&EPA
           United States
           Environmental Protection
           Agency
          Environmental Sciences Research
          Laboratory
          Research Triangle Park NC 27711
EPA 600 7 79-088
April 1979
           Research and Development
Surface Reactions of
Oxides of Sulfur

Interagency
Energy/Environment
R&D Program
Report

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                                        EPA-600/7-79-088
                                        April 1979
    SURFACE REACTIONS OF OXIDES OF SULFUR
                      by

                J.  H. -Lunsford
            Department of Chemistry
             Texas  A&M University
         College Station, Texas  77843
              Grant No.  R-801136
                Project Officer

                Jack L. Durham
  Atmospheric Chemistry and Physics Division
  Environmental  Sciences Research Laboratory
 Research Triangle Park, North Carolina  27711
  ENVIRONMENTAL SCIENCES R£SEARCH LABORATORY
     OFFICE OF RESEARCH AND DEVELOPMENT
    U.S.  ENVIRONMENTAL PROTECTION AGENCY
RESEARCH  TRIANGLE PARK, NORTH CAROLINA  27711

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                                 DISCLAIMER
     This report has been reviewed by the Environmental Sciences Research
Laboratory, U.S. Environmental Protection Agency, and approved for publica-
tion.  Approval does not signify that the contents necessarily reflect the
views and policies of the U.S. Environmental Protection Agency, nor does
mention of trade names or commercial products constitute endorsement or
recommendation for use.
                                      n

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                                   ABSTRACT


     Surface reactions of several sulfur-containing molecules have been studied
in order to understand the mechanism by which sulfate ions are formed on atmos-
pheric aerosols.  At 25°C the heterogeneous oxidation of S02 by N02 to sulfuric
acid and sulfate ions occurred on hydrated silica and silica-alumina surfaces.
Nitrosonium ions, probably in the form of NOHSOit, underwent surface hydrolysis
to form H2SOi* and NO.  The oxidation of S02 by 02 was undetectably slow on
these surfaces; however, the reaction was catalyzed by Mn2+ ions in a Y-type
zeolite, which is a crystalline aluminosolicate.  In this case the only reac-
tion product was a SOi,2" species which was strongly bound in the zeolite micro-
pores.  Substantial activity was observed only on partially and fully hydrated
zeolites.  Molecular oxygen also reacted with H2S on zeolites and magnesium
oxide, but essentially no reactions were observed on silica-alumina.  The pri-
mary reaction on zeolites resulted in the formation of elemental sulfur; where-
as, on MgO a variety of products were observed including elemental sulfur, sul-
fide ions, sulfite ions and a number of paramagnetic ions such as $3, S20~ and
Sn.  Sulfate ions were not formed from H2S following the reactions at 25°C.

     Experiments were also carried out to identify and to determine the mecha-
nism by which S20~ and H2S2 ions are formed on MgO.  The S20" ion was observed
following the surface reaction of H2S with S02, and formation of the ion was
promoted by ultraviolet light.  A mechanism has been proposed in which S2 mole-
cules react with oxide ions of the lattice.  The H2S2 ion was formed upon
reacting H2S with trapped electrons on the surface.  Information on the elec-
tronic structure of both paramagnetic species has been obtained from sulfur-33
hyperfine data.

     In order to establish the geometric structure of the S20" ion and other
paramagnetic sulfur-containing molecules on MgO, CNDO semi empirical calcula-
tions were carried out to determine theoretical values of g tensors and spins
densities as a function of bond angles and bond length.   By comparing the cal-
culated and experimental values, one could establish the structure of the mole-
cule.  This represents one of the first attempts to determine the structure of
adsorbed paramagnetic ions.

     This report was submitted in fulfillment of Grant No. R-801136 by Texas
A&M University under the sponsorship of the U.S. Environmental Protection
Agency.  This report covers the period December 15, 1973 to May 15, 1978 and
the work was completed as of November 15, 1978.
                                      m

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                                 CONTENTS





Abstract	iii




Figures	vi



Tables	vii



Acknowledgment  	 viii



     1.  Introduction 	   1



     2.  Experimental 	   3



     3.  Results	4



     4.  Discussion	27



     5.  List of Publications	30



References	  31

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                               FIGURES

Number
  1    S(2p) and N(ls) ESCA spectra produced by  reacting  S02 with  N02.   5
  2   Infrared spectra of S02 and N02 on hydrated  Si02	   7
  3   ESCA spectra of sulfur and manganese 2p  levels	   9
  4   Initial rate of SO^ formation versus S02  partial pressure.  .  .  13
  5   XPS spectrum of sulfur 2p lines	17
  6   EPR spectrum of S2(T on MgO	18
  7   EPR spectrum of S20" containing sulfur-33 on MgO	20
  8   EPR spectra of H2S2 on MgO.	22
  9   EPR spectra of H233S2 on MgO	23
                                      VI

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TABLES
Number
1
2
3
4
C
6
7
8

Binding EnergiGS (eV) of Adsorbed Species 	
Observed Frequencies of Adsorbed Species 	
Reactive Capacities of MnY Zeolite Cat?lysts. . . 	 	

n-\/alijp«; of thp Isoelectroni c SOo SoO" and S^ Ions 	 ,
A Comparison of the Experimental and CNDO/2-Calculated
A Comparison of Spin Densities Determined from CNDO/2
Calculations and Experimental Hyperfine Data 	
Spin Density of the Isoelectronic SOI, $20" and $3 Ions on
MqO 	
Pacje
4
8
10
14
19
25
26
28
   VI1

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                               ACKNOWLEDGMENT
     The contributions of Dr.  Jack L.  Durham in keeping the author abrest of
current views on the oxidation of S02  in the atmosphere was a significant
factor in this work.  The author also  wishes to express appreciation to
Prof. R.  M.  Hedges for the double-precision version of the CNDO/2 program
and to Dr. T. T. Yu for assistance in  programming.
                                    vm

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                                   SECTION 1

                                 INTRODUCTION


     Expanding utilization of coal  and lignite as primary fuel  sources has
prompted concern over the fate of sulfur dioxide in the atmosphere.   This major
pollutant is produced during combustion at a rate in excess of seventy billion
pounds per year in the United States (1).  In addition, sulfur, mainly in a
more reduced state such as found in hydrogen sulfide, is introduced  into the
atmosphere during the decay of organic matter.  Aerosols which contain adsorbed
oxides of sulfur have been implicated as causative agents for vegetation dam-
age, reduced visibility, and chronic pulmonary diseases (2,3).   For  lack of
conclusive evidence, the harmful form of sulfur is believed to be the sulfate
ion.  Of particular importance in this respect are the poorly understood mecha-
nisms through which sulfur dioxide  or hydrogen sulfide may be transformed into
surface sulfate ions.  Potential oxidizing agents include molecular  oxygen,
ozone, and nitrogen dioxide.

     Catalysts for the oxidation of S02 have long been known.  In 1871, Deacon
(4) demonstrated that a solution of CuSOit was capable of producing sulfuric
acid from a gaseous mixture of SOa  and air.  Since that time, solutions of many
other salts have been shown to display similar catalytic activity.  More re-
cently, several research groups (4-6) have explored the oxidation of S02 in
water droplets containing dissolved metal salts.  The objective of these
studies has been to more closely approximate atmospheric conditions  by using
droplets of a size comparable to those occuring naturally in atmospheric fogs.
These studies of S02 oxidation have shown that the catalysts in the  droplets
can display appreciable activity under ideal conditions.  Furthermore, the
experiment repeatedly indicate that Mn2+ is one of the most active catalysts in
such systems at ambient temperatures.

     No significant results are available regarding the reactivity of adsorbed
S02 with oxides of nitrogen.  This  is unfortunate from a practical viewpoint
because NO and N02 are also common  constituents of stack gases, along with S02.
The related gas phase S02-N02 reactions have attracted continued interest
(7,8).  The results generally imply that the photoxidation of S02 to S03 may
occur at high concentration levels; however, at atmospheric levels,  which are
on the order of lO^-lO"2 ppm, quenching by molecular oxygen essentially pre-
cludes SOs production.  Recent evidence (9,10) suggests that photolysis of S02-
N02-air mixtures yields NOHSOit aerosol which slowly hydrolyzes in air to form
sulfuric acid and NO.

     It has been suggested that it  is possible to obtain sulfate ions from H2S
under ambient conditions, prov/ided  a catalyst (an aerosol) is employed.  The

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oxidation of H?S by molecular oxygen has indeed been observed,  but the major
product is elemental sulfur.   Moreover, the catalyzed reaction  usually requires
elevated temperatures and high humidity.  Catalysts include activated carbon,
molecular sieves, alumina, bauxite and Al-Mg alloy (11-17).

     The purpose of this study has been to explore the surface  reactions of S02
with 02  (18) and N02 (19,20) as well as the reactions of H2S with 02 (21).
The solids included both acidic alumino-silicates and a basTC metal oxide.  MgO.
Hydrated silica, which is generally considered to be a rather inert solid,  was
also used during the study with N02.  The oxidized forms of sulfur were de-
tected  both spectroscopically  (electron paramagnetic resonance, inf™re°.a™coc
X-ray photoelectron spectroscopy) and by wet chemical techniques.  In all cases
temperatures near ambient were used, although the concentrations of S02, H2S
and N02 were much higher than  those found under atmospheric conditions.

      In addition to studying  the  reactions  involving the oxidation of S02 or
H2S,  research  has also been  carried out on  the formation and structure of para-
magnetic sulfur-containing molecules.   These molecules  include H2S2,  which  is
formed  by  allowing  H2S to  react with  trapped electrons  on  MgO, and S20  . wh  ch
 is formed  by  reacting H2S  and S02 on  the  same metal  oxide  (22, 23).   In  addi-
 l on  to yielding S2C)-, the  reaction between H2S  and  S02 produces  elemental  sul-
 fur and water (the  Claus  reaction).   The  geometric  structure of  S20   and other
 sulfur-containing  radicals  has been determined  by comparing calculated magnetic
 oarameters with those which  have  been observed  experimentally  (24).

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                                   SECTION 2

                                 EXPERIMENTAL
     Details of the experiments may be found in refs.  18-23;  however, a sum-
mary of the materials and techniques will  be described here.    Amorphous silica
gel and silica-alumina (9.3% alumina) were used as supplied from a commercial
source.  The BET surface areas of the silica and silica-alumina, obtained from
nitrogen adsorption data, were 310 and 360 m2/g, respectively.   The MnY zeo-
lites were obtained by exchanging a sodium form in aqueous solutions of MnCl2
which yielded Mn2+ concentrations between  0.4 and 23 ions per unit cell.  High
surface area magnesium oxide was prepared  by reacting  reagent grade powder
with water at 100°C.  The resulting Mg(OH)2 was decomposed under vacuum at
300°C and then 500°C giving MgO which had  surface area ca_. 200 m2/g.

     With the exception of isotopically enriched S02 and H2S, all of the gases
were obtained from commercial sources.  Sulfur-33 enriched S02 was prepared by
allowing 3 mg of sulfur containing 25.5 or 59.2% 33S to react with an excess of
pure oxygen at 450°C for 2 hr.  Oxygen-17  labeled S02  was prepared in a similar
manner by using 41.7% enriched 1702-  Sulfur-33 enriched H2S was prepared by
allowing 5 mg of sulfur containing 25.5% 33S to react  with an excess of pure
hydrogen at 300°C for 10 hr.  The unreacted gases were removed by the freeze-
pump technique prior to adsorption.

     The S02 uptake and reaction products  were determined by gravimetrically
measuring the adsorption, by analyzing for the sulfate formed and by several
spectroscopic techniques.  The sulfate formed in the zeolite was determined by
using a barium titration procedure, following the digestion of the zeolite in
HC1.  The ESCA spectra were obtained on a  photoelectron spectrometer using alu-
minum Ka x-radiation.  From the binding energies of the emitted electrons the
oxidation state of the sulfur could be determined.  Binding energies are re-
ferenced relative to the Au 4f7/2 level (84.0 eV) of gold which was vacuum
sputtered onto the samples.  Transmission  infrared spectra were obtained with
the samples in the form of thin self-supporting wafers.  The paramagnetic ions
were identified by electron paramagnetic resonance (EPR) spectroscopy.

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                                   SECTION  3

                                    RESULTS
SURFACE REACTIONS OF S02 WITH N02

     Using ESCA it was determined that S02 does not chemisorb on silica or
silica-alumina at 25°C, and neither does it react on the surface with 02 or
air.  Markedly different behavior was observed when S02 and N02 were allowed to
react at 25°C on the hydrated surfaces.  Curve a of Figure 1 was recorded after
admitting 25 Torr S02 to a silica sample for 4 hr, expanding the excess gas
phase to about 2 Torr, and introducing 25 Torr of N02 for 4 hr.  An intense
S(2p) line demonstrates that a strongly bound sulfur oxoanion was formed in
the surface reaction.  Likewise, curve b illustrates spectra collected from
a hydrated Si02-Al203 sample after admitting 8 Torr S02 for 20 min, expanding
the excess to less than 1 Torr, and subsequently adding 8 Torr N02 for 4 addi-
tional hr.  Both samples were in the spectrometer about 12 hr at 60°C before
collecting the N(ls) spectrum, and desorption of the residual species was not
detected.

     For comparison purposes, curve c depicts the S(2p) and N(ls) ESCA spectrum
for  (NHit)2 SOt,  .  The 2p3/2 and 2pi/2 binding energies in each spectrum are
very close to 168.9 and 169.9 eV, respectively.  Based upon the similarity in
binding energies following the surface reaction and those observed for (NH^
S0i», we conclude that sulfate ions are present on the surface  in both cases.
The  identification of this and other surface  species is given  in Table 1.
       TABLE 1.  BINDING ENERGIES  (eV)a OF ADSORBED SPECIES
Adsorbate Orbital

background N(ls)
NO2 N(ls)

S02 + N02 S^2p3/2^
S(2p1/2)
S(2s)
N(ls)
a) ±0.2 eV
b) (Fwhm)
SiO2

-
407.2(1.8)b
400.6(1.9)
168.9(1.4)
169.9(1.4)
233.1(1.9)
401.2(1.8)


Si02-Al203

401.9(1.9)
407.3(1.8)
400.5(1.9)
168.8(1.4) ~J
169.9(1.4) >
233.0(1.9) J
401.3(1.8)


Assignment
+
NHit
N03~
phys. ads. N2Oit

SOi^

NO+ or -O-N=O



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                   174    170    166    162 408   404   400    396
                             BINDING  ENERGY, eV
Figure 1.  S(2p) and N(ls)  ESCA spectra produced by reacting S02 with  N02:
(a) Si02; (b) Si02-Al203-, (c)  pure (NHJ2S(V

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Tt  should be noted  that the formation of N
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                         1400  2000   1800  1600  1400  1200

                                WAVENUMBER, cm"'
Figure 2.  Infrared spectra  of  S02  and N02 on hydrated Si02: (a) background;
(b) 5 Torr S02 added 20 min  with  excess expanded to about 2 Torr;  (c)  7
Torr NOa-Mu admitted 30 min  [(--)  18 Torr]; (d) degassed at 25°C  for
3 hr (6 hr);  (e) 8 Torr H20  adsorbed.

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                                                            -IN a
      TABLE 2.  OBSERVED FREQUENCIES OF ADSORBED SPECIES  (cm" )


   AdsorbateSiCbSiO2-Al203              Assignment
      H2o         1635         1635     U2 phys.  ads. H20

      S02         1337         1336     03 phys.  ads. S02

      N204        1735         1730     Ug-U(NO)  phys. ads. N^

      N02       1315(sh)        1320     u
                                                H
                                                H
                                690
1680         1672     Uit(B2);
^OiiiiN.	 phys. ads.
                  1420       1420(sh)   03

                               1545     VJ(AI) bidentate nitrato species

                               1590     UNQ  antisym.
                               1650

        N02        595          610

                   975          960
                  2460         2465     0    sym. H2SOif
                                         U—M

                  2280         2270     \)\ NO
                                                     Tl
                  1400         1398     UN02>- Si-0-N-Si<
  sh = shoulder

   (a) ± cm'1
   (b) only  on  Si02'Al203  degassed to  500°

SURFACE REACTIONS OF S02 WITH 02

     The ESCA spectra of a representative MnY sample, both before and after
exposure to the S02-02 mixture, are shown in Figure 3.  The spectrum of pure
Mnsoti   ncluded for comparison purposes.   From the observed binding energies
at 168 8 and 169.9 eV it is evident that sulfate ions were formed in the zeo-
lite during reaction.  It also may be noted from the spectra that no other
strongly adsorbed sulfur species were present on the catalyst surface either
before or after reaction.

     Adsorption experiments were undertaken to determine the reactive capacties
of the various zeolites.  The zeolite samples were allowed 24 hr Jo react and
equilibrate with the  reactant gases which contained  40 Torr 02 and 10 Torr  S02.
To determine quantitatively the fraction of the total irreversible adsorption
that was due to the  formation of  sulfate ions, several samples of MnY used  in
the adsorption experiments were analyzed for SO,2' via the barium titration

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BINDING   ENERGY  (eV)
165

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technique.  It was found in all cases that the irreversibly adsorbed material
observed gravimetrically was completely recoverable as SO^2" using the titra-
tion; therefore, the results of the adsorption experiments are reported in
Table 3 where all irreversible adsorption has been considered to be due only
to the formation of the sulfate ion.
      TABLE 3.   REACTIVE CAPACITIES OF MnY ZEOLITE CATALYSTS
Manganese concentration
(Mn (II) /Unit Cell)
0. 0
0.4
1.7
9.0
16
0.0
0.4
1.7
9.0
16
0. 0
0.4
1.7
9.0
16
Pretreatment Irreversible
procedure _
(no. S0~ /Unit Cell)
Fill Iv nphvHt-aforl TPAPF
1. \lMMjf LyCl 1 y UJ. u L.CU H\f\\^Ci
1.9
2.1
1.6
2.2
Partially Hydrated 0
9.9
12.1
19.0
21.2
Fnl Iv HuHr Ai-oH TPnfP
-tvJXijrri^'«^H.clUt;*«l J. XUAV^ij
45.2
50.5
46.7
49.1
adsorption
(no. SO" /Mn(II))

4.7
1.2
0.2
0.2
0
24
7.0
2.1
1.4
113
29
5.1
3.2
                                    10

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     From these results one may conclude that both  the Mn2+  ion  and  Oz  must  be
present for the oxidation of S02 to occur.   The formation of S(V~ was  not ob-
served on any of the zeolite samples in the absence of 02 while  only trace
amounts of S042- could be detected on NaY in the absence of  Mn^  .  These trace
amounts of SOi*2' could be explained by the presence of iron  impurities  in the
original zeolite.

     The reactive capacity of the zeolites was found to be strongly  dependent
                                                                      '
on the degree of dehydration of the MnY catalysts.   The amount of S(X ' formed
per unit cell in the fully hydrated samples was more than an order of magnitude
greater than the amount formed in the correspond ihg fully hydrated samples.
For any given sample pretreatment, the number of S0i*2~ ions formed per unit
cell was nearly constant.  In contrast, the number of SOi,2' ions produced per
Mn2+ ion was highly variable and reached its maximum value of 113 for the fully
hydrated MnY sample containing 0.4 Mn2+ ions per unit cell.  This large turn-
over simply demonstrates that the reaction was catalytic with respect to manga-
nese.

     The above observations show that water in the zeolite strongly affects the
reaction.  It is possible that water functions as a reactant according to the
following scheme:
                 S02(g) ->  S02(adsorbed)

                 S02(adsorbed) +   ^2 -> S03                                (2)
                 S0  + H20 -> H2SQk
 This  production  of  sulfuric  acid would  be expected to make the catalyst more
 acidic.   Since the  catalytic oxidation  of S02  by  some solutions of Mn(II)  salts
 is  known  to  have pH limitations  (27), it is  possible that the reaction within
 the zeolite  micropores  is  likewise  pH limited.  As an alternative, SOa may
 react with  lattice  oxide  ions

                       S03  +  02-(lattice)  ->   S042-(adsorbed)               (4)

 and water may simply provide a  transport mechanism for  the migration  of  SOi* "
 ions away from  the  active  sites  within  the  zeolite.

      The  crystallinity of  the zeolite during reaction comes  under question
 since the above  mechanisms involve  the  participation of lattice  oxide ions and
 the production  of sulfuric acid.  The x-ray  powder diffraction  patterns  of the
 catalysts indeed were modified after the  reaction occurred.   There was a de-
 crease in the intensity of some of  the  reflections while the background  level
 remained reasonably constant.  It is not  known at this  time  whether  (a)  the
 crystal lattice was partially disrupted as  a result  of  the  reaction  or (b) tne
 changes in  the pattern were simply  a result of the added electron density in
 the interior of the catalyst due to the production of  large  amounts  of sulfate
 product.   This matter is presently  under investigation.

      Initial rate experiments were  conducted using partially hydrated MnY zeo-
 lite to determine the reaction rate dependence, if any, on the concentrations


                                     11

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of S02, 02 and Mn2+.  Initial rate studies were not conducted on the fully
hydrated and fully dehydrated MnY sample because in the former case the rate
of adsorption of the reactant gases was extremely slow due to occlusion of
the micropores by water molecules, and in the latter case only small amounts
of S042~ ions could be formed, which led to a relatively large experimental
error.

     The results of the rate study are presented in Table 4 and in Figure 4.
There is an apparant first order rate dependence which is best described in
Figure 4 by the linear rate dependence on the pressure of S02.  Table 4A  de-
monstrates that the reaction was independent ot total pressure as was found by
increasing the total pressure in the system with helium.  Furthermore, Tables
4B and 40 show that the initial rates of reaction were independent of 02 pres-
sure and temperature respectively.

     It is recognized that the observed kinetics in such heterogeneous reac-
tions on porous catalysts may not be representative of the true reaction kine-
tics if there are diffusion processes in action which can influence the rate
of reaction.  The fact that the initial rate did not significantly increase as
the temperature was raised from 5°C to 60 C is an indication that diffusion in-
deed may be limiting the overall reaction.  Further evidence that the reaction
is diffusion limited may be found in the fact that the reaction rate increased
significantly upon addition of small amounts of Mn2+ to the zeolite, but addi-
tional exchange of Mn + resulted in only modest rate enhancement as shown in Table 4C,

     Of the three various types of diffusional limitations, only Knudsen dif-
fusion fits the experimental observations.  The Knudsen diffusion coefficient
is independent of total pressure, P, while the rates of bulk diffusion and
diffusion across a static film are inversely proportional to /P".  That Knudsen
diffusion is operative in this system is not surprising since the conditions
for Knudsen flow is that X, the mean free path of a gas molecule be much larger
than the micropore radius.  The value of X is given approximately by
which is on the order of ID"4 cm in this system.  Obviously, this is consider-
ably larger than the micropore radius of 8 x 10~8 cm in the Y zeolite.

     Under conditions of Knudsen diffusion the pseudo-order of the initial
rate of reaction with respect to SOa pressure may be found from the equation:

                              Observed Order = (n + l)/2                  (6)

where n is the true reaction order.  Thus, it is postulated that the oxidation
of S02 on MnY catalysts would be a first order process in the absence of the
Knudsen diffusion limitation.  This result is reassuring since it agrees with
the findings of many other authors, most notably Cheng e_t al_. (6), who have
studied other heterogeneous  catalysts containing maganese.
                                      12

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                        SOa.  PARTIAL  PRESSURE  (torr)
20

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TABLE 4. INITIAL RATES OF REACT J.UN 	 . 	
A. Initial rate as functions
of SC>2 pressure and total
Manganese concentration Reaction temperature
(Mn(II)/Unit Cell) <°c>
20.2
20.2
20.2
20.2
20.2
20.2
20.2
B. Initial rate as function
25
25
25
25
25
25
25
of O2 pressure
Manganese concentration Reaction temperature
(Mn(II)/Unit Cell) (°c)

20.2

20.2

20. 2
20.2
20.2
25

25

25

25
25
Pso2
(Torr)
2.5
5.0
8.0
13
17
17
17

Pso2
(Torr)
10

10

10

10
10
pressure
Po2
(Torr)
20
20
20
20
20
20
20

P°2
(Torr)
40

25

20

10
5

PHe
(Torr)
27.5
25
22
17
13
63
163

PHe
(Torr)
0

15

20

30
35

Initial rate
(mg 504 g catalyst"1 min )
19.3
31.1
37.5
71.6
84.2
83.6
85.2

Initial rate
(mg SO^ g catalyst"1 min"1)
97

103

116

101
96
	 	 	 (rv-mhirmpdl

-------
                                      TABLE 4 (cont.)


C.  Initial rate as function  of  manganese concentration


    Manganese concentration    Reaction temperature     Pso->
                                      / O (~* \                 ^

                                                        (Torr)
(Mn (II) /Unit Cell)
                                                          (Torr)
      Initial


(mg SO^ g catalyst"  rain" )
0
0.4
1.7
9
16
23
D. Initial rate as function
Manganese concentration
(Mn (II) /Unit Cell)
16
16
16
16
16
16
16
25
25
25
25
25
25
of temperature
Reaction temperature
60
50
40
30
20
10
5
7.5
7.5
7.5
7.5
7.5
7.5

Pso2
(Torr)
10
10
10
10
10
10
10
24
24
24
24
24
24

(Torr)
40
40
40
40
40
40
40
0
26.2
29.0
35.8
39.1
40.9

Initial rate
(mg SC>4 g catalyst" min"1)
56
55
59
47
47
59
54

-------
SURFACE REACTIONS OF H2S WITH 02

     The ESCA spectrum of a MnY zeolite after the introduction of H2S  and  02
showed only one sulfur species which is assigned to elemental  sulfur by its
lpv?and 2pi/? binding energies of 162.8 and 164.0, respectively.   A  spectrum
of sulfur  howlver of much lower intensity, was obtained without the exposure
of the sample to oxygen.  The elemental sulfur remained on the surface after
it had been exposed to the atmosphere for 2 weeks.  On NaY a "miTar spectrum
was observed after the reaction, although the concentration of elemental sul-
fur was  less than half as great as with the MnY zeolite.  The dissociation of
H?S over zeolites to form elemental sulfur has been previously studied, and
the results reported here further demonstrate that no higher oxidation states
of sulfur  are formed.  On amorphous silica-alumina virtually no sulfur lines
were  present in  the  ESCA spectrum.

      The ESCA spectrum  of the dehydrated MgO, after it  had  been treated with
H2S,  followed by a  3 min exposure to air during  the transfer of the sample to
the spectrometer,  indicated  the formation  of  two  sulfur species; elemental
sulfur and sulfide  ions  (Figure 5A).  Brief exposure to the atmosphere
showed no  evidence  of  further oxidation; however,  when  the  H2S-treated  MgO
was purposely  exposed  to  pure oxygen,  the  ESCA  spectrum indicated an  additional
 peak  (Figure  5b).   Deconvolution  of the spectrum suggested  the  sulfur 2p3/2
maxima at  167.0, 162.9 and  160.8  eV, which are  in good  agreement with the
 binding energies of sulfites. elemental sulfur  and sulfides,  respectively.   The
 formation  of sulfite ions  was favored  by low coverage of H2S  and  by long  expo-
 sure  of the sample in air,  which  is evident in  Figure 5c.   This sample of MgO
 was first exposed to H2S and 02,  and then  to the atmosphere for 2 weeks.   On a
 hydrated MgO/Mg(OH)2 surface similar results were obtained; however,  the  sulfur
 bands were much less intense.  The fractional monolayer coverage of the sulfite
 ions  formed on MgO varied from 0.1  to 0.8, depending on the equilibrium pres-
 sure of the H2S and the duration of exposure in air.

      Upon freezing the H2S  and 02 above the dehydrated MgO which was  at -196°C
 a small amount  of SO3 was evident in the EPR spectrum with g = 2.0034.  Upon
 warming to 25°C for 5 min the  catalyst turned yellow and the spectrum of SOs
 disappeared.  A much greater concentration of S20~, which  is characterized by
 9! =  2.030, g2  = 2.010 and  g3  = 2.001 was observed.  Moreover, the EPR spectrum
 recorded  at -196°C  indicated the formation of the $3 ion, which is charac-
 terized by gi = 2.043 and gii= 2.004.  A relatively small  peak at g = 2.052
 was  observed at both 25°C and  -196°C,  in addition to the spectrum of S20~ and
 $3,  following the  oxidation of H2S by  02.  This species dominated the spectrum
 at higher coverages of H2S, and the g  values (gi  = 2.052,  g2 = 2.033, g3 =
 2.002)  correspond well with those  assigned to  Sn. No  EPR  signals were detected
 for  sulfur species  on  zeolites or  on  silica-alumina.

 ELECTRON  PARAMAGNETIC  RESONANCE EVIDENCE  FOR THE  FORMATION OF S20~ ON MgO

       Hydrogen  sulfide  and  sulfur dioxide  react  on many types of surfaces, form-
  ing  elemental  sulfur  and water (the Claus  reaction).   In addition, on MgO a
  paramagnetic  ion  identified as S20~ was also formed.   This ion  exhibited the
  spectrum  shown  in  Figure  6  with  the indicated  g  values.   Four  hyperfine  lines
 with a splitting  of 47.6G,  centered on gxx,  were  observed  when  S02 enriched
  to 25.5%  33S  was  used  (Figure 7a).  When  H2S enriched  to  25.5%  33S was
                                      16

-------
                       (0
                       K
                       Z
                       3
                       o
                       u
                        175     167    159
                           BINDING  ENERGY
                                   EV
                                             151
Figure 5.  XPS spectrum of sulfur 2p lines, formed on MgO after the  adsorp-
tion of (a) H2S, (b) H2S and 02 and (c)  H2S and 02, in atmosphere  for 2
weeks, at 25°C.

                                 17

-------
                            g«=2.oio
                9  =2.030
                                    9xx=2.001
Figure  6.  EPR spectrum of S20 formed by allowing H2S and S02 to react
on magnesium oxide at room temperature, followed by irradiation at 254 nm:
(a) X-band, (b) Q-band.
                             18

-------
employed, another set of four hyperfine lines  with  a  splitting  of  32.6G,  also
centered on gxx, was detected as shown in  Figure  7b.   Both  sets  of hyperfine
lines of approximately equal  intensity were observed  as  the result of  the re-
action of H2S with enriched S02  which contained 59.2% 33S.   Hyperfine  struc-
ture resulting from the adsorption of S02  enriched  to 41.7% in  170 was not ob-
served.  No change in the EPR spectrum was detected when D2S was used  instead
of H2S.

     From the 33S (1=3/2) hyperfine splitting  observed it is evident that two
sets of four lines result from two nonequivalent  33S  atoms.  Although  some iso-
tope mixing occurred during the  formation  of tno  paramagnetic  ion, the results
suggest that the hyperfine splitting of 48.66  was mainly due to the 33S which
originated from S02; whereas, the splitting of 32.6 was  mainly  due to  the 33S
which originated from H2S.  The  mixing was more apparent in the spectrum  of
the more highly enriched (59.2%  33S) S02.

     Morton (25) originally based the assignment  of the  S20~ ion on a  compari-
son of trends in principal g values for the ions  S02, S20~, and 83 where  the
effect of the larger spin orbit  coupling becomes  increasingly  greater  with
more sulfur atoms in the molecule.  Since  oribitals available  for  mixing  with
the ground state are rather far  removed in energy,  the effect  of local environ-
ment is small, and the spectra are reasonably  independent of the particular
matrix or surface.  This is evident, for example, when one compares the g
values of S02 on $3 on surfaces  and irradiated crystals, as shown  in Table 5.
           TABLE 5.   g-VALUES OF THE ISOELECTRONIC SO", S2(T AND 85

SO^/MgO (A)
(B)
S02 /Zeolites
SQa'/KCl
S2OVMgO
S^'/Sodalite
S20-/Na2S203-5H20
SsYMgO
Sl/Sodalite
Sa/KCl
9i
2.0097
2.0078
2.002
2.0100
2.030
2.029
2.0287
2.043
2.046
2.0499
92
2.0052
2.0033
2.002
2.0071
2.010
2.011
2.0106
2.043
2.036
2.0319
93
2.0028
2.0014
2.009
2.0025
2.001
2.001
2.0035
2.004
2.005
2.0026
ref .
26
26
27
28
this work
29
25
30
29
28
     The absence of any oxygen hyperfine splitting is somewhat difficult to
 understand since 170 has a rather large nuclear magnetic moment, and even a
 spin density as low as 0.05 would result in a separation of approximately 25G
 between terminal hyperfine lines.  It seems more reasonable that the oxygen in

                                    19

-------
                       »OG	-|
Figure 7   EPR spectrum of S20' formed by allowing (a) H2S to react wit
25.5% 33S-enriched S02, (b) 25.5% 33S.enriched H2S to react with S02 on MgO
                                    20

-------
$20~ is derived from the oxide ions  of  the  lattice,  rather  than from the S02.
Furthermore,justification for this model  comes  from  the  observation that S20"
could be formed by irradiation of CSz or  COS  adsorbed  on MgO.  We  suggest that
sulfur molecules (S2, S3,...Sn) are  deposited on  the surface  of MgO by  the
reaction of H2S with S02 and by irradiation of  adsorbed  COS or CS2.  The sub-
sequent reactions

                S2 + 02-(MgO)   +    S20- + e-                            (7)
and                             nv
                       S3 + e-  £v   S-3                                  (8)

yield the observed paramagnetic ions.   It is  likely  that S2 was also formed,
but the EPR spectrum was not observed at  -196°C because  of  a  short spin relaxa-
tion time.  The partial pressures of H2S  and  S02 over  the MgO may  affect the
distribution of molecular weights of the  sulfur species, and  thereby alter  the
concentration of S20".  The role of  oxide ions  is further substantiated by  the
absence of S20~ on MgO-Mg(OH)2 where the  surface is  covered with  hydroxide
ions.

ELECTRON PARAMAGNETIC RESONANCE EVIDENCE  FOR  THE FORMATION  OF H2S2 ON  MgO

     Trapped electrons (S centers) may be produced by  irradiating  MgO  in  the
presence of hydrogen with a 254-nm ultraviolet  lamp.  Upon  warming a  sample
tube containing frozen H2S and MgO with S centers to -78°C  the EPR spectrum
shown in Figure 8a was observed.  This spectrum can  best be understood in
terms of two forms of H2S2.  One form (A) is  characterized  by g^ (A)=2.015
and gn  (A)=2.003 with two nonequivalent  protons having  aj_H(A)=  an H(A)=9.4G
and a H' (A) = an H'(A) = 6.6G.  The other  form (B)  is isotopic and is charac-
terizid by giso(B) = 2-009 with AisoH(B)  = 9-4G and  aisoH'(B) = 6.6G.   The
simulated spectrum using these parameters and a concentration ratio of A/B  =
5.7 is given in Figure 8b.

     The relative intensities of A and B may be altered  by  changing the mode
of formation.  When the sample was irradiated at -196°C following  the adsorption
of H2S on S centers, the color of the sample became yellow  and species A domi-
nated the spectrum. The hydrogen hyperfine lines in the  parallel  direction  be-
came more evident, although some of the isotropic spectrum  was still  observed.
Upon warming the sample to 25°C the color changed to white and no paramagnetic
species was observed.

     When H2S enriched to 25.5% in sulfur -33 was adsorbed  on MgO containing
S centers, the EPR spectrum revealed additional hyperfine  lines as depicted
in Figure 9A.  Upon irradiation at 254 nm for  10 min the relative intensity
of species B was greatly reduced; whereas, two sets of quartet lines having
splitting constants 61 and 41  G, centered on g,,  of species A became apparent.
These additional hyperfine lines were much more obvious when H2S enriched  to
59.2% in sulfur  - 33 was used.  Using the statistical isotope distributions
for 25.5% 33S the spectrum of  Figure 9b was  simulated for  the g values and hy-
drogen  hyperfine splitting indicated previously, and with  |aj.s(A)|  =  jar5
(A)|= 26, |a,,s(A)|  =  61G,  |a,,sY(A)| =  41G, |aiso s(B)|  =136, |aiso s' (Bj =96,
and a concentration ratio of A/B = 5.7.
                                     21

-------
                                           9=2.009
Figure 8.  EPR spectra of H2S2" obtained by  allowing H2S to react with trapped
electrons on MgO at -78°C:  (a) experimental spectrum;  (b) simulated spectrum
using a mixing ratio A/B =5.7.
                                 22

-------
                          111   II  '
Figure 9.   EPR spectra of H2  S2"(B)  obtained by allowing 25.5%   33S-enriched
H2S to react with trapped electrons on MgO at -78°C;   (a) experimental spec-
trum;  (b)  simulated spectrum.
                                 23

-------
     The g values obtained for species A are in reasonably good agreement
with those reported by Bennett £t al_. (31) for the spectrum assigned to the
H2S" radical.  We believe, however, that the hyperfine structure is derived
from two nonequivalent hydrogen atoms and two nonequivalent sulfur atoms for
species A, and perhaps species B.  The situation is not so clear with respect
to species B since there is overlapping of hyperfine lines in the EPR spec-
trum.  Better agreement between the experimental and simulated spectra was
obtained using the model H2S2, rather than H2S".  It is proposed that the
isotropic spectrum is the result of ion motion on the surface in three dimen-
sions.

    The mode of formation of the radicals via the transfer of electrons from
the surface to the adsorbed H2S confirms that the observed species are anions.
When H2S is adsorbed on the S centers of MgO, the H2S~ ion may be formed ini-
tially.  This ion may then react with a neutral H2S molecule, forming H2S~2
and H2.  Subsequent irradiation undoubtedly leads to the photolysis of HaS
and other reactions which may result in additional  H2S2 and elemental sulfur.
The nonequivalency of the two sulfur and two hydrogen atoms may be due to the
effect of the surface environment.   The reason for the high mobility ex-
perienced by part of the H2S2 molecules is not understood at this time.

CALCULATIONS OF THE g TENSORS AND SPIN DENSITIES OF SMALL PARAMAGNETIC SULFUR-
CONTAINING ANIONS ON MAGNESIUM OXIDE

     Using a CNDO semiempirical calculation principal values of g tensors and
spin densities have been determined for the sulfur-containing molecules SQ~2,
SSO~, S"3, SCO", and CS~2, as well as CQ~2.  A deviation A is defined as the
average of the absolute deviation between the principal values of the experi-
mental and the calculated g tensors: A  = I(|AX«| +  |Ayi|  +  |AZI|).  In the
course of minimizing A, we started with the bond lengtn suggested for the
neutral molecule, and the bond angles were varied between 90 and 150°.  By
plotting A versus bond angle a curve with a minimum was generally obtained.
By varying both the bond length and bond angle within reasonable values a true
minimum, which corresponds to the most likely molecular structure of the ion
on the surface of MgO was found.  These calculate g tensors that correspond
to the minimum A values are tabulated in Table 6.  The calculated g values
were often within experimental error.

      The calculations  also yielded  spin densities which are  compared with  the
experimental  values  in Table  7.  The spin densities  of the sulfur  and  oxygen
atoms  are generally  consistent with the experimental finding; however, the
spin'densities in  the  p  orbital  of  the  central  sulfur atoms  are usually  lower
by  7  to  16%  than the experimental values.  The  difference is  reasonable  since
the  estimates  based  on  hyperfine data were obtained  by neglecting  the  d-
orbital  contribution.   Nevertheless, the  theoretical calculations  indicate
that  the contribution  of sulfur  d orhitals is  only 3 to 11%.
                                    24

-------
                              TABLE  6.   A COMPARISON OF THE  EXPERIMENTAL AND CNDO/2-CALCULATED g-TENSORS
MOLECULE
S02 (A)
S02(B)
sso~
S3
CO2
SCO

CS2
BOND
LENGTH
S-0 1.560
S-0 1.500
S-0 1.560
S-S 2.100
S-S 2.100
C-0 1.060
C-0 1.159
C-S 1.653
C-S 1.850
BOND
ANGLE
o
120
110
120
110
121
113

130
EXPERIMENTAL
*g
2.
2.
2.
2.
2.
1 .

1.
iso
0059
0042
014
030
0007
9977

9902
gxx
2.0097
2.0078
2.030
2.043
2.0032
2.0049

1.9999
9yy
2.0052
2.0033
2.010
2.043
1.9975
1.986

1.963
gzz
2.0028
2.0014
2.003
2.004
2.0014
2.0022

2.0078
CNDO/2
giso
2.0058
2.0043
2.0151
2.0304
2.0010
1.9973

1.9885
gxx
2.0097
2.0075
2.0287
2.0452
2.0032
2.0049

1.9991
9yy
2.0057
2.0033
2.0144
2.0439
1.9975
1.9858

1.9653
gzz
2.0021
2.0021
2.0021
2.0022
2.0023
2.0012

2.0012
PO
en
                        isotropic

-------
ro
                TABLE 7.  A COMPARISON OF  SPIN  DENSITIES  DETERMINED FROM CNDO/2 CALCULATIONS
                                    AND EXPERIMENTAL HYPERFINE DATA
\™
C s
C p
°Pzl
° Pz2
S° sd
S° pd
z
S Pzl
5 Pz2
d-orbital
contribution
SO-(A) S02(B) SSO Sg C02 SCO
ExptlaCNDO Exptl CNDO Exptl CNDO Exptl CNDO Exptl CNDO Exptl CNDO
0.18 0.18 NAb 0.11
_ 0.45 0.34 0.20
0.14 0.15 0.12 0.12 0.07C 0.08 - 0.20 0.24 0.19
0.14 0.150.12 0.12 - - 0.20 0.24 (OPy0.05)
0.01 0.00 0.01 0.00 0.02 0.00 0.01 0.00 - 0.00
0.75 0.64 0.71 0.64 0.54 0.45 0.53 0.37
0.37 0.43 0.27 0.30 - 0.26
_ 0.27 0.30 - (S p 0.16)
0.07 0.11 0.05 0.03 0.00 0.03
CS2
Exptl CNDO
NAb 0 . 08
0.34
0.00
0.24
0.24
0.08
        Calculated from experimental hyperfine data
        3Not available
        =Spin density estimated by difference  from  unity
         Central sulfur atom

-------
                                  SECTION  4

                                 DISCUSSION


     The results presented here confirm that a  variety  of  reactions  involving
sulfur-containing molecules can occur on solid  surfaces.   Nitrogen dioxide  is
an active molecule for the oxidation of sulfur  dioxide  to  adsorbed sulfuric
acid on hydrated silica and silica-alumina at 25°C.   Although direct proof
for NOHSOU as an intermediate is lacking,  the experimental  evidence  strongly
favors this interpretation.  Nitrosonium  bisulfate  is  an  important  inter-
mediate in the gas phase oxidation of S02  to H2SOit with N02 and water at high
pressures and temperatures; e.g., the lead chamber process incorporates  this
reaction.  In the chamber process the reaction,

           2NOHS04  + 2H20 + S02 •*• 3H2S04  + 2ND                        (9)

is postulated, and a similar reaction apparently takes  place on the  surface
of silica and silica-alumina.  Similar reactions may occur among air pollu-
tants on the surfaces of particulates suspended in the  atmosphere.   It re-
mains to be demonstrated, however, that the rate of  reaction will be signifi-
cant at the lower concentrations of N02 and S02 that are found under most
atmospheric conditions.

     In contrast to nitrogen dioxide, it is not possible to oxidize sulfur
dioxide using molecular oxygen on the same silica or silica-alumina surfaces
at ambient temperatures.  The  latter reaction did occur on a crystalline alu-
minosilicate, known as a zeolite, which contained manganese ions.  The reac-
tion was catalytic in that up  to 113 sulfate ions were formed per manganese
ion.  The maximum amount of  sulfate  ion was about 48 per unit cell or 7 per
large cavity.   This maximum  is probably not due to geometric constraints;
more likely, it  results from the availability of  lattice oxygen  ions for sul-
fate formation,  assuming that  reaction  4  is correct.   Since the  reaction was
diffusion  controlled,  the  inherent  rate of  reaction  is much greater  than was
observed  in  these experiments.   Although  the concentration of exchange sites
is  more limited, in  principle  similar reactions should occur on amorphous
silica-alumina  containing  manganese,  or perhaps other  transition metal ions
as  impurities.

     The  surface oxidation of  hydrogen  sulfide  also  occurs at moderate temper-
atures,  but  the products  are elemental  sulfur  and sulfite  ions  on magnesium
oxide    In addition,  small  concentractions  of  the paramagnetic  ions  SB, S20~,
S02,  SOs,  and  S~ were also observed on  the  surface  of  MgO  during the various
 stages  of the  oxidation  reaction.   The  oxidation  of  H2S by 02  at 25°C was
different on the three materials:   MgO, zeolites  and amorphous  silica-alumina.
                                       27

-------
The oxidation was carried out to the greatest extent (sulfite  ions)  on  the
basic MgO surface; whereas, it proceeded to form elemental  sulfur on zeolites,
and was negligibly slow on the acidic silica-alumina surface.   The Mn2   ions
in the zeolite enhanced the formation  of elemental  sulfur.   There was  no evi-
dence for the formation of sulfate ions on any of these surfaces; thus, it
appears unlikely that natural sources of H2S in the environment would con-
tribute significantly to the formation of sulfate ions.
     In the process of
netic S20" ions were
f the reaction between H2S and SO.  on MgO paramag-
produced, in addition to elemental  sulfur and water.
The  33S hyperfine structure observed in these experiments confirms the previous
identification of the ion by EPR spectroscopy.  The spin densities of S20~
and  the isoelectronic SO; and S; ions are compared in Table 8.  The variations
 TABLE 8.  SPIN DENSITY OF THE ISGELECTRONIC SO;?,  S2Q-  and $3 ON MgO
                                      SO^A)        S02(B)     S20-     Sj

 S3p  (total)                           0.75          0.71       0.91    1.08

 S3p  (Sulfur  1)                        0.75          0.71       0.54    0.53

 S3p  (Sulfur  2)                          -              -         0-37    0.27

 S3p  (Sulfur  3)                          -                               °-27

 02p  (Oxygen  1)                        0.14          0.12       0.07

 02p  (Oxygen  2)                        0.14          0.12

 ref-                                 26            26         this     30
                                                               work
 in spin density for SO;, S20", and S3 are in agreement with a simple argument
 based on electron repulsion.  The unpaired electron which occupies a highly
 antibonding 2b", orbital is repelled to the less electronegative sulfur atom
 by the concentration of electron charge in bonding orbitals near the more
 electronegative oxygen atom.  It is expected', therefore, that the central sul-
 fur atom would increase in spin density as one moves up the series from S02 to
 S3.  By a similar argument  one would predict that the replacement of an oxy-
 gen atom by sulfur in SOj would result in a greater charge density but a
 smaller spin density on the remaining oxygen atom.
      At considerable lower  temperatures trapped electrons on the surface of
 MgO react with H,S forming  a  paramagnetic ion which has been identified as
 H,S;    It has been suggested  that  the ion was H2S~; however, the sulfur -33 hy-
 perfine data provides convincing  evidence that the molecule contains two, non-
 equivalent  sulfur atoms.  The spin density  of the unpaired electron was pre-
 dominantly  localized in the 3p  orbitals of  the two nonequivalent sulfur atoms
 of the  H2$2 radical.  Since the sulfur atom has low-lying  3d onbtals, the
                                       28

-------
energy levels for the 3p and 3d orbitals may be close;  thus,  in  principle,
either a 03^ bonding orbital or a o3p* antibonding orbital  may accomodate  the
unpaired electron.   Consideration for the occupancy of  the  unpaired  electron
in the two possible molecular oribtals has been given by Akasaka et  al.  (32)
in their study of the radicals  R-CH2- S-S-CH2-R  obtained  by y  irradiation of
L-cystine dihydrochloride.  Using their experimental  g  tensor they found an
energy splitting between the ground and the first excited state  which  was  much
too large when an occupancy of the a3^ orbital  was assumed.  Therefore,  the
unpaired electron probably occupies the 03^* antibonding orbital.

      The CNDO calculations have further confirmed that the d orbital  contri-
 bution to the bonding in sulfur-containing molecules is relatively  small.
 These calculations also provide one of the first attempts  to determine  the
 structure of adsorbed molecules by comparing calculated and experimental  mag-
 netic parameters.   The approach is unique in that we attempt to minimize the
 differences between calculated and experimental parameters, in  contrast to
 the usual method of estimating geometries whereby the total energy is mini-
 mized with respect to bond lengths and bond angles.  The latter method  suffers
 from the fact that the calculated minimum energies may not be directly  com-
 pared with experimental values.  Comparing the CNDO/2 - calculated g tensors
 with those reported by Chuvylkin and Zhidomorov  (33) on the CO^ ion we  found
 that our calculated values (2.0032,  1.9975, 2.0023) are much closer to  the
 experimental values (2.0032,  1.9975, 2.0014) than theirs  (2.0085, 1.9957,
 2.0024).  Moreover, the CNDO/2 calculation gives  121° as the best possible
 bond angle for  the CO;? ion, which is very close  to  the 124° predicted  from
 the sp hybridization as calculated from  the hyperfine structure  (34,35).  The
 calculated bond angles from the EPR  spectroscopic study were 115±5° for the
 502 ion, according  to  Dinse and Mb'bius  (36), and  the CNDO/2 calculation indi-
 cates  120 and  110°  for S02  (A) and  (B),  respectively.  More support for the
 accuracy of  the CNDO/2 method comes  from comparison with  the scattered wave-
 SCF-Xa method,  by which  a  bond  length  and bond angle of the 85 ion were calcu-
 lated  (37)  to  be  2.05-2.10A and 110±5°,   respectively.  The CNDO/2 method to-
 gether with  experimental  g  values indicates a  best  fit  at  2.1A and 110°.  The
 bond  lengths of the sulfur-containing  anions  are long  by  0.1 to  0.3A,  compared
 to  the neutral  molecules.   This may  be due  to  the repulsion which  arises from
 the extra electron.
                                      29

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                                  SECTION 5

                            LIST OF  PUBLICATIONS


1.   "Electron Paramagnetic Resonance Evidence for the Formation of S20~ on
    Magnesium Oxide", M.  J. Lin and  J.  H. Lunsford,  J.  Phys.  Chem., 8£, 635-
    639 (1976).

2   "An Electron Paramagnetic Resonance Study of the H2S£ Radical  on Magnesium
    Oxide", M. J.  Lin and J.  H. Lunsford, J.  Phys.  Chem., 80_, 2015-2018 (1976).

3.   "Surface Reactions of S02 with N02  on Hydrated Silica Gel", S.  M.  Davis
    and J.  H. Lunsford, J. Environ.  Sci. Health, All. 735-741 (1976).

4.   "Low-Temperature Surface Oxidation  of Hydrogen Sulfide by Oxygen", M.  J.
    Lin and J. H.  Lunsford, J. Environ. Sci.  Health, A12. 127-136 (1977).

5.   "CNDO Calculations of the g Tensors and Spin Densities of Small Paramag-
    netic Sulfur-Containing Anions on Magnesium Oxide", M. J. Lin and J. H.
    Lunsford, J. Magnetic Res., 29_,  151-157 (1978).

6.   "Surface Reactions of S02 with N02  on Hydrated Silica and Silica-Alumina",
    S. M. Davis and J. H. Lunsford,  J.  Colloid Interface Sci., 65_, 352-364
    (1978).

7.   "The Oxidation of S02 with 02 on MnY Zeolites", J. R. Pearce and J. H.
    Lunsford, J. Colloid  Interface Sci., in press.
                                     30

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                                  REFERENCES


1.   Maurin, P.  G.,  and J.  Jonakin.   Removing  sulfur  oxides  from  stacks.
    Chem.  Eng.  (New York), 77(9):  173-80,  1969.

2.   Shy, C. M., and J. F.  Finklea.  Air  pollution  affects  community  health.
    Environ. Sci.  Technol.,  7:204-208,  1973.

3.   Prince, R., and F. F.  Rose.   Sulfur in air and soil.  Water,  Air and  Soil
    Pollut., 1:286-302, 1972.

4.   Johnstone,  H.  F.  Metallic ions as  catalysts  for the  removal  of sulfur
    dioxide from boiler furnace gases.   Ind.  Eng.  Chem.,  23:559-561,  1931.

5.   Johnstone,  H.  F. and D.  R. Coughanowr. Absorption of  sulfur  dioxide  from
    air.   Ind.  Eng. Chem., 50:1169-1172, 1958.

6.   Cheng. R. T.,  M. Corn and J. 0. Frohliger.  Contribution to  the reaction
    kinetics of water soluble aerosols  and S02 in air at  ppm concentrations.
    Atmospheric Environment, 5:987-1008, 1971.

7.   Renzetti, N. A., and G.  J. Doyle.  Photochemical aerosol formation in sul-
    fur dioxide-hydrocarbon systems.  Int. J. Air Pollut.,  2:327-345, 1960.

8.   Jaffe, S., and F. S. Klein.  Photolysis of N02 in the presence of S02 at
    3660A.  Trans. Faraday Soc., 62:2150-7, 1966.

9.   Bourbigot Y., J. Bricard, G. Madelaine, and D.  Vigla.  Identification of
    aerosols produced by photolysis in the presence of sulfur dioxide.  C.  R.
    Acad.  Sci., 276:547-50, 1973.

10. Canosa, C., W. G. Filby, and R. D.  Penzhorn.   On the gas phase products
    from  the thermal  and photochemical  nitrous oxide-sulfur oxide  (SOX)  reac-
    tion.  J.  Environ. Sci. Health, Part A, All(l):93-8,  1976.

11. Cook.  W. G. and R. A. Ross, Heterogeneous oxidation of hydrogen sulfide at
    concentrations below  1000 ppm  in nitrogen/air mixtures over supported
    metal  oxide catalysts.  Atmos.  Environ.,  7:145-51, 1973.

12. Steijns, M., and  P. Mars.   Role of sulfur trapped in micropores in the
    catalytic  partial oxidation of  hydrogen sulfide with oxygen.   J. Catal.,
    35:11-17,  1974.
                                     31

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13           ct                       .
     hydrogen sulfide oxidation catalyzed by sulfur.   J.
     1976.

14   Menon, P  G., R. Sreeramamurthy,  and P. S.  Murti.   Experimental  study
     of temperature and rate profiles  in a rapidly fouling  catalyst  bed.
     Chem. Eng.  Sci., 27:641-4, 1972.

15   Steiins  M , P.  Koooman, B. Nieuwenhuijse-  and P.  Mars.   The mechanism of
     t e c Ulyt c oxidation of hydrogen sulfide. Ill  An electron spin reso-
     nance study of  the sulfur catalyzed oxidation of hydrogen sulfide.  J.
     Catal., 42:96-106, 1976.

16   Belitskus, D. L.  Oxidation of molten  aluminum-magnesium alloy in air,
     air-sulfur dioxide, and air-hydrogen  sulfide atmospheres.  Oxid. Metals,
     3:313-17, 1971.

17   Fischer F  ,  L. Goens, and H.  Kraus.  Reactions  of hydrogen sulfide in
     sorption from oxygen-rich  gases  on  activated carbon.  Chem.  Ingr. Tech.,
     36:963-8, 1964.

 18    Pearce, J.  R.,  and J.  H.  Lunsford.   The  oxidation of  S02 with  02  on MnY
      Zeolites.   J.  Colloid  Interface  Sci., in press.

 19.  Davis,  S.M., and  J.  H.  Lunsford.  Surface  reactions of  SO, with  N02 on
      hydrated silica gel.   J.  Environ.  Sci. Health,  All.735-741,  19/b.

 20   Davis  S  M. and  J.  H.  Lunsford.  Surface  reactions of  S02  with N02 on
      hydrated silica and  silica-alumina.  J.  Colloid Interface  Sci., 65:352-
      364, 1978.

 21.  Lin, M. J., and J. H.  Lunsford   Low-temperature surface oxidation of hy-
      drogen sulfide by oxygen.  J. Environ. Sci. Health, A12.127-136, I9//.

 22   Lin  M  J  , and J. H.  Lunsford.  An  electron paramagnetic resonance study
      of  the H^1  radical on magnesium oxide.  J. Phys. Chem. 80:2015-3018,
      1976.

  23  Lin, M. J.,  and  J. H. Lunsford.   Electron  paramagnetic resonance evi-
      dence  for  the  formation  of S2Q- on  magnesium oxide.  J. Phys. Chem., 80:
      635-639, 1976.

  24   Lin  M J   and J. H.  Lunsford.  CNDO calculations  of the g  tensors and
       spin densities of small  oaramagnetic sulfur-containing  anions  on mag-
       nesium oxide.  J. Magnetic Res.,  29:151-157,  1978.

  25   Morton, J.  R.   Identification of  some sulfur-containing radicals traoped
       in single  crystals.   J.  Phys. Chem., 71:89-92, 1967.
                                       32

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26.   Schoonheydt,  R.  A.,  and  J.  H.  Lunsford.   Electron paramagnetic resonance
     of SO! on magnesium  oxide.   J.  Phys.  Chem.,  76:323-8,  1972.

27.   Ono, Y.,  H.  Tokunaga,  and  T.  Keii.   Electron spin resonance  study of sul-
     fur dioxide  (1-) radicals  on synthetic  zeolites.  J. Phys. Chem.  79:
     752-6, 1975.

28.   Schneider, J., B.  Dischler, and A.  Raeuber.   Electron  spin resonance of
     sulfur and selenium  radicals in alkali  halides.  Phys.  Status  Solidi,
     13:141-57, 1966.

29.   Mclaughlin,  S. D., and D.  J.  Marshall.   Paramagnetic resonance of sulfur
     radicals  in  synthetic  sodalites.   J.  Phys.  Chem., 74:1359-63,  1970.

30.   Lunsford, J.  H., and D.  P.  Johnson.   Electron paramagnetic resonance
     study of  triatomic sulfur  ion formed on magnesium oxide.  J. Chem.  Phys.,
     58:2079-83,  1973.

31.   Bennett,  J.E., B.  Mile,  and A. Thomas.   Preparation and properties  of  the
     H2S negative ion.   Chem. Commun.  7:182-4, 1966.

32.   Akasaka,  K., S.  Ohnishi, T. Suita, and  I. Nitta.  Electron spin  resonance
     (E.S.R.)  of  a single crystal of L-cystine dihydrochloride irradiated at
     low temperature.  J. Chem.  Phys., 40:3110-16, 1964. Akasaka,  K., S.
     Kominami, and H. Hatano.  Photoinduced  hole-electron recombination  in  a
     y-irradiated single crystal of L-cystine dihydrochloride. J.  Phys. Chem.,
     75:3746-50.  1971.

33.   Chuvylkin, N. D., and G. M. Zhidomirov.  Calculations  of the anisotropic
     hyperfine coupling constants in free radicals.  J.  Magn.  Resonance.   11:
     367-72, 1973.

34.   Meriaudeau,  P., J. C.  Vedrine, Y. Ben Taarit, and  C. Naccache.  Electron
     paramagnetic resonance studies of carbon dioxide anion radicals  adsorbed
     on magnesium oxide.   Identification and structure  of the species using
     carbon-13 and oxygen-17 labeling.  J. Chem. Soc.  Faraday Trans.  II,
     71:736-48, 1975.

35.   Lunsford, J. H. and J. P.  Jayne.  Formation of C02  radical  ions  when  C02
     is adsorbed on  irradiated magnesium oxide.  J. Phys..Chem.,  69:2182-4,
     1965.

36.  Dinse, K. P., and K. Moebius.  E. P. R. studies of electrolytically gener-
     ated  S02  .  Z.  Naturforsch, 23:695-702, 1968.

37.  Cotton,  F. A.,  J. B. Harmon, and R. M.  Hedges.  Calculation  of the ground
     state electronic  structures and  electronic  spectra of  di- and trisulfide
     radical  anions  by the scattered wave SCF-Xa method.  J. Am.  Chem.  Soc.,
     98:1417-24,  1976.
                                     33

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                                    TECHNICAL REPORT DATA     .
                             (Please read Instructions on the reverse before completing}
                                	"           r~^
 1 REPORT NO.
    EPA-600/7-79-088
\A. TITLE ANDSUBTITLE
   SURFACE REACTIONS  OF OXIDES OF  SULFUR
 7. AUTHOR(S)


   J.H.  Lunsford	_
 9. PERFORMING ORGANIZATION NAME AND ADDRESS
                                                             8. PERFORMING ORGANIZATION REPORT NO.
   Department of Chemistry
   Texas A&M University
   College Station,  Texas
         77843
 12. SPONSORING AGENCY NAME AND ADDRESS
    Environmental  Sciences Research Laboratory  - RTF, NC
    Office of Research and Development
    U.S.  Environmental Protection Agency
    Research Triangle ParkT North Carolina   27711	
 15. SUPPLEMENTARY NOTES
                                                              . RECIPIENT'S ACCESSION-NO.
                                          . REPORT DATE
                                           April  1979
                                         ,. PERFORMING ORGANIZATION CODE
                                         10. PROGRAM ELEMENT NO.

                                            1NE625 (EA  21)  FY77
                                         11. CONTRACT/GRANT NO.

                                           801136
                                          13. TYPE OF REPORT AND PERIOD COVERED
                                           Final   12m to 5/78
                                          14. SPONSORING AGENCY CODE
                                           EPA/600/09
    ^ereas '""go": °"rie°  of 'products^  observed including elemental sulfur,
            '               ions  and a number  of  paramagnetic  ions such as  S3,  S20
          5
                                             function of bond  angles and bond lengths.
  17.
  a.
                                   KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
                             b.lDENTIFIERS/OPEN ENDED TERMS
     *Air  pollution
     *Sulfur oxides
     *Chemical reactions
     *Aerosols
     *Surface chemistry
     *Ion exchange  resins
   18. DISTRIBUTION STATEMENT


      RELEASE TO  PUBLIC


   EPA Form 2220-1 (9-73)
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21. NO. OF PAGES

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