The Decomposition of Aqueous Sodium Bromite

Similar documents
Ion Pairing and the Reaction of Alkali Metal Ferrocyanides and Persulfates

Three experiments were carried out using different initial concentrations of the three reactants x 10 5

For the element X in the ionic compound MX, explain the meaning of the term oxidation state.

3.2.5 Group VII. Trends in Physical Processes. 70 minutes. 70 marks. Page 1 of 7

Nomenclature. A Systematic Approach to Naming Chemical Compounds

Complete the table to show the relative charge of each particle and the number of each particle found in a 140 Ce 2+ ion.

A New Bromite Oscillator. Large-Amplitude ph Oscillations in the Bromite-Thiosulfate-Phenol Flow System1

3.2.5 Group VII. Trends in oxidising abilities. 167 minutes. 167 marks. Page 1 of 19

+ IO3-, at a rate proportional to [H+]2[Br Thirdly, the iodine bromide reacts by the overall

EXPERIMENT NINE Part I - The Standardization of Thiosulfate Solutions

1 Three redox systems, C, D and E are shown in Table 6.1. C Ag(NH 3. ) 2 + (aq) + e Ag(s) + 2NH 3. (aq) D Ag + (aq) + e Ag(s)

Chapter 6. Chemical Reactions. Sodium reacts violently with bromine to form sodium bromide.

+ 30C1- + H20 + 2HCO3- + 3C1- + Np.

Advanced Unit 6: Chemistry Laboratory Skills II

SIR MICHELANGELO REFALO

*ac112* Chemistry. Assessment Unit AS 1 [AC112] WEDNESDAY 10 JUNE, AFTERNOON. assessing Basic Concepts in Physical and Inorganic Chemistry

SO 4... [2], to an excess of dilute sulfuric acid. A student adds a sample of solid potassium carbonate, K [3]

N-Chlorination of secondary amides. I. Kinetics of N-chlorination of N-methyl acet amide

Anhydrous strontium chloride is not used in toothpaste because it absorbs water from the atmosphere. The hexahydrate, SrCl 2.6H 2O, is preferred.

Name AP CHEM / / Collected Essays Chapter 17

3.2.5 Group VII. Trends in reducing abilities. 222 minutes. 218 marks. Page 1 of 21

State the strongest type of interaction that occurs between molecules of hydrogen peroxide and water.

A-level CHEMISTRY (7405/1)

Elements in the Periodic Table show a periodic trend in atomic radius. In your answer you should use appropriate technical terms, spelled correctly.

Questions Q1. Describe, in detail, how you would carry out this experiment. (6) ...

UNIVERSITY OF CAMBRIDGE INTERNATIONAL EXAMINATIONS General Certificate of Education Ordinary Level

Paper Reference. (including synoptic assessment) Thursday 12 June 2008 Afternoon Time: 1 hour 30 minutes

... [1] (ii) Draw a dot-and-cross diagram to show the bonding in NH 3

Paper Reference. London Examinations IGCSE. Foundation Tier. Tuesday 10 November 2009 Afternoon Time: 1 hour 30 minutes

Unit 4: General Principles of Chemistry I Rates, Equilibria and Further Organic Chemistry (including synoptic assessment)

Chem!stry. Assignment on Redox

Paper Reference. (including synoptic assessment) Thursday 11 June 2009 Afternoon Time: 1 hour 30 minutes

UNIVERSITY OF CAMBRIDGE INTERNATIONAL EXAMINATIONS General Certificate of Education Advanced Subsidiary Level and Advanced Level

Identification of ions and gases

Science 1206 Ch. 3 - Chemical names, formulas and equations

Scholarship 2006 Chemistry

4.4. Revision Checklist: Chemical Changes

Q = Enthalpy change for the formation of calcium chloride (P). D Twice the enthalpy change of atomization of chlorine (S).

» Composed of more than one type of atom chemically bonded.» A pure substance, meaning its properties are the same throughout the substance.

Chemistry Assessment Unit AS 1

Chemical Reactions. Chemical changes are occurring around us all the time

Transition Metals Webinar Qs

AQA Chemistry Checklist

Gas Laws. Bonding. Solutions M= moles solute Mass %= mass solute x 100. Acids and Bases. Thermochemistry q = mc T

NECTA A-Level CHEMISTRY 2 May 2004

Name: Class: Redox revision questions. 50 minutes. Time: Marks: 50. Comments: Page 1 of 17

(24) WMP/Jun12/CHEM2

(a) Explain what is happening in stages 1 and 2. (3) (b) (i) Identify the products formed in stages 5, 6 and 7.

(03) WMP/Jun10/CHEM4

Advanced Subsidiary Unit 3: Chemistry Laboratory Skills I

Redox. Question Paper. Cambridge International Examinations Chemical Reactions. Score: /43. Percentage: /100

+ 10Cl 2Mn H 2 O + 5Cl 2. Deduce the half-equation for the oxidation of chloride ions to chlorine.

PhD Thesis. Investigation of the oxidation of iron(iii) complexes of porphyrin derivatives by bromate. Dénesné Rácz Krisztina

2 Answer all the questions. 1 Born Haber cycles can be used to calculate enthalpy changes indirectly.

Our country, our future 525/1 S6 CHEMISTRY PAPER 1 DURATION: 2 HOUR 45 MINUTES

4.4.1 Reactivity of metals Metal oxides The reactivity series. Key opportunities for skills development.

4.4. Revision Checklist: Chemical Changes

D = (Ut+)E4+ (UOH3+)E3,

Paper Reference. Paper Reference(s) 6246/02 Edexcel GCE Chemistry Advanced Unit Test 6B (Synoptic)

Name HONORS CHEMISTRY / / Oxide Reactions & Net Ionic Reactions

Paper Reference. Advanced Unit Test 6B (Synoptic) Monday 25 June 2007 Morning Time: 1 hour 30 minutes

Describe the structure and bonding in a metallic element. You should include a labelled diagram in your answer. ... [3] ...

Edexcel Chemistry Checklist

OXIDATION/REDUCTION REACTIONS

PRACTICAL QUESTIONS TEST TUBE REACTIONS 4&11 Questions. Dr Chris Clay

CHERRY HILL TUITION AQA CHEMISTRY A2 PAPER Section A (2 marks) (1 mark) (Extra space) Property

Lower Sixth Chemistry. Sample Entrance Examination

3. Which of the following compounds is soluble? The solubility rules are listed on page 8.

Cambridge International Examinations Cambridge International Advanced Subsidiary and Advanced Level

Unit 7 Chemical Reactions. Ch. 8 & 19.1

SOME BASIC CONCEPTS IN CHEMISTRY

Preparation of a Coordination Compound. Step 1 Copy the balanced equation for the preparation of FeC 2 O 4.. 3H2 O from FeC 2 O 4. Mass of watch glass

Chemistry Assessment Unit A2 1

What is the major difference between a molecular formula and formula unit?

Ternary Compounds. , to give the compound, NaNO 3, sodium nitrate.

The pk, values of simple aldehydes determined by kinetics of chlorination

CHEM J-14 June 2014

TYPES OF CHEMICAL REACTIONS

CHERRY HILL TUITION AQA CHEMISTRY A2 PAPER Section A. Answer all questions in the spaces provided.


*AC112* *20AC11201* Chemistry. Assessment Unit AS 1 [AC112] FRIDAY 26 MAY, MORNING. assessing Basic Concepts in Physical and Inorganic Chemistry

2. The accepted density for copper is 8.96 g/ml. Calculate the percent error for a measurement of 8.86 g/ml.

High temperature potentiallph diagrams for the chlorine-water system BARBARA KOLODZIEJ' AND FATHI HABASHI. Received March 26.

Due Friday, August 18 th, 2017 Mrs. Hockstok - AP Chemistry Class Olentangy Orange High School Summer Assignment

KINETICS AND MECHANISM OF KEGGIN TYPE 12-TUNGSTOCOBALTATE (II) CATALYZED POTASSIUM IODIDE OXIDATION BY PERBORATE

Unit 2 Foundation Physical and Inorganic Chemistry

3.2.2 Kinetics. Effect of temperature. 145 minutes. 145 marks. Page 1 of 22

(09) WMP/Jun10/CHEM1

(13) WMP/Jun14/CHEM2

Reactions (Chapter 4) Notes 2016.notebook. October 14, Chemical Reactions. Chapter 4 Notes. Oct 21 8:44 AM. Oct 22 10:14 AM

Chemical measurements QuestionIT

Advanced Subsidiary Unit 1: The Core Principles of Chemistry

IB Chemistry 1 Mole. One atom of C-12 has a mass of 12 amu. One mole of C-12 has a mass of 12 g. Grams we can use more easily.

Unit 4: General Principles of Chemistry I Rates, Equilibria and Further Organic Chemistry (including synoptic assessment)

TIME 1 hour 30 minutes, plus your additional time allowance.

Electrochemistry: Oxidation numbers. EIT Review F2006 Dr. J.A. Mack. Electrochemistry: Oxidation numbers

INSTRUCTIONS ON EVERY AP EXAM:

Properties of Aqueous Mixtures of Pure Salts. Thermodynamics of the Ternary System: Water-Calcium Chloride-Magnesium Chloride at 25 C

Chem!stry. Mole Calculations Assignment Twelve

3 Chemical Equilibrium

Transcription:

The Decomposition of Aqueous Sodium Bromite C. L. LEE AND M. W. LISTER Department of Chemistry, University of Toronto, Toronto 181, Ontario Received March 24, 1971 An investigation of the rate of decomposition of aqueous sodium bromite is described. The main reactions are: 2BrOZ- + BrO- + Br03- and Br- + Br0,- + 2Br0-, followed by BrO- + BrOz- + Br- + Br03-. The rate constants and activation parameters of the decomposition reactions are reported. As the second reaction is the reverse of that previously studied in the decomposition of sodium hypobromite, its equilibrium constant (at various temperatures) can be obtained, and hence the thermodynamic properties of aqueous bromite ions. These are briefly compared with the properties of similar ions containing bromine or chlorine. On dkcrit les recherches entreprises en vue de determiner la vitesse de decomposition d'une solution aqueuse de bromite de sodium. Les reactions principales sont: 2Br02- + BrO- + Br03- et Br- + Br02- +2Br0- puis,bro- + Br0,- + Br- + Br03-. On rapporte les constantes de vitesse et les parametres d'activation pour ces reactions de dccomposition. Puisque la deuxieme reaction est I'inverse de celle ktudike preckdemment pour la dkcomposition de l'hypobromite de sodium, sa constante d'equilibre (B diffkrente temperature) peut Btre obtenue et par consequent les proprietks thermodynamique des ions bromites en solution aqueuse. Celles-ci sont brievement comparkes avec les proprietes d'ions similaires contenant du brome ou du chlore. Canadian Journal of Chemistry, 49, 2822 (1971) This paper is concerned with the kinetic and, to a lesser extent, thermodynamic stability of bromite ions in aqueous solution. The results permit some comparisons to be made amongst the series of bromine oxvions. and these in turn are briefly compared witi the gnalogous chlorine compounds. Bromite ions have been relatively little investigated, but a study of their kinetic stability was made by Engel, Oplatka, and Perlmutter-Hayman (I) as part of their research on hypobromite ions. We have examined their decomposition under somewhat different conditions and over a range of temperature, and a comparison with their results will be made later in this paper. A fairly extensive investigation of the conditions of formation of bromite from hypobromite ions, and of the preparation of sodium bromite, has been made by Breiss (2). The present work was done at suficiently high ph, so that protonated species (particularly HOBr) would be present only at very low concentrations. Acidified sodium bromite decomposes rapidly, so presumably other reactions, not investigated in the present work, are then important. Experimental Sodium Bronzite Several sources were used for the reagent. Firstly, it was prepared by the method of Breiss (2), which gave crystals of the trihydrate, NaBrOz.3HZ0. Secondly, crystals of the same composition were made available by La SocietB d'~tudes Chimiques pour 1'Industrie et I'Agriculture, of Argenteuil, France, to whom we are much indebted. Thirdly, a solution of the compound was obtained from the Olin Mathieson Chemical Corporation of New York, and this solution was evaporated and the sodium bromite recrystallized. Most of the experiments used material from the first two sources. Since the solid showed a tendency to decompose, the crystals were dissolved in dilute sodium hydroxide solution to give a stock solution that was reasonably stable, and which was diluted as required for the experiments. Sodium hydroxide and bromine, used in the preparation of sodium bromite, were of analytical reagent grade, as were the sodium bromide and sodium perchlorate which were added to the solutions in the kinetic experiments. Apparatlrs In the kinetic runs, samples of the appropriate solution were sealed in Pyrex glass ampoules, and immersed in a thermostat for known lengths of time. The thermostat contained silicone oil, controlled to f 0.02 "C. The solutions contained sodium bromite, sodium. hydroxide, sodium bromide (not added in some runs), and sodium perchlorate to adjust the ionic strength to a value of 0.50. At suitable times the ampoules were removed, rapidly cooled, and the contents analyzed. Analysis of Sol~rtions The solutions in general contained sodium bromide, hypobromite, bromite, and bromate, sodium hydroxide and possibly a little carbonate. The sodium perchlorate present was assumed not to react, so its concentration was known from the amount added initially. The sodium bromide concentration was also known from the amount put in initially, plus the amount formed in the reaction (see below). The sodiilm bromite and hypobromite were estimated

LEE AND LISTER: DECOMPOSlTlON OF AQUEOUS SODIUM BROMITE 2823 spectrophotometrically with a Beckmann DU Spectrophotometer. Their extinction coefficients were measured from the absorbances of freshly prepared alkaline solutions; in the case of sodium hypobromite this was made in the usual way by adding bromine to cold sodium hydroxide solution. It was checked by polarography that these solutions did not contain appreciable amounts of the other ion (e.g. hypobromite in the bromite solution). The polarographic experiments would have detected 0.5% of the other ion as impurity. The extinction coefficients found were as follows: Extinction coefficient Wavelength (nm) NaBrO NaBrO, The solutions used to obtain these extinction coefficients were standardized by titration with arsenious oxide at a ph regulated by excess sodium bicarbonate (3). The arsenious oxide reacts with both sodium hypobromite and bromite. In the kinetic runs measurements were made at 296 and 380 mp, and it was checked that the other species present did not contribute appreciably to the absorbances at these wavelengths. It was found that the total oxidizing normality, measured by the iodine liberated on adding excess potassium iodide and sulfuric acid, did not change during a run, so presumably oxygen is not evolved. Consequently changes in bromide and bromate concentrations could be calculated from the mass balance of bromine and oxygen atoms. The absence of oxygen evolution was confirmed (within moderate limits) by the fact that the ampoules did not develop increased pressure during a run. The concentration of sodium hydroxide was found by adding excess hydrogen peroxide to a sample, boiling to destroy the excess, followed by titration with standard acid. The hydrogen peroxide reacts with both sodium bromite and hypobromite. Mechanism and Calculation of Rate Constants Ellgel, Oplatka, and Perlmutter-Hayman (1) proposed a mechanism for the decomposition of sodium bromite. Our results fit their mechanism, though with some difference in the relative contributions of the various reactions. They found a dependence of the rate on ph,while under the conditions of the present experiments (0.06 to 0.18 M sodium hydroxide), no change in rate constant was found with varying [OH-]. They interpreted their results as showing that at the lower ph of most of their experiments protonated species are reacting. Presumably these species are present in such low concentrations under the conditions of our experiments as to have no effect. However, it should be mentioned that in the somewhat analogous decomposition of hyperbromite ions, the rate increases with [OH-], and the rate in fact passes through a minimum at about the ph values we have used (3, 4). It is possible, therefore, that a similar minimum occurs for bromite ions, and that the apparent lack of ph dependence arises because our experiments fall in the region of this minimum. We can therefore re-write their mechanism, and propose that the following reactions occur: Reaction 4 is the reverse of reaction 3, and is the initial step in the decomposition of hypobromite ions. Engel, Oplatka, and Perlmutter-Hayman found that, at 25 "C and at the concentrations they used, reaction 3 was more important than reaction 1. However, in our experiments, both reaction paths made appreciable contributions, with reaction 1 predominating. The mechanism above gives rate equations which could not be integrated, but since k2 is relatively high, the steady state approximation was made that d[bro-]/dt = 0. From this, putting [Br-] = x, [BrO-] = y, and [BrO,-] = z, we get Values of k4 are known (1, 4, 5), and also of k2 (5), and these combined with the values of k, and k, obtained below show that the term 2k4y2 is small enough to be neglected. Hence y = (klz + 2k3x)/k2. With this approximation, the rate equations can be integrated to give (with P = xolzo)

2824 CANADIAN JOURNAL OF ZHEMISTRY. VOL. 49, 1971 A plot of l/z against t should give an exponential curve of increasing slope, but it was found that our experimental results were such that the curvature was very slight during the decomposition of the first 20-25% of the sodium bromite. The slope d(l/z)/dt is and the initial slope is 3(k3j3 + k,). In practice, we took an average slope, (l/z - l/zo)/t, over the first part of the reaction. This average slope can be shown to be So (ect - l)/ct,where Sois the initial slope, and c = k3(3p + l)z,. The average slope was therefore corrected to give the initial slope by this expression. This involves a knowledge of k,, which was obtained as described below. The process of correction was repeated until the value of k, used to obtain So was the same as the final value of k,. Finally So was plotted against P, which gave a linear plot, though with some scatter. The best line through the points was obtained by least mean squares, and k, and k, were obtained from this line, since So = 3(k,P + k,). The corrections from the average to the initial slopes were mostly under 574, and in only one run above 10%. After the rate constants had been obtained, the validity of the steady state approximation was checked as follows. Firstly, the concentrations of hypobromite ion, which are also obtainable from the measured absorbances, were compared with the steady state values given by (k,z + 2k,x)/k,. However, [BrO-] was always so low, that the most that can be said is that the values were of the right order of magnitude. In a typical run [BrO,-] = 0.05 M, and the calculated [BrO-] = 0.0004 M. As the extinction coefficients are not very different, it follows that a very small error in absorbance gives a large error in [BrO-1. Secondly, the differential equations were integrated numerically, with the assumption that initially [BrO-] = 0. It was found that the steady state concentration of hypobromite had developed rapidly compared with the rate of decomposition of the bromite. 95% of the steady state [BrO-] was reached during the first 1 to 23% of the bromite decomposition, the exact amount depending chiefly on the concentration of bromide ions. At the same time the slope, which starts low if [BrO-] is initially zero, had risen to 97 to 98% of its steady state value. The first sample was taken after a time that was long enough to ensure firstly that temperature equilibrium had been reached and secondly that steady state conditions had been virtually established. Results Table 1 gives the results for the main series of runs at 76.6 "C. The slopes are corrected on the assumption that k, = 3.925 x M-l s-', and the least mean squares line drawn through So plotted against P gives k, = 3.917 x 10-7~-1 s-'. The best value for k, is therefore 3.92 x M- ' s-'. The value derived for k, is 3.04 x M-' sc1. Similar data for 86.0 "C are given in Table 2. Here the slopes are corrected on the assumption that k, = 6.90 x M-' s-l, and the resulting plot of So against j3 makes k, = 6.896 x 10-7 M-l s-l. Hence the best value for k, is 6.90 lo-' M-' s-,, and the value for k, is found to be 8.10 x M-' s-'. Table 2 also contains data for 96.7 "C. The slopes are corrected with k, = 12.08 x M-' s-', and these in turn give k, = 12.06 x M-' s-'. The best value for k, is taken to be 12.07 x M-' s-', and the value of k, is found to be 24.79 x M-' s-l. A plot of log k, or log k3 against 1/Tis reasonably linear in both cases. For k,, the activation energy is 26.8, kcal/mol. If we assume that AH* isindependent of temperature, then AH* = 26.2, kcal/mol (at 25 "C) and AS* = -7.3 cal/deg mol; log k, extrapolated to 25 "C is -8.43. For k,, the activation energy is 13.7 kcal/mol. From this, AH* = 13.1 kcal/mol (at 25 "C) and AS* is - 47 cal/deg mol; log k, extrapolated to 25 "C is -7.96. The slope, So, and hence the rate constants do not appear to depend on the concentration of hydroxide ions present. Neither k, nor k, gave any systematic trend with [OH-] over the range 0.06 to 0.18 M. Discussion The results of the present work differ somewhat from those of Engel, Oplatka, and Perlmutter- Hayman (I), but the differences can be attributed to different experimental conditions. Firstly, these workers find the rate decreases with increasing ph, by a factor of 3 for every ph unit. However, their results are only for ph values of 8.5, 9.7, and 13.0, and they did not investigate whether there is any change around ph 13. Our

LEE AND LISTER: DECOMPOSlTlON OF AQUEOUS SODlUM BROMlTE 2825 TABLE 1. Decomposition of sodium bromite at 76.6 "C [BrOz-lo x lo2 [Br-Io x lo2 [OH-] so x lo5 Run (M) (M) (M) (M-I s-i) P TABLE 2. Decomposition of sodium bromite at 86.0 "C Temperature [Br02-lo x [Br-lo x [OH- 1 so x lo5 Run c'c) (M) (M) (M) (M-I s-l) P results indicate that at high ph, the rate does not change with ph; this is presumably because protonated species (such as HOBr), which could offer alternative routes for the reaction, are effectively absent in 0.1 M sodium hydroxide. Hence we have written the reactions as occurring between ions. Secondly, the earlier workers found that at 25 "C the reaction Br- + Br02- -, 2Br0- predominated under their experimental conditions. However, the rate constants they quote are not very different: in our nomenclature, they give k, = 1.3 x M-' s - ', and k, = 1.43 x lop4 M-' s-'. At high temperatures, we find k1 greater than k,, but the activation parameters are such that this order reverses at low temperatures, and the rate constants extrapolated to 25 "C are k, = 3.7 x lo-', k, = 1.1 x lo-' M-' s-'. This is a long extrapolation, but at least it agrees with Engel, Oplatka, and Perlmutter- Hayman's result that k, is more important at low temperatures. Their rate constants quoted above are for a ph of 8.5, which is presumably why they are much larger than ours. However, the discrepancy is larger than would be expected from their observations on the effect of ph, and cannot at present be explained. The results allow some calculations to be made on the thermodynamic properties of bromite ions. Reactions 3 and 4 above lead to an equilibrium k3 Br- + BrO2-=2Br0- k4 with the activation parameters: reaction 3 has AH* = 13.1 kcal/mol, AS* = -47 cal/deg mol;

2.9 2826 CANADIAN JOURNAL OF CHEMISTRY. VOL. 49, 1971 TABLE 3. Conventional thermodynamic quantities for aqueous ions at 25 "C Ion AHOr AGO, So - Ion AHor AGOr So C1- -40.0-31.35 13.2 Br- -28.9-24.6 19.3 C10- -25.4-8.9 10.0 BrO- -21.9-8.0 12.0 CIOz - -16.6 2.7 24.1 Br02- -8.9 6.5 30.5 C10,- -25.15-2.15 38.8 Br03- -16.2, 4.3 38.6 c104- -31.0-2.1 + 43.5 BrOo; - 28.9 44.7 clzozz -* -26.3 10.1 8.7 BrzOz -25.0 9.1 3.0 and reaction 4 has AH* = 18.8 kcal/mol, AS* = -21 cal/deg mol (5). Hence AH for the reaction in the k, direction is - 5.7 kcal/mol, and AS is - 26 cal/deg mol. Thermodynamic data on dilute aqueous solutions are for sodium bromide : AH0, = -86.2, AGO, = - 87.2 kcal/mol, SO = 33.7 cal/deg mol; and for sodium hypobromite: AH0, = -79.1, AGO, = -70.6 kcal/mol, So = 26.4 cal/deg mol (6, 7). Hence calculated values for sodium bromite (aq) are: AH,' = -66.3 kcal/mol, and So = 45 cal/deg mol. These results, combined with data for the elements in sodium bromite, make the value for its AGO, = -56.1 kcal/mol. Some confirmation of this is provided by the value for AHO, of - 66.0 kcallmol from calorimetric measurements on the reaction of aqueous sodium bromite and sodium sulfite (8). Table 3 summarizes values for chlorine and bromine oxyions, in order to show that the values deduced above for sodium bromite (aq) are reasonable. The data come from refs. 6,7, and 9. Values are included for the activated species X2OZ2- * (for C12022- *, see ref. 10). The values in Table 3 are conventional values, relative to H+ (aq) as zero. The general trends of these quantities are similar, apart from the well-known low stability of perbromates. As regards bromite ions, their AH0,, relative to the other bromine ions, is somewhat more positive compared to the chlorine series. This is somewhat offset by their higher entropy, so that there is less contrast inagof. Thus the equilibrium constant for X- + X0,- =$ 2x0- is calculated to be 1.4 x for the bromine compounds, and 1.4 x lo-'' for chlorine. The activated species X2OZ2- * are also not very different in the two series, although here the entropy of the bromine species is somewhat lower. At present, it does not seem to be possible to explain these differences in detail. In a recent paper (ll), Massagli, Indelli, and Pergola report results of the decomposition of bromite at ph of 8.5 and below. Their results follow a rate equation Rate = [HBr02][Br-]{kl + k, [H']} which is evidently a different mechanism from ours, the difference being presumably attributable the much lower ph of their experiments. 1. P. ENGEL, A. OPLATKA, and B. PERLMUTTER-HAYMAN. J. Am. Chem. Soc. 76, 2010 (1954). 2. J. BREISS. Ph.D. Thesis. L'universitC de Strasbourg, Strasbourg, France. 1959. 3. R. M. CHAPIN. J. Am. Chem. Soc. 56, 2211 (1934). 4. B. PERLMUTTER-HAYMAN and G. STEIN. J. Phys. Chem. 63, 734 (1959). 5. M. W. LISTER and P. E. MCLEOD. Can. J. Chem. In publication. 6. W. M. LATIMER. Oxidation potentials. 2nd ed. Prentice-Hall, Inc., New York. 1952. 7. National Bureau of Standards Circular 500, U.S. Government Printing Office, Washington. 8. M. B. KENNEDY and M. W. LISTER. Unpublished result. 9. G. K. JOHNSON, P. N. SMITH, E. H. APPELMAN, and W. N. HUBBARD. Inorg. Chem. 9, 119 (1970). 10. M. W. LISTER. Can. J. Chem. 34, 465 (1956). 11. A. MASSAGLI, A. INDELLI, and F. PERGOLA. Inorg. Chim. Acta, 4, 593 (1970).