la pyridine représente une structure omniprésente dans la chimie organique et médicinale. Ainsi, le développement de méthodes fiables de synthèse est continuellement désiré. Traditionnellement, les cycles azotés biarylés sont efficacement synthétisés par des réactions de couplage croisé catalytique. Cependant, la pyridine peut être difficilement fonctionnalisée en position C-2 compte tenu de sa déficience en électrons. Cette propriété limite son utilisation en tant que partenaire nucléophile dans les réactions de couplage croisé. Par exemple, dans le couplage de Suzuki-Miyaura, l’acide 2-pyridyle boronique est connu pour son instabilité. À l’inverse, les organométalliques du 2-pyridyle sont peu réactifs pour faire des réactions de substitution aromatique électrophile. La synthèse des pyridines 2-substituées est par conséquent un défi qui reste difficile à relever. La première partie de ce mémoire est consacrée au développement récent des méthodes pour résoudre les problèmes de couplage avec des nucléophiles 2-pyridyles. En particulier, les approches classiques comme le couplage modifié de Suzuki-Miyaura, l’activation de liaison C-H des composés pyridinium N-activés, et l’arylation directe du cycle pyridine sont présentées. De plus, les approches alternatives qui utilisent la partie pyridine comme partenaire électrophile dans la réaction couplage avec les réactifs organométalliques sont également discutées. Dans la deuxième partie de ce mémoire, une méthode de couplage croisée entre des esters de sulfonate de 2-pyridyles et des organolithiens est rapportée. Une variété de pyridines 2-substituées a été synthétisées avec succès en faisant réagir des sulfonates de pyridine avec des organolithiens (aryl, alkane, heteroaryle lithium) à basse température. La méthode permet également de s’affranchir de l’utilisation d’un quelconque métal de transition. Des études mécanistiques montrent que le processus impliquant les composés lithiés s’apparente à une réaction de substitution nucléophile aromatique. Cependant, le mécanisme diffère lorsque la réaction met en jeu des réactifs de Grignard, où un processus de couplage entre deux ligands d’un intermédiaire σ-sulfurane peut être impliqué. / Biaryl compounds containing the pyridine moiety represent a ubiquitous structure in both organic and medicinal chemistry. Therefore, finding new and reliable approaches for their synthesis is still of interest. Traditionally, azine containing biaryls are efficiently synthesized via transition-metal catalyzed cross-coupling reactions. However, due to its π-deficient nature, pyridine cannot be easily functionalized at the C-2 position to serve as nucleophile partner. For examples, in the Suzuki-Miyaura cross-coupling reaction, 2-pyridyl boronates are well known for their instability. 2-Pyridyl organometallics undergo electrophilic aromatic substitution poorly. Thus, the synthesis of 2-substituted pyridines remains a challenging task. The first part of the thesis focuses on the recent methods to address the coupling issues of 2-pyridyl nucleophiles in cross-coupling reactions. Of note, the classical methods including Suzuki-Miyaura cross-coupling reactions, C-H activation of N-activated pyridinium species, and direct coupling reaction of pyridine are presented. Alternative approaches using the pyridine moiety as an electrophilic entity in the coupling with organometallic reagents are also discussed. In the second part of the thesis, a transition metal-free desulfinative cross-coupling reaction of 2-pyridyl sulfonates with organolithium reagents is reported. A variety of 2-substituted pyridines were successfully synthesized in good yields, by treatment of neopentyl 2-pyridyl sulfonates and phenyl 2-pyridyl sulfonate with aryl, alkyl, and heteroaryl-lithium reagents at low temperature. Mechanistic studies showed that the coupling reaction with lithium reagents undergoes an SNAr pathway. However, a ligand coupling process of a σ-sulfurane intermediate may be involved in the reaction with Grignard reagents to form the biaryl.

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Desenvolveu-se um método espectrofotométrico para determinação de íons Cu(II), Fe(II) e Fe(III) com o reagente cromogênico di-2-piridil cetona benzoilhidrazona (DPKBH), em condições estacionárias e em fluxo. Fez-se a caracterização estrutural e estequiométrica do complexo de Cu(II) com DPKBH usando-se técnicas espectroscópicas de infravermelho e massas, além de análise térmica e elementar. Estudou-se, ainda, a estequiometria dos complexos de Fe(II) e Fe(III) com DPKBH utilizando espectrometria de massas com ionização por electrospray. Desenvolveu-se, preliminarmente, um método espectrofotométrico para a determinação de íons Cu(II) com DPKBH e aplicou-se em amostras de aguardente. Posteriormente, adaptou-se para análise por injeção em fluxo, utilizando-se injetor comutador manual. Em seguida, desenvolveu-se em condições estacionárias um método espectrofotométrico para determinação de Fe(II) e Fe(III) e Cu(II) em uma mesma amostra, com o uso de agentes mascarantes. Fez-se também a adaptação do método para análise em fluxo empregando multicomutação e amostragem binária. Finalmente, determinou-se a concentração de íons Cu(II), Fe(II) e Fe(III) em amostras sintéticas e Cu(II) e ferro total em amostras de sedimento coletadas no reservatório de Guarapiranga. Os resultados obtidos foram comparados com o método de referência de ICP-OES, apresentando concordância para um nível de confiança de 95% da média. / A spectrophotometric method was developed to the determination of Cu(II), Fe(II) and Fe(III) with the chromogenic reagent di-2pyridyl ketone benzoylhydrazone (DPKBH) in stationary conditions as a flow injection process. The structural characterization and the stoichiometry of Cu(II)/DPKBH complex were achieved using infrared spectrometry, mass spectrometry, thermal and elementar analysis. Toe stoichiometry of the Fe(II) and Fe(III) complexes with DPKBH was studied by electrospray ionization mass spectrometry. The spectrophotometric method for the determination of Cu(II) with DPKBH was developed in stationary conditions and, after this, it was adapted to flow injection analysis, using a manual commutator. Subsequently, a spectrophotometric method was developed to determine Fe(II), Fe(III) and Cu(II) in the same sample, in stationary conditions, using masking reagents. This method was also adapted to flow injection analysis, using multicommutation and binary sampling. Finally, Cu(II), Fe(II) and Fe(III) were determined in sediments from Guarapiranga reservoir. The obtained results were compared with the ICP-OES standard methods, showing a good agreement into a 95% confidence level (t-test).

Desenvolveu-se um método espectrofotométrico para determinação de íons Cu(II), Fe(II) e Fe(III) com o reagente cromogênico di-2-piridil cetona benzoilhidrazona (DPKBH), em condições estacionárias e em fluxo. Fez-se a caracterização estrutural e estequiométrica do complexo de Cu(II) com DPKBH usando-se técnicas espectroscópicas de infravermelho e massas, além de análise térmica e elementar. Estudou-se, ainda, a estequiometria dos complexos de Fe(II) e Fe(III) com DPKBH utilizando espectrometria de massas com ionização por electrospray. Desenvolveu-se, preliminarmente, um método espectrofotométrico para a determinação de íons Cu(II) com DPKBH e aplicou-se em amostras de aguardente. Posteriormente, adaptou-se para análise por injeção em fluxo, utilizando-se injetor comutador manual. Em seguida, desenvolveu-se em condições estacionárias um método espectrofotométrico para determinação de Fe(II) e Fe(III) e Cu(II) em uma mesma amostra, com o uso de agentes mascarantes. Fez-se também a adaptação do método para análise em fluxo empregando multicomutação e amostragem binária. Finalmente, determinou-se a concentração de íons Cu(II), Fe(II) e Fe(III) em amostras sintéticas e Cu(II) e ferro total em amostras de sedimento coletadas no reservatório de Guarapiranga. Os resultados obtidos foram comparados com o método de referência de ICP-OES, apresentando concordância para um nível de confiança de 95% da média. / A spectrophotometric method was developed to the determination of Cu(II), Fe(II) and Fe(III) with the chromogenic reagent di-2pyridyl ketone benzoylhydrazone (DPKBH) in stationary conditions as a flow injection process. The structural characterization and the stoichiometry of Cu(II)/DPKBH complex were achieved using infrared spectrometry, mass spectrometry, thermal and elementar analysis. Toe stoichiometry of the Fe(II) and Fe(III) complexes with DPKBH was studied by electrospray ionization mass spectrometry. The spectrophotometric method for the determination of Cu(II) with DPKBH was developed in stationary conditions and, after this, it was adapted to flow injection analysis, using a manual commutator. Subsequently, a spectrophotometric method was developed to determine Fe(II), Fe(III) and Cu(II) in the same sample, in stationary conditions, using masking reagents. This method was also adapted to flow injection analysis, using multicommutation and binary sampling. Finally, Cu(II), Fe(II) and Fe(III) were determined in sediments from Guarapiranga reservoir. The obtained results were compared with the ICP-OES standard methods, showing a good agreement into a 95% confidence level (t-test).

Εξαιτίας των πολλών εφαρμογών του καδμίου στη βιομηχανία αλλά και των ταυτόχρονα τοξικών ιδιοτήτων του στα έμβια όντα, η απομάκρυνση του Cd(II) από υδατικά απόβλητα είναι σήμερα ένα ενδιαφέρον θέμα έρευνας στην Περιβαλλοντική Χημεία. Η υγρή εκχύλιση (εκχύλιση με διαλύτη) είναι μια αποτελεσματική μέθοδος για την απομάκρυνση του Cd(II) από διαλύματα που περιέχουν ιόντα χλωριδίων, θειικά ή φωσφορικά διαλύματα. Κατά την υγρή εκχύλιση το μεταλλοϊόν συμπλοκοποιείται με έναν οργανικό υποκαταστάτη σχηματίζοντας ένα χημικό είδος που μεταφέρεται από την υδατική στην οργανική φάση σε ένα διφασικό σύστημα. Αναφέρθηκε πρόσφατα ότι το κάδμιο(II) μπορεί να εκχυλιστεί από μέσα που περιέχουν ιόντα χλωριδίων ή ιόντα χλωριδίων/νιτρικών χρησιμοποιώντας δύο 2-πυρίδυλο κετονοξίμες, και συγκεκριμένα την 1-(2-πυριδυλο)-δεκατρια-1-όνη οξίμη (2PC12) και την 1-(2-πυριδυλο)-δεκαπεντε-1-όνη (2PC14), ως μέσα εκχύλισης. Ο στόχος αυτής της εργασίας είναι να μοντελοποιήσει την φύση των χημικών ειδών που σχηματίζονται κατα την διαδικασία της υγρής εκχύλισης του Cd(II) χρησιμοποιώντας 2-πυρίδυλο κετονοξίμες ως μέσα εκχύλισης. Έτσι μελετήσαμε τις αντιδράσεις διαφόρων πηγών Cd(II) με 2-πυρίδυλο οξίμες ως υποκαταστάτες (Σχήμα I). Οι υποκαταστάτες που χρησιμοποιήθηκαν ήταν οι 2-πυριδίνη αλδοξίμη (paoH), μέθυλο 2-πυρίδυλο κετονοξίμη (mepaoH), φαίνυλο 2-πυρίδυλο κετονοξίμη (phpaoH) και πυριδινη-2-αμιδοξίμη (ampaoH). Η συστηματική συνθετική μας διερεύνηση οδήγησε στα προϊόντα [CdI2(paoH)2] (1), [Cd(NO3)2(paoH)2] (2), [Cd(NO3)(H2O)(paoH)2](NO3) (3), [Cd(paoH)3](ClO4)2 (4), [Cd(pao)2(paoH)2] (5), [CdI2(mepaoH)2] (6), [Cd(NO3)2(mepaoH)2] (7), [Cd(O2CMe)2(mepaoH)2] (8), [CdCl2(phpaoH)2] (9), [Cd4Br8(phpaoH)4]n (10), [CdI2(phpaoH)2] (11), [Cd(NO3)2(phpaoH)2] (12), [Cd2(Ο2CMe)4(phpaoH)2]n (13), [CdCl2(ampaoH)2] (14), [CdBr2(ampaoH)2] (15), [CdI2(ampaoH)2] (16) και [Cd(NO3)2(ampaoH)2] (17). Οι μοριακές και κρυσταλλικές δομές των συμπλόκων προσδιορίστηκαν με κρυσταλλογραφία ακτίνων Χ επί μονοκρυστάλλων των ενώσεων (Σχήμα II). Τα σύμπλοκα χαρακτηρίσθηκαν με στοιχειακές αναλύσεις και διάφορες φασματοσκοπικές μεθόδους (IR, Raman, NMR, Φωτοφωταύγεια). Τα φασματοσκοπικά δεδομένα μελετήθηκαν σε σχέση με τις γνωστές δομές των ενώσεων. Tα περισσότερα σύμπλοκα είναι μονοπυρηνικά. Οι ενώσεις 10 και 13 είναι 1D πολυμερή ένταξης. Τα μόρια paoH, mepaoH, phpaoH και ampaoH συμπεριφέρονται ως Ν(πυρίδυλο), Ν(οξιμικό)-διδοντικοί χηλικοί υποκαταστάτες. Τα ιόντα CdII στα σύμπλοκα είναι 6-, 7- και 8-ενταγμένα. Οι κρυσταλλικές δομές των περισσοτέρων συμπλόκων σταθεροποιούνται από δεσμούς Η. Τα περισσότερα σύμπλοκα διασπώνται στο DMSO, όπως προκύπτει από τα 1Η ΝΜR φάσματά τους. Τα σύμπλοκα 9, 14 και 12, 17 μοντελοποιούν τα χημικά είδη [CdCl2(μέσο εκχύλισης)2] και [Cd(NO3)2(μέσο εκχύλισης)2] που έχει προταθεί ότι σχηματίζονται κατά τη διαδικασία της υγρής εκχύλισης του Cd(II) με τη χρησιμοποίηση των 2PC12 και 2PC14 σε διαλύματα χλωριδίων και χλωριδίων/νιτρικών, αντίστοιχα. Με επιφύλαξη προτείνουμε ότι η ικανότητα των 2-πυρίδυλο κετοξιμών να απομακρύνουν Cd(II) από υδατικά απόβλητα οφείλεται στην ισχυρά χηλική φύση των μέσων εκχύλισης. / Because of the wide application of cadmium in various industrial facilities and its simultaneous toxic properties for organisms, the removal of Cd(II) from wastewater is a currently hot topic in environmental chemistry. Solvent extraction is an efficient method from the removal of Cd(II) from chloride, sulfate or phosphate solutions. Solvent extraction occurs when a metal ion is coordinated to an organic ligand to form a species that is transferred from the aqueous to the organic phase in a two-phase system. It has recently been reported that cadmium(II) can be extracted from chloride or chloride/nitrate media using two 2-pyridyl ketoximes, namely 1-(2-pyridyl)-trideca-1-one oxime (2PC12) and 1-(2-pyridyl)-pentadeca-one oxime (2PC14), as extractants and chloroform or hydracarbons as organic solvents [A. Parus, K. Wieszczycka, A. Olszanowski (2011) Hydrometallurgy, 105, 284]. The goal of this work is to model the nature of the chemical species that are formed during the solvent extraction of Cd(II) using 2-pyridyl ketoximes as extractants. Thus, we studied the reactions of various Cd(II) sources with 2-pyridyl oximes as ligands (Scheme I). The ligands used were 2-pyridine aldoxime (paoH), methyl 2-pyridyl ketoxime (mepaoH), phenyl 2-pyridyl ketoxime (phpaoH) and pyridine-2-amidoxime (ampaoH). Our systematic investigations gave the products [CdI2(paoH)2] (1), [Cd(NO3)2(paoH)2] (2), [Cd(NO3)(H2O)(paoH)2](NO3) (3), [Cd(paoH)3](ClO4)2 (4), [Cd(pao)2(paoH)2] (5), [CdI2(mepaoH)2] (6), [Cd(NO3)2(mepaoH)2] (7), [Cd(O2CMe)2(mepaoH)2] (8), [CdCl2(phpaoH)2] (9), [Cd4Br8(phpaoH)4]n (10), [CdI2(phpaoH)2] (11), [Cd(NO3)2(phpaoH)2] (12), [Cd2(Ο2CMe)4(phpaoH)2]n (13), [CdCl2(ampaoH)2] (14), [CdBr2(ampaoH)2] (15), [CdI2(ampaoH)2] (16) and [Cd(NO3)2(ampaoH)2] (17). The molecular and crystal structures of the complexes have been determined by single-crystal, X-ray crystallography (Scheme II). The complexes have been characterized by elemental analyses and various spectroscopic techniques (IR, Raman, NMR, Photoluminescence). The spectroscopic data are discussed in terms of the known structures. Most complexes are mononuclear. Compounds 10 and 13 are 1D coordination polymers. The paoH, mepaoH, phpaoH and ampaoH molecules behave as N(pyridyl), N(oxime)–bidentate chelating ligands. The CdII ions in the complexes are 6-, 7- and 8-coordinate. The crystal structures of most complexes are stabilized by H bonds. Most of the complexes decompose in DMSO, as evidenced by 1H NMR spectroscopy. Complexes 9, 14 and 12, 17 model the chemical species [CdCl2(extractant)2] and [Cd(NO3)2(extractant)2] that have been proposed to form during the solvent extraction of Cd(II) using 2PC12 and 2PC14 in chloride and dilute chloride/concentrated nitrate solutions, respectively. We tentatively propose that the ability of 2-pyridyl ketoximes to remove Cd(II) from wastewater is due to the strongly chelating nature of the extractants.