Conducting polymers have been extensively investigated in a wide range of applications due to their ability to achieve near metallic conductivity while possessing the flexibility and processability of traditional polymers. However, interchain and solid-state effects have made direct investigation of the polymer systems difficult. A series of systematically varied model compounds have been designed to provide detailed information about through-chain charge transport in well-defined oligothiophenes. Our design incorporates two metal binding pockets at either end of an oligothiophene bridge to investigate the interaction of redox centers and charge transport properties between conducting polymers and bound transition metal centers. Synthesis, characterization, electrochemistry, and detailed EPR investigations of this new series of oligothiophene model compounds and the analogous mononuclear compounds will be discussed herein. Conjugated polymer matrices possess a large number of available oxidation states making them an attractive choice for use as redox-active ligands. This variety of oxidation states offers a means to easily tune the amount of electron density on a metal center and consequently affect the binding of an additional ligand. Our approach utilizes conducting metallopolymers with metal complexes synthetically incorporated directly into the conducting polymer backbone. The redox-dependent properties of this class of materials and their development as small molecule storage and delivery systems have been explored utilizing a variety of novel electropolymerizable transition metal complexes. The design, synthesis, characterization, and redox-affected properties of the monomers, corresponding conducting metallopolymers, and model complexes are discussed. The tub-shaped dibenzo[a,e]cyclooctatetraene molecule undergoes a large change in geometry upon reduction to form the planar aromatic species. Herein, we seek to prepare and investigate a supramolecular assembly utilizing this redox-active molecule. In contrast to electrochemically active frameworks where redox changes occur at the metal centers, incorporation of a functionalized dibenzo[a,e]cyclooctatetraene ligand into an assembly has the potential to result in a redox-active framework. Not only would the redox-activity occur at the organic bridge, but reduction of the system should result in a large geometry change. / text

The synthesis of diiron thiolate complexes was carried out using two ligands that were expected to furnish improved catalytic activity, solubility in water, and stability to the metal complexes. The water-soluble phosphine 1,3,5-triaza-7- phosphaadamantane, PTA, coordinates to the Fe centers forming the disubstituted complex (m-pdt)[Fe(CO)2PTA]2, which presents one PTA in each iron in a transoid arrangement. Substitution of one CO ligand in the (m-pdt)[Fe(CO)3]2 parent complex forms the asymmetric (m-pdt)[Fe(CO)3][Fe(CO)2PTA]. Enhanced water solubility was achieved through reactions with electrophiles, H+ and CH3 +, which reacted with the N on the PTA ligand forming the protonated and methylated derivatives, respectively. The 1,3-bis(2,4,6-trimethylphenyl)imidazol-2-ylidene), IMes, was reacted with (m-pdt)[Fe(CO)3]2 yielding the asymmetric (m-pdt)[Fe(CO)3][Fe(CO)2IMes], an electron rich, air stable complex that does not show reactivity with H+. Electrocatalytic production of hydrogen was studied for the all-CO, bis-PMe3, mono- and di-PTA FeIFeI complexes, as well as the PTA-protonated and -methylated derivatives. The all-CO species produce H2, in the presence of the weak HOAc, at their second reduction event, FeIFe0 ?? Fe0Fe0, that occurs at ca. ??1.9 V, through an EECC mechanism. The mono- and di-substituted phosphine complexes present electrocatalytic production of H2 from the Fe0FeI redox state; this reduction takes place at ??1.54 V for (m-pdt)[Fe(CO)3][Fe(CO)2PTA], and at ca. ??1.8 for the disubstituted PMe3 and PTA derivatives. A positive charge on the starting complex does not have an effect on the production of H2. It was found that the protonated and methylated derivatives are not the catalytic species for H2 production. At their first reduction event the neutral precursor forms, and catalysis occurs from the FeIFeI complex in all cases. The possibility of enhanced catalytic activity in the presence of H2 O was explored by conducting electrochemical experiments in the mixed CH3CN:H2O solvent system for the PTA-substituted complexes. The reduction potential of the catalytic peak is shifted to more positive values by the presence of H2 O. The cyclic voltammogram of {(m-pdt)[Fe(CO)2(PTA?? H)]2}2+ in CH3CN:H2O 3:1 shows the reduction of a more easily reduced species in the return scan. This curve-crossing event provides evidence for the (h2-H2)FeII intermediate proposed in the ECCE mechanism.

Biomimetic catalysis is an important research field, as a better understanding of nature´s powerful toolbox for the conversion of molecules can lead to technological progress. [FeFe]-hydrogenases are very efficient catalysts for hydrogen production. These enzymes play a crucial role in the metabolism of green algae and certain cyanobacteria. Their active site consists of a diiron complex that is embedded in an interactive protein matrix. In this thesis, two pathways for mimicking the outer coordination sphere effects resulting from the protein matrix are explored. The first is the construction of model complexes containing phosphine ligands that are coordinated to the iron center as well as covalently linked to the bridging ligand of the complex. The effect of such linkers is an increased energy barrier for the rotation of the Fe(CO2)(PL3)-subunit, which potentially could stabilize a terminal hydride that is an important intermediate in the proton reduction cycle. The second pathway follows the incorporation of [FeFe]-hydrogenase active site model complexes into metal-organic frameworks (MOFs). Resulting MOF-catalysts exhibit increased photocatalytic activity compared to homogenous references due to a stabilizing effect on catalytic intermediates by the surrounding framework. Catalyst accessibility within the MOF and the influence of the framework on chemical reactivity are examined in the work presented. Furthermore, an initial step towards application of MOF-catalysts in a device was made by interfacing them with electrodes. The work of this thesis highlights strategies for the improvement of biomimetic model catalysts and the knowledge gained can be transferred to other systems mimicking the function of enzymes.

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.