Ettore Virga1,2, Evan Spruijt3, Wiebe M de Vos1, P M Biesheuvel2. 1. Membrane Science and Technology , University of Twente , Drienerlolaan 5 , 7522 NB Enschede , The Netherlands. 2. Wetsus, European Centre of Excellence for Sustainable Water Technology, Oostergoweg 9 , 8911 MA Leeuwarden , The Netherlands. 3. Institute for Molecules and Materials , Radboud University , Heyendaalseweg 135 , 6525 AJ Nijmegen , The Netherlands.
Abstract
We present a novel theory to predict the contact angle of water on amphoteric surfaces, as a function of pH and ionic strength. To validate our theory, experiments were performed on two commonly used amphoteric materials, alumina (Al2O3) and titania (TiO2). We find good agreement at all pH values, and at different salt concentrations. With increasing salt concentration, the theory predicts the contact angle-pH curve to get steeper, while keeping the same contact angle at pH = PZC (point of zero charge), in agreement with data. Our model is based on the amphoteric 1-p K model and includes the electrostatic free energy of an aqueous system as well as the surface energy of a droplet in contact with the surface. In addition, we show how our theory suggests the possibility of a novel responsive membrane design, based on amphoteric groups. At pH ∼ PZC, this membrane resists flow of water but at slightly more acidic or basic conditions the wettability of the membrane pores may change sufficiently to allow passage of water and solutes. Moreover, these membranes could act as active sensors that only allow solutions of high ionic strength to flow through in wastewater treatment.
We present a novel theory to predict the contact angle of water on amphoteric surfaces, as a function of pH and ionic strength. To validate our theory, experiments were performed on two commonly used amphoteric materials, alumina (Al2O3) and titania (TiO2). We find good agreement at all pH values, and at different salt concentrations. With increasing salt concentration, the theory predicts the contact angle-pH curve to get steeper, while keeping the same contact angle at pH = PZC (point of zero charge), in agreement with data. Our model is based on the amphoteric 1-p K model and includes the electrostatic free energy of an aqueous system as well as the surface energy of a droplet in contact with the surface. In addition, we show how our theory suggests the possibility of a novel responsive membrane design, based on amphoteric groups. At pH ∼ PZC, this membrane resists flow of water but at slightly more acidic or basic conditions the wettability of the membrane pores may change sufficiently to allow passage of water and solutes. Moreover, these membranes could act as active sensors that only allow solutions of high ionic strength to flow through in wastewater treatment.
Surface wettability is of key relevance
in many applications in
daily life[1−3] and industry.[4−6] The wettability of a surface results
from a dynamic equilibrium between interaction forces taking place
at solid–gas, solid–liquid, and gas–liquid interfaces.[1,7] By far the most common liquid involved in this balance is water.
This balance can be shifted in many different ways.[8] For example, by changing pH, surfaces can be switched from
hydrophilic to hydrophobic and back,[9] as
demonstrated by various applications,[10,11] including
new smart membranes with antifouling properties,[12] sponges for oil–water separation[13] and advanced drug delivery systems.[14] The possibility of switching results from weakly basic
or acidic groups, of which the degree of ionization depends on solution
pH.[15,16] Rios et al. exploit these material properties
by developing membranes that are impermeable at neutral and basic
conditions because of their hydrophobicity but are opened to a flux
of aqueous solutions at slightly acidic pH because of protonation
of amino groups, and subsequently wetting of the membrane pores.[17]Within the class of ionizable materials,
amphoteric surfaces are
especially interesting. Amphoteric materials can be both positively
and negatively charged, depending on pH in solution relative to their
point of zero charge (PZC) (see Figure ). The effects of pH and ionic strength on the wettability
of amphoteric surfaces have already been experimentally investigated
for titania (TiO2) surfaces, coated with a thin silane
layer (octadecyltryhydrosilane, OTHS), in a wide range of pH values
around PZC.[18] For unmodified amphoteric
surfaces, the effect of pH on wettability has only been investigated
qualitatively for alumina (Al2O3) in order to
determine PZC.[19] However, the role of the
electrical double layer (EDL) on the wettability of amphoteric surfaces
is not yet fully understood.[18] The salt
concentration influences the diffuse part of the EDL, which in turn
affects the surface charge and thereby the surface wettability. A
quantitative understanding of the impact of the characteristics of
the EDL on the surface energy of amphoteric solids is still missing.
Figure 1
Illustration
of the wettability of amphoteric materials in response
to pH relative to the PZC.
Illustration
of the wettability of amphoteric materials in response
to pH relative to the PZC.In addition to theoretical challenges, earlier experimental
work
may not have chosen the best possible method to measure contact angle.
Indeed, when contact angle (CA) measurements are based on the sessile
drop technique,[20] the effect of a change
in droplet pH during measurements may have been underestimated. Because
when a droplet of water is placed on a solid surface, the ionization
of the surface groups in such a small liquid volume can easily lead
to a change of droplet pH. We advocate to work with the captive bubble
technique, in which small volume effects can safely be neglected,
as water constitutes the continuous phase with a large volume.In this paper, we present a novel theory to predict the contact
angle of water on amphoteric surfaces, as a function of pH and ionic
strength. To validate our theory, we performed experiments on two
commonly used amphoteric materials, alumina (Al2O3) and titania (TiO2).
Theory
In this
section, starting from general expressions for isolated
ionizable surfaces,[21] we derive an equation
that relates the water contact angle to the sum of surface and diffuse
electrostatic free energies. Free energies discussed in this work
have an electrical origin, due to the formation of the EDL, as well
as a chemical origin, due to the adsorption/desorption of protons
and ions to/from the surface. A possible Stern layer[22] is neglected in this work. Our system consists of a liquid
interacting with a solid ionizable surface that is not soluble in
that liquid. Because the Gibbs energy and Helmholtz energy are identical
for a system in which the redistribution of ions (which is required
for the formation of EDLs) does not affect the volume, the general
term free energy is used here. The equations below are derived for
an electrolyte with monovalent ions only. The electrostatic free energy,
scaled with kT, of an aqueous system containing a
ionizable surface is given by[21]where FS and FD are the surface and the diffuse contributions
to the electrostatic free energy.The diffuse contribution for
an isolated surface is given by[23]where n∞ is the salt concentration
expressed in m–3 (n∞ = Navc∞, with c∞ in mol/m3 = mM and Nav Avogadro’s
number), and the Debye length λD is given bywith e as the elementary
charge, ε is the dielectric constant (= εrε0 = 78·8.854 × 10–12 C/(V m) in
water), k is the Boltzmann constant, and T is temperature.In order to calculate Fel, we also
need to know the surface contribution, FS. The expression for FS depends on the
surface chemistry.[21] For an acidic or basic
material, the ionization degree α is a number in between 0 and
1 and is given by[21]where z is the charge sign
of the surface groups (for an acidic site, z = −1,
and for a basic site, z = +1), ys is the dimensionless electrostatic potential at the
surface (= eψs/kT, with ψs as the electrostatic potential at the
surface), and where yN is given by[21]For an acidic/basic material for which
ionization is described
by eq , the surface
part of the free energy, FS, is given
by[21]where N is the number density
of ionizable groups on the surface (m–2). One class
of amphoteric materials consists of a mixture of acidic and basic
surface groups. In that case, the above theory applies with eqs –6 evaluated for each group separately (and added up). This
approach can be applied to various biological materials, such as protein
molecules, the surface of which consists of an assembly of basic and
acidic groups.[24]In the present work,
we focus on a second class of amphoteric materials,
that includes as examples titania and alumina. For these materials,
it is known that they have a fractional charge which goes from a number
below zero, to above. For alumina, applying the 1-pK model, the surface consists of OH–1/2 groups that
can be protonated to OH2+1/2 groups.[25,26] In this case the pK of this material is the pH
at which the surface is globally uncharged. The effective surface
charge, α (), is obtained fromand, as shown in ref (10), the surface contribution
to the free energy in this case isCombining eq and eq , we can now
rewrite eq for this
amphoteric material
toAccording to Hiemstra et al.,[26] titania
is different from alumina, because titania has two ionizable groups,
one that goes from −2/3 to +1/3 in charge, the other from −1/3
to +2/3. However, because the pK value of both groups
can be assumed to be the same, and the number of groups can also be
assumed to be the same,[26] after adding
up these groups we obtain the same equations for α and FS as for alumina (i.e., eqs and 8). Equation was derived in ref (10) but not tested experimentally
before, and this test is one of the objectives of the present work.In order to calculate Fel, the value
of surface potential ys is needed. To
that end, we solve the 1D Poisson–Boltzmann equation for a
planar surface,with the boundary conditionwhere the number
density of charged groups
σ in m–2 is given by σ = αN. For isolated surfaces the solution of eq is well-known to be[27]By solving eq with
an expression for α, such as eq , both ys and α are
obtained.Fel can be seen as an
electrostatic
contribution to the free energy per unit of surface area, or the solid–liquid
surface energy, which has units mN/m when multiplied by kT. From this point onward, we refer to it as the electrostatic contribution
to the surface energy, γel.For smooth surfaces,
the different surface energies are related
to the static contact angle by Young’s equation,where γsl, γsg, and γlg refer to
the surface energy of the solid–liquid,
solid–gas, and liquid–gas interface, respectively. In
particular, we can think of γsl as sum of an electrostatic
term, γel, and a nonelectrostatic term, γslpzc (value of γsl when the material is uncharged, i.e., when pH = PZC)Thus, eq 1 can
be rewritten towhere Δγ = γsg –
γslpzc. The value of γlg, the surface energy
of the water–air (liquid–gas) interface has been fixed
in our study to a value of to γlg = 73 mN/m.[28] The term Δγ is independent of pH
and salt concentration and can be obtained by experimental data fitting.
This means that if the contact angle at the point of zero charge is
known, the model allows us to predict values of contact angle for
every other value of pH and ionic strength. This is correct only if
these parameters (pH and ionic strength) have a reversible effect
on the surface chemistry hence on the dissociation of surface groups.
Materials and Methods
Chemicals
For
preparation of the solutions at different
ionic strength, we used Milli-Q water and NaCl. We added small quantities
of 1 M NaOH or HCl (37%) in order to obtain the desired solution pH.
We tested two materials, alumina and titania, supplied respectively
as sapphire and rutile. Sapphire (1ALO 402E, Al2O3 substrate (0001)) and rutile (1TIO 109E, TiO2 substrate
(100)) were supplied by Crystal GmbH (Berlin, Germany). These substrates
are polished (on one side, R < a0.5 nm) and have dimensions 10 × 10 × 0.5 mm3. To improve the measurement of the contact angle, a customized sample
holder was designed and constructed (PLA, 3D printing, Ultimaker2+, Geldermalsen, The Netherlands) (see Figure ), as discussed next.
Figure 2
Illustration of 3D printed
sample holder (blue) containing a sample
of inorganic material (10 × 10 × 0.5 mm3) (green).
Illustration of 3D printed
sample holder (blue) containing a sample
of inorganic material (10 × 10 × 0.5 mm3) (green).
Contact Angle Measurements
In order to obtain a higher
control on the water solution properties, the static contact angle
was measured using the captive bubble approach. The advantage of this
technique compared to the more common sessile drop method is that
the volume of the surrounding aqueous solution is much larger than
that of a single droplet, and thus pH and salt concentration will
be much more stable. Another important advantage of the captive bubble
method, relatively to the method where a droplet is placed on top
of the material (sessile drop), is that in the captive bubble approach,
the gas phase humidity is well-controlled.The sample surface
was first flushed with ethanol (70%) and then with Milli-Q water before
every measurement. Then, the sample was placed into the 3D printed
sample holder with its polished side facing downward and submerged
in an aqueous solution of predetermined ionic strength and pH. Before
measuring the contact angle, the sample was left in contact with the
solution for at least 5 min and only then we injected a gas bubble
from below, displacing water from part of the surface.The measurements
were performed with an instrument for contact
angle and contour analysis (OCA 35, Dataphysics, Filderstadt, Germany)
used to measure the static contact angle. A clean stainless steel
needle was used to produce a bubble of ∼3 mm in diameter on
the surface, and the bubble contour, measured through the aqueous
phase, was recorded. At least five measurements were taken for every
condition. Image analysis of the shapes of the air bubbles were performed
with the software provided with the instrument by using the method
of Young–Laplace fitting.
Results and Discussion
In this section, we compare our model predictions to experimental
data from literature, and compare to data obtained in our own experiments.
Subsequently, we will discuss more detailed predictions on how amphoteric
surfaces can inspire the design of a responsive membrane that acts
as a sensor for the quality of the water in wastewater treatment plants,
allowing, streams at high ionic strength to flow through and go directly
to appropriate disposal units. In this design the membrane would thus
act as both a sensor and a valve, with the ability to react to a change
in water chemistry automatically and in an autonomic fashion.Our model prediction are compared with experimental data found
in literature[18] for a silanized titania
surface (54% OTHS) and are shown in Figure .
Figure 3
Contact angle of water on a partially silanized
titania wafer in c∞ = 1 mM (A)
and 100 mM (B) KNO3 as a function of pH. Experiments[18] (symbols)
and theory (lines) based on eqs , 7, 9, 12, and.15 Input model parameters: N = 3.0 nm–2,[18] pK = 4.4,[18] Δγ
= 37 mN/m.
Contact angle of water on a partially silanized
titania wafer in c∞ = 1 mM (A)
and 100 mM (B) KNO3 as a function of pH. Experiments[18] (symbols)
and theory (lines) based on eqs , 7, 9, 12, and.15 Input model parameters: N = 3.0 nm–2,[18] pK = 4.4,[18] Δγ
= 37 mN/m.According to our model fit, the
contact angle (CA) has a maximum
for pH = 4.4 (PZC of titania[18]), while
CA decreases when pH moves away from PZC. Indeed, when we move pH
away from PZC, the surface becomes more charged due to the ionization
of surface groups, thus it becomes more hydrophilic. We also observe
that when the salt concentration is increased, from 1 mM (Figure A) to 100 mM (Figure B), the steepness
of the curve of contact angle versus pH increases considerably. This
can be explained by the influence of salt concentration on the Debye
length λ, thus on the EDL thickness.
An increase in ionic strength leads to a reduction in EDL thickness,
which translates into a concentration of H+ or OH– at the surface that is much closer to the one in the bulk. Thus,
for an amphoteric material, if we increase the ionic strength, keeping
the pH constant, the ionization of the surface groups will increase.It is possible to note a plateau at high pH in the experimental
results collected by Hanly et al. (CA∼ 50° in Figure A and CA∼
40° in Figure B). This behavior differs from our predictions at high pH. It can
possibly be explained by looking at the composition of the surfaces
studied by Hanly et al., namely titania partially covered with OTHS
(54%). The hydrophobic interactions due to the silane coverage of
titania are not taken into account in our model and these may be responsible
for the observed plateau at high pH.To validate our model against
data for amphoteric surfaces without
hydrophobic modifications, we collected experimental data for the
CA of two surfaces, titania and alumina, at different values of pH
and ionic strength. Model predictions and experimental data are shown
in Figure for a concentration
of NaCl equal to c∞ = 1 mM. As
can be observed in Figure A, also in this case the contact angle has a maximum for titania
at pH ≅ 4.4, while for alumina, Figure B, the maximum is at pH ≅ 8.7 (PZC
of alumina[19]), and in both cases the contact
angle decreases when the pH moves away from PZC.
Figure 4
Contact angle of water
on titania in c∞ = 1 mM (A) and
100 mM (B), and alumina, in c∞ =
1 mM (C) and 100 mM (D), substrates as a function
of pH. Experiments (circles and diamonds [this work], and triangles
[Cuddy et al.]) and theory (lines). Input model parameters for titania: N = 8.0 nm–2,[18] pK = 4.4,[18] Δγ
= 56 mN/m. Input model parameters for alumina: N =
7.25 nm–2,[29] pK = 8.7,[19] Δγ = 45
mN/m.
Contact angle of water
on titania in c∞ = 1 mM (A) and
100 mM (B), and alumina, in c∞ =
1 mM (C) and 100 mM (D), substrates as a function
of pH. Experiments (circles and diamonds [this work], and triangles
[Cuddy et al.]) and theory (lines). Input model parameters for titania: N = 8.0 nm–2,[18] pK = 4.4,[18] Δγ
= 56 mN/m. Input model parameters for alumina: N =
7.25 nm–2,[29] pK = 8.7,[19] Δγ = 45
mN/m.In Figure B, we
also show data collected by Cuddy et al.[19] (triangles) for alumina. Cuddy et al. used the sessile drop technique
and worked initially with deionized water. Thus, as discussed previously
the exact salt concentration of their aqueous phase (after contacting
the surface) is unknown. Their data overlap with our data (see Figure B) and therefore,
our model calculations, based on c∞ = 1 mM, fit their data well.In our model, for an amphoteric
material the contact angle has
a maximum for a value of pH equal to pK, which is
the point where the surface is on average uncharged (for these materials),
that is, the PZC. When we move pH away from PZC, the surface becomes
more charged due to the ionization of surface groups, thus it becomes
more hydrophilic and CA decreases. Next, in Figure A, we show how water contact angle changes
if both pH and ionic strength are varied. When salt concentration
is increased, the contact angle at the PZC is expected to be unchanged,
in line with literature data reported for titania (see Figure ). Shifting pH away from PZC,
our model predicts that the influence of ionic strength on contact
angle becomes increasingly prominent. One may, indeed, observe an
increased curves steepness when ionic strength is increased. Indeed,
an increase in ionic strength leads to a reduction in EDL thickness,
that translates into a concentration of H+ or OH– at the surface closer to the one in the bulk. Thus, if we increase
ionic strength, keeping pH constant, the ionization of the surface
groups will increase.
Figure 5
Predictions of water contact angle on an intrinsically
hydrophobic
membrane with amphoteric groups as a function of pH and ionic strength.
Input model parameters: N = 8.0 nm–2, pK = 6.5, Δγ = −12 mN/m.
Predictions of water contact angle on an intrinsically
hydrophobic
membrane with amphoteric groups as a function of pH and ionic strength.
Input model parameters: N = 8.0 nm–2, pK = 6.5, Δγ = −12 mN/m.These trends of the dependence
of CA on salt concentration are
confirmed by Hanly et al.[18] and by our
own experiments at 100 mM salinity (see Figure C,D). The experimental data show an increase
in steepness of the curve for CA, if compared to low salt concentration,
such as 1 mM (see Figure ). This is in line with the theory where we can observe a
decrease of the pH region delimited by our theoretical lines.As already mentioned above, our theory shows that if we keep pH
constant and away from PZC, an increase in ionic strength leads to
an increase in surface hydrophilicity (see Figure A). On the basis of that prediction, we can
now think of the possibility of a membrane, where the ionic strength
determines the permeability. These membranes will be analogous to
the ones already developed by Rios et al.[17] but also more versatile. Their modified membranes are dry at neutral
and basic conditions because of their hydrophobicity but open to flux
of aqueous solutions at slightly acidic pH because of the protonation
of amino groups. The same response is expected by switching the ionic
strength at constant pH (away from the PZC). Thus, the corresponding
membranes will perform as ionic strength-dependent switchable valves.
If an intrinsically hydrophobic membrane with amphoteric groups is
employed, it will resist flow of water through the pores of the membrane
at pH ∼ PZC, but at slightly more acidic or basic conditions,
the wettability of the membrane pores may change sufficiently to allow
passage of water and ions. As explained in ref (30), the boundary between
an open and closed configuration is at value of CA = 90° for
ideal surfaces. Indeed, by varying the contact angle (when CA >
90°)
we are able to show in theory that the critical pressure needed to
push the water through a membrane can be varied. But, when CA <
90° we ideally do not need any difference in pressure between
the two sides of the membrane in order to make water pass through
it.[30] Thus, operating below the critical
pressure, it is possible to open and close ideal membrane pores by
shifting the surface from hydrophobic to hydrophilic. These membranes
will be able to work in a much larger range of pH (Figure A), then the membranes described
by Rios et al. Our model predicts that these membranes could possibly
act as active sensors that only allow solutions of high ionic strength
to flow through. This would be especially useful for wastewater treatment,
when the ionic strength and/or pH of the water vary strongly in time.
Streams with a more extreme pH or a high salt concentration would
permeate through the membrane and be treated, while low salinity streams
with moderate pH could simply be disposed. If we look at Figure B, we can see the
effect of salt concentration when pH is kept constant. For pH values
too close to the PZC, such as pH = 6 and pH = 7, this shift from hydrophobic
to hydrophilic is not possible. But when pH is sufficiently far away
from PZC, by changing the ionic strength it becomes possible to switch
the membrane surface from hydrophobic to hydrophilic. This effect
increases when pH is increasingly different from the PZC of the membrane,
that we fixed to PZC = pK = 6.5 in this calculation.
The high contrast between the open and closed states, as well as high
fluxes in the open state because of a large pore size[17] can be useful in different applications for ionic strength/pH
switchable membranes.
Conclusions
This study focused on
the effects of pH and ionic strength on the
wettability of amphoteric metal oxide surfaces. We studied the contact
angle of water on two oxidic (inorganic) materials: alumina (Al2O3) and titania (TiO2). We present a
novel theory that is able to predict the contact angle for these materials
as a function of both ionic strength and pH. This theory is based
on the amphoteric 1-pK model. Experimentally, we
work with the captive bubble technique which gives a better control
over solution and air properties. Data were very well described by
the new theory for the lowest salt concentration tested (1 mM NaCl)
and their trend confirmed also at high salt concentration (100 mM).
For higher salt concentration, the theory predicts the contact angle-pH
curve to get steeper, while keeping the same contact angle at pH =
PZC. Both literature data and our own experiments do show this effect,
thus in line with our theory. Indeed, our theory shows that, if we
keep pH constant, away from PZC, an increase in ionic strength leads
to an increase in hydrophilicity. Thus, if an intrinsically hydrophobic
membrane with amphoteric groups is employed, it will resist the flow
of water through the membrane at pH ∼ PZC but at slightly more
acidic or basic conditions the wettability of the membrane pores may
change sufficiently to allow passage water and ions. These membranes
could also act as valves that only allow solutions of high ionic strength
to flow through. The high contrast between the open and closed states
can be particularly useful for water treatment.
Authors: Wiebe M de Vos; P Maarten Biesheuvel; Arie de Keizer; J Mieke Kleijn; Martien A Cohen Stuart Journal: Langmuir Date: 2008-05-29 Impact factor: 3.882
Authors: Jake W Polster; Fikret Aydin; J Pedro de Souza; Martin Z Bazant; Tuan Anh Pham; Zuzanna S Siwy Journal: J Am Chem Soc Date: 2022-06-21 Impact factor: 16.383