This article appeared in a journal published by Elsevier. The attached copy is furnished to the author for internal non-commercial research and education use, including for instruction at the authors institution and sharing with colleagues. Other uses, including reproduction and distribution, or selling or licensing copies, or posting to personal, institutional or third party websites are prohibited. In most cases authors are permitted to post their version of the article (e.g. in Word or Tex form) to their personal website or institutional repository. Authors requiring further information regarding Elsevier’s archiving and manuscript policies are encouraged to visit: http://www.elsevier.com/copyright Author's personal copy Chemosphere 87 (2012) 644–648 Contents lists available at SciVerse ScienceDirect Chemosphere journal homepage: www.elsevier.com/locate/chemosphere Short Communication Kinetics of the oxidation of sucralose and related carbohydrates by ferrate(VI) Virender K. Sharma ⇑, Mary Sohn, George A.K. Anquandah, Nasri Nesnas Department of Chemistry and Center of Ferrate Excellence, Florida Institute of Technology, 150 West University Boulevard, Melbourne, FL 32901, USA a r t i c l e i n f o Article history: Received 20 August 2011 Received in revised form 21 December 2011 Accepted 13 January 2012 Available online 15 February 2012 Keywords: Ferrate Rates Saccharides Carbohydrates Radicals Remediation a b s t r a c t The kinetics of the oxidation of sucralose, an emerging contaminant, and related monosaccharides and disaccharides by ferrate(VI) (Fe(VI)) were studied as a function of pH (6.5–10.1) at 25 °C. Reducing sugars (glucose, fructose, and maltose) reacted faster with Fe(VI) than did the non-reducing sugar sucrose or its chlorinated derivative, sucralose. Second-order rate constants of the reactions of Fe(VI) with sucralose and disaccharides decreased with an increase in pH. The pH dependence was modeled by considering 2 the reactivity of species of Fe(VI), (HFeO 4 and FeO4 ) with the studied substrates. Second-order rate constants for the reaction of Fe(VI) with monosaccharides displayed an unusual variation with pH and were explained by considering the involvement of hydroxide in catalyzing the ring opening of the cyclic form of the carbohydrate at increased pH. The rate constants for the reactions of carbohydrates with Fe(VI) were compared with those for other oxidant species used in water treatment and were briefly discussed. Ó 2012 Elsevier Ltd. All rights reserved. 1. Introduction Sucralose (4-chloro-4-deoxy-a-D-galactopyranosyl-1,6-dichloro1,6-dideoxy-b-D-fructofuranoside) is a chlorinated derivative of the disaccharide sucrose; in which three hydroxyl groups are replaced by chlorine atoms (Fig. 1). Sucralose is about 600 times sweeter by weight than sucrose (Wiet and Miller, 1997). The use of sucralose is widespread in over 80 countries and it is present in more than 4000 different products (Torres et al., 2011). For example, sucralose is being used as a non-nutritive sweetener in the sugar substitute known commercially as SPLENDA, which contains 1% sucralose and 99% maltodextrin and dextrose in the granulated product. The human consumption of sucralose has been found safe (Grotz and Munro, 2009), however, it is also considered an emerging contaminant due to its persistence in the environment, with a half-life of up to several years (Lubick, 2008; Richardson and Ternes, 2011). Recently, several studies have determined sucralose concentrations up to 1 lg L1 in river, coastal, and marine waters of North America and Europe (Loos et al., 2009; Lubick, 2009; Mead et al., 2009). The input of sucralose to the environment is likely through municipal wastewater treatment effluents (Torres et al., 2011). The present study thus sought the removal of sucralose by ferrate(VI) (FeO2 4 , Fe(VI)) in order to minimize release of this emerging contaminant to aquatic ecosystems. ⇑ Corresponding author. Tel.: +1 321 674 7310; fax: +1 321 674 8951. E-mail address: vsharma@fit.edu (V.K. Sharma). 0045-6535/$ - see front matter Ó 2012 Elsevier Ltd. All rights reserved. doi:10.1016/j.chemosphere.2012.01.019 There have been several studies on the novel properties of Fe(VI) as an oxidant, disinfectant, and coagulant (Eng et al., 2006; Jiang, 2007; Lee et al., 2009; Sharma et al., 2009; Sharma, 2010a; Sharma et al., 2010), but no data has been published on rate constants for the oxidation of sucralose or any carbohydrate by Fe(VI). In this paper, the kinetics of the reactions between Fe(VI) with sucralose and carbohydrates were determined as a function of pH (6.5–10.1) at 25 °C. Structures of the selected carbohydrates are shown in Fig. 1. The kinetic study of sucrose provided an interesting comparison with that of sucralose. Sucrose, also known as table sugar, is a disaccharide of D-glucose and D-fructose. Therefore, the six-carbon monosaccharides glucose and fructose were also chosen for this study. D-Glucose, also called dextrose, was found to be the most abundant sugar in groundwater (Spitzy, 1982). D-Fructose is an isomer of glucose (Fig. 1). Another carbohydrate of interest in this study is the disaccharide maltose containing two D-glucose units. Carbohydrate-type structures are also found in humic substances (Canellas et al., 2010) and the results of the present study may thus have implications in reducing levels of humic substances by reaction with Fe(VI). The objectives of the study were: (i) to determine rate laws and rate constants for the oxidation of sucralose and various related carbohydrates by Fe(VI); (ii) to compare the rate constants of the carbohydrates with Fe(VI) to each other to see if differences in rate constants can be related to structural differences. This should allow for better predictions to be made regarding the reactivity of Fe(VI) with a greater variety of carbohydrates and (iii) to understand the pH dependence of the oxidation of carbohydrates by Fe(VI) in order to expand the relevance of the results to a greater variety of environmental conditions. Author's personal copy 645 V.K. Sharma et al. / Chemosphere 87 (2012) 644–648 OH HO O HO HO 1 OH H HO OH HO O 1 Fructose OH 4 O OH HO OH OH Glucose H O HO 2 H 1 OH HO HO O HO O HO 1 O HO 2 OH O H HO OH OH HO HO Maltose Sucrose H HO O Cl Cl 1 O HO 2 OH O HO Cl HO Sucralose Fig. 1. Structures of studied carbohydrates and sucralose. 2. Experimental approach All glassware used in this study was soaked overnight in 50% nitric acid and rinsed thoroughly with distilled water before use. All solutions were prepared in water which had been distilled and then further purified through a Milli-Q system (18.2 MO cm). A solution of 200 lM Fe(VI) was prepared by dissolving solid potassium ferrate(VI) (K2FeO4) (purity > 98%) into a 5 mM Na2HPO4/ 1 mM borate ((Na2B4O710H2O) buffer solution at pH 9.0 (Luo et al., 2011). Substrate solutions were prepared in 0.01 M phosphate buffer in a concentration range of 0.05–0.25 M. This concentration range was selected based on the desire to maintain substrate concentrations at least ten times greater than ferrate concentrations for pseudo-order conditions to perform kinetics measurements. The pH of the substrate solution was adjusted by adding either concentrated phosphoric acid or sodium hydroxide solution. All kinetic studies were performed on a stopped-flow spectrophotometer (SX-18 MV, Applied Photophysics, UK) with a photomultiplier detector. Time spectra were collected in the wavelength range from 350 to 750 nm. Kinetic traces were collected at a wavelength of 510 nm to determine the pseudo-first-order rate constants using solutions in which the substrate was in excess. Stopped flow experimental data was analyzed using the nonlinear least-square algorithm of the SX-18MV global software (Applied Photophysics, UK). Rate constants reported represent the average of six replicate runs. The spontaneous self-decay rate of Fe(VI) was measured under conditions identical to the experimental oxidation conditions to allow for a correction in the rate constant. Routine spectral measurements were performed on an Agilent Model 8453 UV–Vis spectrophotometer. 3. Results and discussion Initially, the reactivity of Fe(VI) with monosaccharides was studied at pH 9.0 and 25 °C. The spectral measurements for monitoring the reactions are shown in Fig. SM-1 and indicate the decay of Fe(VI) without any suggestion of the formation of any intermediate(s) such as Fe(VI)-carbohydrate complexes. The complexation of carbohydrates with high-valent chromium species has been observed (Roldán et al., 2002; Codd et al., 2003; García et al., 2006), however it appears that the oxidation of monosaccharides by Fe(VI) occurred without precursor complexation for the time scale of the studied reactions. Similar results were observed for the reactions of Fe(VI) with disaccharides and with sucralose (Fig. SM-2). The rates of the reactions were followed at 510 nm at different concentrations of substrates (S) under pseudo-first order conditions at pH 9.0. The insets of Figs. SM-1 and SM-2 show the decrease in absorbance of Fe(VI) with time, which fit nicely to single exponential decays. This suggests that the reactions are first-order with respect to the concentration of Fe(VI). The pseudo-first-order rate constants (k0 ) were obtained at different concentrations of monosaccharides, disaccharides, and sucralose. A plot of k0 versus concentration of substrate ([S]) consistently showed linear relationships (Fig. 2). A log–log plot of the data from Fig. 2 was constructed to obtain order with respect to the concentration of substrate (n) (Fig. SM-3). Slopes of the plot were nearly unity (Table 1); indicating the reaction is also first-order with respect to the concentration of substrate. The rate law is represented by the following equation: dð½FeðVIÞÞ=dt ¼ k½FeðVIÞ½S ð1Þ where k is the second-order rate constant for the reaction of Fe(VI) with substrate. The values of k obtained at pH 9.0 are given in Table 1. The values of k did not span a large range varying from 1.0 101 to 2.5 101 M1 s1. The slowest rate constants in this study were those for sucrose and sucralose (Table 1). Maltose had the highest rate constant (Table 1). The order of reactivity for monosaccharides was fructose > glucose while maltose > sucralose > sucrose was the order of reactivity for disaccharides. Of the carbohydrates studied here, only sucrose is classified as a non-reducing sugar. Carbohydrates which can be oxidized by mild oxidizing agents such as Fe(III) or Cu(II) are referred to as reducing sugars (Nelson and Cox, 2005). The oxidation of sugars with Fe(III) Author's personal copy 646 V.K. Sharma et al. / Chemosphere 87 (2012) 644–648 HFeO4 þ S ! FeðIIIÞ þ productðsÞ 2.5 k', 10-2 s-1 FeO2 4 þ S ! FeðIIIÞ þ productðsÞ Maltose 2.0 ð3Þ (H3 FeOþ 4; Fructose 1.5 ð2Þ The more highly protonated species of Fe(VI), and H2 FeO4 ) were not considered because their pKa values are much lower than the pH of this study and contributions of these species would be negligible. The rate constant can thus be expressed as k½FeðVIÞ ¼ k2 ½HFeO4 þ k3 ½FeO2 4 ð4Þ where k2 and k3 are the species-specific rate constants for reactions (2) and (3), respectively. The expression for k can be simplified to Eq. (5) using an equilibrium expression for HFeO 4 species 1.0 Glucose k ¼ k2 f½Hþ =ðKa3 þ ½Hþ Þg þ k3 fK a3 =ðK a3 þ ½Hþ Þg 0.5 Sucralose Sucrose 0.0 0 20 40 [Substrate], 60 10-3 80 100 M Fig. 2. A plot of pseudo-first-order rate constants, k0 (s1) versus concentration of various carbohydrates and sucralose at pH 9.0 and 25 °C. or Cu(II) occurs at the anomeric carbon and only the linear form of the carbohydrate is reactive, not the cyclic form which is in equilibrium with the linear form. When two monosaccharides combine to form a disaccharide, a glycosidic bond forms as the hydroxyl group of one molecule reacts with the anomeric carbon of the other molecule (see Fig. 1). Sucrose, a disaccharide formed by the bonding of glucose and fructose has no free anomeric carbons since both are involved in the glycosidic bond. Thus sucrose is classified as a non-reducing sugar, e.g. it is not oxidized by either Fe(III) or Cu(II). Sucralose, its chlorinated derivative would also be expected to show similar behavior. All of the other substrates used in this study (glucose, fructose, and maltose) are classified as reducing sugars and are relatively easier to oxidize by Fe(VI) than are sucrose and sucralose (Table 1). The k values for the reaction of Fe(VI) with substrates were then determined at different pHs (Fig. 3). Generally, the k values increased with decrease in pH (Fig. 3a and b), similar to results from most studies with Fe(VI) (Sharma et al., 2011; Sharma, 2011). However, the reactions of glucose and fructose with Fe(VI) showed unusual pH dependence behavior in which rates slightly increased with increasing pH (pH P 8.0; Fig 3a). The variation in the k values with pH in Fig. 3 can be explained by considering reactions between + acid–base species of Fe(VI) (H3 FeOþ 4 H + H2FeO4, pKa1 = 1.9; + H2FeO4 H + HFeO4 , pKa2 = 3.5; HFeO4 H+ + FeO2 4 , pKa3 = 7.23 (Sharma et al., 2001)) and substrates. In the pH range studied, substrates do not exhibit more than one pH-dependent species, hence the pH dependence of k for the reaction of Fe(VI) was modeled using only two reactions (Eqs. (2) and (3)). ð5Þ Values of k2 and k3 were determined using Eq. (5) by fitting the experimentally determined values of k at different pH. Estimated values of species-specific rate constants are given in Table 1 for disaccharides, which fit reasonably well with the experimental results (solid lines, Fig 3b). The rate constants for the reaction of 2 HFeO 4 were greater for disaccharides than for FeO4 , which confirms results from earlier studies which indicate that monoprotonated species of Fe(VI) react faster with substrates than do unprotonated species of Fe(VI) (Sharma, 2010b). Comparatively, values of k for oxidation of monosaccharides at different pH could not be fitted using Eq. (5) (dashed lines, Fig. 3a). It seems that other factors besides the change in the fraction of species with pH are involved in the reactivity of Fe(VI) with monosaccharides. Base catalysis of monosaccharides may be one of the factors involved where the slight increase in the reaction rate at pH > 8 was observed (Fig. 3a). The tendency of the conversion of fructose to glucose in alkaline medium increases with increase in pH because such transformation is base catalyzed. Significantly, this conversion involves opening of the cyclic ring structure before fructose can be transformed to glucose. As the pH increased beyond 8.0, higher concentrations of open structures of monosaccharides are expected than those of closed (or ring) structures. Open structures of carbohydrates are more susceptible to oxidation than the ring structures. Proportions of open structures (i.e. active reductant) would increase with increase in pH and may increase the reaction rate at higher pH as observed in the present study. Increase in the formation of the active reductant form of glucose with increase in pH has also been experimentally determined (Roepke and Ort, 1931). The disaccharide, sucrose and its chlorinated derivative, sucralose behave differentially fron monosaccharides because they are non-reducing agents due to the link between C-1 and C-2 (1 ? 2) anomeric carbons (Fig. SM-1). Rates are not expected to be influenced by an increase in the hydroxide ion concentration. Therefore their rates of oxidation are solely dependent on the predominant Fe(VI) species present at that pH. Although maltose is a reducing sugar, it behaved more like the other disaccharides, and explanation of such observed rates will stimulate further studies in this area through the investigation of oxidation rates of a multitude of other disaccharides. Table 1 n and k (M1 s1) for oxidation of carbohydrates and sucralose by Fe(VI) at 25 °C. Substrate (S) Glucose (G) Fructose (F) Maltose (G-G) Sucrose (G–F) Sucralose n 1.02 ± 0.07 0.97 ± 0.04 0.93 ± 0.07 1.19 ± 0.07 1.20 ± 0.11 k, 101 M1 s1 pH 9.0 k, 101 M1 s1 HFeO 4 þS FeO2 4 þS k, 101 M1 s1 1.6 ± 0.1 2.1 ± 0.2 2.5 ± 0.3 1.0 ± 0.1 1.3 ± 0.1 – – (6.8 ± 0.3) 101 (5.3 ± 0.4) 101 (5.7 ± 0.3) 101 – – (2.2 ± 0.2) 101 (0.7 ± 0.1) 101 (1.2 ± 0.1) 101 Author's personal copy 647 V.K. Sharma et al. / Chemosphere 87 (2012) 644–648 8.0 Table 2 Rate constants of carbohydrates with different oxidants at 25 °C. (a) Glucose Fructose k, 10-1 M-1s-1 6.0 Oxidant 4.0 a b c (b) Maltose Sucralose Sucrose k, 10-1 M-1s-1 6.0 4.0 k, M1 s1 pH k, M1 s1 Glucose Fe(VI) ClO2 O3 OH CO 3 2.0 pH 7.0 – 6.0 7.5 9.3 2.0 101 <1.0 102a 4.8 100b 1.5 109b 4.3 105c 7.0 – 6.0 6.5 – 5.0 101 – 6.9 100b 2.3 109b – pH k, M1 s1 Maltose Sucrose 7.0 – 5.5 7.0 8.3 3.7 101 – 2.3 100b 2.3 109b 2.4 104c Hoigne and Bader, 1994. National Institute of Science and Technology, 2002. Stenman et al., 2003. the anomeric OH group (i.e. the hemiacetal or the aldehyde in the open form). However, in the case of the non-reducing sucrose and sucralose, it is likely that oxidation occurs at the hydroxymethyl groups as described in the oxidation of alkyl glycosidic type carbohydrates by Fe(VI) (BeMiller et al., 1972). 4. Conclusions 2.0 0.0 6.0 7.0 8.0 9.0 10.0 pH Fig. 3. Dependence of second-order rate constants (k, M1 s1) on pH for the oxidation of carbohydrates and sucralose by Fe(VI) at 25 °C. Reactivity of carbohydrates with Fe(VI) and other oxidants are compared (Table 2). Fe(VI), ClO2, and O3 are much less reactive than the radical species, OH and CO 3 . ClO2 had no reactivity while both Fe(VI) and O3 reacted sluggishly with carbohydrates. CO 3 has been reported to be less reactive than OH (Gilbert et al., 1999; Stenman et al., 2003). The reaction of OH with carbohydrates was not selective and oxidation occurred through abstraction of carbon bound hydrogen atoms to form different radicals (Diehl et al., 1978; Gilbert et al., 1982). Comparatively, oxidation of carbo hydrates by CO 3 , and SO4 were more selective than was OH radical (Gilbert et al., 1999; Gierer et al., 2001; Reitberger et al., 2001; Stenman et al., 2003). The mechanism of oxidation of carbohydrates by CO involved hydrogen abstraction and/or electron 3 transfer steps (Stenman et al., 2003). In the case of oxidation of carbohydrates by SO 4 , the preference for hydrogen abstraction was from the C-H a to a ring oxygen atom in five membered ring carbohydrates (e.g. sucrose). The reactivity of SO 4 with a-D-glucose and b-D-glucose also differed. The reaction with a-D-glucose was selective towards the C-2, C-5, and C-6 positions while a hydrogen atom was abstracted from C1 from b-D-glucose by SO 4 (Gilbert et al., 1999). In the case of Fe(VI), oxidation of tested carbohydrates with Fe(VI) showed the formation of aldehydes via attack on the primary hydroxymethyl group (BeMiller et al., 1972). The tested carbohydrates in this study were essentially the alkyl glycosidic type, e.g. D-methyl hexopyranoside, which are non-reducing, i.e. they lack the anomeric OH. Another study of oxidation of aliphatic alcohols by Fe(VI) include similar examples in which the corresponding aldehydes were formed (Bartzatt et al., 1985). In the present study, however, in the case of glucose, fructose, and maltose, the sugar substrate was present in excess under studied conditions of determining rate constants, which should result in the oxidation of the most oxidant susceptible functionality; namely, The kinetics of the oxidation of selected carbohydrates and sucralose by Fe(VI) were shown to be first-order with respect to each reactant and the observed second-order rate constants, k, increased with a decrease in pH for disaccharides. However, the pH dependence for monosaccharides was different in which initial rate constant decreases were followed by increases at pH P 8.0, which were attributed to the hydroxide catalyzed ring opening/ isomerization of fructose and glucose. Comparison of the reactivity of Fe(VI) with other oxidants suggests that free radical species such as OH, have much higher reactivity than Fe(VI) towards carbohydrates. The reactivity of Fe(VI) with sucralose and carbohydrates may be enhanced by an Fe(VI)–TiO2–UV system, which would likely generate the reactive species OH and Fe(V) to oxidize substrates more efficiently. An ozone–TiO2–UV system may also be appropriate in degrading carbohydrates in water. Appendix A. Supplementary material Supplementary data associated with this article can be found, in the online version, at doi:10.1016/j.chemosphere.2012.01.019. References Bartzatt, R., Tabatabai, A., Carr, J., 1985. Kinetics of oxidation of low molecular weight alcohols by potassium ferrate. Synth. React. Inorg. Met. Org. Chem. 15, 1171–1187. BeMiller, J.N., Kumari, V.G., Darling, S.D., 1972. Oxidation of carbohydrates with the ferrate(VI) ion. Tetrahedron Lett. 13, 4143–4146. Canellas, L.P., Piccolo, A., Dobbss, L.B., Spaccini, R., Olivares, F.L., Zandonadi, D.B., Façanha, A.R., 2010. Chemical composition and bioactivity properties of sizefractions separated from a vermicompost humic acid. Chemosphere 78, 457– 466. Codd, R., Irwin, J.A., Lay, P.A., 2003. Sialoglycoprotein and carbohydrate complexes in chromium toxicity. Curr. Opin. Chem. Biol. 7, 213–219. Diehl, J.F., Adam, S., Delincée, H., Jakubick, V., 1978. Radiolysis of carbohydrates and of carbohydrate-containing foodstuffs. J. Agric. Food Chem. 26, 15–20. Eng, Y.Y., Sharma, V.K., Ray, A.K., 2006. Ferrate(VI): green chemistry oxidant for degradation of cationic surfactant. Chemosphere 63, 1785–1790. García, S., Ciullo, L., Olivera, M.S., González, J.C., Bellú, S., Rockembauer, A., Korecz, L., Sala, L.F., 2006. Kinetics and mechanism of the reduction of chromium(VI) by Dfructose. Polyhedron 25, 1483–1490. Gierer, J., Reitberger, T., Yang, E., Yoon, B.H., 2001. Formation and involvement of radicals in oxygen delignification studied by the autoxidation of lignin and carbohydrate model compounds. J. Wood Chem. Technol. 21, 313–341. Gilbert, B.C., King, D.M., Barry, T.C., 1982. Radical reactions of carbohydrates. Part 3: An electron spin resonance investigation of base-catalyzed rearrangements of radicals derived from d-glucose and related compounds. J. Chem. Soc. Perkin Trans. 2, 169–179. Gilbert, B.C., Smith, L.J.R., Taylor, P., Ward, S., Whitwood, A.C., 1999. The interplay of electronic, steric and stereoelectronic effects in hydrogen-atom abstraction Author's personal copy 648 V.K. Sharma et al. / Chemosphere 87 (2012) 644–648 . reactions of SO 4 revealed by EPR spectroscopy. J. Chem. Soc. Perkin Trans. 2, 1631–1637. Grotz, V.L., Munro, I.C., 2009. An overview of the safety of sucralose. Regul. Toxicol. Pharm. 55, 1–5. Hoigne, J., Bader, H., 1994. Kinetics of reactions of chlorine dioxide (OClO) in water – I. Rate constants for inorganic and organic compounds. Water Res. 28, 45–55. Jiang, J.Q., 2007. Research progress in the use of ferrate(VI) for the environmental remediation. J. Hazard. Mater. 146, 617–623. Lee, Y., Zimmermann, S.G., Kieu, A.T., Gunten, G.V., 2009. Ferrate (Fe(VI)) application for municipal wastewater treatment: a novel process for simultaneous micropollutant oxidation and phosphate removal. Environ. Sci. Technol. 43, 3831–3838. Loos, R., Gawlik, B.M., Boettcher, K., Locoro, G., Contini, S., Bidoglio, G., 2009. Sucralose screening in European surface waters using a solid-phase extractionliquid chromatography-triple quadrupole mass spectrometry method. J. Chromatgr. A 1216, 1126–1131. Lubick, N., 2009. Artificial sweetener makes ideal tracer. Environ. Sci. Technol. 43, 4220. Lubick, N., 2008. Artificial sweetener persists in the environment. Environ. Sci. Technol. 42, 3125. Luo, Z., Strouse, M., Jiang, J.Q., Sharma, V.K., 2011. Methodologies for the analytical determination of ferrate(VI): a review. J. Environ. Sci. Health – Part A: Toxic/ Hazard. Subs. Environ. Eng. 46, 453–460. Mead, R.N., Morgan, J.B., Avery Jr., G.B., Kieber, R.J., Kirk, A.M., Skrabal, S.A., Willey, J.D., 2009. Occurrence of the artificial sweetener sucralose in coastal and marine waters of the United States. Mar. Chem. 116, 13–17. National Institute of Science and Technology, 2002. NDRL/NIST Solution Kinetics Database on the Web. 40. Nelson, D.L., Cox, M.M., 2005. Principles of Biochemistry. WH Freeman and Co, New York, NY. Reitberger, T., Gierer, J., Yang, E., Yoon, B.H., 2001. Involvement of oxygen-derived free radicals in chemical and biochemical degradation of lignin. ACS Symp. Ser. 785, 255–271. Richardson, S.D., Ternes, T.A., 2011. Water analysis: emerging contaminants and current issues. Anal. Chem. 83, 4616–4648. Roepke, M.H., Ort, J.M., 1931. The rates of formation of the active reductants of several sugars. J. Phys. Chem. 35, 3596–3611. Roldán, V., González, J.C., Santoro, M., García, S., Casado, N., Olivera, S., Boggio, J.C., Salas-Peregrin, J.M., Signorella, S., Sala, L.F., 2002. Kinetics and mechanism of the oxidation of disaccharides by CrVI. Can. J. Chem. 80, 1676–1686. Sharma, V.K., 2010a. Oxidation of nitrogen containing pollutants by novel ferrate(VI) technology: a review. J. Environ. Sci. Health, Part A: Toxic/Hazard. Subst. Environ. Eng. 45, 645–667. Sharma, V.K., 2010b. Oxidation of inorganic compounds by ferrate(VI) and ferrate(V): one-electron and two-electron transfer steps. Environ. Sci. Technol. 45, 5148–5152. Sharma, V.K., 2011. Oxidation of inorganic contaminants by ferrates(Fe(VI), Fe(V), and Fe(IV))- Kinetics and mechanisms – a review. J. Environ. Manage. 92, 1051– 1073. Sharma, V.K., Anquandah, G.A.K., Nesnas, N., 2009. Kinetics of the oxidation of endocrine disruptor nonylphenol by ferrate(VI). Environ. Chem. Lett. 7, 115– 119. Sharma, V.K., Burnett, C.R., Millero, F.J., 2001. Dissociation constants of monoprotic ferrate(VI) ions in NaCl media. Phys. Chem. Chem. Phys. 3, 2059–2062. Sharma, V.K., Graham, N.J.D., Li, X.Z., Yuan, B.L., 2010. Ferrate(VI) enhanced photocatalytic oxidation of pollutants in aqueous TiO2 suspensions. Environ. Sci. Pollut. Res. 17 (2), 453–461. Sharma, V.K., Luther III, G.W., Millero, F.J., 2011. Mechanisms of oxidation of organosulfur compounds by ferrate(VI). Chemosphere 82, 1083–1089. Spitzy, A., 1982. Amino acids and sugars in deep and shallow groundwater from the Hamburg region. Mitteilungen aus dem Geologisch-Palaeontologischen Institut der Universitaet Hamburg. vol. 52, pp. 743–748. Stenman, D., Carlsson, M., Jonsson, M., Reitberger, T., 2003. Reactivity of the carbonate radical anion towards carbohydrate and lignin model compounds. J. Wood Chem. Technol. 23, 47–69. Torres, C.I., Ramakrishna, S., Chiu, C.-A., Nelson, K.G., Westerhoff, P., KrajmalnikBrown, R., 2011. Fate of sucralose during wastewater treatment. Environ. Eng. Sci. 28, 325–331. Wiet, S.G., Miller, G.A., 1997. Does chemical modification of tastants merely enhance their intrinsic taste qualities? Food Chem. 58, 305–311.
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