The catalytic role of uranyl in formation of polycatechol complexes
© Halada et al 2011
Received: 2 November 2010
Accepted: 11 March 2011
Published: 11 March 2011
To better understand the association of contaminant uranium with natural organic matter (NOM) and the fate of uranium in ground water, spectroscopic studies of uranium complexation with catechol were conducted. Catechol provides a model for ubiquitous functional groups present in NOM. Liquid samples were analyzed using Raman, FTIR, and UV-Vis spectroscopy. Catechol was found to polymerize in presence of uranyl ions. Polymerization in presence of uranyl was compared to reactions in the presence of molybdate, another oxyion, and self polymerization of catechol at high pH. The effect of time and dissolved oxygen were also studied. It was found that oxygen was required for self-polymerization at elevated pH. The potential formation of phenoxy radicals as well as quinones was monitored. The benzene ring was found to be intact after polymerization. No evidence for formation of ether bonds was found, suggesting polymerization was due to formation of C-C bonds between catechol ligands. Uranyl was found to form outer sphere complexes with catechol at initial stages but over time (six months) polycatechol complexes were formed and precipitated from solution (forming humic-like material) while uranyl ions remained in solution. Our studies show that uranyl acts as a catalyst in catechol-polymerization.
Uranium is present in our environment due to its natural occurrence, mining, processing and subsequent use. Radionuclides from mill sites, nuclear facilities and waste disposal sites can be spread by air and groundwater which necessitates the study of uranium transport and reactions in the environment: a number of such studies have been conducted [1–8]. Many factors affect the speciation and transportation of uranium in soil and groundwater including minerals in soil, nature and amount of organic matter in soil, pH of soil and water, rate and direction of groundwater flow, and hydraulic gradient. Contaminant uranium in the subsurface has been found in very diverse forms including as uranyl phosphate, uranyl hydroxide, and an ill-defined uranyl organic phase at Fernald . In studies conducted at Oak Ridge National Laboratory, uranyl has been found to exist complexed with phosphates and carbonates, associated with iron and manganese phosphates , and complexed with soil organic matter .
Humic substances form the majority of natural organic matter (NOM) in soil. Humic substances are high molecular weight, naturally occurring complex aggregates of aliphatic and aromatic chains having a number of common functional groups. Humic substances interact with metal ions through functional groups, forming soluble complexes, precipitating metal ions by reduction or by ion exchange, modifying the sorption behavior of mineral surfaces towards metal ions and modifying colloidal particles containing metal ions . More than 40 binding sites for complexation have been reported for humic materials including carboxylate, carbonyl, polyphenolic and amine functional groups . Catechol (o-diphenol benzene) is the simplest aromatic molecule containing highly reactive diphenol groups similar to many larger polyphenols constituting humic material, which makes catechol an ideal candidate for study of metal ion association relevant to contaminant mobility in soils. Due to its common presence as a functional group in NOM, catechol is also an ideal candidate for the study of oxidative polymerization . Oxidative polymerization is an important process to understand because of its role in humic polymers originating from decomposition of plant residue .
In addition to the relevance of using catechol as a model ligand to understand reactions of mobile metal ions with subsurface organic constituents, catechol itself in the subsurface originates from both natural and man-made sources. It is produced in nature by bacterial degradation of plants and animals . Catechol and other phenolic compounds are produced by many chemical industries and need to be removed from wastewater discharged by those industries . While catalytic polymerization of catechol was first demonstrated by Ziechmann using silica , it has also been observed using alumina, FeO, MnO, Ag2O, soil, silver colloids  and various enzymes, including laccase , horseradish peroxidase and soybean peroxidase . These enzymes, along with an oxidizing agent (hydrogen peroxide/dissolved oxygen), oxidize phenols to the phenoxy radical. In turn, the generated phenoxy radicals associate to form dimers, trimers and polymers . Abiotic oxidative polymerization of phenolic compounds was investigated by Colarieti et al. al using soil samples, and it was established that both soil and dissolved oxygen are required for polymerization . These authors later formulated a three step mechanism for abiotic oxidation of catechol: (1) catechol is oxidized by metal oxide(Fe and Mn oxides) and the metal oxide is reduced (2) complexation occurs between the reduced metal and remaining catechol, and (3) the metal-catechol complex is oxidized by dissolved oxygen to form polymers .
In this study we have investigated uranyl (UO22+) interactions with catechol using spectroscopic techniques including Raman, FTIR and UV-vis spectroscopies. Catechol was found to polymerize in the presence of uranyl. Catechol polymerization was further investigated for effects of pH and dissolved oxygen and presence of other oxyions. Molybdate was used for comparison as it is well known oxidizer, and molybdenum is a known catalyst for benzene hydroxylation . Moreover, molybdenum occurs naturally with uranium and is present in the form of MoO42- in leach solutions generated during hydrometallurgical extraction of uranium . Molybdenum is also present in spent fuel rods formed by fission of uranium and beta decay of niobium, where it is found that Mo6+ converts to MoO22+ under oxidizing condition with an ionic potential similar to UO22+ . For these reasons as well as the fact that molybdenum itself is a contaminant in groundwater makes molybdate an ideal candidate for comparison with uranyl.
2.1 Synthesis of complexes
0.1M aqueous solutions of catechol (o-dihydroxybenzene, Aldrich chemical Corp.), uranyl nitrate(Analar, BDH Chemicals Ltd.) and sodium molybdate(Aldrich Chemical Corp.) were prepared by dissolution in DI (>18MΩ/cm) water. To obtain complexes, catechol was added to uranyl nitrate and sodium molybdate in 1:1 volume ratios. All the solutions as well as 1:1 molar ratio complexes were adjusted to 2, 4, 6, 8, 10 and 12 pH using 1M and 0.1M NaOH and HCl solutions. The pHs of solution were measured using a Corning Scholar 425 pH meter. Solutions and complexes were analyzed using UV-Vis, Raman and IR-ATR spectroscopy. Spectra of solutions of uranyl nitrate and sodium molybdate at various pH were taken before spectra of uranyl-catechol and catechol-molybdate to distinguish effects of complexation from the effect of pH change.
A Nicolet Model Magna 760 FTIR spectrometer with a ZnSe ATR crystal was used for analysis. Solutions containing complexes were placed on the crystal (in their liquid state). A 4 cm-1 resolution was used and 256 scans were averaged to improve the signal-to-noise ratio. The range selected for data acquisition was 3000-900 cm-1 (below 900 cm-1 noise was too high for meaningful signal to be observed). DI water (>18MΩ/cm) was chosen as background to minimize signal from water peaks during data collection.
A Nicolet Almega dispersive Raman spectrometer with a 785 nm laser source was used for analysis. Samples were put on a gold slide as droplets and the Raman microscope was focused at the gold-solution interface. Data from averaging 256 scans in the 3444-108 cm-1 range was collected. OMNIC for Nicolet Almega software version 7.3 was used to process data.
UV-Vis measurements were taken using an Ocean Optics S2000 spectrometer and OOIBase32 operating software. For UV-Vis measurements 1 mM samples were used; deionized water was used as reference spectrum. Spectra were collected with 80 mSec integration time with an average of 10 measurements.
For anaerobic UV-Vis measurements 1 mM catechol solution was deaerated by bubbling nitrogen through the solution for four hours. NaOH pellets were then added to solution until pH was greater than 12 while the solution continued to be deaerated with nitrogen. This anaerobic catechol solution at high pH was then transferred to a quartz cuvette and which remained capped for the initial measurement: for subsequent readings the cap was removed to allow air to interact with the solution.
3. Results and discussion
3.1 Impact of pH on uranyl nitrate and sodium molybdate
3.2 Polymerization of Catechol at Elevated pH
3.3 Catechol complexes in the presence of uranyl and molybdate
By visual observation it appeared that sodium molybdate had a similar and more intense effect on catechol than uranyl nitrate, as color change was observed even at pH 2 in fresh solution (as opposed to the requirement for a pH 6 for the uranyl-catechol solution). Molybdate is capable of catalyzing polymerization at even more acidic pH due to its high affinity for aromatic o-dihydroxy compounds  as shown by the FTIR spectrum of the molybdate/catechol solution. At pH 6 (Figure 10), the substituted benzene ring intensity at 1483 cm-1 increased accompanied by a larger increase in the C-O band at 1264 cm-1 than in the case of uranyl association with catechol at pH 6. The results indicate that oxygen substitution is much faster in presence of molybdate as opposed to uranyl at acidic pH. In the Raman spectrum (Figure 11) from the molybdate/catechol solution, C-H bands were not present at any pH, and the C = C peak was shifted to 1563 cm-1 showing substitution and conjugation. The peak associated with Mo = O stretching in molybdate was also shifted from 900 to 932 cm-1 showing evidence of complexation with catechol.
In all cases, whether by pH-induced polymerization of pure catechol solution or whether catalyzed by uranyl or molybdate ions at lower pH, it seems the mechanism of catechol polymerization is by formation of C-C bonds between benzene rings and not by C-O-C bond formation, as characteristic peaks of benzyl ether1090 cm-1 were not observed in any case. Polymerization is associated with a high degree of substitution in the benzene ring as proposed by Arana et al.  and with formation of quinones . No polymerization was observed under anaerobic conditions, which implies that substitution takes place before polymerization. Formation of quinones and substitution of H by OH in the benzene ring may be facilitated by an alkaline environment.
Raman spectra of six month old uranyl/catechol solution were obtained to investigate the effect of time on complexation. All the characteristic peaks of polymerization of catechol were observed even at pH as low as 2 (Figure 11), whereas a pH of 6 was required for immediate polymerization. Polycatechol formed was found to have precipitated out of solution, likely forming humic-like material. No uranium was found in the precipitate; all the uranyl remained in solution after the polymerization was complete. Hence the uranyl ion in solution acts as a catalyst for formation of polycatechol over time (even under quite acidic conditions) by complex formation with oxygen from hydroxyl and quinone groups.
While further study is needed for developing accurate models of the kinetics of long term uranyl association with aromatic molecules with phenolic ligands, this result has a number of significant implications. These include (a) understanding uranium sorption and transportation in surface and some subsurface environments, (b) optimizing the operation of any remediation process which either uses organic ligands or which is used to remove contaminant uranium from groundwater containing natural or pollutant organic material, and (c) for understanding the humification process through oxidative coupling of phenols, as this result shows that uranyl ion can act as a catalyst in the process of polymerization with complexation between catechol ligands and uranyl acting as an intermediate step.
This work has been supported by U.S. Department of Energy Office of Science Environmental Management Science Program (EMSP), contract number DEFG0204ER63729 and the Center for Environmental Molecular Science, (CEMS) funded by the National Science Foundation, contract number CHE0221934.
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