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8/10/2019 Mechanisms of Alkyl Sulfoate ... Water Interface
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y
00
P. SOKASUNDARAN AND
D. W. FUEBSTF.~A
C>r)re f --4 D./A. However, care should be taken
sincewe nitially assumed hat 'P'
.
a.ndP'B are orthogonal
a.nd n this case he homopolar dipole vanishes. If we
had included the overlap integral, then the primary
moments would have changedsomewhat.
Ackr&OtDlIgmentB.
e wish to thank Proiessor
Harrison Shull for his interest and hospitality. Our
tha.nksa.re&Isodue to Mr. John P. Chandlerand ~Ir.
Robert Fern for their help with computational pro\>-
lems.
Mechanisms of Alkyl Sulfonate Adsorption at the Alumina-Water Interface
by P. Somasundaran nd D. W. Fuerstenau
~ 0/ MtII-z T~. U 0/ Cal~ B.-~. Calt/omiA ~ J",.. S. 19f1)
Adsorption iaothermsof sodium dodecyl sulfonateon alumina were determined at con-
trolled ionic strength, pH, and temperature. Electrophoreticmobilities of the alumina
werealsom~ for the sameconditions. The ~ts indicate hat at a certain critical
concentrationor critical pH, adsorption ncreasesmarkedly through 88SOOiationf the
hydrocarbon chains of the adsorbed ulfonate ons to form hemimicellesat the solid-
liquid interface. The dependencef the isothermson surfactantconcentrationand on pH
is interpreted n terms of the Stern-Grahamemodelof the electricaldouble ayer.
Indications of interactions at the interface can be
found in the work by Wayman and co-workers~7on
the adsorptionof surfactantaon clay minerals. Ad-
sorption sothennsof surfactantson silica and alumina
determined by other workers'-lo do 'exhibit marked
changes t certain critical concentrations. However,
these nvestigationshave not been extensive and no
Introduction
In previouspapers"a t was shown hat such nter-
facial parameters sr potential and ftotation ~ponse
dependupon the number of caroon atoms n the hy-
drocaroonchain of a surfactant and upon the concen-
tration of the surfactant n solution. Correlation of
the various nterfacial parameters howed hat nuked
changesn eachof the parameters ccurat somecritical
concentration of the surfactant. It was postulated
that these abrupt changes re due to the association
of adsorbedsurfactant ions to form two-dimensional
aggregates r hemimicellesat the solid-solution in-
terface. From the dependence f the flotation and
electrokineticbehavioron the chain ength of the sur-
factant, the van der Wa.aJs ohesiveenergy ~pon-
sible for latera. nteraction between urfactant ons at
the interface was calculatedon a molar basis to be
-0.6 kcal for eachCH, group n the chain. A direct
test of the proposedadsorption mechanismss best
obtained through the measurement f the adsorption
of the surfactant tself and that is the purpoeeof this
study.
(1) Baaed in part on the Ph.D. m-tation of P. Somuundalan,
University of California, Berkeley, Calif., 1960&.
(2) D. W, Fuerstenau, T, W. Healy, and P. Somaaunduan, Tram.
AlAtE. 129, 321 (1964). .
(3) P. Somuundalan, T. W. H.I7, and D. W. Fueratenau, J.
Ph.-. C1I8m,. 8, 3562 (1964).
(4.) C. H. Wayman, Proc. I~ CZII~Coni" I, 329 (1963).
(6) C. H. Wayman, J. B. Robert8OD,and H. G. Pap, C. S. Geo-
IoIic81 8uney Prof~ Paper 47&-B (1968).
(8) C. H. Wayman, ~., 45()..C 1962).
(7) C. H. Wayman, H. G. Pap. and J. B. Robertson, ib1'd., 4.76-0
(1968).
(8) L W. Wark and A. B. Cox, ~. AlMB', liZ, 189 (19M).
(9) K. Shinoda, d aI., "CoIloidal Surfactant.." Academic ~
New York. N. Y., 1963, Chapter 3,
(10) M. J. J&)'COCk nd R. H. Otte1ril1, Btdl.lf&1t. MimiIg JIet., n.
497 (1968).
TM J--Z of p~ ~
8/10/2019 Mechanisms of Alkyl Sulfoate ... Water Interface
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j
.
1
j
i
1
MECH.~"'ISMS OF ALKYL SULFONATE ADSORPTION
91
quantitative d{',.rription of the adsorption process has
becn presented In :\,'conunt nr the breaks in the iso-
tbcnlls or for tht: ,;i: [UII.::~rll~",j thc slope of the iso-
thl'n\l:;, T:~.I1:lrllu,.lli :1/111 :~m:lkil' attemptal to
e.~pl:lill sucll i.~IIII1'r\II'; ill t('rlll ' oj:\ Bnmaucr-Emmctt-
Teller (B,E. T.) tY11C f equ:Ltion. but the va.lidity
of tllcir :lpl,roach i" flU{': l ollablc I~su:;c of their neglect
of clcctri(':\I,'ffi.,'"". .\1 ), ;Id-"'()rplioll wthc~ gCllcr-
ally have not been detemlined over a sufficiently wide
range or with a precise control of such variables 88
ionic ~lrell~lh, i,ll, ;111.1t'lllr,,'r:llI.n ",lli,'11 :ItT..." tIll.'
ad.-~rptionprocf':;~.
The objective of tllis ImI~r is to present the re1'ult,-s
of detailed studies of the adsorption isothem1S of s0-
dium dodecyl sulfonate on alumina in aqueous media,
These isothenns together with the electrophoretic
behavior of alumina suggest mecha lLR DSf adsorp-
tion of surfactant ions at the solid-liquid interface.
where is the dielectric onstant f the medium,R
is the gas constant, T is the absolute emperature,z
is the valence of counterions ncluding the sign, F
is the Faraday constant,and C is the molesof ions/
cm.' n the bulk solution. Based n the Stem-Grahame
treatmentof the double ayer, expressionor the ad-
sorptionof counterionsat the planea s given by the
equation
(2)
il
where , is the adsorption density in moles/cm.' at the
Plane &, r is the effective radius of the adsorbed ion in
centimeters, C is the concentration of ions in the bulk
in moles/em. , and W, is the work required to bring
the ions to the plane &.
Vol- 10,N-- 1 J~ 1966
Equation 2 can be modified o take into account he
interaction of surfactant ions at the interface by
scparotingW. into electrostaticand interaction terms
8/10/2019 Mechanisms of Alkyl Sulfoate ... Water Interface
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92
P. SOM:A8UNDARAN AND D. W. FUEBSTE.."i411
-c
10""'
*-~~A;._~~_A ~~~
...~
=..
...,
G...
00
~>
+1 "c
-..
::...
+2 ooj
%..
Go.,.
+3 ~~
~~
.
2
U
...
oJ
~
>-"
..
Ui
z
...
0
Z
0
~
Go
~
0
III
0
4 /
ALUMINA
pH 7.2
25.C
IOMC STREfGTH 2aI0-a..
(WITH HoCI)
-
ADSORPTION
- LECTROPHORESIS
+5
10"'-
,I
10"
10-5 0-4 io-.
EQUILIBRIUM CONCENTRATIONOf' SOOIUM OOOECYL
SULFONATE. MOLE PER LITER
Figure 1. Adsorption density of dodecyl suJfonateons
on alumina and the electrophoreticmobility of alumina as a
function of the concentrationof sodium dodecyl sulfonate at
pH 7.2 and at constant emperature and ionic strength.
culated by taking the averageof the area occupied
by cubic packing and by hexagona.l lose-packing f
iOllSof 5.9-:\. diameter (the diameterof the sulfonate
head). Sodium dodecyl sulfonate usedwas prepared
from high-purity dodecyl sulfonic acid by treating it
,,-ith -"Odium y,lroxide, and the resulting sodium salt
,,-;'-.; lurifi"ll by rt"'rY8tallization rom hot absolute
ethyl alcohol. Triply distilled conductivity water
wasused or adsorption nd electrokinetic tudies.
.\l~"or Jti"ll oj :;odiumdodecylsulfonateunder var-
ious conditions was measured y determining he dif-
ference n I'onl','ntration of the surfactant n solution
before and after adding alumina. Experimentswere
carried out at a. constant emperatureof 25 = 0.2,
and an atmosphereof purified nitrogen was main-
tained n the adsorptioncell. Total ionic strengthwas
also kept constant at 2 X 10-1 M by additions of
decinormal solutions of ~dium chloride and hydro-
chloric acid and sodiumhydroxidewhich wereused or
pH adjustment. The: adsorption cell, which was
stirred magnetica.1ly, onnaUy contained 200 ml. of
solution and 4 g. of al~ for ~h experiment,
but for caseswhere he adsorption was ower, 8 g. of
alumina. and 150 mi. of solution were used. The
lowest point was obtained using 16 g. of alumina and
100 mi. of solution. Although equilibrium was at-
tained in much less han 1 hr. under the conditions
used, each sample was agitated for 2 hr. (but more
vigorous agitation was found to decrease he equi-
librium time appreciably). After the equilibrium was
attained, sampleswere collected or detennination of
the equilibrium concentration f sodiumdodecylsulfo-
nate and for electrophoresis xperiments. Determin-
ations of pH were made after a.1lowinghe suspension
to settle or at least30min.
The sulfonate concentrationwas determinedby a
variation of the methyleneblue method described y
Jones.20 t is basedon the principle hat the anionic
dodecylsulfonate n water combineswith the cationic
methyleneblue to give a blue complex hat is soluble
in chloroform. Hence, the concentrationof sodium
dodecyl sulfonate n any aqueous olution can be de-
termined by extracting the methyleneblue sulfonate
complexwith chloroformand evaluating he concentra.-
tion colorimetrica.1ly y comparisonwith the color
produced by known quantities of sodium dodecyl
sulfonate. The possible xperimental rrorshave been
examined by Wayma.n.1 Since the readings could
vary from one dye to another, he same ype of dye
was used through each set of analyses. Absorption
by the methylene blue sulfonate complex was de-
termined rom 640 o 660mp n a Cary Model 14 spec-
trophotometer. The mAximum optical density ob-
tained was used for evaluation of the sulfonate
centration. The lowest concentration hat could
measured as 10-6M in the aqueous olution.
The electrophoreticmobility of the alumina
was determined by means of a Zeta-Meter
method was necessaryf the measurement f
kinetic behavior was to be determinedwith the
small particles that were used n the adsorption ex';
periments. In addition, this method has the advan-
tage over the streamingpotential technique n that it
givesan ndication of the distribution of charges mong
the particles rather than only a net value for the
charge f the particles n the system.
Results
The adsorption sothermof sodiumdodecylsulfonate
by alumina at pH 7.2 and 25 is given in Figure 1.
Electrophoretic mobilities of the particles under the
same conditions are also given in Figure
1.
The adsorption sotherm consistsof t~ regions:
region 1, characterized y a low increasen adsorption
with surfactant concentration; egion 2 by an abrupt
increase n the slope of the isotherm; and region 3
again by a lower dependence f adsorption on sur.
factant concentration. The electrophoreticmobility
exhibits an almost negligibledependence n sulfonate
addition n region 1, but it decreasesbruptly through
region2. The end of region 2 is characterized y the "
(20) J. H. Jon_. J. A_. Agr. ClIemw.. 28, 398.409 (1945).
(21) C. H. Wayman, U. B. GeoIocicalSurvey ProfessionalPaper
4ro-B (1962).
TA. JwnIGl 01 Ph1/aicalChemi#)JI
10"i'
10-12
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~{ECHA.NISMS OF ALKYL SULFON.~TE ADSORPTION
93
mobility becoming ero. In region3, the mobility i5
opposite n sign. Moreover, n region3 a number of
particles were observed o have a positive ch~\rge,
and hoseparticleswith a negati\',~ h:irgehave a wide
distribution of electrophoreticmobilities. This prob-
ably results rom a distributionof particleswith varying
surfaceactivities, thereby giving rise to a distribution
of adsorption densities. However, the net elect oo
phoretic mobility is characterized y a slower change
in region 3.
10-t01-
fr I
..
.
..2
r
0 :;~
-..
-..
00
/
+12>
~ + 2 ~ ~
%".
Go...
+3 O~
~o
,- 'M ~~
;: .\' \.4 a i
J
I
.
I
...
... .
'W ;
... ,
0 '
2 I
..- 10."L
... ,
in 1
z '
w
0
z
l ' ALUMINA
;: pH 6.9
Go 10-'1
U 25.C,/
-:..,c STAENGTM 2.
~ i
/' - .. (WITHQt.,
-
DSORPTION
-ELECT~OP"CAES.S S
10"
EQUILIBRJUM CONCENTRATION OF SODIUM DOOECYL
SULFONATE, MOLE PER LITER.
Figure 3. Adsorption density of dodecyl sulfonate ons on
alumina and the electrophoreticmobility of alumina as a
function of the concentrationof sodium dodecylsulfonate at
pH 6.9 and at constant temperature and ionic strength.
fl"
'5
...
...
0
2
..
..
~
...
0
..
..
~
~
i
.- 5
~
8
9
Discussion of Results
In interpreting these results, we shall consider that
sulfonate ions are adsorbed at the alumina-water
interface. as counterions in the electrical double layer.
Furthermore, since sulfonate ions are not chemisorbed
they are adsorbed appreciably only below the zero-
point-of-charge of alumina, namely below pH 9.
Effect of Surfactant Coocentration 00 Adsorption.
The shape of the adsorption isotherm supports the
adsorption mechanism mentioned earlier. In region
1 of Figure 1 or in region A of Figure 2, at low concen-
trations of surfactants or at low surface potentials,
the surfactant ions :)ore dsorbed individually and ad-
sorption results primarily from electrostatic forces
between surfactant ions and the charged solid surface.
However, when the concentration of the reagent reaches
the hemimicelle concentration or hemimicelle pH,
that is the pH at which hemimicelles start forming
at the solid-liquid interface at constant equilibrium
concentration of surfactant, the ions begin to associate
with each other. This associationenhances he adsorp-
tion of sulfonate ions considerably and, hence, he rapid
rise in the adsorption isothenns result. Thus, in
region 2, the adsorption is due to the electrostatic at-
traction between the ions and the charged solid surface
and hemimicelle association of hydrocarbon chains.
When sulfonate ions equivalent in number to the surface
sites have been adsorbed, the contribution due to the
electrostatic attraction disappears, and the further
increase in adsorption will be only due to association
between the hydrocarbon chains. Thus, in region 3,
pH
Figure
2. Adsorption density of sodiwn dodecyl sulfonate on
alumina and the electrophoretic mobility of alumina as a
function of pH at constant residual sodium dodecyl sulfonate
concentration, ionic strength, and temperature. The ionic
strength or the point at pH 1.98,however,exceeds X 10-1 N
The adsorption isotherm for sodium dodecyl sul-
fonateon alumina.s given n Figure 2 as a function of
pH at constant onic strength of 2 X 10-1 N and an
equilibrium concentrationof approximately3 X 10-6
mole/I. This curve also consists of three parts:
region A showing a low increase n adsorption with
lowering of pH, region B with a greater ncrease n
adsorption,and region C with a constantly decreas-
ing.rateof increase f adsorptionwith loweringof pH.
F.igure3 presents he adsorptiondensity and elec-
tro.phoreticmobility 88 a function of sulfonateconcen-
tration at pH 6.9underconditions f constant empera-
ture an~ constant onic strength. This set of curves
is siriillar to that given in Figure 1 for pH 7.2. The
adsorption sothermsat pH 6.9 and 7.2 are now put
togethern Figure4-forcomparative urposes.
Volum. 70. N-.b..1 JGmA477/986
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9-1
P. SOMASUNDARAN AND D. W. FUERSTENA.1
",lope n the second egion is due to this specific adsorp
tion. Equation 5 can be modified in the following
manner to take this into account. At any particula
value of 1ft.
001-
Asswning the specific adsorPtion >Qtential f chlorid
ions negligible compared to that of alkyl sulfonat
ions and differentiating eq. 7 in the logarithmic form
with respect o In (JR-yields
the slope of the adsorJ)tinn i.o:ntherm dcCTe:L",cs. Thc
rc:~on melltiont.-d above for tht: d~cre~~~ in ~lopc from
n'~ion 2 to rt gion :~ ,; ~\IPI)(lrt~'(1by the el('ctrophoretic
mobility ("In'c \\'hi
8/10/2019 Mechanisms of Alkyl Sulfoate ... Water Interface
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MEcHANISMS OJ' ALKYL SULJ'ONATm ADSoRPTION 95
(23) D. W. Fuerstenau and H. J.Modi, J.Bl.ceroeAem.8oc..106.336
(1959).
Volu_10. Number 1 JGAVIJrV 966
In regionA, dn/d pH is nil and he change f adsorp-
tion densitywith pH should hen be determinedby the
change f
1/-. with pH. Sincehe potentials directly
proportional o the electrophoreticmobility at constant
temperature, ""a/dpH will be determinedby the slope
of the mobility-pH curve. In region A, d1/-a/d H
is negativeand d In ra/ d pH must also be negative,as
canbeseenn Figure2.
The transition point from regionA to B corresponds
to the hemimicellepH for that particular equilibrium
concentration and association between the hydro-
carbon chains begins to take place at that point.
Hence, n region B, the second erm (dn/d pH) also
becomeseffective. The term dn/d pH is negative,
whereasd1/-a/d H is positive in region B. It can be
seen hat the magnitudeof the seconderm, dn/d pH,
due o hemimicelleassociations very high so that the
slopeof the adsorption sothermd In ""./d pH is nega-
tive. The drop in r potential in region B is indicative
of the strong effect of this rapid hemimicelleassocia..-
tion.
As the pH is further increased,he effect of sudden
hemimicelle ormation diminishes and the slope of
the isotherm decreases. n region 0, the association
of a new ion going to the surfacewith a hemimicelle
probably still takes place, but its effect will be very
small compared o that of the association f a number
of individually adsorbed ons to form a new hemi-
micelle. In other words, n region 0, dnld p~ dimin-
ishes and, correspondingly, he rate of increase n
adsorption ecreasesontinuously.
Figure 4 showsa very strong dependence f the ad-
sorption of sulfonate ons on the pH of the system.
The nteresting eatureof this set of curv~ is the change
in hemimicelleconcentration with pH. Hemimicelle
concentrationat pH 7.2 is 8 X 10-6 mole/ . and at
pH 6.9 it is 3.5 X 10-6 mole/ . At a lower pH, the
8/10/2019 Mechanisms of Alkyl Sulfoate ... Water Interface
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P. SoKASUNDARANAND D. W. FUEBSTENAU
6
M 10
2
u
...
~ I
0 '
2
>-"
.. 10""
~
z
...
0
z
0
-=
~ la'
0
I/)
0
~
10-11 mole/cm.s, or at a coverage of only about one..
tenth of a monolayer. The much higher coverage
at about pH 2 as compared to pH 7 may result partly
from the presence of and coadsorption of sulfonic
acid molecul~ which occur n appreciable concentration
at low pH valu~ since the pK of sulfonic acid is about
1.5. Extensive adsorption of the sulfonic acid mole..
cul~ would occur through interaction of hydrocarbon
chains, but without electrostatic repulsion because he
polar eads .re ncharged.
Summary
Detailed adsorption measurementsof sodium dodecyl
sulfonate ions on alumina together with electrophoretic
mobility measurements at constant - ionic strength
and pH indicate that sulfonate ions a.re adsorbed in-
ilividually as counterions in the electrical double layer:'
at low sulfonate concentrations. Adsorption under
th~ conditions occurs by an ion-exchange process.
The adsorption of sulfonate ions was found to be ex-
ceedingly dependent upon the pH of the liquid with no
adsorption occurring above the zero-point-of-charge
of alumina (pH 9), which suggests that chemisorp-
tion doesnot exist in this system. At a certain critical
concentration or critical pH, adsorption increases
rapidly through the formation of two-dimensional
aggregates of the surfactant ions or hemimicelles at
the solid-solution interface. At still greater adsorp-
tion densiti~, the increasen adsorptionwith in-
creasing sulfonate concentration decreases because
the sign of the net electrical charge at the interface is
reversed by the adsorbed surfactant ions. The' de-
pendence of the adsorption isotherms on surfactant
concentrationndon pH is interpreted
terms of the
Stem-Grahame model of the electrical double layer.
Acknowledgments. This research was sponsored by
the National Science Foundation. The authors wish
to thank Dr. T. W. Healy of the University of Cali-
fornia, Berkeley, for helpful discussions and Dr. W.
M. Sawyer of the Shell Development Company,
Emeryville, California, for the sample of dodecyl sul-
fonic cid. .
lC1"a
10-- 10-. K)-4 10-S
EQUILIBRIUM CONCENTRATIOff OF SODIUM DODECYL
SULFOffATE. MOLE PER LITER
Figure 4. Comp&riaon f adsorption BOtherma f dodecyl
sulfonate ons on alumina at pH 6.9 and 7.2.
particles are more positive and, hence, there is an in-
crease n adsorption at the lower pH. Greater charge
on the particle at lower pH will need a greater adsorp-
tion density of sulfonate before the r potential is
brought to zero and this can be observed in Figure 4
by the change in adsorption density at the transition
between region 2 and region 3.
Surface Coverage. From surface area.measurements,
aMuming that saturation adsorption of stearic acid
on alumina. corresponds to a' monolayer, maximum
adsorption in Figure 2 approaches a calculated mono-
layer of dodecyl sulfonate on al'1minA. At the lowest
pH value studied (pH 1.98), the ionic strength exceeds
the value used for all the other experiments, that is
2 X 10-8 M. At these low pH values where the sur-
face charge will be high, the amount of sulfonate ad-
sorbed approachesmonolayer coverage.
Data. on adsorption of the sulfonate ions at pH 7.2
show that association of the adsorbed ions begins at a
coverage of about 10-12 mole/cm.S (based on the area
of the sulfonate head) and that zero mobility (the
transition from region 2 to region 3) occurs at about 3 X
M Joumol 01 Pial/tical C1IcmWFV