Fe (III) complexed with SCN- was found to be reduced to Fe(II) in the

presence of activated carbon. The rate of disappearance of the complex was

determined spectro photometrically and was found to be first order with respect

to Fe(I1I). The enthalpy and entropy of activation are 100 ± 10 kJ/mole and

14.1 ± 0.8 J/mole-K respectively. Some Fe was found to be adsorbed on the

catalyst where the actual reduction was suggested to take place. The accompanying

oxidation reaction has been suggested to be mainly that of the thiocyanate

ions adsorbed at the positive centres on the catalyst

Badri, M.

Crouse, Karen Anne

Universiti Putra Malaysia Institutional Repository

Pertanika J. Sci. & Techno!. 1(2): 159-168 (1993)1SSN: 0128-7680© Universiti Pertanian Malaysia PressReduction of Thiocyanate Complexes of Fe(III)in the Presence of Activated CarbonKaren A. Crouse and M. BadriDepartment of ChemistryUniversiti Pertanian Malaysia43400 UPM Serdang, Selangor Darul EhsanMalaysiaReceived 7 April 1990ABSTRAKKehadiran karbon teraktif didapati menurunkan Fe(III) yang berkompleksdengan SCN- kepada Fe(II). Kadar susutan ketumpatan kompleks telahditentukan dengan menggunakan spektrofotometer. Tindakbalas didapatimenurut tertib pertama terhadap ion Fe(III). Entalpi dan entropi keaktifanadalah masing-masing 100 ± 10kJ/mol dan 14.1 ± 0.8 J/mol-K. Sesetengahdaripada Fe didapati terjerap pada permukaan mangkin di mana tindakbalaspenurunan itu dijangka berlaku. Tindakbalas pengoksidaan seiring yang utamadicadangkan sebagai pengoksidaan ion tiosianat yang terjerap pada titik-titikpositif pada mangkin.ABSTRACTFe (III) complexed with SCN- was found to be reduced to Fe(II) in thepresence of activated carbon. The rate of disappearance of the complex wasdetermined spectrophotometrically and was found to be first order with respectto Fe(I1I). The enthalpy and entropy of activation are 100 ± 10 kJ/mole and14.1 ± 0.8 J/mole-K respectively. Some Fe was found to be adsorbed on thecatalyst where the actual reduction was suggested to take place. The accompa-nying oxidation reaction has been suggested to be mainly that of the thiocyanateions adsorbed at the positive centres on the catalyst.Keywords: activated carbon, thiocyanate complexes of Fe(III), quinone/hydroquinone, thiocyanate ion, reduction of Fe(ill)INTRODUCTIONActivated carbon has been known to act as a catalyst in many chemicalreactions (e.g. Bente and Walton 1942). It is widely used in teachinglaboratories during some inorganic preparations (e.g. Lambert and Muir1973; Rendle et al. 1976). Short reviews on the subject have also beenwritten (Hassler 1974;. Kalra et al. 1989). Activated carbon is similar toother heterogeneous catalysts in that its catalytic behaviour is a manifesta-tion of its ability to adsorb reacting species. Thus it was suggested that theoxidation of CN- to CNO- in the presence of activated carbon, forexample, occurred through the reaction of the adsorbed CN- with dis-solved oxygen or the adsorbed oxygen on the same carbon surfaceKaren A. Crouse and M. Badri(Bernadin 1973). More recent work in this area mainly concerned theremoval of toxic substances such as Hg and CN-from industrial and mining wastes(Parentich and Kinsella 1984; Saito 1984; Tsuchida and Muir 1986a, 1986b).Much has been published concerning the complexation of Fe (III) withSCN- (Korondan and Nagypal 1983 and references therein). Despite thecommon belief that the complex is hexa-coordinated, it has been shownthat at concentrations less than O.lM, virtually all the ions are present asFeSCN++ and Fe (SCN); (Betts and Dainton 1953). Even at higher concen-trations, only a small fraction of tetra- and penta-thiocyanateiron(III) wereformed (Korondan and Nagypal 1983). It has also been'shown that thecomplex undergoes thermal and perhaps photochemical decompositioneven at room temperature (Betts and Dainton 1953; Sultan and Bishop1982). The results reported herein show that the rate of decomposition ofthe complex is enhanced in the presence of activated carbon.MATERIALS AND METHODSA solution of Fe(III) was prepared by dissolving 2.34 g iron sheet(Goodfellow, 99.99% pure) in a beaker containing 100 ml HNOs 6M(Merck, selectipur). When the rate of reaction decreased, the solution washeated to near boiling for five hours to ensure complete dissolution of themetal. It was allowed to cool to room temperature before being quanti-tatively transferred into a one-litre volumetric flask. The volume was madeup with HNOs(lM). The concentration of the stock solution (0.042M) wasdetermined by AAS with solutions of FeS04.7H20 (Ajax, AR) being usedfor standardization.A 0.6M solution of KCNS was prepared by dissolving about 6.0 g KCNS(Merck, pure) in 100 ml distilled water.Preparation of CarbonLarge pieces of activated carbon were prepared by a method describedearlier (British Patent 1984). A fairly flat piece was ground with sandpaperinto a disc having a diameter of about 15 mm and thickness of 1.8 mm.The disc, which weighed 0.3605 g, was boiled in 1M HCl for one week andthen was continuously washed with distilled water in a Soxhlet apparatusfor another week. It was left soaking in distilled water until it was used. Asthe same piece was used for all kinetic measurements, the same washingprocedure was followed after each experiment.Kinetic Studies2.50 ml of the Fe(III) stock solution was pipetted into a 100-ml volumetricflask followed by 1 ml of KCNS 0.6M. The flask was then filled to the markwith HNOs 1M. The solution (1.05X10,3M in Fe3+, 6.00XlO,3M in SCN-)was then transferred into a Pyrex glass reaction vessel of about 200 ml160 Pertanika J. Sci. & Techno!. Vo!. 1 No.2, 1993Reduction of Thiocyanate Complexes of Fe(Ill) in the Presence of Activated Carboncapacity. Nitrogen gas was bubbled through the solution for the durationof the experiment. The reaction vessel was placed in a water bath whichwas covered to eliminate light and maintained at various temperatures asgiven in Table 1. Before the start of a kinetic run, about 3 ml of thesolution was withdrawn for spectrophotometric measurement at A = 454nm (Shimadzu UV-160).TABLE 1Rate constants for the bleaching of ferricthiocyanate in the presenceof activated carbont(deg C) 105 (sec) 1/Tx10-3 (K1) In (k/T)23.5 1.93 ± .04 3.37 -16.5525.5 2.57 ± .24 3.35 -16.2729.5 2.94 ± .05 3.30 -16.1534.5 5.95 ± .14 3.25 -15.4637.5 13.66 ± .31 3.21 -14.6443.5 25.51 ± .21 3.16 -14.03The carbon disc was dried with soft tissue paper and was dropped intothe reaction vessel. The progress of the reaction was followedspectrophotometrically by measuring the absorbance as a function of timefor periods of at least five hours. Initial and final absorbance readings weretaken for control solutions at each temperature to determine the extent ofautodecomposition of the complex in the absence of activated carbon overthe period of reaction. The autoreduction of the complex was alsofollowed as a function of time at 30·C for the solution in the absence ofcarbon.Product AnalysesThe reaction mixture was left standing overnight at room temperature(23.5"C) on completion of the experiment. Mter the carbon disc wasremoved, the total Fe in the solution was determined by AAS. Four 5 mlportions were subjected to the following analyses:(i) Addition of a few drops of ferricyanide solution,(ii) Addition of a few drops of ferrocyanide solution,(iii) Addition of a few drops of Fe (III) stock solution followed by a fewdrops of HP2 (RDH, 35%)(iv) Addition of a few drops of KCNS solution, followed by a fewdrops of H 20 2•Pertanika J. Sci. & Techno!. Vo!. 1 No.2, 1993 161Karen A. Crouse and M. BadriRESULTSThe results obtained from the control experiments (Table 2) showed thatthe thiocyanate complex of Fe (III) was stable throughout the duration ofthe experiments over the concentration and temperature ranges used inthis investigation. Hence, the marked decrease with time of the absorb-ance due to the Fe(III) complex in the presence of carbon has beenattributed to the catalytic reduction to Fe (II). The kinetic data show thatthe decrease in absorption is first order. Sample first-order plots are givenin Fig. 1. An Eyring plot is given in Fig. 2. The activation enthalpy andentropy have been calculated to be 100 ± 10 kJ/mole and 14.1 ± 0.8J/mol-K respectively.TABLE 2Initial and final* readings for the absorbance at 454 nmfor ferricthiocyanate and final times(with Activated C) (without Activated C)t(deg C) Initial Final Initial Final Final time(min)23.4 2.480 0.371 2.480 2.479 168025.5 2.466 1.414 2.466 2.457 42029.5 2.475 0.165 2.475 2.470 153034.5 2.490 0.776 2.477 2.470 33043.5 2.470 0.019 2.470 2.460 310* Final reading was the reading taken at the final time for a given kinetic run and wasnot the absorbance at infinite time. Final times for samples with and without activatedcarbon were the same at the same temperature.The qualitative tests gave the following results:(i) The product solution became dark green with slight precipitationupon the addition of a few drops of ferricyanide reagent, indicat-ing the presence of Fe(II).(ii) The addition of ferrocyanide turned the solution to light bluewhich indicated the presence of Fe (III) .(iii) The addition of Fe(III) caused the solution to become slightlydarker red in colour indicating the presence of SCN- but in aquantity much less than the original amount. \JVhen the additionof Fe (III) solution was followed by the addition of a few drops ofH20 2 there was no apparent change in the colour intensitydespite the increase of Fe (III) through reoxidation of Fe (II).(iv) The addition of SCN- caused the solution to become faintly red.However, when SCN- was followed by H 20 2, the solution instantly162 Pertanika J. Sci. & Techno!. Vol. I No.2, 1993Reduction of Thiocyanate Complexes of Fe(ill) in the Presence of Activated Carbono-2~~"""--------30·C.53.5o200 600 1000 1400Time (Minutes)Fig. 1. First-order plots for the bleaching of Fe(III)-thiocyanate solutions in thepresence of activated carbon (Filled squares: uncatalysed reaction)-14.0-14.5•s: -15.0:5-15.5-16.0-16.53.15 3.20•3.25•3.30 3.35 3.40Fig. 2. Eyring plot for the bleaching of Fe(III)-thiocyanate solutions inthe presence of activated carbonPertanika J. Sci. & Techno!. Vo!. I No.2, 1993 163Karen A. Crouse and M. Badribecame dark red. The evolution of heat and gas was ob-served. The reaction continued until the red colour fadedcompletely.The initial concentration of iron in solution at 23.5'C was 1.05X lO-3Mwhile after the reaction its concentration was 8.0lxlO-14M indicating thatabout 23.7% of the iron had been adsorbed onto activated carbon.DISCUSSIONThe qualitative analyses performed on the product samples clearly indi-cated that Fe(III) had indeed been reduced to Fe(II). A similar reactionhas been observed for the cyanide complexes (Saito 1984). That the rateof reduction of the SCN- complex in the presence of carbon was muchfaster than that in the absence of carbon indicates that some electroactivespecies on the surface of carbon was responsible for the transfer ofelectrons necessary for the reaction to occur. These electroactive speciesmay be associated with quinone/hydroquinone, Q/QH2, structures whichhave been suggested to be present on the surface of activated carbon(Drushel and Hallum 1958; Jones and Kaye 1969; Epstein et al. 1971). Thetheoretical electrode potentials of these species have been estimated (AItet al. 1972). The quinone/hydroquinone couple, for example,(1)has been assigned a value of EO = O.69V (CRC Handbook 1970-71) and wasexpected to be lower at lower pH. Since the potential for Fe(III)/Fe(II)couple is 0.77V, the overall emfwould be at least O.08V indicating that thereaction should be spontaneous.Working with carbon black, Kinoshita and Belt (1973) observed thatthe concentration of Q/QH2 on the surface of carbon was of the orderof lO-lO_lO-n mole/cm2. The surface of activated carbon used in thisinvestigation was about 190 m2/ g (British Patent 1984). Therefore thetotal Q/QH2 available for the reaction was of the order of 10-5 mole, aquantity certainly sufficient for its suggested catalytic function. The elec-tron transfer was enhanced by the dynamic interconversion between Qand QH2. This affected the rate of the overall redox reaction (Fe (II)reduction/thiocyanate oxidation) in a positive manner.The half-reaction likely to have been involved is that of the (SCN)/SCN- couple:164(SCN)2 + 2e ~ 2SCN- EO = 0.77VPertanika J. Sci. & Technol. Vol. 1 No.2, 1993(2)Reduction of Thiocyanate Complexes of Fe(III) in the Presence of Activated CarbonThe overall standard potential of this combination is zero. At the concen-trations used in this experiment the potential would be positive and thereaction therefore spontaneous. SCN- was found to be consumed in thereaction. Free SCN- could be adsorbed on carbon moderately (Kunz andGianelli 1976) perhaps through its interaction with the positive centres onthe carbon surface. The following reactions might also have been respon-sible for the production of these positive centres)yo HI R~ (3)o RXJ + ~ 0 + HCl ~ )[yo. R ct" + ~ H 0Z 2 Z Z 1fi(Garten and Weiss 1957)0 OH (4)IIyY+CI-IIi( + HCI----------')l)l ~~0 o +(Boehm and Voll 1970)The quantity of (SCN)2 that would have been produced in the reactionwould have been too small to observe. Also, any (SCN)2 produced wouldhave undergone hydrolysis as shown in reaction 5 (Gauguin 1945, 1949;Cotton and Wilkinson 1972) to give soluble products such as CN- andSO42- with CN- reacting further with carbon to yield products similar tothose suggested for the cyanide system (Tsuchida and Muir 1986a, 1986b).(5)The fact remains that ferric thiocyanate has been reported to undergothermal auto-reduction in aqueous solutions of perchloric acid (Betts andDainton 1953). Competition of product (ferrous ion) with reactant (ferricion) for the intermediate reactant (SCN)2 was said to retard the reduction.It appears that decomposition approached a limit of about 15% at 29.89'Cin solution containing (FeIII)o = 0.00230M; (SCN-)o = 0.0784M in HCl04•Retardation was observed to begin after only 30 minutes at which time thesolution had undergone about 5% decomposition. Control experiments inPertanika J. Sci. & Techno!. Vo!. 1 No.2, 1993 165Karen A. Crouse and M. Badrinitric acid in this study showed a maximum of -1.5% decomposition aftera period of nine hours at 30·C in the absence of activated carbon.Solutions kept for ten days showed <20% decomposition. In the presenceof activated carbon, the reduction of the Fe+++ - SCN- complex proceededvery rapidly. Fe+++ - SCN- solutions were eventually decolorized at alltemperatures, i.e. A", (454 nm) - O.As has been discussed by Sandell (1978), the spectrophotometricmethod for determining Fe3+ by complexation with SCN- requires carewith attention being given to SCN- concentration which should be thesame for all determinations and preferably in excess, to temperature whichshould be held constant, and to deviation from Beer's Law at low concen-tration of Fe3+ ion. Any error arising in accurate determination of Fe3+using this method under the experimental conditions used in this workwould be due only to deviation from Beer's Law. Any such error, however,is within the acceptable experimental error for these kinetic determinationsand therefore would not invalidate the kinetic data reported herein.CONCLUSIONIt can be concluded that activated carbon catalyzed the reduction ofFe (III) in the form of thiocyanate complex to Fe (II). Quinone/hydroquinone redox couple that has been suggested to be present on thecarbon surface might have been responsible for the catalytic behaviour butit seems that the ionic CNS- species was the primary source of theelectrons required for the reaction to go to completion. The reaction hasbeen regarded to be of pseudo-first order ~ven though it followed first-order kinetic equation in view of the fact that carbon also physicallyadsorbed the reacting species.ACKNOWLEDGEMENTSFinancial assistance in the form of a grant from MPKSN (Proj. No. 2-06-03-009) is gratefully acknowledged. The authors also wish to express theirappreciation to the referee whose suggestions and comments were veryvaluable in the preparation of the final version of this manuscript.REFERENCESALT, H., H. BINDER, A. KOHLING and G. SANDSTEDE. 1972. Investigation into the use ofquinone compounds for battery cathodes. Electrochim. Acta. 17: 873-887.BERNADIN, F.E. 1973. Cyanide detoxification using adsorption and catalytic oxidation ongranular activated carbon. J Water Pollut. Control Fed. 45: 221-231.BENTE, P.F. and J.H. WALTON. 1942. The catalytic activity of activated nitrogenouscarbons. J Phys. Chern. 47: 133-148.166 Pertanika J. Sci. & Techno!. Vol. 1 No.2, 1993Reduction of Thiocyanate Complexes of Fe(III) in the Presence of Activated CarbonBETTS, RH. and F.S. DAI 'TON. 1953. Electron transfer and other processes involved inthe spontaneous bleaching of acidified aqueous solutions of ferric thiocyanate. J.Am. Chem. Soc. 75(4): 5721-5727.BOEHM, H.P. and M. VaLL. 1970. Baische Oberfliichenoxide auf Kohlenstoff - I: Adsorp-tion von Sauren. Carbon 8: 227-240.BRITISH PATENT. 1984. No. 2086864. Preparation of activated carbon under reducedpressure.COTTON, F.A. and G. WILKINSON. 1972. Advanced Inorganic Chemistry. 3rd ed. IntersciencePub!. p. 301.CRC Handbook of Chemistry and Physics. 1970-71. R.C. West. 51st. ed. Cleveland.Chemical Rubber Co.DRUSHEL, H.V. and J.v. HALLUM. 1958. The organic nature of carbon black surface II.Quinones and hydroquinones by coulometry at controlled potentia!. J. Phys. Chem.62: 1502-1505.EpSTEI ,B.D., E. DALLE-MOLLE and J. S. MATTSO . 1971. Electrochemical investigation ofsurface functional groups on isotropic pyrolytic carbon. Carbon 9: 609-615.GARTEN, VA and D.E. WEISS. 1957. A new interpretation of acidic and basic structure in carbonsII. The chromene-<:arbonium ion couple in carbon. AUI"t. J Chem. 10: 309-328.GAUGUIN, R 1945. Potentimetric study of the reducing properties of the thiocyanate ion.J. Chim. Phys. 42: 136-148. (CA 40: 39684).GAUGUIN, R. 1949. Reducing properties of thiocyanate and cyanate ions. Ann. Chim. 4:832-880 (CA 44: 47571)HAsSLER, J.W. 1974. Purification with Activated Carbon Industrial, Commercial, Environmental..Y.: Chemical Pub!. Co. pp. 248-273.JONES I.F. and RC. KAYE. 1969. Polarography of carbon suspensions. J. Electroanal. Chem.20: 213-321.K.<\LRA, KC., P. KATYAL and K.C. SINGH. 1989. Catalytic reactions of carbon. J. Sci. Ind. Res.48: 186-192.KJNOSHITA, K and J.A.S. BELT. 1973. Potentiodynamic analysis of surface oxides oncarbon black. Carbon 11: 403-411.KOROl DAN I. and I. NAGYI'AL. 1983. NMR relaxation studies in solutions of transitionmetal complexes X. The stepwise equlibria in the iron (III) - thiocyanate systemstudies by MR relaxation. Inorg. Chim. Acta 73: 131-134.KUNZ, R.G. and J.F. GIANNELJ. 1976. Activated carbon adsorption of cyanide complexesand thiocyanate ion from petrochemical wastewater. Carbon 14: 157-161.LAMBERT J. and TA MUIR. 1973. Practical Chemistry. 3rd. ed. Heinemann. pp. 95-96.PARENTICH, A. and B. KJNSELLA. 1984. Titrimetric studies on activated carbon. In The Aust.IMM Perth and Kalgoorlie Branches Regional Conference on "Gold-Mining, Metallurgy andGeology". Oct. 1984. pp.1 - 9.RENDLE, P., M. VOKINS and P. DAVIS. 1976. Experimental Chemistry. A Laboratory Manual.2nd. ed. Peter Arnold. pp. 49-50.Pertanika J. Sci. & Techno!. Vo!. I No.2, 1993 167Karen A. Crouse and M. BadriSAITO, 1. 1984. The removal of hexacyanoferrate (III) and (II) ions in dilute aqueoussolution by activated carbon. Water Res. 18(3): 319-323.SANDELL, E.B. 1978. Potentiometric Determination of Trace Metals. Wiley. pp. 525-536.SULTAJ"I, S.M. and E. BISHOP. 1982. A study of the formation and stability of the iron(III)-thiocyanate complex in acidic media. Analyst 107: 1060-1064.TSUCHIDA, N. and D.M. MUIR. 1986a. Potentiometric studies on the adsorption ofAu(CN); and Ag(CN); onto activated carbon. Metall. Trans. 17B: 523-528.TSUCHIDA, N. and D.M. MUIR. 1986b. Studies on role of oxygen in the adsorption ofAu(CN); and Ag(CN); onto activated carbon. Metall. Trans. 17B: 529-533.168 Pertanika J. Sci. & Techno!. Vol. 1 No.2, 1993

Reduction of Thiocyanate Complexes of Fe(III)

in the Presence of Activated Carbon

http://psasir.upm.edu.my/3091/1/Reduction_of_Thiocyanate_Complexes_of_Fe%28III%29.pdf

Reduction of Thiocyanate Complexes of Fe(III) in the Presence of Activated Carbon

Abstract

Similar works

Full text

Available Versions

Universiti Putra Malaysia Institutional Repository